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CHANG, YOON SEOK (장윤석)

Div of Environmental Science & Engineering(환경공학부)

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DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX MEDIATORS:2||WATERS:2||DISPERSION:2||Odor:2||OXIDE NANOPARTICLES:2||DEBROMINATION:2||SILVER NANOPARTICLES:2||Inventory:2||AROCLOR 1254:2||MIXTURE:2||polychlorinated dibenzofurans (PCDFs):2||TITANIUMDIOXIDE:2||MIXTURES:2||DEEP OCEAN:2||SWEDISH HUMANMILK:2||SERUM CONCENTRATIONS:2||Decolorization:2||Nanotoxicity:2||OUTDOOR AIR:2||THERMODYNAMIC PROPERTIES:2||LAURENTIAN GREATLAKES:2||ENVIRONMENTAL APPLICATIONS:2||PHENOLS:2||DIBENZOFURANS:2||FUNGAL LACCASES:2||AREA:2||ISLAND:2||polychlorinated dibenzopdioxins and dibenzofurans:2||ATMOSPHERIC TRANSPORT:2||polychlorinated biphenyl:2||INTERANNUAL VARIABILITY:2||TERRESTRIAL ECOSYSTEMS:2||BIOCONCENTRATION:2||ORGANICSOLVENTS:2||fly ash:2||SAMPLERS:2||SPHINGOMONASWITTICHII RW1:2||ABYSSAL OCEAN:2||MIXEDLAYER:2||carbon emission:2||Stormwater catch basin:2||WATER TREATMENT PLANTS:2||Bacterial viability:1||DLPCBs:1||PCDD/F LEVELS:1||Polybrominated diphenyl ethers (PBDEs):1||Dietary daily intake:1||STABILIZATION:1||INACTIVATION:1||Foods:1||SEAFOOD CONSUMPTION:1||DUST INGESTION:1||HYDROTHERMAL SYNTHESIS:1||laccasemediator system:1||LIGNIN:1||Metabolic intermediates:1||BIOREMEDIATION:1||Porphyrin:1||2,4,6TRICHLOROPHENOL:1||IMPEDANCE SPECTROSCOPY:1||NATURAL ORGANICMATTER:1||INSITU REMEDIATION:1||FATE:1||Acetone:1||nZVI:1||Chromate:1||HEXAVALENT CHROMIUM:1||ASPERGILLUSFUMIGATUS:1||RATIOS:1||MOUNTAINS:1||AREAS:1||PBDE MIXTURE:1||triazines:1||EFFICIENCIES:1||POLLUTANTS:1||POLYPHENOLS:1||,3TRIHYDROXYBIPHENYL:1||PUTIDA GJ31:1||BODY BURDEN:1||FUSION:1||POLYCHLORINATED PHENOLS:1||HAPs:1||animal feed:1||SERUM DIOXIN:1||ATMOSPHERIC PROCESSES:1||model:1||KINASEC ACTIVATION:1||MEMBRANE:1||ADAPTATION:1||degradation:1||FLUORENE:1||season:1||PARTICULATE MATTER:1||GRAMPOSITIVE BACTERIUM:1||PCDD/Fs (polychlorinated dibenzopdioxins and dibenzofurans):1||DGGE (denaturing gradient gel electrophoresis) analysis:1||passive air sampling:1||steel production:1||steel complex:1||RBBR:1||TEXTILE WASTEWATER:1||RISKASSESSMENT:1||TNTCONTAMINATED SOIL:1||onion:1||solute:1||2,4,6TRINITROTOLUENE:1||RHIZOSPHERE:1||RESISTANCE:1||FIRES:1||BOREAL FORESTFIRES:1||airborne particles:1||CONTINUOUS PARTICLE FRACTIONATION:1||polychlorinated dibenzopdioxin/furans:1||environmental monitoring:1||Antimicrobial:1||PERSONAL CARE PRODUCTS:1||AMMONIA:1||CELLPROLIFERATION:1||BLOOD:1||ASSOCIATION:1||Monofluorophenols:1||Isomer fraction:1||Urban source:1||Antimicrobial compound:1||ADSORPTIVE REMOVAL:1||BETACYCLODEXTRIN:1||Freshwater fish:1||WHITEROT FUNGI:1||YUSHO:1||Polychlorinated dibenzopdioxin (PCDD):1||HYDROGENPEROXIDE:1||hexabromocyclododecane:1||risk assessment:1||ETHYL CELLULOSE:1||CYTOTOXICITY:1||CORTICAL MICROTUBULES:1||PHYTOTOXICITY:1||CHILDRENS EXPOSURE:1||Quantitative structureactivity relationship (QSAR):1||Dioxinlike activity:1||Nanoscale zerovalent iron:1||REMEDIATION:1||SERUM:1||COOKING:1||Microbial catabolism:1||Small organic stimulants:1||PCB11:1||LFER model:1||ISOMER PATTERNS:1||2CHLORODIBENZOFURAN:1||Chlorophenols:1||Hydrophobicity:1||PD/FE NANOPARTICLES:1||TAFEL ANALYSIS:1||Polychlorinated biphenyls (PCBs):1||Antarctica:1||Borohydride reduction:1||Nanocomposite:1||FERROUS IRON:1||DENSITY:1||reductive debromination:1||Serum:1||Urban areas:1||NATURAL MEDIATORS:1||SULFIDE:1||dibenzopdioxin:1||CHLORINATED DIBENZOFURANS:1||BACTERIUM:1||fish:1||shellfish:1||TOKYO BAY:1||EQUIVALENCY FACTORS:1||RESPONSES:1||polychlorinated biphenyls (PCBs):1||DIABETESMELLITUS:1||AROCLOR:1||infant feeding:1||NEUROLOGICAL CONDITION:1||protein identification:1||FLUIDIZEDBED INCINERATOR:1||POLYAROMATIC HYDROCARBONS:1||passive air sampler:1||POLYETHYLENE:1||CHLORIDES:1||DAILY MORTALITY:1||DYE DECOLORIZATION:1||KOREAN MUNICIPAL:1||Flue gas treatment system:1||HEALTHRISK:1||HYBRID POPLAR TREES:1||CLIMATE:1||ASSIMILATION:1||BACTERIA:1||TROPOSPHERIC OZONE:1||polychlrorinated dibenzopdioxins:1||serum:1||ORGANICSUBSTANCES:1||PCDD/PCDF LEVELS:1||CHLORONAPHTHALENE CONGENERS:1||CARDIOVASCULARDISEASE:1||CANCER RISK:1||ACTIVATION:1||PARTITIONCOEFFICIENTS:1||RIVER DELTA:1||Redox process:1||Chlorinated flame retardant:1||MARASMIUSQUERCOPHILUS:1||DYNAMICS:1||FRESHFALLEN SNOW:1||Natural phenolic compounds:1||ELECTRICARC FURNACE:1||PORTLANDCEMENT:1||BED:1||WASTE TREATMENT:1||tetrabromobisphenol A:1||concentration (parameters):1||health hazard:1||home:1||NUCLEARWASTE STREAMS:1||MINE WATER:1||SOIL MICROBIAL COMMUNITY:1||Multimedia and multipathway exposure:1||UNITEDSTATES:1||Reactivity:1||AQUIFER:1||BROMINATED FLAMERETARDANTS:1||Northeast Asia:1||Dechlorination:1||Spatial distribution:1||Ironiron oxide:1||CR(VI):1||LIGNIN BIOSYNTHESIS:1||Steel complex:1||Forest fire:1||ATMOSPHERIC BULK DEPOSITION:1||REDUCTIVE DEBROMINATION:1||BIPHENYLS PCBS:1||WOMEN:1||dithionite:1||NANOCOMPOSITE:1||GREEN:1||Pseudomonas veronii PH03:1||DIARYL ETHERS:1||ESCHERICHIACOLI STRAIN:1||REDUCTIVE DEHALOGENASE:1||MICROBIAL BIOMASS:1||2,3,7,8TETRACHLORODIBENZOPDIOXIN:1||INCINERATORS:1||MS/MS:1||SOXHLET EXTRACTION:1||WASTES:1||DICARBOXYLICACIDS:1||Pseudomonas putida:1||DIBENZOTHIOPHENE:1||ABSORPTIONMODEL:1||POLYCHLORINATED NAPHTHALENES:1||ARCTIC AIR:1||PRODUCTS:1||DIBENZOFURAN:1||CONTAMINANTS:1||INDICATOR PARAMETERS:1||ACEASIA:1||indicator:1||ENZYMEPRODUCTION:1||Municipal solid waste incinerator:1||rhizosphere:1||Korean forest:1||sediment:1||PLUMES:1||TIME:1||TOLUENE:1||EMISSION INVENTORY:1||metallurgy industry:1||CARBAZOLEDEGRADER:1||CELL FRACTIONATION:1||size dependent distribution of PCDD/Fs:1||ANTIBACTERIAL ACTIVITY:1||BIOACCUMULATION:1||Ammonia:1||VOCs:1||Aldehydes:1||NORTHCAROLINA:1||FOODCHAIN:1||ORGANOCHLORINE CONTAMINANTS:1||School:1||DELIGNIFICATION:1||MECHANISM:1||Body burden:1||Fentonlike oxidation:1||DENOVO SYNTHESIS:1||Reactive dyes:1||POTENTIAL APPLICATIONS:1||flame retardant:1||Article:1||public indoor environment:1||WATERPURIFICATION:1||VANADIUM:1||GROUNDWATER:1||CATALYST:1||MAGNETIC NANOPARTICLES:1||EFFICIENT REMOVAL:1||Agrobacterium sp PH08:1||Catechol oxidation:1||CELLULAR TOXICITY:1||ZNO:1||INDUSTRIAL:1||Risk assessment:1||Nanoscale zerovalent iron (nZVI):1||ANAEROBIC MICROBIAL DEBROMINATION:1||ISOMERSPECIFIC BIOACCUMULATION:1||HOMEPRODUCED EGGS:1||1,4Dioxane:1||Mycobacterium sp PH06:1||PEROXIDE:1||HOUSEDUST:1||FOODWEB:1||DEGRADING BACTERIA:1||Longrange transport:1||FE/FES NANOPARTICLES:1||oxidative coupling:1||Carbazole:1||2,2,3TRIHYDROXYBIPHENYL DIOXYGENASE:1||Star block copolymer:1||4CHLOROPHENOL:1||DIOXINLIKE PCBS:1||2,3,7,8TeCDD:1||Reduction:1||Nanobio redox process:1||Hybrid treatment:1||CUTICLE SCLEROTIZATION:1||DIETARY EXPOSURE:1||Nanobio hybrid:1||nanoscale zero valent iron (nZVI):1||PH07:1||Laccasemediator system:1||ARCTIC ATMOSPHERE:1||zerovalent iron:1||fioxins:1||edible frogs:1||blood:1||CLASSIFICATION:1||2,4,5TRICHLOROPHENOXYACETIC ACID:1||PCPA:1||adsorption:1||distribution:1||THYROIDHORMONE STATUS:1||POSTNATAL EXPOSURE:1||ADIPOSETISSUE:1||sequencing:1||SP STRAIN HH69:1||PDIOXIN:1||homologue:1||WASTE COMBUSTION:1||GINSENG:1||209 PCB CONGENERS:1||bioremediation of dioxins:1||BASIDIOMYCETE PHANEROCHAETECHRYSOSPORIUM:1||MOUSE:1||MECOP:1||HCB:1||Asian dust:1||AIR PARTITIONCOEFFICIENT:1||ENVIRONMENTALIMPACT:1||ORGANICCARBON:1||PROTEIN:1||CHLORODIBENZOPDIOXINS:1||SURFACTANT:1||pinched inlet GSF:1||METALS:1||PSEUDOMONASPUTIDA:1||Malodor:1||REDUCED SULFURCOMPOUNDS:1||MSWI:1||CATECHOL:1||LACCASE:1||Floor dust:1||WATERTREATMENT:1||CONSTANTS:1||Natural redox mediator:1||GOLD(III) IONS:1||Human exposures:1||RAYABSORPTION SPECTROSCOPY:1||CHEMISTRY:1||TUNICATE:1||ASSISTED CHEMICALSEPARATION:1||DRINKINGWATER:1||NITRICACID:1||VERTICAL PROFILE:1||HYDROXYL RADICALS:1||PLANTGROWTH:1||NEONATAL EXPOSURE:1||Foodstuffs:1||FEPD NANOPARTICLES:1||CHEMICALBIOLOGICAL TREATMENT:1||ENDOSULFAN:1||USAGE:1||magnetic separation:1||recyclable adsorbent:1||CD(II):1||in vivo metabolism:1||GREEN CHEMISTRY:1||PULP:1||OCDD:1||WATER SAMPLES:1||GENECLUSTER:1||Toxicity:1||SYSTEM:1||COPLANAR PCBS:1||Bimetallic nanoparticles:1||Surface snow:1||CELLWALL:1||PAPER PULP:1||Biomass burning:1||ACTIVATEDSLUDGE SYSTEMS:1||SOURCE IDENTIFICATION:1||IRA743 resin bulk sampler:1||TAIWAN:1||OCPs:1||Ganoderma lucidum laccase:1||PLEUROTUSERYNGII:1||COLORATION:1||chlorodibenzopdioxins:1||FORESTFIRE:1||Masan Bay:1||HRGC/HRMS:1||maternal body burden:1||SOURCE DECAY:1||PEPTIDE:1||COEFFICIENT:1||very long chain bifunctional fatty acyl component:1||DIOXYGENASE:1||environmental level:1||REFUSE INCINERATION:1||FABRIC FILTER:1||COMBUSTION CONDITIONS:1||TRANSECT:1||GENETICALLYENGINEERED MICROORGANISMS:1||TERMINAL OXYGENASE COMPONENT:1||incinerator fly ash:1||plastic:1||IRONOXIDE CATALYST:1||bulk:1||PLANT:1||fine particle:1||NEWBEDFORD HARBOR:1||carbon monoxide:1||RETRIEVAL ALGORITHM:1||emission factors:1||WASTE:1||NATIONALHEALTH:1||NONDIABETIC ADULTS:1||HEALTHRISKS:1||4Fluorophenol:1||RHODOCOCCUSOPACUS:1||Pd/nFe:1||METALIONS:1||Fish:1||MAJOR UK CONURBATION:1||INDOOR AIR:1||ENDOCRINE DISRUPTING CHEMICALS:1||FUNGUS CORIOLOPSISPOLYZONA:1||DIPHENYL ETHER:1||2NDSPHERE COORDINATION:1||WHEAT BRAN:1||ELECTRONTRANSFER:1||TBBPA:1||dust:1||office:1||SIZE:1||CINCA RIVER:1||TIO2 NANOPARTICLES:1||COPPER NANOPARTICLES:1||Time trend:1||Elementary school student:1||ADULT MICE:1||TRANSITIONMETALS:1||Alginate bead:1||Oxygen release:1||Bioremediation:1||HEXACHLOROBENZENE:1||iron oxide nanoparticles:1||DIOXIDE:1||laccases:1||DIVERSITY:1||Incinerator:1||Indicator congener:1||COALTAR CREOSOTE:1||CA10:1||NHANES:1||CRYPTOCOCCUSNEOFORMANS:1||MEDIATED OXIDATION:1||General population:1||Deposition:1||Soil:1||Reductive dechlorination:1||Sphingomonas sp:1||FORMULATIONS:1||Steel complexes:1||EXTRACTION:1||SUPERCRITICALFLUID EXTRACTION:1||SOXHLET:1||HEALTH:1||LIGNIN MODELCOMPOUND:1||PHENOLICCOMPOUNDS:1||multicomponent nanoparticles:1||MAGNETICPROPERTIES:1||DITHIONITE:1||PHENYLENEDIAMINE:1||edible freshwater fish:1||ISOMERSPECIFIC DETERMINATION:1||daily intake:1||OPERATION RANCH HAND:1||HUMANMILK:1||DICHLORODIPHENYL DICHLOROETHENE DDE:1||RINGCLEAVAGE:1||DIBENZOPARADIOXINS:1||MSW INCINERATORS:1||URBAN AIR:1||NORTHAMERICAN ATMOSPHERE:1||microbial biocatalysts:1||diphenyl ether:1||Sphingomonas sp.:1||MASSSPECTROMETRY:1||dioxinlike PCBs:1||TRAMETESHIRSUTA:1||response surface methodology:1||Human health:1||DEPOSITION:1||BIOLOGICAL TREATMENT:1||ASH:1||GROWTH:1||carbon flux:1||ESI/LCMS:1||SATELLITE DATA:1||CO:1||biological removal:1||DEGRADING BACTERIUM:1||METHYLTRICLOSAN:1||RSCs:1||QUANTIFICATION:1||NONHODGKINSLYMPHOMA:1||Diabetes:1||Pseudonocardia benzenivorans:1||BACTERIALDEGRADATION:1||WASTEWATER TREATMENT:1||OXIDATIVE TRANSFORMATION:1||ONTARIO:1||SHIHWA:1||OTTAWA:1||GREATLAKES:1||MANGANESE PEROXIDASE:1||Natural organic coagulants:1||Grape seed extract:1||Syringaldehyde:1||AQUEOUSSOLUTIONS:1||GREEN RECOVERY:1||AUSTRALIA:1||Incinerator workers:1||Steel dust:1||Industrial wastes:1||MECHANISMS:1||Chemical contamination:1||Flame retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM ALGINATE:1||TDS:1||Dietary exposure:1||Zerovalent irons:1||Dechlorane plus:1||Polychlorinated biphenyls:1||Passive air sampling:1||manganese oxides:1||heavy metal ions:1||ADSORBENT:1||SYNTHETIC APPLICATIONS:1||Zinc Nanoparticles:1||PCDD/F FORMATION:1||Biotransformation:1||INCINERATOR FLYASH:1||Photocatalytic degradation:1||ENVIRONMENTAL CONCERN:1||Health risk:1||WET DEPOSITION:1||UASB REACTOR:1||Bulk deposition:1||PROFILES:1||CATALYZED OXIDATIVE POLYMERIZATION:1||CAPILLARYZONEELECTROPHORESIS:1||NATURALWATERS:1||PEPTIDES:1||ENVIRONMENTALSAMPLES:1||Pentachlorophenol:1||ELECTRONTRANSFERREACTIONS:1||TCE:1||2,2&apos:1||ANGULAR DIOXYGENATION:1||JAPANESE:1||cancer risk:1||polychlorinated dibenzopdioxins polychlorinated biphenyls:1||DIBENZOPDIOXIN:1||GENES:1||RHODOCOCCUSCHLOROPHENOLICUS:1||CEPACIA:1||PH01:1||industrial waste incinerator:1||oxidative stress:1||OCCUPATIONALEXPOSURE:1||VETERANS:1||HUMANS:1||AEROSOLS:1||VAPORPRESSURE:1||TEMPERATURE:1||STRESS:1||DENOVOSYNTHESIS:1||PARAMETERS:1||SAPONINS:1||AIRBORNE PARTICLES:1||TRENDS:1||bioremediation:1||CHLORINATED ETHENES:1||ORGANIC CONTAMINANTS:1||UK BACKGROUND AIR:1||SINTERING PLANTS:1||TSP:1||SIZE DISTRIBUTION:1||white rot fungus:1||dye decolorization:1||congenerspecific analysis:1||NUTRIENT TRANSPORT:1||human bloods:1||PLASMA:1||heavy metals:1||BIVALVES:1||isotope effect:1||GCMS:1||biomass burning:1||TRANSPORT:1||JAPAN:1||size dependent distribution of dioxin:1||gravitational SPLITT fractionation:1||marine sediment:1||INTERNAL EXPOSURE:1||CONSTRUCTION:1||PCN:1||CHLORINATED NAPHTHALENES:1||DYSFUNCTION:1||DDE:1||ENDOCRINEDISRUPTING CHEMICALS:1||SURFACE WATERS:1||Dechlorane Plus:1||Surface dust:1||INDUSTRIALAREA:1||Natural polyphenols:1||MALACHITE GREEN:1||MORINGAOLEIFERA:1||FLAVONOIDS:1||ALUMINUM:1||MT. QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX MEDIATORS:2||WATERS:2||DISPERSION:2||Odor:2||OXIDE NANOPARTICLES:2||DEBROMINATION:2||SILVER NANOPARTICLES:2||Inventory:2||AROCLOR 1254:2||MIXTURE:2||polychlorinated dibenzofurans (PCDFs):2||TITANIUMDIOXIDE:2||MIXTURES:2||DEEP OCEAN:2||SWEDISH HUMANMILK:2||SERUM CONCENTRATIONS:2||Decolorization:2||Nanotoxicity:2||OUTDOOR AIR:2||THERMODYNAMIC PROPERTIES:2||LAURENTIAN GREATLAKES:2||ENVIRONMENTAL APPLICATIONS:2||PHENOLS:2||DIBENZOFURANS:2||FUNGAL LACCASES:2||AREA:2||ISLAND:2||polychlorinated dibenzopdioxins and dibenzofurans:2||ATMOSPHERIC TRANSPORT:2||polychlorinated biphenyl:2||INTERANNUAL VARIABILITY:2||TERRESTRIAL ECOSYSTEMS:2||BIOCONCENTRATION:2||ORGANICSOLVENTS:2||fly ash:2||SAMPLERS:2||SPHINGOMONASWITTICHII RW1:2||ABYSSAL OCEAN:2||MIXEDLAYER:2||carbon emission:2||Stormwater catch basin:2||WATER TREATMENT PLANTS:2||Bacterial viability:1||DLPCBs:1||PCDD/F LEVELS:1||Polybrominated diphenyl ethers (PBDEs):1||Dietary daily intake:1||STABILIZATION:1||INACTIVATION:1||Foods:1||SEAFOOD CONSUMPTION:1||DUST INGESTION:1||HYDROTHERMAL SYNTHESIS:1||laccasemediator system:1||LIGNIN:1||Metabolic intermediates:1||BIOREMEDIATION:1||Porphyrin:1||2,4,6TRICHLOROPHENOL:1||IMPEDANCE SPECTROSCOPY:1||NATURAL ORGANICMATTER:1||INSITU REMEDIATION:1||FATE:1||Acetone:1||nZVI:1||Chromate:1||HEXAVALENT CHROMIUM:1||ASPERGILLUSFUMIGATUS:1||RATIOS:1||MOUNTAINS:1||AREAS:1||PBDE MIXTURE:1||triazines:1||EFFICIENCIES:1||POLLUTANTS:1||POLYPHENOLS:1||,3TRIHYDROXYBIPHENYL:1||PUTIDA GJ31:1||BODY BURDEN:1||FUSION:1||POLYCHLORINATED PHENOLS:1||HAPs:1||animal feed:1||SERUM DIOXIN:1||ATMOSPHERIC PROCESSES:1||model:1||KINASEC ACTIVATION:1||MEMBRANE:1||ADAPTATION:1||degradation:1||FLUORENE:1||season:1||PARTICULATE MATTER:1||GRAMPOSITIVE BACTERIUM:1||PCDD/Fs (polychlorinated dibenzopdioxins and dibenzofurans):1||DGGE (denaturing gradient gel electrophoresis) analysis:1||passive air sampling:1||steel production:1||steel complex:1||RBBR:1||TEXTILE WASTEWATER:1||RISKASSESSMENT:1||TNTCONTAMINATED SOIL:1||onion:1||solute:1||2,4,6TRINITROTOLUENE:1||RHIZOSPHERE:1||RESISTANCE:1||FIRES:1||BOREAL FORESTFIRES:1||airborne particles:1||CONTINUOUS PARTICLE FRACTIONATION:1||polychlorinated dibenzopdioxin/furans:1||environmental monitoring:1||Antimicrobial:1||PERSONAL CARE PRODUCTS:1||AMMONIA:1||CELLPROLIFERATION:1||BLOOD:1||ASSOCIATION:1||Monofluorophenols:1||Isomer fraction:1||Urban source:1||Antimicrobial compound:1||ADSORPTIVE REMOVAL:1||BETACYCLODEXTRIN:1||Freshwater fish:1||WHITEROT FUNGI:1||YUSHO:1||Polychlorinated dibenzopdioxin (PCDD):1||HYDROGENPEROXIDE:1||hexabromocyclododecane:1||risk assessment:1||ETHYL CELLULOSE:1||CYTOTOXICITY:1||CORTICAL MICROTUBULES:1||PHYTOTOXICITY:1||CHILDRENS EXPOSURE:1||Quantitative structureactivity relationship (QSAR):1||Dioxinlike activity:1||Nanoscale zerovalent iron:1||REMEDIATION:1||SERUM:1||COOKING:1||Microbial catabolism:1||Small organic stimulants:1||PCB11:1||LFER model:1||ISOMER 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intake:1||OPERATION RANCH HAND:1||HUMANMILK:1||DICHLORODIPHENYL DICHLOROETHENE DDE:1||RINGCLEAVAGE:1||DIBENZOPARADIOXINS:1||MSW INCINERATORS:1||URBAN AIR:1||NORTHAMERICAN ATMOSPHERE:1||microbial biocatalysts:1||diphenyl ether:1||Sphingomonas sp.:1||MASSSPECTROMETRY:1||dioxinlike PCBs:1||TRAMETESHIRSUTA:1||response surface methodology:1||Human health:1||DEPOSITION:1||BIOLOGICAL TREATMENT:1||ASH:1||GROWTH:1||carbon flux:1||ESI/LCMS:1||SATELLITE DATA:1||CO:1||biological removal:1||DEGRADING BACTERIUM:1||METHYLTRICLOSAN:1||RSCs:1||QUANTIFICATION:1||NONHODGKINSLYMPHOMA:1||Diabetes:1||Pseudonocardia benzenivorans:1||BACTERIALDEGRADATION:1||WASTEWATER TREATMENT:1||OXIDATIVE TRANSFORMATION:1||ONTARIO:1||SHIHWA:1||OTTAWA:1||GREATLAKES:1||MANGANESE PEROXIDASE:1||Natural organic coagulants:1||Grape seed extract:1||Syringaldehyde:1||AQUEOUSSOLUTIONS:1||GREEN RECOVERY:1||AUSTRALIA:1||Incinerator workers:1||Steel dust:1||Industrial wastes:1||MECHANISMS:1||Chemical contamination:1||Flame retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM ALGINATE:1||TDS:1||Dietary exposure:1||Zerovalent irons:1||Dechlorane plus:1||Polychlorinated biphenyls:1||Passive air sampling:1||manganese oxides:1||heavy metal ions:1||ADSORBENT:1||SYNTHETIC APPLICATIONS:1||Zinc Nanoparticles:1||PCDD/F FORMATION:1||Biotransformation:1||INCINERATOR FLYASH:1||Photocatalytic degradation:1||ENVIRONMENTAL CONCERN:1||Health risk:1||WET DEPOSITION:1||UASB REACTOR:1||Bulk deposition:1||PROFILES:1||CATALYZED OXIDATIVE POLYMERIZATION:1||CAPILLARYZONEELECTROPHORESIS:1||NATURALWATERS:1||PEPTIDES:1||ENVIRONMENTALSAMPLES:1||Pentachlorophenol:1||ELECTRONTRANSFERREACTIONS:1||TCE:1||2,2&apos:1||ANGULAR DIOXYGENATION:1||JAPANESE:1||cancer risk:1||polychlorinated dibenzopdioxins polychlorinated biphenyls:1||DIBENZOPDIOXIN:1||GENES:1||RHODOCOCCUSCHLOROPHENOLICUS:1||CEPACIA:1||PH01:1||industrial waste incinerator:1||oxidative stress:1||OCCUPATIONALEXPOSURE:1||VETERANS:1||HUMANS:1||AEROSOLS:1||VAPORPRESSURE:1||TEMPERATURE:1||STRESS:1||DENOVOSYNTHESIS:1||PARAMETERS:1||SAPONINS:1||AIRBORNE PARTICLES:1||TRENDS:1||bioremediation:1||CHLORINATED ETHENES:1||ORGANIC CONTAMINANTS:1||UK BACKGROUND AIR:1||SINTERING PLANTS:1||TSP:1||SIZE DISTRIBUTION:1||white rot fungus:1||dye decolorization:1||congenerspecific analysis:1||NUTRIENT TRANSPORT:1||human bloods:1||PLASMA:1||heavy metals:1||BIVALVES:1||isotope effect:1||GCMS:1||biomass burning:1||TRANSPORT:1||JAPAN:1||size dependent distribution of dioxin:1||gravitational SPLITT fractionation:1||marine sediment:1||INTERNAL EXPOSURE:1||CONSTRUCTION:1||PCN:1||CHLORINATED NAPHTHALENES:1||DYSFUNCTION:1||DDE:1||ENDOCRINEDISRUPTING CHEMICALS:1||SURFACE WATERS:1||Dechlorane Plus:1||Surface dust:1||INDUSTRIALAREA:1||Natural polyphenols:1||MALACHITE GREEN:1||MORINGAOLEIFERA:1||FLAVONOIDS:1||ALUMINUM:1||MT. QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX MEDIATORS:2||WATERS:2||DISPERSION:2||Odor:2||OXIDE NANOPARTICLES:2||DEBROMINATION:2||SILVER NANOPARTICLES:2||Inventory:2||AROCLOR 1254:2||MIXTURE:2||polychlorinated dibenzofurans (PCDFs):2||TITANIUMDIOXIDE:2||MIXTURES:2||DEEP OCEAN:2||SWEDISH HUMANMILK:2||SERUM CONCENTRATIONS:2||Decolorization:2||Nanotoxicity:2||OUTDOOR AIR:2||THERMODYNAMIC PROPERTIES:2||LAURENTIAN GREATLAKES:2||ENVIRONMENTAL APPLICATIONS:2||PHENOLS:2||DIBENZOFURANS:2||FUNGAL LACCASES:2||AREA:2||ISLAND:2||polychlorinated dibenzopdioxins and dibenzofurans:2||ATMOSPHERIC TRANSPORT:2||polychlorinated biphenyl:2||INTERANNUAL VARIABILITY:2||TERRESTRIAL ECOSYSTEMS:2||BIOCONCENTRATION:2||ORGANICSOLVENTS:2||fly ash:2||SAMPLERS:2||SPHINGOMONASWITTICHII RW1:2||ABYSSAL OCEAN:2||MIXEDLAYER:2||carbon emission:2||Stormwater catch basin:2||WATER TREATMENT PLANTS:2||Bacterial viability:1||DLPCBs:1||PCDD/F LEVELS:1||Polybrominated diphenyl ethers (PBDEs):1||Dietary daily intake:1||STABILIZATION:1||INACTIVATION:1||Foods:1||SEAFOOD CONSUMPTION:1||DUST INGESTION:1||HYDROTHERMAL SYNTHESIS:1||laccasemediator system:1||LIGNIN:1||Metabolic intermediates:1||BIOREMEDIATION:1||Porphyrin:1||2,4,6TRICHLOROPHENOL:1||IMPEDANCE SPECTROSCOPY:1||NATURAL ORGANICMATTER:1||INSITU REMEDIATION:1||FATE:1||Acetone:1||nZVI:1||Chromate:1||HEXAVALENT CHROMIUM:1||ASPERGILLUSFUMIGATUS:1||RATIOS:1||MOUNTAINS:1||AREAS:1||PBDE MIXTURE:1||triazines:1||EFFICIENCIES:1||POLLUTANTS:1||POLYPHENOLS:1||,3TRIHYDROXYBIPHENYL:1||PUTIDA GJ31:1||BODY BURDEN:1||FUSION:1||POLYCHLORINATED PHENOLS:1||HAPs:1||animal feed:1||SERUM DIOXIN:1||ATMOSPHERIC PROCESSES:1||model:1||KINASEC ACTIVATION:1||MEMBRANE:1||ADAPTATION:1||degradation:1||FLUORENE:1||season:1||PARTICULATE MATTER:1||GRAMPOSITIVE BACTERIUM:1||PCDD/Fs (polychlorinated dibenzopdioxins and dibenzofurans):1||DGGE (denaturing gradient gel electrophoresis) analysis:1||passive air sampling:1||steel production:1||steel complex:1||RBBR:1||TEXTILE WASTEWATER:1||RISKASSESSMENT:1||TNTCONTAMINATED 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SAMPLES:1||GENECLUSTER:1||Toxicity:1||SYSTEM:1||COPLANAR PCBS:1||Bimetallic nanoparticles:1||Surface snow:1||CELLWALL:1||PAPER PULP:1||Biomass burning:1||ACTIVATEDSLUDGE SYSTEMS:1||SOURCE IDENTIFICATION:1||IRA743 resin bulk sampler:1||TAIWAN:1||OCPs:1||Ganoderma lucidum laccase:1||PLEUROTUSERYNGII:1||COLORATION:1||chlorodibenzopdioxins:1||FORESTFIRE:1||Masan Bay:1||HRGC/HRMS:1||maternal body burden:1||SOURCE DECAY:1||PEPTIDE:1||COEFFICIENT:1||very long chain bifunctional fatty acyl component:1||DIOXYGENASE:1||environmental level:1||REFUSE INCINERATION:1||FABRIC FILTER:1||COMBUSTION CONDITIONS:1||TRANSECT:1||GENETICALLYENGINEERED MICROORGANISMS:1||TERMINAL OXYGENASE COMPONENT:1||incinerator fly ash:1||plastic:1||IRONOXIDE CATALYST:1||bulk:1||PLANT:1||fine particle:1||NEWBEDFORD HARBOR:1||carbon monoxide:1||RETRIEVAL ALGORITHM:1||emission factors:1||WASTE:1||NATIONALHEALTH:1||NONDIABETIC ADULTS:1||HEALTHRISKS:1||4Fluorophenol:1||RHODOCOCCUSOPACUS:1||Pd/nFe:1||METALIONS:1||Fish:1||MAJOR UK CONURBATION:1||INDOOR AIR:1||ENDOCRINE DISRUPTING CHEMICALS:1||FUNGUS CORIOLOPSISPOLYZONA:1||DIPHENYL ETHER:1||2NDSPHERE COORDINATION:1||WHEAT BRAN:1||ELECTRONTRANSFER:1||TBBPA:1||dust:1||office:1||SIZE:1||CINCA RIVER:1||TIO2 NANOPARTICLES:1||COPPER NANOPARTICLES:1||Time trend:1||Elementary school student:1||ADULT MICE:1||TRANSITIONMETALS:1||Alginate bead:1||Oxygen release:1||Bioremediation:1||HEXACHLOROBENZENE:1||iron oxide nanoparticles:1||DIOXIDE:1||laccases:1||DIVERSITY:1||Incinerator:1||Indicator congener:1||COALTAR CREOSOTE:1||CA10:1||NHANES:1||CRYPTOCOCCUSNEOFORMANS:1||MEDIATED OXIDATION:1||General population:1||Deposition:1||Soil:1||Reductive dechlorination:1||Sphingomonas sp:1||FORMULATIONS:1||Steel complexes:1||EXTRACTION:1||SUPERCRITICALFLUID EXTRACTION:1||SOXHLET:1||HEALTH:1||LIGNIN MODELCOMPOUND:1||PHENOLICCOMPOUNDS:1||multicomponent nanoparticles:1||MAGNETICPROPERTIES:1||DITHIONITE:1||PHENYLENEDIAMINE:1||edible freshwater fish:1||ISOMERSPECIFIC DETERMINATION:1||daily intake:1||OPERATION RANCH HAND:1||HUMANMILK:1||DICHLORODIPHENYL DICHLOROETHENE DDE:1||RINGCLEAVAGE:1||DIBENZOPARADIOXINS:1||MSW INCINERATORS:1||URBAN AIR:1||NORTHAMERICAN ATMOSPHERE:1||microbial biocatalysts:1||diphenyl ether:1||Sphingomonas sp.:1||MASSSPECTROMETRY:1||dioxinlike PCBs:1||TRAMETESHIRSUTA:1||response surface methodology:1||Human health:1||DEPOSITION:1||BIOLOGICAL TREATMENT:1||ASH:1||GROWTH:1||carbon flux:1||ESI/LCMS:1||SATELLITE DATA:1||CO:1||biological removal:1||DEGRADING BACTERIUM:1||METHYLTRICLOSAN:1||RSCs:1||QUANTIFICATION:1||NONHODGKINSLYMPHOMA:1||Diabetes:1||Pseudonocardia benzenivorans:1||BACTERIALDEGRADATION:1||WASTEWATER TREATMENT:1||OXIDATIVE TRANSFORMATION:1||ONTARIO:1||SHIHWA:1||OTTAWA:1||GREATLAKES:1||MANGANESE PEROXIDASE:1||Natural organic coagulants:1||Grape seed extract:1||Syringaldehyde:1||AQUEOUSSOLUTIONS:1||GREEN RECOVERY:1||AUSTRALIA:1||Incinerator workers:1||Steel dust:1||Industrial wastes:1||MECHANISMS:1||Chemical contamination:1||Flame retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM ALGINATE:1||TDS:1||Dietary exposure:1||Zerovalent irons:1||Dechlorane plus:1||Polychlorinated biphenyls:1||Passive air sampling:1||manganese oxides:1||heavy metal ions:1||ADSORBENT:1||SYNTHETIC APPLICATIONS:1||Zinc Nanoparticles:1||PCDD/F FORMATION:1||Biotransformation:1||INCINERATOR FLYASH:1||Photocatalytic degradation:1||ENVIRONMENTAL CONCERN:1||Health risk:1||WET DEPOSITION:1||UASB REACTOR:1||Bulk deposition:1||PROFILES:1||CATALYZED OXIDATIVE POLYMERIZATION:1||CAPILLARYZONEELECTROPHORESIS:1||NATURALWATERS:1||PEPTIDES:1||ENVIRONMENTALSAMPLES:1||Pentachlorophenol:1||ELECTRONTRANSFERREACTIONS:1||TCE:1||2,2&apos:1||ANGULAR DIOXYGENATION:1||JAPANESE:1||cancer risk:1||polychlorinated dibenzopdioxins polychlorinated biphenyls:1||DIBENZOPDIOXIN:1||GENES:1||RHODOCOCCUSCHLOROPHENOLICUS:1||CEPACIA:1||PH01:1||industrial waste incinerator:1||oxidative stress:1||OCCUPATIONALEXPOSURE:1||VETERANS:1||HUMANS:1||AEROSOLS:1||VAPORPRESSURE:1||TEMPERATURE:1||STRESS:1||DENOVOSYNTHESIS:1||PARAMETERS:1||SAPONINS:1||AIRBORNE PARTICLES:1||TRENDS:1||bioremediation:1||CHLORINATED ETHENES:1||ORGANIC CONTAMINANTS:1||UK BACKGROUND AIR:1||SINTERING PLANTS:1||TSP:1||SIZE DISTRIBUTION:1||white rot fungus:1||dye decolorization:1||congenerspecific analysis:1||NUTRIENT TRANSPORT:1||human bloods:1||PLASMA:1||heavy metals:1||BIVALVES:1||isotope effect:1||GCMS:1||biomass burning:1||TRANSPORT:1||JAPAN:1||size dependent distribution of dioxin:1||gravitational SPLITT fractionation:1||marine sediment:1||INTERNAL EXPOSURE:1||CONSTRUCTION:1||PCN:1||CHLORINATED NAPHTHALENES:1||DYSFUNCTION:1||DDE:1||ENDOCRINEDISRUPTING CHEMICALS:1||SURFACE WATERS:1||Dechlorane Plus:1||Surface dust:1||INDUSTRIALAREA:1||Natural polyphenols:1||MALACHITE GREEN:1||MORINGAOLEIFERA:1||FLAVONOIDS:1||ALUMINUM:1||MT. QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX 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retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM 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QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE 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QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX MEDIATORS:2||WATERS:2||DISPERSION:2||Odor:2||OXIDE NANOPARTICLES:2||DEBROMINATION:2||SILVER NANOPARTICLES:2||Inventory:2||AROCLOR 1254:2||MIXTURE:2||polychlorinated dibenzofurans (PCDFs):2||TITANIUMDIOXIDE:2||MIXTURES:2||DEEP OCEAN:2||SWEDISH HUMANMILK:2||SERUM CONCENTRATIONS:2||Decolorization:2||Nanotoxicity:2||OUTDOOR AIR:2||THERMODYNAMIC PROPERTIES:2||LAURENTIAN GREATLAKES:2||ENVIRONMENTAL APPLICATIONS:2||PHENOLS:2||DIBENZOFURANS:2||FUNGAL LACCASES:2||AREA:2||ISLAND:2||polychlorinated dibenzopdioxins and dibenzofurans:2||ATMOSPHERIC TRANSPORT:2||polychlorinated biphenyl:2||INTERANNUAL VARIABILITY:2||TERRESTRIAL ECOSYSTEMS:2||BIOCONCENTRATION:2||ORGANICSOLVENTS:2||fly ash:2||SAMPLERS:2||SPHINGOMONASWITTICHII RW1:2||ABYSSAL OCEAN:2||MIXEDLAYER:2||carbon emission:2||Stormwater catch basin:2||WATER TREATMENT PLANTS:2||Bacterial viability:1||DLPCBs:1||PCDD/F LEVELS:1||Polybrominated diphenyl ethers (PBDEs):1||Dietary daily intake:1||STABILIZATION:1||INACTIVATION:1||Foods:1||SEAFOOD 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intake:1||OPERATION RANCH HAND:1||HUMANMILK:1||DICHLORODIPHENYL DICHLOROETHENE DDE:1||RINGCLEAVAGE:1||DIBENZOPARADIOXINS:1||MSW INCINERATORS:1||URBAN AIR:1||NORTHAMERICAN ATMOSPHERE:1||microbial biocatalysts:1||diphenyl ether:1||Sphingomonas sp.:1||MASSSPECTROMETRY:1||dioxinlike PCBs:1||TRAMETESHIRSUTA:1||response surface methodology:1||Human health:1||DEPOSITION:1||BIOLOGICAL TREATMENT:1||ASH:1||GROWTH:1||carbon flux:1||ESI/LCMS:1||SATELLITE DATA:1||CO:1||biological removal:1||DEGRADING BACTERIUM:1||METHYLTRICLOSAN:1||RSCs:1||QUANTIFICATION:1||NONHODGKINSLYMPHOMA:1||Diabetes:1||Pseudonocardia benzenivorans:1||BACTERIALDEGRADATION:1||WASTEWATER TREATMENT:1||OXIDATIVE TRANSFORMATION:1||ONTARIO:1||SHIHWA:1||OTTAWA:1||GREATLAKES:1||MANGANESE PEROXIDASE:1||Natural organic coagulants:1||Grape seed extract:1||Syringaldehyde:1||AQUEOUSSOLUTIONS:1||GREEN RECOVERY:1||AUSTRALIA:1||Incinerator workers:1||Steel dust:1||Industrial wastes:1||MECHANISMS:1||Chemical contamination:1||Flame retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM ALGINATE:1||TDS:1||Dietary exposure:1||Zerovalent irons:1||Dechlorane plus:1||Polychlorinated biphenyls:1||Passive air sampling:1||manganese oxides:1||heavy metal ions:1||ADSORBENT:1||SYNTHETIC APPLICATIONS:1||Zinc Nanoparticles:1||PCDD/F FORMATION:1||Biotransformation:1||INCINERATOR FLYASH:1||Photocatalytic degradation:1||ENVIRONMENTAL CONCERN:1||Health risk:1||WET DEPOSITION:1||UASB REACTOR:1||Bulk deposition:1||PROFILES:1||CATALYZED OXIDATIVE POLYMERIZATION:1||CAPILLARYZONEELECTROPHORESIS:1||NATURALWATERS:1||PEPTIDES:1||ENVIRONMENTALSAMPLES:1||Pentachlorophenol:1||ELECTRONTRANSFERREACTIONS:1||TCE:1||2,2&apos:1||ANGULAR DIOXYGENATION:1||JAPANESE:1||cancer risk:1||polychlorinated dibenzopdioxins polychlorinated biphenyls:1||DIBENZOPDIOXIN:1||GENES:1||RHODOCOCCUSCHLOROPHENOLICUS:1||CEPACIA:1||PH01:1||industrial waste incinerator:1||oxidative stress:1||OCCUPATIONALEXPOSURE:1||VETERANS:1||HUMANS:1||AEROSOLS:1||VAPORPRESSURE:1||TEMPERATURE:1||STRESS:1||DENOVOSYNTHESIS:1||PARAMETERS:1||SAPONINS:1||AIRBORNE PARTICLES:1||TRENDS:1||bioremediation:1||CHLORINATED ETHENES:1||ORGANIC CONTAMINANTS:1||UK BACKGROUND AIR:1||SINTERING PLANTS:1||TSP:1||SIZE DISTRIBUTION:1||white rot fungus:1||dye decolorization:1||congenerspecific analysis:1||NUTRIENT TRANSPORT:1||human bloods:1||PLASMA:1||heavy metals:1||BIVALVES:1||isotope effect:1||GCMS:1||biomass burning:1||TRANSPORT:1||JAPAN:1||size dependent distribution of dioxin:1||gravitational SPLITT fractionation:1||marine sediment:1||INTERNAL EXPOSURE:1||CONSTRUCTION:1||PCN:1||CHLORINATED NAPHTHALENES:1||DYSFUNCTION:1||DDE:1||ENDOCRINEDISRUPTING CHEMICALS:1||SURFACE WATERS:1||Dechlorane Plus:1||Surface dust:1||INDUSTRIALAREA:1||Natural polyphenols:1||MALACHITE GREEN:1||MORINGAOLEIFERA:1||FLAVONOIDS:1||ALUMINUM:1||MT. QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX MEDIATORS:2||WATERS:2||DISPERSION:2||Odor:2||OXIDE NANOPARTICLES:2||DEBROMINATION:2||SILVER NANOPARTICLES:2||Inventory:2||AROCLOR 1254:2||MIXTURE:2||polychlorinated dibenzofurans (PCDFs):2||TITANIUMDIOXIDE:2||MIXTURES:2||DEEP OCEAN:2||SWEDISH HUMANMILK:2||SERUM CONCENTRATIONS:2||Decolorization:2||Nanotoxicity:2||OUTDOOR AIR:2||THERMODYNAMIC PROPERTIES:2||LAURENTIAN GREATLAKES:2||ENVIRONMENTAL APPLICATIONS:2||PHENOLS:2||DIBENZOFURANS:2||FUNGAL LACCASES:2||AREA:2||ISLAND:2||polychlorinated dibenzopdioxins and dibenzofurans:2||ATMOSPHERIC TRANSPORT:2||polychlorinated biphenyl:2||INTERANNUAL VARIABILITY:2||TERRESTRIAL ECOSYSTEMS:2||BIOCONCENTRATION:2||ORGANICSOLVENTS:2||fly ash:2||SAMPLERS:2||SPHINGOMONASWITTICHII RW1:2||ABYSSAL OCEAN:2||MIXEDLAYER:2||carbon emission:2||Stormwater catch basin:2||WATER TREATMENT PLANTS:2||Bacterial viability:1||DLPCBs:1||PCDD/F LEVELS:1||Polybrominated diphenyl ethers (PBDEs):1||Dietary daily intake:1||STABILIZATION:1||INACTIVATION:1||Foods:1||SEAFOOD CONSUMPTION:1||DUST INGESTION:1||HYDROTHERMAL SYNTHESIS:1||laccasemediator system:1||LIGNIN:1||Metabolic intermediates:1||BIOREMEDIATION:1||Porphyrin:1||2,4,6TRICHLOROPHENOL:1||IMPEDANCE SPECTROSCOPY:1||NATURAL ORGANICMATTER:1||INSITU REMEDIATION:1||FATE:1||Acetone:1||nZVI:1||Chromate:1||HEXAVALENT CHROMIUM:1||ASPERGILLUSFUMIGATUS:1||RATIOS:1||MOUNTAINS:1||AREAS:1||PBDE MIXTURE:1||triazines:1||EFFICIENCIES:1||POLLUTANTS:1||POLYPHENOLS:1||,3TRIHYDROXYBIPHENYL:1||PUTIDA GJ31:1||BODY BURDEN:1||FUSION:1||POLYCHLORINATED PHENOLS:1||HAPs:1||animal feed:1||SERUM DIOXIN:1||ATMOSPHERIC PROCESSES:1||model:1||KINASEC ACTIVATION:1||MEMBRANE:1||ADAPTATION:1||degradation:1||FLUORENE:1||season:1||PARTICULATE MATTER:1||GRAMPOSITIVE BACTERIUM:1||PCDD/Fs (polychlorinated dibenzopdioxins and dibenzofurans):1||DGGE (denaturing gradient gel electrophoresis) analysis:1||passive air sampling:1||steel production:1||steel complex:1||RBBR:1||TEXTILE WASTEWATER:1||RISKASSESSMENT:1||TNTCONTAMINATED 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SAMPLES:1||GENECLUSTER:1||Toxicity:1||SYSTEM:1||COPLANAR PCBS:1||Bimetallic nanoparticles:1||Surface snow:1||CELLWALL:1||PAPER PULP:1||Biomass burning:1||ACTIVATEDSLUDGE SYSTEMS:1||SOURCE IDENTIFICATION:1||IRA743 resin bulk sampler:1||TAIWAN:1||OCPs:1||Ganoderma lucidum laccase:1||PLEUROTUSERYNGII:1||COLORATION:1||chlorodibenzopdioxins:1||FORESTFIRE:1||Masan Bay:1||HRGC/HRMS:1||maternal body burden:1||SOURCE DECAY:1||PEPTIDE:1||COEFFICIENT:1||very long chain bifunctional fatty acyl component:1||DIOXYGENASE:1||environmental level:1||REFUSE INCINERATION:1||FABRIC FILTER:1||COMBUSTION CONDITIONS:1||TRANSECT:1||GENETICALLYENGINEERED MICROORGANISMS:1||TERMINAL OXYGENASE COMPONENT:1||incinerator fly ash:1||plastic:1||IRONOXIDE CATALYST:1||bulk:1||PLANT:1||fine particle:1||NEWBEDFORD HARBOR:1||carbon monoxide:1||RETRIEVAL ALGORITHM:1||emission factors:1||WASTE:1||NATIONALHEALTH:1||NONDIABETIC ADULTS:1||HEALTHRISKS:1||4Fluorophenol:1||RHODOCOCCUSOPACUS:1||Pd/nFe:1||METALIONS:1||Fish:1||MAJOR UK CONURBATION:1||INDOOR AIR:1||ENDOCRINE DISRUPTING CHEMICALS:1||FUNGUS CORIOLOPSISPOLYZONA:1||DIPHENYL ETHER:1||2NDSPHERE COORDINATION:1||WHEAT BRAN:1||ELECTRONTRANSFER:1||TBBPA:1||dust:1||office:1||SIZE:1||CINCA RIVER:1||TIO2 NANOPARTICLES:1||COPPER NANOPARTICLES:1||Time trend:1||Elementary school student:1||ADULT MICE:1||TRANSITIONMETALS:1||Alginate bead:1||Oxygen release:1||Bioremediation:1||HEXACHLOROBENZENE:1||iron oxide nanoparticles:1||DIOXIDE:1||laccases:1||DIVERSITY:1||Incinerator:1||Indicator congener:1||COALTAR CREOSOTE:1||CA10:1||NHANES:1||CRYPTOCOCCUSNEOFORMANS:1||MEDIATED OXIDATION:1||General population:1||Deposition:1||Soil:1||Reductive dechlorination:1||Sphingomonas sp:1||FORMULATIONS:1||Steel complexes:1||EXTRACTION:1||SUPERCRITICALFLUID EXTRACTION:1||SOXHLET:1||HEALTH:1||LIGNIN MODELCOMPOUND:1||PHENOLICCOMPOUNDS:1||multicomponent nanoparticles:1||MAGNETICPROPERTIES:1||DITHIONITE:1||PHENYLENEDIAMINE:1||edible freshwater fish:1||ISOMERSPECIFIC DETERMINATION:1||daily intake:1||OPERATION RANCH HAND:1||HUMANMILK:1||DICHLORODIPHENYL DICHLOROETHENE DDE:1||RINGCLEAVAGE:1||DIBENZOPARADIOXINS:1||MSW INCINERATORS:1||URBAN AIR:1||NORTHAMERICAN ATMOSPHERE:1||microbial biocatalysts:1||diphenyl ether:1||Sphingomonas sp.:1||MASSSPECTROMETRY:1||dioxinlike PCBs:1||TRAMETESHIRSUTA:1||response surface methodology:1||Human health:1||DEPOSITION:1||BIOLOGICAL TREATMENT:1||ASH:1||GROWTH:1||carbon flux:1||ESI/LCMS:1||SATELLITE DATA:1||CO:1||biological removal:1||DEGRADING BACTERIUM:1||METHYLTRICLOSAN:1||RSCs:1||QUANTIFICATION:1||NONHODGKINSLYMPHOMA:1||Diabetes:1||Pseudonocardia benzenivorans:1||BACTERIALDEGRADATION:1||WASTEWATER TREATMENT:1||OXIDATIVE TRANSFORMATION:1||ONTARIO:1||SHIHWA:1||OTTAWA:1||GREATLAKES:1||MANGANESE PEROXIDASE:1||Natural organic coagulants:1||Grape seed extract:1||Syringaldehyde:1||AQUEOUSSOLUTIONS:1||GREEN RECOVERY:1||AUSTRALIA:1||Incinerator workers:1||Steel dust:1||Industrial wastes:1||MECHANISMS:1||Chemical contamination:1||Flame retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM ALGINATE:1||TDS:1||Dietary exposure:1||Zerovalent irons:1||Dechlorane plus:1||Polychlorinated biphenyls:1||Passive air sampling:1||manganese oxides:1||heavy metal ions:1||ADSORBENT:1||SYNTHETIC APPLICATIONS:1||Zinc Nanoparticles:1||PCDD/F FORMATION:1||Biotransformation:1||INCINERATOR FLYASH:1||Photocatalytic degradation:1||ENVIRONMENTAL CONCERN:1||Health risk:1||WET DEPOSITION:1||UASB REACTOR:1||Bulk deposition:1||PROFILES:1||CATALYZED OXIDATIVE POLYMERIZATION:1||CAPILLARYZONEELECTROPHORESIS:1||NATURALWATERS:1||PEPTIDES:1||ENVIRONMENTALSAMPLES:1||Pentachlorophenol:1||ELECTRONTRANSFERREACTIONS:1||TCE:1||2,2&apos:1||ANGULAR DIOXYGENATION:1||JAPANESE:1||cancer risk:1||polychlorinated dibenzopdioxins polychlorinated biphenyls:1||DIBENZOPDIOXIN:1||GENES:1||RHODOCOCCUSCHLOROPHENOLICUS:1||CEPACIA:1||PH01:1||industrial waste incinerator:1||oxidative stress:1||OCCUPATIONALEXPOSURE:1||VETERANS:1||HUMANS:1||AEROSOLS:1||VAPORPRESSURE:1||TEMPERATURE:1||STRESS:1||DENOVOSYNTHESIS:1||PARAMETERS:1||SAPONINS:1||AIRBORNE PARTICLES:1||TRENDS:1||bioremediation:1||CHLORINATED ETHENES:1||ORGANIC CONTAMINANTS:1||UK BACKGROUND AIR:1||SINTERING PLANTS:1||TSP:1||SIZE DISTRIBUTION:1||white rot fungus:1||dye decolorization:1||congenerspecific analysis:1||NUTRIENT TRANSPORT:1||human bloods:1||PLASMA:1||heavy metals:1||BIVALVES:1||isotope effect:1||GCMS:1||biomass burning:1||TRANSPORT:1||JAPAN:1||size dependent distribution of dioxin:1||gravitational SPLITT fractionation:1||marine sediment:1||INTERNAL EXPOSURE:1||CONSTRUCTION:1||PCN:1||CHLORINATED NAPHTHALENES:1||DYSFUNCTION:1||DDE:1||ENDOCRINEDISRUPTING CHEMICALS:1||SURFACE WATERS:1||Dechlorane Plus:1||Surface dust:1||INDUSTRIALAREA:1||Natural polyphenols:1||MALACHITE GREEN:1||MORINGAOLEIFERA:1||FLAVONOIDS:1||ALUMINUM:1||MT. QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX 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retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM 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QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE 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QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX MEDIATORS:2||WATERS:2||DISPERSION:2||Odor:2||OXIDE NANOPARTICLES:2||DEBROMINATION:2||SILVER NANOPARTICLES:2||Inventory:2||AROCLOR 1254:2||MIXTURE:2||polychlorinated dibenzofurans (PCDFs):2||TITANIUMDIOXIDE:2||MIXTURES:2||DEEP OCEAN:2||SWEDISH HUMANMILK:2||SERUM CONCENTRATIONS:2||Decolorization:2||Nanotoxicity:2||OUTDOOR AIR:2||THERMODYNAMIC PROPERTIES:2||LAURENTIAN GREATLAKES:2||ENVIRONMENTAL APPLICATIONS:2||PHENOLS:2||DIBENZOFURANS:2||FUNGAL LACCASES:2||AREA:2||ISLAND:2||polychlorinated dibenzopdioxins and dibenzofurans:2||ATMOSPHERIC TRANSPORT:2||polychlorinated biphenyl:2||INTERANNUAL VARIABILITY:2||TERRESTRIAL ECOSYSTEMS:2||BIOCONCENTRATION:2||ORGANICSOLVENTS:2||fly ash:2||SAMPLERS:2||SPHINGOMONASWITTICHII RW1:2||ABYSSAL OCEAN:2||MIXEDLAYER:2||carbon emission:2||Stormwater catch basin:2||WATER TREATMENT PLANTS:2||Bacterial viability:1||DLPCBs:1||PCDD/F LEVELS:1||Polybrominated diphenyl ethers (PBDEs):1||Dietary daily intake:1||STABILIZATION:1||INACTIVATION:1||Foods:1||SEAFOOD 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intake:1||OPERATION RANCH HAND:1||HUMANMILK:1||DICHLORODIPHENYL DICHLOROETHENE DDE:1||RINGCLEAVAGE:1||DIBENZOPARADIOXINS:1||MSW INCINERATORS:1||URBAN AIR:1||NORTHAMERICAN ATMOSPHERE:1||microbial biocatalysts:1||diphenyl ether:1||Sphingomonas sp.:1||MASSSPECTROMETRY:1||dioxinlike PCBs:1||TRAMETESHIRSUTA:1||response surface methodology:1||Human health:1||DEPOSITION:1||BIOLOGICAL TREATMENT:1||ASH:1||GROWTH:1||carbon flux:1||ESI/LCMS:1||SATELLITE DATA:1||CO:1||biological removal:1||DEGRADING BACTERIUM:1||METHYLTRICLOSAN:1||RSCs:1||QUANTIFICATION:1||NONHODGKINSLYMPHOMA:1||Diabetes:1||Pseudonocardia benzenivorans:1||BACTERIALDEGRADATION:1||WASTEWATER TREATMENT:1||OXIDATIVE TRANSFORMATION:1||ONTARIO:1||SHIHWA:1||OTTAWA:1||GREATLAKES:1||MANGANESE PEROXIDASE:1||Natural organic coagulants:1||Grape seed extract:1||Syringaldehyde:1||AQUEOUSSOLUTIONS:1||GREEN RECOVERY:1||AUSTRALIA:1||Incinerator workers:1||Steel dust:1||Industrial wastes:1||MECHANISMS:1||Chemical contamination:1||Flame retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM ALGINATE:1||TDS:1||Dietary exposure:1||Zerovalent irons:1||Dechlorane plus:1||Polychlorinated biphenyls:1||Passive air sampling:1||manganese oxides:1||heavy metal ions:1||ADSORBENT:1||SYNTHETIC APPLICATIONS:1||Zinc Nanoparticles:1||PCDD/F FORMATION:1||Biotransformation:1||INCINERATOR FLYASH:1||Photocatalytic degradation:1||ENVIRONMENTAL CONCERN:1||Health risk:1||WET DEPOSITION:1||UASB REACTOR:1||Bulk deposition:1||PROFILES:1||CATALYZED OXIDATIVE POLYMERIZATION:1||CAPILLARYZONEELECTROPHORESIS:1||NATURALWATERS:1||PEPTIDES:1||ENVIRONMENTALSAMPLES:1||Pentachlorophenol:1||ELECTRONTRANSFERREACTIONS:1||TCE:1||2,2&apos:1||ANGULAR DIOXYGENATION:1||JAPANESE:1||cancer risk:1||polychlorinated dibenzopdioxins polychlorinated biphenyls:1||DIBENZOPDIOXIN:1||GENES:1||RHODOCOCCUSCHLOROPHENOLICUS:1||CEPACIA:1||PH01:1||industrial waste incinerator:1||oxidative stress:1||OCCUPATIONALEXPOSURE:1||VETERANS:1||HUMANS:1||AEROSOLS:1||VAPORPRESSURE:1||TEMPERATURE:1||STRESS:1||DENOVOSYNTHESIS:1||PARAMETERS:1||SAPONINS:1||AIRBORNE PARTICLES:1||TRENDS:1||bioremediation:1||CHLORINATED ETHENES:1||ORGANIC CONTAMINANTS:1||UK BACKGROUND AIR:1||SINTERING PLANTS:1||TSP:1||SIZE DISTRIBUTION:1||white rot fungus:1||dye decolorization:1||congenerspecific analysis:1||NUTRIENT TRANSPORT:1||human bloods:1||PLASMA:1||heavy metals:1||BIVALVES:1||isotope effect:1||GCMS:1||biomass burning:1||TRANSPORT:1||JAPAN:1||size dependent distribution of dioxin:1||gravitational SPLITT fractionation:1||marine sediment:1||INTERNAL EXPOSURE:1||CONSTRUCTION:1||PCN:1||CHLORINATED NAPHTHALENES:1||DYSFUNCTION:1||DDE:1||ENDOCRINEDISRUPTING CHEMICALS:1||SURFACE WATERS:1||Dechlorane Plus:1||Surface dust:1||INDUSTRIALAREA:1||Natural polyphenols:1||MALACHITE GREEN:1||MORINGAOLEIFERA:1||FLAVONOIDS:1||ALUMINUM:1||MT. QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX MEDIATORS:2||WATERS:2||DISPERSION:2||Odor:2||OXIDE NANOPARTICLES:2||DEBROMINATION:2||SILVER NANOPARTICLES:2||Inventory:2||AROCLOR 1254:2||MIXTURE:2||polychlorinated dibenzofurans (PCDFs):2||TITANIUMDIOXIDE:2||MIXTURES:2||DEEP OCEAN:2||SWEDISH HUMANMILK:2||SERUM CONCENTRATIONS:2||Decolorization:2||Nanotoxicity:2||OUTDOOR AIR:2||THERMODYNAMIC PROPERTIES:2||LAURENTIAN GREATLAKES:2||ENVIRONMENTAL APPLICATIONS:2||PHENOLS:2||DIBENZOFURANS:2||FUNGAL LACCASES:2||AREA:2||ISLAND:2||polychlorinated dibenzopdioxins and dibenzofurans:2||ATMOSPHERIC TRANSPORT:2||polychlorinated biphenyl:2||INTERANNUAL VARIABILITY:2||TERRESTRIAL ECOSYSTEMS:2||BIOCONCENTRATION:2||ORGANICSOLVENTS:2||fly ash:2||SAMPLERS:2||SPHINGOMONASWITTICHII RW1:2||ABYSSAL OCEAN:2||MIXEDLAYER:2||carbon emission:2||Stormwater catch basin:2||WATER TREATMENT PLANTS:2||Bacterial viability:1||DLPCBs:1||PCDD/F LEVELS:1||Polybrominated diphenyl ethers (PBDEs):1||Dietary daily intake:1||STABILIZATION:1||INACTIVATION:1||Foods:1||SEAFOOD CONSUMPTION:1||DUST INGESTION:1||HYDROTHERMAL SYNTHESIS:1||laccasemediator system:1||LIGNIN:1||Metabolic intermediates:1||BIOREMEDIATION:1||Porphyrin:1||2,4,6TRICHLOROPHENOL:1||IMPEDANCE SPECTROSCOPY:1||NATURAL ORGANICMATTER:1||INSITU REMEDIATION:1||FATE:1||Acetone:1||nZVI:1||Chromate:1||HEXAVALENT CHROMIUM:1||ASPERGILLUSFUMIGATUS:1||RATIOS:1||MOUNTAINS:1||AREAS:1||PBDE MIXTURE:1||triazines:1||EFFICIENCIES:1||POLLUTANTS:1||POLYPHENOLS:1||,3TRIHYDROXYBIPHENYL:1||PUTIDA GJ31:1||BODY BURDEN:1||FUSION:1||POLYCHLORINATED PHENOLS:1||HAPs:1||animal feed:1||SERUM DIOXIN:1||ATMOSPHERIC PROCESSES:1||model:1||KINASEC ACTIVATION:1||MEMBRANE:1||ADAPTATION:1||degradation:1||FLUORENE:1||season:1||PARTICULATE MATTER:1||GRAMPOSITIVE BACTERIUM:1||PCDD/Fs (polychlorinated dibenzopdioxins and dibenzofurans):1||DGGE (denaturing gradient gel electrophoresis) analysis:1||passive air sampling:1||steel production:1||steel complex:1||RBBR:1||TEXTILE WASTEWATER:1||RISKASSESSMENT:1||TNTCONTAMINATED 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SAMPLES:1||GENECLUSTER:1||Toxicity:1||SYSTEM:1||COPLANAR PCBS:1||Bimetallic nanoparticles:1||Surface snow:1||CELLWALL:1||PAPER PULP:1||Biomass burning:1||ACTIVATEDSLUDGE SYSTEMS:1||SOURCE IDENTIFICATION:1||IRA743 resin bulk sampler:1||TAIWAN:1||OCPs:1||Ganoderma lucidum laccase:1||PLEUROTUSERYNGII:1||COLORATION:1||chlorodibenzopdioxins:1||FORESTFIRE:1||Masan Bay:1||HRGC/HRMS:1||maternal body burden:1||SOURCE DECAY:1||PEPTIDE:1||COEFFICIENT:1||very long chain bifunctional fatty acyl component:1||DIOXYGENASE:1||environmental level:1||REFUSE INCINERATION:1||FABRIC FILTER:1||COMBUSTION CONDITIONS:1||TRANSECT:1||GENETICALLYENGINEERED MICROORGANISMS:1||TERMINAL OXYGENASE COMPONENT:1||incinerator fly ash:1||plastic:1||IRONOXIDE CATALYST:1||bulk:1||PLANT:1||fine particle:1||NEWBEDFORD HARBOR:1||carbon monoxide:1||RETRIEVAL ALGORITHM:1||emission factors:1||WASTE:1||NATIONALHEALTH:1||NONDIABETIC ADULTS:1||HEALTHRISKS:1||4Fluorophenol:1||RHODOCOCCUSOPACUS:1||Pd/nFe:1||METALIONS:1||Fish:1||MAJOR UK CONURBATION:1||INDOOR AIR:1||ENDOCRINE DISRUPTING CHEMICALS:1||FUNGUS CORIOLOPSISPOLYZONA:1||DIPHENYL ETHER:1||2NDSPHERE COORDINATION:1||WHEAT BRAN:1||ELECTRONTRANSFER:1||TBBPA:1||dust:1||office:1||SIZE:1||CINCA RIVER:1||TIO2 NANOPARTICLES:1||COPPER NANOPARTICLES:1||Time trend:1||Elementary school student:1||ADULT MICE:1||TRANSITIONMETALS:1||Alginate bead:1||Oxygen release:1||Bioremediation:1||HEXACHLOROBENZENE:1||iron oxide nanoparticles:1||DIOXIDE:1||laccases:1||DIVERSITY:1||Incinerator:1||Indicator congener:1||COALTAR CREOSOTE:1||CA10:1||NHANES:1||CRYPTOCOCCUSNEOFORMANS:1||MEDIATED OXIDATION:1||General population:1||Deposition:1||Soil:1||Reductive dechlorination:1||Sphingomonas sp:1||FORMULATIONS:1||Steel complexes:1||EXTRACTION:1||SUPERCRITICALFLUID EXTRACTION:1||SOXHLET:1||HEALTH:1||LIGNIN MODELCOMPOUND:1||PHENOLICCOMPOUNDS:1||multicomponent nanoparticles:1||MAGNETICPROPERTIES:1||DITHIONITE:1||PHENYLENEDIAMINE:1||edible freshwater fish:1||ISOMERSPECIFIC DETERMINATION:1||daily intake:1||OPERATION RANCH HAND:1||HUMANMILK:1||DICHLORODIPHENYL DICHLOROETHENE DDE:1||RINGCLEAVAGE:1||DIBENZOPARADIOXINS:1||MSW INCINERATORS:1||URBAN AIR:1||NORTHAMERICAN ATMOSPHERE:1||microbial biocatalysts:1||diphenyl ether:1||Sphingomonas sp.:1||MASSSPECTROMETRY:1||dioxinlike PCBs:1||TRAMETESHIRSUTA:1||response surface methodology:1||Human health:1||DEPOSITION:1||BIOLOGICAL TREATMENT:1||ASH:1||GROWTH:1||carbon flux:1||ESI/LCMS:1||SATELLITE DATA:1||CO:1||biological removal:1||DEGRADING BACTERIUM:1||METHYLTRICLOSAN:1||RSCs:1||QUANTIFICATION:1||NONHODGKINSLYMPHOMA:1||Diabetes:1||Pseudonocardia benzenivorans:1||BACTERIALDEGRADATION:1||WASTEWATER TREATMENT:1||OXIDATIVE TRANSFORMATION:1||ONTARIO:1||SHIHWA:1||OTTAWA:1||GREATLAKES:1||MANGANESE PEROXIDASE:1||Natural organic coagulants:1||Grape seed extract:1||Syringaldehyde:1||AQUEOUSSOLUTIONS:1||GREEN RECOVERY:1||AUSTRALIA:1||Incinerator workers:1||Steel dust:1||Industrial wastes:1||MECHANISMS:1||Chemical contamination:1||Flame retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM ALGINATE:1||TDS:1||Dietary exposure:1||Zerovalent irons:1||Dechlorane plus:1||Polychlorinated biphenyls:1||Passive air sampling:1||manganese oxides:1||heavy metal ions:1||ADSORBENT:1||SYNTHETIC APPLICATIONS:1||Zinc Nanoparticles:1||PCDD/F FORMATION:1||Biotransformation:1||INCINERATOR FLYASH:1||Photocatalytic degradation:1||ENVIRONMENTAL CONCERN:1||Health risk:1||WET DEPOSITION:1||UASB REACTOR:1||Bulk deposition:1||PROFILES:1||CATALYZED OXIDATIVE POLYMERIZATION:1||CAPILLARYZONEELECTROPHORESIS:1||NATURALWATERS:1||PEPTIDES:1||ENVIRONMENTALSAMPLES:1||Pentachlorophenol:1||ELECTRONTRANSFERREACTIONS:1||TCE:1||2,2&apos:1||ANGULAR DIOXYGENATION:1||JAPANESE:1||cancer risk:1||polychlorinated dibenzopdioxins polychlorinated biphenyls:1||DIBENZOPDIOXIN:1||GENES:1||RHODOCOCCUSCHLOROPHENOLICUS:1||CEPACIA:1||PH01:1||industrial waste incinerator:1||oxidative stress:1||OCCUPATIONALEXPOSURE:1||VETERANS:1||HUMANS:1||AEROSOLS:1||VAPORPRESSURE:1||TEMPERATURE:1||STRESS:1||DENOVOSYNTHESIS:1||PARAMETERS:1||SAPONINS:1||AIRBORNE PARTICLES:1||TRENDS:1||bioremediation:1||CHLORINATED ETHENES:1||ORGANIC CONTAMINANTS:1||UK BACKGROUND AIR:1||SINTERING PLANTS:1||TSP:1||SIZE DISTRIBUTION:1||white rot fungus:1||dye decolorization:1||congenerspecific analysis:1||NUTRIENT TRANSPORT:1||human bloods:1||PLASMA:1||heavy metals:1||BIVALVES:1||isotope effect:1||GCMS:1||biomass burning:1||TRANSPORT:1||JAPAN:1||size dependent distribution of dioxin:1||gravitational SPLITT fractionation:1||marine sediment:1||INTERNAL EXPOSURE:1||CONSTRUCTION:1||PCN:1||CHLORINATED NAPHTHALENES:1||DYSFUNCTION:1||DDE:1||ENDOCRINEDISRUPTING CHEMICALS:1||SURFACE WATERS:1||Dechlorane Plus:1||Surface dust:1||INDUSTRIALAREA:1||Natural polyphenols:1||MALACHITE GREEN:1||MORINGAOLEIFERA:1||FLAVONOIDS:1||ALUMINUM:1||MT. QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX 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retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM 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QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE 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QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX MEDIATORS:2||WATERS:2||DISPERSION:2||Odor:2||OXIDE NANOPARTICLES:2||DEBROMINATION:2||SILVER NANOPARTICLES:2||Inventory:2||AROCLOR 1254:2||MIXTURE:2||polychlorinated dibenzofurans (PCDFs):2||TITANIUMDIOXIDE:2||MIXTURES:2||DEEP OCEAN:2||SWEDISH HUMANMILK:2||SERUM CONCENTRATIONS:2||Decolorization:2||Nanotoxicity:2||OUTDOOR AIR:2||THERMODYNAMIC PROPERTIES:2||LAURENTIAN GREATLAKES:2||ENVIRONMENTAL APPLICATIONS:2||PHENOLS:2||DIBENZOFURANS:2||FUNGAL LACCASES:2||AREA:2||ISLAND:2||polychlorinated dibenzopdioxins and dibenzofurans:2||ATMOSPHERIC TRANSPORT:2||polychlorinated biphenyl:2||INTERANNUAL VARIABILITY:2||TERRESTRIAL ECOSYSTEMS:2||BIOCONCENTRATION:2||ORGANICSOLVENTS:2||fly ash:2||SAMPLERS:2||SPHINGOMONASWITTICHII RW1:2||ABYSSAL OCEAN:2||MIXEDLAYER:2||carbon emission:2||Stormwater catch basin:2||WATER TREATMENT PLANTS:2||Bacterial viability:1||DLPCBs:1||PCDD/F LEVELS:1||Polybrominated diphenyl ethers (PBDEs):1||Dietary daily intake:1||STABILIZATION:1||INACTIVATION:1||Foods:1||SEAFOOD 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intake:1||OPERATION RANCH HAND:1||HUMANMILK:1||DICHLORODIPHENYL DICHLOROETHENE DDE:1||RINGCLEAVAGE:1||DIBENZOPARADIOXINS:1||MSW INCINERATORS:1||URBAN AIR:1||NORTHAMERICAN ATMOSPHERE:1||microbial biocatalysts:1||diphenyl ether:1||Sphingomonas sp.:1||MASSSPECTROMETRY:1||dioxinlike PCBs:1||TRAMETESHIRSUTA:1||response surface methodology:1||Human health:1||DEPOSITION:1||BIOLOGICAL TREATMENT:1||ASH:1||GROWTH:1||carbon flux:1||ESI/LCMS:1||SATELLITE DATA:1||CO:1||biological removal:1||DEGRADING BACTERIUM:1||METHYLTRICLOSAN:1||RSCs:1||QUANTIFICATION:1||NONHODGKINSLYMPHOMA:1||Diabetes:1||Pseudonocardia benzenivorans:1||BACTERIALDEGRADATION:1||WASTEWATER TREATMENT:1||OXIDATIVE TRANSFORMATION:1||ONTARIO:1||SHIHWA:1||OTTAWA:1||GREATLAKES:1||MANGANESE PEROXIDASE:1||Natural organic coagulants:1||Grape seed extract:1||Syringaldehyde:1||AQUEOUSSOLUTIONS:1||GREEN RECOVERY:1||AUSTRALIA:1||Incinerator workers:1||Steel dust:1||Industrial wastes:1||MECHANISMS:1||Chemical contamination:1||Flame retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM ALGINATE:1||TDS:1||Dietary exposure:1||Zerovalent irons:1||Dechlorane plus:1||Polychlorinated biphenyls:1||Passive air sampling:1||manganese oxides:1||heavy metal ions:1||ADSORBENT:1||SYNTHETIC APPLICATIONS:1||Zinc Nanoparticles:1||PCDD/F FORMATION:1||Biotransformation:1||INCINERATOR FLYASH:1||Photocatalytic degradation:1||ENVIRONMENTAL CONCERN:1||Health risk:1||WET DEPOSITION:1||UASB REACTOR:1||Bulk deposition:1||PROFILES:1||CATALYZED OXIDATIVE POLYMERIZATION:1||CAPILLARYZONEELECTROPHORESIS:1||NATURALWATERS:1||PEPTIDES:1||ENVIRONMENTALSAMPLES:1||Pentachlorophenol:1||ELECTRONTRANSFERREACTIONS:1||TCE:1||2,2&apos:1||ANGULAR DIOXYGENATION:1||JAPANESE:1||cancer risk:1||polychlorinated dibenzopdioxins polychlorinated biphenyls:1||DIBENZOPDIOXIN:1||GENES:1||RHODOCOCCUSCHLOROPHENOLICUS:1||CEPACIA:1||PH01:1||industrial waste incinerator:1||oxidative stress:1||OCCUPATIONALEXPOSURE:1||VETERANS:1||HUMANS:1||AEROSOLS:1||VAPORPRESSURE:1||TEMPERATURE:1||STRESS:1||DENOVOSYNTHESIS:1||PARAMETERS:1||SAPONINS:1||AIRBORNE PARTICLES:1||TRENDS:1||bioremediation:1||CHLORINATED ETHENES:1||ORGANIC CONTAMINANTS:1||UK BACKGROUND AIR:1||SINTERING PLANTS:1||TSP:1||SIZE DISTRIBUTION:1||white rot fungus:1||dye decolorization:1||congenerspecific analysis:1||NUTRIENT TRANSPORT:1||human bloods:1||PLASMA:1||heavy metals:1||BIVALVES:1||isotope effect:1||GCMS:1||biomass burning:1||TRANSPORT:1||JAPAN:1||size dependent distribution of dioxin:1||gravitational SPLITT fractionation:1||marine sediment:1||INTERNAL EXPOSURE:1||CONSTRUCTION:1||PCN:1||CHLORINATED NAPHTHALENES:1||DYSFUNCTION:1||DDE:1||ENDOCRINEDISRUPTING CHEMICALS:1||SURFACE WATERS:1||Dechlorane Plus:1||Surface dust:1||INDUSTRIALAREA:1||Natural polyphenols:1||MALACHITE GREEN:1||MORINGAOLEIFERA:1||FLAVONOIDS:1||ALUMINUM:1||MT. QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX MEDIATORS:2||WATERS:2||DISPERSION:2||Odor:2||OXIDE NANOPARTICLES:2||DEBROMINATION:2||SILVER NANOPARTICLES:2||Inventory:2||AROCLOR 1254:2||MIXTURE:2||polychlorinated dibenzofurans (PCDFs):2||TITANIUMDIOXIDE:2||MIXTURES:2||DEEP OCEAN:2||SWEDISH HUMANMILK:2||SERUM CONCENTRATIONS:2||Decolorization:2||Nanotoxicity:2||OUTDOOR AIR:2||THERMODYNAMIC PROPERTIES:2||LAURENTIAN GREATLAKES:2||ENVIRONMENTAL APPLICATIONS:2||PHENOLS:2||DIBENZOFURANS:2||FUNGAL LACCASES:2||AREA:2||ISLAND:2||polychlorinated dibenzopdioxins and dibenzofurans:2||ATMOSPHERIC TRANSPORT:2||polychlorinated biphenyl:2||INTERANNUAL VARIABILITY:2||TERRESTRIAL ECOSYSTEMS:2||BIOCONCENTRATION:2||ORGANICSOLVENTS:2||fly ash:2||SAMPLERS:2||SPHINGOMONASWITTICHII RW1:2||ABYSSAL OCEAN:2||MIXEDLAYER:2||carbon emission:2||Stormwater catch basin:2||WATER TREATMENT PLANTS:2||Bacterial viability:1||DLPCBs:1||PCDD/F LEVELS:1||Polybrominated diphenyl ethers (PBDEs):1||Dietary daily intake:1||STABILIZATION:1||INACTIVATION:1||Foods:1||SEAFOOD CONSUMPTION:1||DUST INGESTION:1||HYDROTHERMAL SYNTHESIS:1||laccasemediator system:1||LIGNIN:1||Metabolic intermediates:1||BIOREMEDIATION:1||Porphyrin:1||2,4,6TRICHLOROPHENOL:1||IMPEDANCE SPECTROSCOPY:1||NATURAL ORGANICMATTER:1||INSITU REMEDIATION:1||FATE:1||Acetone:1||nZVI:1||Chromate:1||HEXAVALENT CHROMIUM:1||ASPERGILLUSFUMIGATUS:1||RATIOS:1||MOUNTAINS:1||AREAS:1||PBDE MIXTURE:1||triazines:1||EFFICIENCIES:1||POLLUTANTS:1||POLYPHENOLS:1||,3TRIHYDROXYBIPHENYL:1||PUTIDA GJ31:1||BODY BURDEN:1||FUSION:1||POLYCHLORINATED PHENOLS:1||HAPs:1||animal feed:1||SERUM DIOXIN:1||ATMOSPHERIC PROCESSES:1||model:1||KINASEC ACTIVATION:1||MEMBRANE:1||ADAPTATION:1||degradation:1||FLUORENE:1||season:1||PARTICULATE MATTER:1||GRAMPOSITIVE BACTERIUM:1||PCDD/Fs (polychlorinated dibenzopdioxins and dibenzofurans):1||DGGE (denaturing gradient gel electrophoresis) analysis:1||passive air sampling:1||steel production:1||steel complex:1||RBBR:1||TEXTILE WASTEWATER:1||RISKASSESSMENT:1||TNTCONTAMINATED 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SAMPLES:1||GENECLUSTER:1||Toxicity:1||SYSTEM:1||COPLANAR PCBS:1||Bimetallic nanoparticles:1||Surface snow:1||CELLWALL:1||PAPER PULP:1||Biomass burning:1||ACTIVATEDSLUDGE SYSTEMS:1||SOURCE IDENTIFICATION:1||IRA743 resin bulk sampler:1||TAIWAN:1||OCPs:1||Ganoderma lucidum laccase:1||PLEUROTUSERYNGII:1||COLORATION:1||chlorodibenzopdioxins:1||FORESTFIRE:1||Masan Bay:1||HRGC/HRMS:1||maternal body burden:1||SOURCE DECAY:1||PEPTIDE:1||COEFFICIENT:1||very long chain bifunctional fatty acyl component:1||DIOXYGENASE:1||environmental level:1||REFUSE INCINERATION:1||FABRIC FILTER:1||COMBUSTION CONDITIONS:1||TRANSECT:1||GENETICALLYENGINEERED MICROORGANISMS:1||TERMINAL OXYGENASE COMPONENT:1||incinerator fly ash:1||plastic:1||IRONOXIDE CATALYST:1||bulk:1||PLANT:1||fine particle:1||NEWBEDFORD HARBOR:1||carbon monoxide:1||RETRIEVAL ALGORITHM:1||emission factors:1||WASTE:1||NATIONALHEALTH:1||NONDIABETIC ADULTS:1||HEALTHRISKS:1||4Fluorophenol:1||RHODOCOCCUSOPACUS:1||Pd/nFe:1||METALIONS:1||Fish:1||MAJOR UK CONURBATION:1||INDOOR AIR:1||ENDOCRINE DISRUPTING CHEMICALS:1||FUNGUS CORIOLOPSISPOLYZONA:1||DIPHENYL ETHER:1||2NDSPHERE COORDINATION:1||WHEAT BRAN:1||ELECTRONTRANSFER:1||TBBPA:1||dust:1||office:1||SIZE:1||CINCA RIVER:1||TIO2 NANOPARTICLES:1||COPPER NANOPARTICLES:1||Time trend:1||Elementary school student:1||ADULT MICE:1||TRANSITIONMETALS:1||Alginate bead:1||Oxygen release:1||Bioremediation:1||HEXACHLOROBENZENE:1||iron oxide nanoparticles:1||DIOXIDE:1||laccases:1||DIVERSITY:1||Incinerator:1||Indicator congener:1||COALTAR CREOSOTE:1||CA10:1||NHANES:1||CRYPTOCOCCUSNEOFORMANS:1||MEDIATED OXIDATION:1||General population:1||Deposition:1||Soil:1||Reductive dechlorination:1||Sphingomonas sp:1||FORMULATIONS:1||Steel complexes:1||EXTRACTION:1||SUPERCRITICALFLUID EXTRACTION:1||SOXHLET:1||HEALTH:1||LIGNIN MODELCOMPOUND:1||PHENOLICCOMPOUNDS:1||multicomponent nanoparticles:1||MAGNETICPROPERTIES:1||DITHIONITE:1||PHENYLENEDIAMINE:1||edible freshwater fish:1||ISOMERSPECIFIC DETERMINATION:1||daily intake:1||OPERATION RANCH HAND:1||HUMANMILK:1||DICHLORODIPHENYL DICHLOROETHENE DDE:1||RINGCLEAVAGE:1||DIBENZOPARADIOXINS:1||MSW INCINERATORS:1||URBAN AIR:1||NORTHAMERICAN ATMOSPHERE:1||microbial biocatalysts:1||diphenyl ether:1||Sphingomonas sp.:1||MASSSPECTROMETRY:1||dioxinlike PCBs:1||TRAMETESHIRSUTA:1||response surface methodology:1||Human health:1||DEPOSITION:1||BIOLOGICAL TREATMENT:1||ASH:1||GROWTH:1||carbon flux:1||ESI/LCMS:1||SATELLITE DATA:1||CO:1||biological removal:1||DEGRADING BACTERIUM:1||METHYLTRICLOSAN:1||RSCs:1||QUANTIFICATION:1||NONHODGKINSLYMPHOMA:1||Diabetes:1||Pseudonocardia benzenivorans:1||BACTERIALDEGRADATION:1||WASTEWATER TREATMENT:1||OXIDATIVE TRANSFORMATION:1||ONTARIO:1||SHIHWA:1||OTTAWA:1||GREATLAKES:1||MANGANESE PEROXIDASE:1||Natural organic coagulants:1||Grape seed extract:1||Syringaldehyde:1||AQUEOUSSOLUTIONS:1||GREEN RECOVERY:1||AUSTRALIA:1||Incinerator workers:1||Steel dust:1||Industrial wastes:1||MECHANISMS:1||Chemical contamination:1||Flame retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM ALGINATE:1||TDS:1||Dietary exposure:1||Zerovalent irons:1||Dechlorane plus:1||Polychlorinated biphenyls:1||Passive air sampling:1||manganese oxides:1||heavy metal ions:1||ADSORBENT:1||SYNTHETIC APPLICATIONS:1||Zinc Nanoparticles:1||PCDD/F FORMATION:1||Biotransformation:1||INCINERATOR FLYASH:1||Photocatalytic degradation:1||ENVIRONMENTAL CONCERN:1||Health risk:1||WET DEPOSITION:1||UASB REACTOR:1||Bulk deposition:1||PROFILES:1||CATALYZED OXIDATIVE POLYMERIZATION:1||CAPILLARYZONEELECTROPHORESIS:1||NATURALWATERS:1||PEPTIDES:1||ENVIRONMENTALSAMPLES:1||Pentachlorophenol:1||ELECTRONTRANSFERREACTIONS:1||TCE:1||2,2&apos:1||ANGULAR DIOXYGENATION:1||JAPANESE:1||cancer risk:1||polychlorinated dibenzopdioxins polychlorinated biphenyls:1||DIBENZOPDIOXIN:1||GENES:1||RHODOCOCCUSCHLOROPHENOLICUS:1||CEPACIA:1||PH01:1||industrial waste incinerator:1||oxidative stress:1||OCCUPATIONALEXPOSURE:1||VETERANS:1||HUMANS:1||AEROSOLS:1||VAPORPRESSURE:1||TEMPERATURE:1||STRESS:1||DENOVOSYNTHESIS:1||PARAMETERS:1||SAPONINS:1||AIRBORNE PARTICLES:1||TRENDS:1||bioremediation:1||CHLORINATED ETHENES:1||ORGANIC CONTAMINANTS:1||UK BACKGROUND AIR:1||SINTERING PLANTS:1||TSP:1||SIZE DISTRIBUTION:1||white rot fungus:1||dye decolorization:1||congenerspecific analysis:1||NUTRIENT TRANSPORT:1||human bloods:1||PLASMA:1||heavy metals:1||BIVALVES:1||isotope effect:1||GCMS:1||biomass burning:1||TRANSPORT:1||JAPAN:1||size dependent distribution of dioxin:1||gravitational SPLITT fractionation:1||marine sediment:1||INTERNAL EXPOSURE:1||CONSTRUCTION:1||PCN:1||CHLORINATED NAPHTHALENES:1||DYSFUNCTION:1||DDE:1||ENDOCRINEDISRUPTING CHEMICALS:1||SURFACE WATERS:1||Dechlorane Plus:1||Surface dust:1||INDUSTRIALAREA:1||Natural polyphenols:1||MALACHITE GREEN:1||MORINGAOLEIFERA:1||FLAVONOIDS:1||ALUMINUM:1||MT. QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX 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retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM 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QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE 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QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX MEDIATORS:2||WATERS:2||DISPERSION:2||Odor:2||OXIDE NANOPARTICLES:2||DEBROMINATION:2||SILVER NANOPARTICLES:2||Inventory:2||AROCLOR 1254:2||MIXTURE:2||polychlorinated dibenzofurans (PCDFs):2||TITANIUMDIOXIDE:2||MIXTURES:2||DEEP OCEAN:2||SWEDISH HUMANMILK:2||SERUM CONCENTRATIONS:2||Decolorization:2||Nanotoxicity:2||OUTDOOR AIR:2||THERMODYNAMIC PROPERTIES:2||LAURENTIAN GREATLAKES:2||ENVIRONMENTAL APPLICATIONS:2||PHENOLS:2||DIBENZOFURANS:2||FUNGAL LACCASES:2||AREA:2||ISLAND:2||polychlorinated dibenzopdioxins and dibenzofurans:2||ATMOSPHERIC TRANSPORT:2||polychlorinated biphenyl:2||INTERANNUAL VARIABILITY:2||TERRESTRIAL ECOSYSTEMS:2||BIOCONCENTRATION:2||ORGANICSOLVENTS:2||fly ash:2||SAMPLERS:2||SPHINGOMONASWITTICHII RW1:2||ABYSSAL OCEAN:2||MIXEDLAYER:2||carbon emission:2||Stormwater catch basin:2||WATER TREATMENT PLANTS:2||Bacterial viability:1||DLPCBs:1||PCDD/F LEVELS:1||Polybrominated diphenyl ethers (PBDEs):1||Dietary daily intake:1||STABILIZATION:1||INACTIVATION:1||Foods:1||SEAFOOD 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intake:1||OPERATION RANCH HAND:1||HUMANMILK:1||DICHLORODIPHENYL DICHLOROETHENE DDE:1||RINGCLEAVAGE:1||DIBENZOPARADIOXINS:1||MSW INCINERATORS:1||URBAN AIR:1||NORTHAMERICAN ATMOSPHERE:1||microbial biocatalysts:1||diphenyl ether:1||Sphingomonas sp.:1||MASSSPECTROMETRY:1||dioxinlike PCBs:1||TRAMETESHIRSUTA:1||response surface methodology:1||Human health:1||DEPOSITION:1||BIOLOGICAL TREATMENT:1||ASH:1||GROWTH:1||carbon flux:1||ESI/LCMS:1||SATELLITE DATA:1||CO:1||biological removal:1||DEGRADING BACTERIUM:1||METHYLTRICLOSAN:1||RSCs:1||QUANTIFICATION:1||NONHODGKINSLYMPHOMA:1||Diabetes:1||Pseudonocardia benzenivorans:1||BACTERIALDEGRADATION:1||WASTEWATER TREATMENT:1||OXIDATIVE TRANSFORMATION:1||ONTARIO:1||SHIHWA:1||OTTAWA:1||GREATLAKES:1||MANGANESE PEROXIDASE:1||Natural organic coagulants:1||Grape seed extract:1||Syringaldehyde:1||AQUEOUSSOLUTIONS:1||GREEN RECOVERY:1||AUSTRALIA:1||Incinerator workers:1||Steel dust:1||Industrial wastes:1||MECHANISMS:1||Chemical contamination:1||Flame retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM ALGINATE:1||TDS:1||Dietary exposure:1||Zerovalent irons:1||Dechlorane plus:1||Polychlorinated biphenyls:1||Passive air sampling:1||manganese oxides:1||heavy metal ions:1||ADSORBENT:1||SYNTHETIC APPLICATIONS:1||Zinc Nanoparticles:1||PCDD/F FORMATION:1||Biotransformation:1||INCINERATOR FLYASH:1||Photocatalytic degradation:1||ENVIRONMENTAL CONCERN:1||Health risk:1||WET DEPOSITION:1||UASB REACTOR:1||Bulk deposition:1||PROFILES:1||CATALYZED OXIDATIVE POLYMERIZATION:1||CAPILLARYZONEELECTROPHORESIS:1||NATURALWATERS:1||PEPTIDES:1||ENVIRONMENTALSAMPLES:1||Pentachlorophenol:1||ELECTRONTRANSFERREACTIONS:1||TCE:1||2,2&apos:1||ANGULAR DIOXYGENATION:1||JAPANESE:1||cancer risk:1||polychlorinated dibenzopdioxins polychlorinated biphenyls:1||DIBENZOPDIOXIN:1||GENES:1||RHODOCOCCUSCHLOROPHENOLICUS:1||CEPACIA:1||PH01:1||industrial waste incinerator:1||oxidative stress:1||OCCUPATIONALEXPOSURE:1||VETERANS:1||HUMANS:1||AEROSOLS:1||VAPORPRESSURE:1||TEMPERATURE:1||STRESS:1||DENOVOSYNTHESIS:1||PARAMETERS:1||SAPONINS:1||AIRBORNE PARTICLES:1||TRENDS:1||bioremediation:1||CHLORINATED ETHENES:1||ORGANIC CONTAMINANTS:1||UK BACKGROUND AIR:1||SINTERING PLANTS:1||TSP:1||SIZE DISTRIBUTION:1||white rot fungus:1||dye decolorization:1||congenerspecific analysis:1||NUTRIENT TRANSPORT:1||human bloods:1||PLASMA:1||heavy metals:1||BIVALVES:1||isotope effect:1||GCMS:1||biomass burning:1||TRANSPORT:1||JAPAN:1||size dependent distribution of dioxin:1||gravitational SPLITT fractionation:1||marine sediment:1||INTERNAL EXPOSURE:1||CONSTRUCTION:1||PCN:1||CHLORINATED NAPHTHALENES:1||DYSFUNCTION:1||DDE:1||ENDOCRINEDISRUPTING CHEMICALS:1||SURFACE WATERS:1||Dechlorane Plus:1||Surface dust:1||INDUSTRIALAREA:1||Natural polyphenols:1||MALACHITE GREEN:1||MORINGAOLEIFERA:1||FLAVONOIDS:1||ALUMINUM:1||MT. QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX MEDIATORS:2||WATERS:2||DISPERSION:2||Odor:2||OXIDE NANOPARTICLES:2||DEBROMINATION:2||SILVER NANOPARTICLES:2||Inventory:2||AROCLOR 1254:2||MIXTURE:2||polychlorinated dibenzofurans (PCDFs):2||TITANIUMDIOXIDE:2||MIXTURES:2||DEEP OCEAN:2||SWEDISH HUMANMILK:2||SERUM CONCENTRATIONS:2||Decolorization:2||Nanotoxicity:2||OUTDOOR AIR:2||THERMODYNAMIC PROPERTIES:2||LAURENTIAN GREATLAKES:2||ENVIRONMENTAL APPLICATIONS:2||PHENOLS:2||DIBENZOFURANS:2||FUNGAL LACCASES:2||AREA:2||ISLAND:2||polychlorinated dibenzopdioxins and dibenzofurans:2||ATMOSPHERIC TRANSPORT:2||polychlorinated biphenyl:2||INTERANNUAL VARIABILITY:2||TERRESTRIAL ECOSYSTEMS:2||BIOCONCENTRATION:2||ORGANICSOLVENTS:2||fly ash:2||SAMPLERS:2||SPHINGOMONASWITTICHII RW1:2||ABYSSAL OCEAN:2||MIXEDLAYER:2||carbon emission:2||Stormwater catch basin:2||WATER TREATMENT PLANTS:2||Bacterial viability:1||DLPCBs:1||PCDD/F LEVELS:1||Polybrominated diphenyl ethers (PBDEs):1||Dietary daily intake:1||STABILIZATION:1||INACTIVATION:1||Foods:1||SEAFOOD CONSUMPTION:1||DUST INGESTION:1||HYDROTHERMAL SYNTHESIS:1||laccasemediator system:1||LIGNIN:1||Metabolic intermediates:1||BIOREMEDIATION:1||Porphyrin:1||2,4,6TRICHLOROPHENOL:1||IMPEDANCE SPECTROSCOPY:1||NATURAL ORGANICMATTER:1||INSITU REMEDIATION:1||FATE:1||Acetone:1||nZVI:1||Chromate:1||HEXAVALENT CHROMIUM:1||ASPERGILLUSFUMIGATUS:1||RATIOS:1||MOUNTAINS:1||AREAS:1||PBDE MIXTURE:1||triazines:1||EFFICIENCIES:1||POLLUTANTS:1||POLYPHENOLS:1||,3TRIHYDROXYBIPHENYL:1||PUTIDA GJ31:1||BODY BURDEN:1||FUSION:1||POLYCHLORINATED PHENOLS:1||HAPs:1||animal feed:1||SERUM DIOXIN:1||ATMOSPHERIC PROCESSES:1||model:1||KINASEC ACTIVATION:1||MEMBRANE:1||ADAPTATION:1||degradation:1||FLUORENE:1||season:1||PARTICULATE MATTER:1||GRAMPOSITIVE BACTERIUM:1||PCDD/Fs (polychlorinated dibenzopdioxins and dibenzofurans):1||DGGE (denaturing gradient gel electrophoresis) analysis:1||passive air sampling:1||steel production:1||steel complex:1||RBBR:1||TEXTILE WASTEWATER:1||RISKASSESSMENT:1||TNTCONTAMINATED 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SAMPLES:1||GENECLUSTER:1||Toxicity:1||SYSTEM:1||COPLANAR PCBS:1||Bimetallic nanoparticles:1||Surface snow:1||CELLWALL:1||PAPER PULP:1||Biomass burning:1||ACTIVATEDSLUDGE SYSTEMS:1||SOURCE IDENTIFICATION:1||IRA743 resin bulk sampler:1||TAIWAN:1||OCPs:1||Ganoderma lucidum laccase:1||PLEUROTUSERYNGII:1||COLORATION:1||chlorodibenzopdioxins:1||FORESTFIRE:1||Masan Bay:1||HRGC/HRMS:1||maternal body burden:1||SOURCE DECAY:1||PEPTIDE:1||COEFFICIENT:1||very long chain bifunctional fatty acyl component:1||DIOXYGENASE:1||environmental level:1||REFUSE INCINERATION:1||FABRIC FILTER:1||COMBUSTION CONDITIONS:1||TRANSECT:1||GENETICALLYENGINEERED MICROORGANISMS:1||TERMINAL OXYGENASE COMPONENT:1||incinerator fly ash:1||plastic:1||IRONOXIDE CATALYST:1||bulk:1||PLANT:1||fine particle:1||NEWBEDFORD HARBOR:1||carbon monoxide:1||RETRIEVAL ALGORITHM:1||emission factors:1||WASTE:1||NATIONALHEALTH:1||NONDIABETIC ADULTS:1||HEALTHRISKS:1||4Fluorophenol:1||RHODOCOCCUSOPACUS:1||Pd/nFe:1||METALIONS:1||Fish:1||MAJOR UK CONURBATION:1||INDOOR AIR:1||ENDOCRINE DISRUPTING CHEMICALS:1||FUNGUS CORIOLOPSISPOLYZONA:1||DIPHENYL ETHER:1||2NDSPHERE COORDINATION:1||WHEAT BRAN:1||ELECTRONTRANSFER:1||TBBPA:1||dust:1||office:1||SIZE:1||CINCA RIVER:1||TIO2 NANOPARTICLES:1||COPPER NANOPARTICLES:1||Time trend:1||Elementary school student:1||ADULT MICE:1||TRANSITIONMETALS:1||Alginate bead:1||Oxygen release:1||Bioremediation:1||HEXACHLOROBENZENE:1||iron oxide nanoparticles:1||DIOXIDE:1||laccases:1||DIVERSITY:1||Incinerator:1||Indicator congener:1||COALTAR CREOSOTE:1||CA10:1||NHANES:1||CRYPTOCOCCUSNEOFORMANS:1||MEDIATED OXIDATION:1||General population:1||Deposition:1||Soil:1||Reductive dechlorination:1||Sphingomonas sp:1||FORMULATIONS:1||Steel complexes:1||EXTRACTION:1||SUPERCRITICALFLUID EXTRACTION:1||SOXHLET:1||HEALTH:1||LIGNIN MODELCOMPOUND:1||PHENOLICCOMPOUNDS:1||multicomponent nanoparticles:1||MAGNETICPROPERTIES:1||DITHIONITE:1||PHENYLENEDIAMINE:1||edible freshwater fish:1||ISOMERSPECIFIC DETERMINATION:1||daily intake:1||OPERATION RANCH HAND:1||HUMANMILK:1||DICHLORODIPHENYL DICHLOROETHENE DDE:1||RINGCLEAVAGE:1||DIBENZOPARADIOXINS:1||MSW INCINERATORS:1||URBAN AIR:1||NORTHAMERICAN ATMOSPHERE:1||microbial biocatalysts:1||diphenyl ether:1||Sphingomonas sp.:1||MASSSPECTROMETRY:1||dioxinlike PCBs:1||TRAMETESHIRSUTA:1||response surface methodology:1||Human health:1||DEPOSITION:1||BIOLOGICAL TREATMENT:1||ASH:1||GROWTH:1||carbon flux:1||ESI/LCMS:1||SATELLITE DATA:1||CO:1||biological removal:1||DEGRADING BACTERIUM:1||METHYLTRICLOSAN:1||RSCs:1||QUANTIFICATION:1||NONHODGKINSLYMPHOMA:1||Diabetes:1||Pseudonocardia benzenivorans:1||BACTERIALDEGRADATION:1||WASTEWATER TREATMENT:1||OXIDATIVE TRANSFORMATION:1||ONTARIO:1||SHIHWA:1||OTTAWA:1||GREATLAKES:1||MANGANESE PEROXIDASE:1||Natural organic coagulants:1||Grape seed extract:1||Syringaldehyde:1||AQUEOUSSOLUTIONS:1||GREEN RECOVERY:1||AUSTRALIA:1||Incinerator workers:1||Steel dust:1||Industrial wastes:1||MECHANISMS:1||Chemical contamination:1||Flame retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM ALGINATE:1||TDS:1||Dietary exposure:1||Zerovalent irons:1||Dechlorane plus:1||Polychlorinated biphenyls:1||Passive air sampling:1||manganese oxides:1||heavy metal ions:1||ADSORBENT:1||SYNTHETIC APPLICATIONS:1||Zinc Nanoparticles:1||PCDD/F FORMATION:1||Biotransformation:1||INCINERATOR FLYASH:1||Photocatalytic degradation:1||ENVIRONMENTAL CONCERN:1||Health risk:1||WET DEPOSITION:1||UASB REACTOR:1||Bulk deposition:1||PROFILES:1||CATALYZED OXIDATIVE POLYMERIZATION:1||CAPILLARYZONEELECTROPHORESIS:1||NATURALWATERS:1||PEPTIDES:1||ENVIRONMENTALSAMPLES:1||Pentachlorophenol:1||ELECTRONTRANSFERREACTIONS:1||TCE:1||2,2&apos:1||ANGULAR DIOXYGENATION:1||JAPANESE:1||cancer risk:1||polychlorinated dibenzopdioxins polychlorinated biphenyls:1||DIBENZOPDIOXIN:1||GENES:1||RHODOCOCCUSCHLOROPHENOLICUS:1||CEPACIA:1||PH01:1||industrial waste incinerator:1||oxidative stress:1||OCCUPATIONALEXPOSURE:1||VETERANS:1||HUMANS:1||AEROSOLS:1||VAPORPRESSURE:1||TEMPERATURE:1||STRESS:1||DENOVOSYNTHESIS:1||PARAMETERS:1||SAPONINS:1||AIRBORNE PARTICLES:1||TRENDS:1||bioremediation:1||CHLORINATED ETHENES:1||ORGANIC CONTAMINANTS:1||UK BACKGROUND AIR:1||SINTERING PLANTS:1||TSP:1||SIZE DISTRIBUTION:1||white rot fungus:1||dye decolorization:1||congenerspecific analysis:1||NUTRIENT TRANSPORT:1||human bloods:1||PLASMA:1||heavy metals:1||BIVALVES:1||isotope effect:1||GCMS:1||biomass burning:1||TRANSPORT:1||JAPAN:1||size dependent distribution of dioxin:1||gravitational SPLITT fractionation:1||marine sediment:1||INTERNAL EXPOSURE:1||CONSTRUCTION:1||PCN:1||CHLORINATED NAPHTHALENES:1||DYSFUNCTION:1||DDE:1||ENDOCRINEDISRUPTING CHEMICALS:1||SURFACE WATERS:1||Dechlorane Plus:1||Surface dust:1||INDUSTRIALAREA:1||Natural polyphenols:1||MALACHITE GREEN:1||MORINGAOLEIFERA:1||FLAVONOIDS:1||ALUMINUM:1||MT. QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX 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retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM 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QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE 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QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX MEDIATORS:2||WATERS:2||DISPERSION:2||Odor:2||OXIDE NANOPARTICLES:2||DEBROMINATION:2||SILVER NANOPARTICLES:2||Inventory:2||AROCLOR 1254:2||MIXTURE:2||polychlorinated dibenzofurans (PCDFs):2||TITANIUMDIOXIDE:2||MIXTURES:2||DEEP OCEAN:2||SWEDISH HUMANMILK:2||SERUM CONCENTRATIONS:2||Decolorization:2||Nanotoxicity:2||OUTDOOR AIR:2||THERMODYNAMIC PROPERTIES:2||LAURENTIAN GREATLAKES:2||ENVIRONMENTAL APPLICATIONS:2||PHENOLS:2||DIBENZOFURANS:2||FUNGAL LACCASES:2||AREA:2||ISLAND:2||polychlorinated dibenzopdioxins and dibenzofurans:2||ATMOSPHERIC TRANSPORT:2||polychlorinated biphenyl:2||INTERANNUAL VARIABILITY:2||TERRESTRIAL ECOSYSTEMS:2||BIOCONCENTRATION:2||ORGANICSOLVENTS:2||fly ash:2||SAMPLERS:2||SPHINGOMONASWITTICHII RW1:2||ABYSSAL OCEAN:2||MIXEDLAYER:2||carbon emission:2||Stormwater catch basin:2||WATER TREATMENT PLANTS:2||Bacterial viability:1||DLPCBs:1||PCDD/F LEVELS:1||Polybrominated diphenyl ethers (PBDEs):1||Dietary daily intake:1||STABILIZATION:1||INACTIVATION:1||Foods:1||SEAFOOD 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intake:1||OPERATION RANCH HAND:1||HUMANMILK:1||DICHLORODIPHENYL DICHLOROETHENE DDE:1||RINGCLEAVAGE:1||DIBENZOPARADIOXINS:1||MSW INCINERATORS:1||URBAN AIR:1||NORTHAMERICAN ATMOSPHERE:1||microbial biocatalysts:1||diphenyl ether:1||Sphingomonas sp.:1||MASSSPECTROMETRY:1||dioxinlike PCBs:1||TRAMETESHIRSUTA:1||response surface methodology:1||Human health:1||DEPOSITION:1||BIOLOGICAL TREATMENT:1||ASH:1||GROWTH:1||carbon flux:1||ESI/LCMS:1||SATELLITE DATA:1||CO:1||biological removal:1||DEGRADING BACTERIUM:1||METHYLTRICLOSAN:1||RSCs:1||QUANTIFICATION:1||NONHODGKINSLYMPHOMA:1||Diabetes:1||Pseudonocardia benzenivorans:1||BACTERIALDEGRADATION:1||WASTEWATER TREATMENT:1||OXIDATIVE TRANSFORMATION:1||ONTARIO:1||SHIHWA:1||OTTAWA:1||GREATLAKES:1||MANGANESE PEROXIDASE:1||Natural organic coagulants:1||Grape seed extract:1||Syringaldehyde:1||AQUEOUSSOLUTIONS:1||GREEN RECOVERY:1||AUSTRALIA:1||Incinerator workers:1||Steel dust:1||Industrial wastes:1||MECHANISMS:1||Chemical contamination:1||Flame retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM ALGINATE:1||TDS:1||Dietary exposure:1||Zerovalent irons:1||Dechlorane plus:1||Polychlorinated biphenyls:1||Passive air sampling:1||manganese oxides:1||heavy metal ions:1||ADSORBENT:1||SYNTHETIC APPLICATIONS:1||Zinc Nanoparticles:1||PCDD/F FORMATION:1||Biotransformation:1||INCINERATOR FLYASH:1||Photocatalytic degradation:1||ENVIRONMENTAL CONCERN:1||Health risk:1||WET DEPOSITION:1||UASB REACTOR:1||Bulk deposition:1||PROFILES:1||CATALYZED OXIDATIVE POLYMERIZATION:1||CAPILLARYZONEELECTROPHORESIS:1||NATURALWATERS:1||PEPTIDES:1||ENVIRONMENTALSAMPLES:1||Pentachlorophenol:1||ELECTRONTRANSFERREACTIONS:1||TCE:1||2,2&apos:1||ANGULAR DIOXYGENATION:1||JAPANESE:1||cancer risk:1||polychlorinated dibenzopdioxins polychlorinated biphenyls:1||DIBENZOPDIOXIN:1||GENES:1||RHODOCOCCUSCHLOROPHENOLICUS:1||CEPACIA:1||PH01:1||industrial waste incinerator:1||oxidative stress:1||OCCUPATIONALEXPOSURE:1||VETERANS:1||HUMANS:1||AEROSOLS:1||VAPORPRESSURE:1||TEMPERATURE:1||STRESS:1||DENOVOSYNTHESIS:1||PARAMETERS:1||SAPONINS:1||AIRBORNE PARTICLES:1||TRENDS:1||bioremediation:1||CHLORINATED ETHENES:1||ORGANIC CONTAMINANTS:1||UK BACKGROUND AIR:1||SINTERING PLANTS:1||TSP:1||SIZE DISTRIBUTION:1||white rot fungus:1||dye decolorization:1||congenerspecific analysis:1||NUTRIENT TRANSPORT:1||human bloods:1||PLASMA:1||heavy metals:1||BIVALVES:1||isotope effect:1||GCMS:1||biomass burning:1||TRANSPORT:1||JAPAN:1||size dependent distribution of dioxin:1||gravitational SPLITT fractionation:1||marine sediment:1||INTERNAL EXPOSURE:1||CONSTRUCTION:1||PCN:1||CHLORINATED NAPHTHALENES:1||DYSFUNCTION:1||DDE:1||ENDOCRINEDISRUPTING CHEMICALS:1||SURFACE WATERS:1||Dechlorane Plus:1||Surface dust:1||INDUSTRIALAREA:1||Natural polyphenols:1||MALACHITE GREEN:1||MORINGAOLEIFERA:1||FLAVONOIDS:1||ALUMINUM:1||MT. QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX MEDIATORS:2||WATERS:2||DISPERSION:2||Odor:2||OXIDE NANOPARTICLES:2||DEBROMINATION:2||SILVER NANOPARTICLES:2||Inventory:2||AROCLOR 1254:2||MIXTURE:2||polychlorinated dibenzofurans (PCDFs):2||TITANIUMDIOXIDE:2||MIXTURES:2||DEEP OCEAN:2||SWEDISH HUMANMILK:2||SERUM CONCENTRATIONS:2||Decolorization:2||Nanotoxicity:2||OUTDOOR AIR:2||THERMODYNAMIC PROPERTIES:2||LAURENTIAN GREATLAKES:2||ENVIRONMENTAL APPLICATIONS:2||PHENOLS:2||DIBENZOFURANS:2||FUNGAL LACCASES:2||AREA:2||ISLAND:2||polychlorinated dibenzopdioxins and dibenzofurans:2||ATMOSPHERIC TRANSPORT:2||polychlorinated biphenyl:2||INTERANNUAL VARIABILITY:2||TERRESTRIAL ECOSYSTEMS:2||BIOCONCENTRATION:2||ORGANICSOLVENTS:2||fly ash:2||SAMPLERS:2||SPHINGOMONASWITTICHII RW1:2||ABYSSAL OCEAN:2||MIXEDLAYER:2||carbon emission:2||Stormwater catch basin:2||WATER TREATMENT PLANTS:2||Bacterial viability:1||DLPCBs:1||PCDD/F LEVELS:1||Polybrominated diphenyl ethers (PBDEs):1||Dietary daily intake:1||STABILIZATION:1||INACTIVATION:1||Foods:1||SEAFOOD CONSUMPTION:1||DUST INGESTION:1||HYDROTHERMAL SYNTHESIS:1||laccasemediator system:1||LIGNIN:1||Metabolic intermediates:1||BIOREMEDIATION:1||Porphyrin:1||2,4,6TRICHLOROPHENOL:1||IMPEDANCE SPECTROSCOPY:1||NATURAL ORGANICMATTER:1||INSITU REMEDIATION:1||FATE:1||Acetone:1||nZVI:1||Chromate:1||HEXAVALENT CHROMIUM:1||ASPERGILLUSFUMIGATUS:1||RATIOS:1||MOUNTAINS:1||AREAS:1||PBDE MIXTURE:1||triazines:1||EFFICIENCIES:1||POLLUTANTS:1||POLYPHENOLS:1||,3TRIHYDROXYBIPHENYL:1||PUTIDA GJ31:1||BODY BURDEN:1||FUSION:1||POLYCHLORINATED PHENOLS:1||HAPs:1||animal feed:1||SERUM DIOXIN:1||ATMOSPHERIC PROCESSES:1||model:1||KINASEC ACTIVATION:1||MEMBRANE:1||ADAPTATION:1||degradation:1||FLUORENE:1||season:1||PARTICULATE MATTER:1||GRAMPOSITIVE BACTERIUM:1||PCDD/Fs (polychlorinated dibenzopdioxins and dibenzofurans):1||DGGE (denaturing gradient gel electrophoresis) analysis:1||passive air sampling:1||steel production:1||steel complex:1||RBBR:1||TEXTILE WASTEWATER:1||RISKASSESSMENT:1||TNTCONTAMINATED 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SAMPLES:1||GENECLUSTER:1||Toxicity:1||SYSTEM:1||COPLANAR PCBS:1||Bimetallic nanoparticles:1||Surface snow:1||CELLWALL:1||PAPER PULP:1||Biomass burning:1||ACTIVATEDSLUDGE SYSTEMS:1||SOURCE IDENTIFICATION:1||IRA743 resin bulk sampler:1||TAIWAN:1||OCPs:1||Ganoderma lucidum laccase:1||PLEUROTUSERYNGII:1||COLORATION:1||chlorodibenzopdioxins:1||FORESTFIRE:1||Masan Bay:1||HRGC/HRMS:1||maternal body burden:1||SOURCE DECAY:1||PEPTIDE:1||COEFFICIENT:1||very long chain bifunctional fatty acyl component:1||DIOXYGENASE:1||environmental level:1||REFUSE INCINERATION:1||FABRIC FILTER:1||COMBUSTION CONDITIONS:1||TRANSECT:1||GENETICALLYENGINEERED MICROORGANISMS:1||TERMINAL OXYGENASE COMPONENT:1||incinerator fly ash:1||plastic:1||IRONOXIDE CATALYST:1||bulk:1||PLANT:1||fine particle:1||NEWBEDFORD HARBOR:1||carbon monoxide:1||RETRIEVAL ALGORITHM:1||emission factors:1||WASTE:1||NATIONALHEALTH:1||NONDIABETIC ADULTS:1||HEALTHRISKS:1||4Fluorophenol:1||RHODOCOCCUSOPACUS:1||Pd/nFe:1||METALIONS:1||Fish:1||MAJOR UK CONURBATION:1||INDOOR AIR:1||ENDOCRINE DISRUPTING CHEMICALS:1||FUNGUS CORIOLOPSISPOLYZONA:1||DIPHENYL ETHER:1||2NDSPHERE COORDINATION:1||WHEAT BRAN:1||ELECTRONTRANSFER:1||TBBPA:1||dust:1||office:1||SIZE:1||CINCA RIVER:1||TIO2 NANOPARTICLES:1||COPPER NANOPARTICLES:1||Time trend:1||Elementary school student:1||ADULT MICE:1||TRANSITIONMETALS:1||Alginate bead:1||Oxygen release:1||Bioremediation:1||HEXACHLOROBENZENE:1||iron oxide nanoparticles:1||DIOXIDE:1||laccases:1||DIVERSITY:1||Incinerator:1||Indicator congener:1||COALTAR CREOSOTE:1||CA10:1||NHANES:1||CRYPTOCOCCUSNEOFORMANS:1||MEDIATED OXIDATION:1||General population:1||Deposition:1||Soil:1||Reductive dechlorination:1||Sphingomonas sp:1||FORMULATIONS:1||Steel complexes:1||EXTRACTION:1||SUPERCRITICALFLUID EXTRACTION:1||SOXHLET:1||HEALTH:1||LIGNIN MODELCOMPOUND:1||PHENOLICCOMPOUNDS:1||multicomponent nanoparticles:1||MAGNETICPROPERTIES:1||DITHIONITE:1||PHENYLENEDIAMINE:1||edible freshwater fish:1||ISOMERSPECIFIC DETERMINATION:1||daily intake:1||OPERATION RANCH HAND:1||HUMANMILK:1||DICHLORODIPHENYL DICHLOROETHENE DDE:1||RINGCLEAVAGE:1||DIBENZOPARADIOXINS:1||MSW INCINERATORS:1||URBAN AIR:1||NORTHAMERICAN ATMOSPHERE:1||microbial biocatalysts:1||diphenyl ether:1||Sphingomonas sp.:1||MASSSPECTROMETRY:1||dioxinlike PCBs:1||TRAMETESHIRSUTA:1||response surface methodology:1||Human health:1||DEPOSITION:1||BIOLOGICAL TREATMENT:1||ASH:1||GROWTH:1||carbon flux:1||ESI/LCMS:1||SATELLITE DATA:1||CO:1||biological removal:1||DEGRADING BACTERIUM:1||METHYLTRICLOSAN:1||RSCs:1||QUANTIFICATION:1||NONHODGKINSLYMPHOMA:1||Diabetes:1||Pseudonocardia benzenivorans:1||BACTERIALDEGRADATION:1||WASTEWATER TREATMENT:1||OXIDATIVE TRANSFORMATION:1||ONTARIO:1||SHIHWA:1||OTTAWA:1||GREATLAKES:1||MANGANESE PEROXIDASE:1||Natural organic coagulants:1||Grape seed extract:1||Syringaldehyde:1||AQUEOUSSOLUTIONS:1||GREEN RECOVERY:1||AUSTRALIA:1||Incinerator workers:1||Steel dust:1||Industrial wastes:1||MECHANISMS:1||Chemical contamination:1||Flame retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM ALGINATE:1||TDS:1||Dietary exposure:1||Zerovalent irons:1||Dechlorane plus:1||Polychlorinated biphenyls:1||Passive air sampling:1||manganese oxides:1||heavy metal ions:1||ADSORBENT:1||SYNTHETIC APPLICATIONS:1||Zinc Nanoparticles:1||PCDD/F FORMATION:1||Biotransformation:1||INCINERATOR FLYASH:1||Photocatalytic degradation:1||ENVIRONMENTAL CONCERN:1||Health risk:1||WET DEPOSITION:1||UASB REACTOR:1||Bulk deposition:1||PROFILES:1||CATALYZED OXIDATIVE POLYMERIZATION:1||CAPILLARYZONEELECTROPHORESIS:1||NATURALWATERS:1||PEPTIDES:1||ENVIRONMENTALSAMPLES:1||Pentachlorophenol:1||ELECTRONTRANSFERREACTIONS:1||TCE:1||2,2&apos:1||ANGULAR DIOXYGENATION:1||JAPANESE:1||cancer risk:1||polychlorinated dibenzopdioxins polychlorinated biphenyls:1||DIBENZOPDIOXIN:1||GENES:1||RHODOCOCCUSCHLOROPHENOLICUS:1||CEPACIA:1||PH01:1||industrial waste incinerator:1||oxidative stress:1||OCCUPATIONALEXPOSURE:1||VETERANS:1||HUMANS:1||AEROSOLS:1||VAPORPRESSURE:1||TEMPERATURE:1||STRESS:1||DENOVOSYNTHESIS:1||PARAMETERS:1||SAPONINS:1||AIRBORNE PARTICLES:1||TRENDS:1||bioremediation:1||CHLORINATED ETHENES:1||ORGANIC CONTAMINANTS:1||UK BACKGROUND AIR:1||SINTERING PLANTS:1||TSP:1||SIZE DISTRIBUTION:1||white rot fungus:1||dye decolorization:1||congenerspecific analysis:1||NUTRIENT TRANSPORT:1||human bloods:1||PLASMA:1||heavy metals:1||BIVALVES:1||isotope effect:1||GCMS:1||biomass burning:1||TRANSPORT:1||JAPAN:1||size dependent distribution of dioxin:1||gravitational SPLITT fractionation:1||marine sediment:1||INTERNAL EXPOSURE:1||CONSTRUCTION:1||PCN:1||CHLORINATED NAPHTHALENES:1||DYSFUNCTION:1||DDE:1||ENDOCRINEDISRUPTING CHEMICALS:1||SURFACE WATERS:1||Dechlorane Plus:1||Surface dust:1||INDUSTRIALAREA:1||Natural polyphenols:1||MALACHITE GREEN:1||MORINGAOLEIFERA:1||FLAVONOIDS:1||ALUMINUM:1||MT. QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX 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retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM 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QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE 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QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX MEDIATORS:2||WATERS:2||DISPERSION:2||Odor:2||OXIDE NANOPARTICLES:2||DEBROMINATION:2||SILVER NANOPARTICLES:2||Inventory:2||AROCLOR 1254:2||MIXTURE:2||polychlorinated dibenzofurans (PCDFs):2||TITANIUMDIOXIDE:2||MIXTURES:2||DEEP OCEAN:2||SWEDISH HUMANMILK:2||SERUM CONCENTRATIONS:2||Decolorization:2||Nanotoxicity:2||OUTDOOR AIR:2||THERMODYNAMIC PROPERTIES:2||LAURENTIAN GREATLAKES:2||ENVIRONMENTAL APPLICATIONS:2||PHENOLS:2||DIBENZOFURANS:2||FUNGAL LACCASES:2||AREA:2||ISLAND:2||polychlorinated dibenzopdioxins and dibenzofurans:2||ATMOSPHERIC TRANSPORT:2||polychlorinated biphenyl:2||INTERANNUAL VARIABILITY:2||TERRESTRIAL ECOSYSTEMS:2||BIOCONCENTRATION:2||ORGANICSOLVENTS:2||fly ash:2||SAMPLERS:2||SPHINGOMONASWITTICHII RW1:2||ABYSSAL OCEAN:2||MIXEDLAYER:2||carbon emission:2||Stormwater catch basin:2||WATER TREATMENT PLANTS:2||Bacterial viability:1||DLPCBs:1||PCDD/F LEVELS:1||Polybrominated diphenyl ethers (PBDEs):1||Dietary daily intake:1||STABILIZATION:1||INACTIVATION:1||Foods:1||SEAFOOD 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intake:1||OPERATION RANCH HAND:1||HUMANMILK:1||DICHLORODIPHENYL DICHLOROETHENE DDE:1||RINGCLEAVAGE:1||DIBENZOPARADIOXINS:1||MSW INCINERATORS:1||URBAN AIR:1||NORTHAMERICAN ATMOSPHERE:1||microbial biocatalysts:1||diphenyl ether:1||Sphingomonas sp.:1||MASSSPECTROMETRY:1||dioxinlike PCBs:1||TRAMETESHIRSUTA:1||response surface methodology:1||Human health:1||DEPOSITION:1||BIOLOGICAL TREATMENT:1||ASH:1||GROWTH:1||carbon flux:1||ESI/LCMS:1||SATELLITE DATA:1||CO:1||biological removal:1||DEGRADING BACTERIUM:1||METHYLTRICLOSAN:1||RSCs:1||QUANTIFICATION:1||NONHODGKINSLYMPHOMA:1||Diabetes:1||Pseudonocardia benzenivorans:1||BACTERIALDEGRADATION:1||WASTEWATER TREATMENT:1||OXIDATIVE TRANSFORMATION:1||ONTARIO:1||SHIHWA:1||OTTAWA:1||GREATLAKES:1||MANGANESE PEROXIDASE:1||Natural organic coagulants:1||Grape seed extract:1||Syringaldehyde:1||AQUEOUSSOLUTIONS:1||GREEN RECOVERY:1||AUSTRALIA:1||Incinerator workers:1||Steel dust:1||Industrial wastes:1||MECHANISMS:1||Chemical contamination:1||Flame retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM ALGINATE:1||TDS:1||Dietary exposure:1||Zerovalent irons:1||Dechlorane plus:1||Polychlorinated biphenyls:1||Passive air sampling:1||manganese oxides:1||heavy metal ions:1||ADSORBENT:1||SYNTHETIC APPLICATIONS:1||Zinc Nanoparticles:1||PCDD/F FORMATION:1||Biotransformation:1||INCINERATOR FLYASH:1||Photocatalytic degradation:1||ENVIRONMENTAL CONCERN:1||Health risk:1||WET DEPOSITION:1||UASB REACTOR:1||Bulk deposition:1||PROFILES:1||CATALYZED OXIDATIVE POLYMERIZATION:1||CAPILLARYZONEELECTROPHORESIS:1||NATURALWATERS:1||PEPTIDES:1||ENVIRONMENTALSAMPLES:1||Pentachlorophenol:1||ELECTRONTRANSFERREACTIONS:1||TCE:1||2,2&apos:1||ANGULAR DIOXYGENATION:1||JAPANESE:1||cancer risk:1||polychlorinated dibenzopdioxins polychlorinated biphenyls:1||DIBENZOPDIOXIN:1||GENES:1||RHODOCOCCUSCHLOROPHENOLICUS:1||CEPACIA:1||PH01:1||industrial waste incinerator:1||oxidative stress:1||OCCUPATIONALEXPOSURE:1||VETERANS:1||HUMANS:1||AEROSOLS:1||VAPORPRESSURE:1||TEMPERATURE:1||STRESS:1||DENOVOSYNTHESIS:1||PARAMETERS:1||SAPONINS:1||AIRBORNE PARTICLES:1||TRENDS:1||bioremediation:1||CHLORINATED ETHENES:1||ORGANIC CONTAMINANTS:1||UK BACKGROUND AIR:1||SINTERING PLANTS:1||TSP:1||SIZE DISTRIBUTION:1||white rot fungus:1||dye decolorization:1||congenerspecific analysis:1||NUTRIENT TRANSPORT:1||human bloods:1||PLASMA:1||heavy metals:1||BIVALVES:1||isotope effect:1||GCMS:1||biomass burning:1||TRANSPORT:1||JAPAN:1||size dependent distribution of dioxin:1||gravitational SPLITT fractionation:1||marine sediment:1||INTERNAL EXPOSURE:1||CONSTRUCTION:1||PCN:1||CHLORINATED NAPHTHALENES:1||DYSFUNCTION:1||DDE:1||ENDOCRINEDISRUPTING CHEMICALS:1||SURFACE WATERS:1||Dechlorane Plus:1||Surface dust:1||INDUSTRIALAREA:1||Natural polyphenols:1||MALACHITE GREEN:1||MORINGAOLEIFERA:1||FLAVONOIDS:1||ALUMINUM:1||MT. QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX MEDIATORS:2||WATERS:2||DISPERSION:2||Odor:2||OXIDE NANOPARTICLES:2||DEBROMINATION:2||SILVER NANOPARTICLES:2||Inventory:2||AROCLOR 1254:2||MIXTURE:2||polychlorinated dibenzofurans (PCDFs):2||TITANIUMDIOXIDE:2||MIXTURES:2||DEEP OCEAN:2||SWEDISH HUMANMILK:2||SERUM CONCENTRATIONS:2||Decolorization:2||Nanotoxicity:2||OUTDOOR AIR:2||THERMODYNAMIC PROPERTIES:2||LAURENTIAN GREATLAKES:2||ENVIRONMENTAL APPLICATIONS:2||PHENOLS:2||DIBENZOFURANS:2||FUNGAL LACCASES:2||AREA:2||ISLAND:2||polychlorinated dibenzopdioxins and dibenzofurans:2||ATMOSPHERIC TRANSPORT:2||polychlorinated biphenyl:2||INTERANNUAL VARIABILITY:2||TERRESTRIAL ECOSYSTEMS:2||BIOCONCENTRATION:2||ORGANICSOLVENTS:2||fly ash:2||SAMPLERS:2||SPHINGOMONASWITTICHII RW1:2||ABYSSAL OCEAN:2||MIXEDLAYER:2||carbon emission:2||Stormwater catch basin:2||WATER TREATMENT PLANTS:2||Bacterial viability:1||DLPCBs:1||PCDD/F LEVELS:1||Polybrominated diphenyl ethers (PBDEs):1||Dietary daily intake:1||STABILIZATION:1||INACTIVATION:1||Foods:1||SEAFOOD CONSUMPTION:1||DUST INGESTION:1||HYDROTHERMAL SYNTHESIS:1||laccasemediator system:1||LIGNIN:1||Metabolic intermediates:1||BIOREMEDIATION:1||Porphyrin:1||2,4,6TRICHLOROPHENOL:1||IMPEDANCE SPECTROSCOPY:1||NATURAL ORGANICMATTER:1||INSITU REMEDIATION:1||FATE:1||Acetone:1||nZVI:1||Chromate:1||HEXAVALENT CHROMIUM:1||ASPERGILLUSFUMIGATUS:1||RATIOS:1||MOUNTAINS:1||AREAS:1||PBDE MIXTURE:1||triazines:1||EFFICIENCIES:1||POLLUTANTS:1||POLYPHENOLS:1||,3TRIHYDROXYBIPHENYL:1||PUTIDA GJ31:1||BODY BURDEN:1||FUSION:1||POLYCHLORINATED PHENOLS:1||HAPs:1||animal feed:1||SERUM DIOXIN:1||ATMOSPHERIC PROCESSES:1||model:1||KINASEC ACTIVATION:1||MEMBRANE:1||ADAPTATION:1||degradation:1||FLUORENE:1||season:1||PARTICULATE MATTER:1||GRAMPOSITIVE BACTERIUM:1||PCDD/Fs (polychlorinated dibenzopdioxins and dibenzofurans):1||DGGE (denaturing gradient gel electrophoresis) analysis:1||passive air sampling:1||steel production:1||steel complex:1||RBBR:1||TEXTILE WASTEWATER:1||RISKASSESSMENT:1||TNTCONTAMINATED 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SAMPLES:1||GENECLUSTER:1||Toxicity:1||SYSTEM:1||COPLANAR PCBS:1||Bimetallic nanoparticles:1||Surface snow:1||CELLWALL:1||PAPER PULP:1||Biomass burning:1||ACTIVATEDSLUDGE SYSTEMS:1||SOURCE IDENTIFICATION:1||IRA743 resin bulk sampler:1||TAIWAN:1||OCPs:1||Ganoderma lucidum laccase:1||PLEUROTUSERYNGII:1||COLORATION:1||chlorodibenzopdioxins:1||FORESTFIRE:1||Masan Bay:1||HRGC/HRMS:1||maternal body burden:1||SOURCE DECAY:1||PEPTIDE:1||COEFFICIENT:1||very long chain bifunctional fatty acyl component:1||DIOXYGENASE:1||environmental level:1||REFUSE INCINERATION:1||FABRIC FILTER:1||COMBUSTION CONDITIONS:1||TRANSECT:1||GENETICALLYENGINEERED MICROORGANISMS:1||TERMINAL OXYGENASE COMPONENT:1||incinerator fly ash:1||plastic:1||IRONOXIDE CATALYST:1||bulk:1||PLANT:1||fine particle:1||NEWBEDFORD HARBOR:1||carbon monoxide:1||RETRIEVAL ALGORITHM:1||emission factors:1||WASTE:1||NATIONALHEALTH:1||NONDIABETIC ADULTS:1||HEALTHRISKS:1||4Fluorophenol:1||RHODOCOCCUSOPACUS:1||Pd/nFe:1||METALIONS:1||Fish:1||MAJOR UK CONURBATION:1||INDOOR AIR:1||ENDOCRINE DISRUPTING CHEMICALS:1||FUNGUS CORIOLOPSISPOLYZONA:1||DIPHENYL ETHER:1||2NDSPHERE COORDINATION:1||WHEAT BRAN:1||ELECTRONTRANSFER:1||TBBPA:1||dust:1||office:1||SIZE:1||CINCA RIVER:1||TIO2 NANOPARTICLES:1||COPPER NANOPARTICLES:1||Time trend:1||Elementary school student:1||ADULT MICE:1||TRANSITIONMETALS:1||Alginate bead:1||Oxygen release:1||Bioremediation:1||HEXACHLOROBENZENE:1||iron oxide nanoparticles:1||DIOXIDE:1||laccases:1||DIVERSITY:1||Incinerator:1||Indicator congener:1||COALTAR CREOSOTE:1||CA10:1||NHANES:1||CRYPTOCOCCUSNEOFORMANS:1||MEDIATED OXIDATION:1||General population:1||Deposition:1||Soil:1||Reductive dechlorination:1||Sphingomonas sp:1||FORMULATIONS:1||Steel complexes:1||EXTRACTION:1||SUPERCRITICALFLUID EXTRACTION:1||SOXHLET:1||HEALTH:1||LIGNIN MODELCOMPOUND:1||PHENOLICCOMPOUNDS:1||multicomponent nanoparticles:1||MAGNETICPROPERTIES:1||DITHIONITE:1||PHENYLENEDIAMINE:1||edible freshwater fish:1||ISOMERSPECIFIC DETERMINATION:1||daily intake:1||OPERATION RANCH HAND:1||HUMANMILK:1||DICHLORODIPHENYL DICHLOROETHENE DDE:1||RINGCLEAVAGE:1||DIBENZOPARADIOXINS:1||MSW INCINERATORS:1||URBAN AIR:1||NORTHAMERICAN ATMOSPHERE:1||microbial biocatalysts:1||diphenyl ether:1||Sphingomonas sp.:1||MASSSPECTROMETRY:1||dioxinlike PCBs:1||TRAMETESHIRSUTA:1||response surface methodology:1||Human health:1||DEPOSITION:1||BIOLOGICAL TREATMENT:1||ASH:1||GROWTH:1||carbon flux:1||ESI/LCMS:1||SATELLITE DATA:1||CO:1||biological removal:1||DEGRADING BACTERIUM:1||METHYLTRICLOSAN:1||RSCs:1||QUANTIFICATION:1||NONHODGKINSLYMPHOMA:1||Diabetes:1||Pseudonocardia benzenivorans:1||BACTERIALDEGRADATION:1||WASTEWATER TREATMENT:1||OXIDATIVE TRANSFORMATION:1||ONTARIO:1||SHIHWA:1||OTTAWA:1||GREATLAKES:1||MANGANESE PEROXIDASE:1||Natural organic coagulants:1||Grape seed extract:1||Syringaldehyde:1||AQUEOUSSOLUTIONS:1||GREEN RECOVERY:1||AUSTRALIA:1||Incinerator workers:1||Steel dust:1||Industrial wastes:1||MECHANISMS:1||Chemical contamination:1||Flame retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM ALGINATE:1||TDS:1||Dietary exposure:1||Zerovalent irons:1||Dechlorane plus:1||Polychlorinated biphenyls:1||Passive air sampling:1||manganese oxides:1||heavy metal ions:1||ADSORBENT:1||SYNTHETIC APPLICATIONS:1||Zinc Nanoparticles:1||PCDD/F FORMATION:1||Biotransformation:1||INCINERATOR FLYASH:1||Photocatalytic degradation:1||ENVIRONMENTAL CONCERN:1||Health risk:1||WET DEPOSITION:1||UASB REACTOR:1||Bulk deposition:1||PROFILES:1||CATALYZED OXIDATIVE POLYMERIZATION:1||CAPILLARYZONEELECTROPHORESIS:1||NATURALWATERS:1||PEPTIDES:1||ENVIRONMENTALSAMPLES:1||Pentachlorophenol:1||ELECTRONTRANSFERREACTIONS:1||TCE:1||2,2&apos:1||ANGULAR DIOXYGENATION:1||JAPANESE:1||cancer risk:1||polychlorinated dibenzopdioxins polychlorinated biphenyls:1||DIBENZOPDIOXIN:1||GENES:1||RHODOCOCCUSCHLOROPHENOLICUS:1||CEPACIA:1||PH01:1||industrial waste incinerator:1||oxidative stress:1||OCCUPATIONALEXPOSURE:1||VETERANS:1||HUMANS:1||AEROSOLS:1||VAPORPRESSURE:1||TEMPERATURE:1||STRESS:1||DENOVOSYNTHESIS:1||PARAMETERS:1||SAPONINS:1||AIRBORNE PARTICLES:1||TRENDS:1||bioremediation:1||CHLORINATED ETHENES:1||ORGANIC CONTAMINANTS:1||UK BACKGROUND AIR:1||SINTERING PLANTS:1||TSP:1||SIZE DISTRIBUTION:1||white rot fungus:1||dye decolorization:1||congenerspecific analysis:1||NUTRIENT TRANSPORT:1||human bloods:1||PLASMA:1||heavy metals:1||BIVALVES:1||isotope effect:1||GCMS:1||biomass burning:1||TRANSPORT:1||JAPAN:1||size dependent distribution of dioxin:1||gravitational SPLITT fractionation:1||marine sediment:1||INTERNAL EXPOSURE:1||CONSTRUCTION:1||PCN:1||CHLORINATED NAPHTHALENES:1||DYSFUNCTION:1||DDE:1||ENDOCRINEDISRUPTING CHEMICALS:1||SURFACE WATERS:1||Dechlorane Plus:1||Surface dust:1||INDUSTRIALAREA:1||Natural polyphenols:1||MALACHITE GREEN:1||MORINGAOLEIFERA:1||FLAVONOIDS:1||ALUMINUM:1||MT. QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX 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retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM 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QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE 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QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX MEDIATORS:2||WATERS:2||DISPERSION:2||Odor:2||OXIDE NANOPARTICLES:2||DEBROMINATION:2||SILVER NANOPARTICLES:2||Inventory:2||AROCLOR 1254:2||MIXTURE:2||polychlorinated dibenzofurans (PCDFs):2||TITANIUMDIOXIDE:2||MIXTURES:2||DEEP OCEAN:2||SWEDISH HUMANMILK:2||SERUM CONCENTRATIONS:2||Decolorization:2||Nanotoxicity:2||OUTDOOR AIR:2||THERMODYNAMIC PROPERTIES:2||LAURENTIAN GREATLAKES:2||ENVIRONMENTAL APPLICATIONS:2||PHENOLS:2||DIBENZOFURANS:2||FUNGAL LACCASES:2||AREA:2||ISLAND:2||polychlorinated dibenzopdioxins and dibenzofurans:2||ATMOSPHERIC TRANSPORT:2||polychlorinated biphenyl:2||INTERANNUAL VARIABILITY:2||TERRESTRIAL ECOSYSTEMS:2||BIOCONCENTRATION:2||ORGANICSOLVENTS:2||fly ash:2||SAMPLERS:2||SPHINGOMONASWITTICHII RW1:2||ABYSSAL OCEAN:2||MIXEDLAYER:2||carbon emission:2||Stormwater catch basin:2||WATER TREATMENT PLANTS:2||Bacterial viability:1||DLPCBs:1||PCDD/F LEVELS:1||Polybrominated diphenyl ethers (PBDEs):1||Dietary daily intake:1||STABILIZATION:1||INACTIVATION:1||Foods:1||SEAFOOD 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intake:1||OPERATION RANCH HAND:1||HUMANMILK:1||DICHLORODIPHENYL DICHLOROETHENE DDE:1||RINGCLEAVAGE:1||DIBENZOPARADIOXINS:1||MSW INCINERATORS:1||URBAN AIR:1||NORTHAMERICAN ATMOSPHERE:1||microbial biocatalysts:1||diphenyl ether:1||Sphingomonas sp.:1||MASSSPECTROMETRY:1||dioxinlike PCBs:1||TRAMETESHIRSUTA:1||response surface methodology:1||Human health:1||DEPOSITION:1||BIOLOGICAL TREATMENT:1||ASH:1||GROWTH:1||carbon flux:1||ESI/LCMS:1||SATELLITE DATA:1||CO:1||biological removal:1||DEGRADING BACTERIUM:1||METHYLTRICLOSAN:1||RSCs:1||QUANTIFICATION:1||NONHODGKINSLYMPHOMA:1||Diabetes:1||Pseudonocardia benzenivorans:1||BACTERIALDEGRADATION:1||WASTEWATER TREATMENT:1||OXIDATIVE TRANSFORMATION:1||ONTARIO:1||SHIHWA:1||OTTAWA:1||GREATLAKES:1||MANGANESE PEROXIDASE:1||Natural organic coagulants:1||Grape seed extract:1||Syringaldehyde:1||AQUEOUSSOLUTIONS:1||GREEN RECOVERY:1||AUSTRALIA:1||Incinerator workers:1||Steel dust:1||Industrial wastes:1||MECHANISMS:1||Chemical contamination:1||Flame retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM ALGINATE:1||TDS:1||Dietary exposure:1||Zerovalent irons:1||Dechlorane plus:1||Polychlorinated biphenyls:1||Passive air sampling:1||manganese oxides:1||heavy metal ions:1||ADSORBENT:1||SYNTHETIC APPLICATIONS:1||Zinc Nanoparticles:1||PCDD/F FORMATION:1||Biotransformation:1||INCINERATOR FLYASH:1||Photocatalytic degradation:1||ENVIRONMENTAL CONCERN:1||Health risk:1||WET DEPOSITION:1||UASB REACTOR:1||Bulk deposition:1||PROFILES:1||CATALYZED OXIDATIVE POLYMERIZATION:1||CAPILLARYZONEELECTROPHORESIS:1||NATURALWATERS:1||PEPTIDES:1||ENVIRONMENTALSAMPLES:1||Pentachlorophenol:1||ELECTRONTRANSFERREACTIONS:1||TCE:1||2,2&apos:1||ANGULAR DIOXYGENATION:1||JAPANESE:1||cancer risk:1||polychlorinated dibenzopdioxins polychlorinated biphenyls:1||DIBENZOPDIOXIN:1||GENES:1||RHODOCOCCUSCHLOROPHENOLICUS:1||CEPACIA:1||PH01:1||industrial waste incinerator:1||oxidative stress:1||OCCUPATIONALEXPOSURE:1||VETERANS:1||HUMANS:1||AEROSOLS:1||VAPORPRESSURE:1||TEMPERATURE:1||STRESS:1||DENOVOSYNTHESIS:1||PARAMETERS:1||SAPONINS:1||AIRBORNE PARTICLES:1||TRENDS:1||bioremediation:1||CHLORINATED ETHENES:1||ORGANIC CONTAMINANTS:1||UK BACKGROUND AIR:1||SINTERING PLANTS:1||TSP:1||SIZE DISTRIBUTION:1||white rot fungus:1||dye decolorization:1||congenerspecific analysis:1||NUTRIENT TRANSPORT:1||human bloods:1||PLASMA:1||heavy metals:1||BIVALVES:1||isotope effect:1||GCMS:1||biomass burning:1||TRANSPORT:1||JAPAN:1||size dependent distribution of dioxin:1||gravitational SPLITT fractionation:1||marine sediment:1||INTERNAL EXPOSURE:1||CONSTRUCTION:1||PCN:1||CHLORINATED NAPHTHALENES:1||DYSFUNCTION:1||DDE:1||ENDOCRINEDISRUPTING CHEMICALS:1||SURFACE WATERS:1||Dechlorane Plus:1||Surface dust:1||INDUSTRIALAREA:1||Natural polyphenols:1||MALACHITE GREEN:1||MORINGAOLEIFERA:1||FLAVONOIDS:1||ALUMINUM:1||MT. QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX MEDIATORS:2||WATERS:2||DISPERSION:2||Odor:2||OXIDE NANOPARTICLES:2||DEBROMINATION:2||SILVER NANOPARTICLES:2||Inventory:2||AROCLOR 1254:2||MIXTURE:2||polychlorinated dibenzofurans (PCDFs):2||TITANIUMDIOXIDE:2||MIXTURES:2||DEEP OCEAN:2||SWEDISH HUMANMILK:2||SERUM CONCENTRATIONS:2||Decolorization:2||Nanotoxicity:2||OUTDOOR AIR:2||THERMODYNAMIC PROPERTIES:2||LAURENTIAN GREATLAKES:2||ENVIRONMENTAL APPLICATIONS:2||PHENOLS:2||DIBENZOFURANS:2||FUNGAL LACCASES:2||AREA:2||ISLAND:2||polychlorinated dibenzopdioxins and dibenzofurans:2||ATMOSPHERIC TRANSPORT:2||polychlorinated biphenyl:2||INTERANNUAL VARIABILITY:2||TERRESTRIAL ECOSYSTEMS:2||BIOCONCENTRATION:2||ORGANICSOLVENTS:2||fly ash:2||SAMPLERS:2||SPHINGOMONASWITTICHII RW1:2||ABYSSAL OCEAN:2||MIXEDLAYER:2||carbon emission:2||Stormwater catch basin:2||WATER TREATMENT PLANTS:2||Bacterial viability:1||DLPCBs:1||PCDD/F LEVELS:1||Polybrominated diphenyl ethers (PBDEs):1||Dietary daily intake:1||STABILIZATION:1||INACTIVATION:1||Foods:1||SEAFOOD CONSUMPTION:1||DUST INGESTION:1||HYDROTHERMAL SYNTHESIS:1||laccasemediator system:1||LIGNIN:1||Metabolic intermediates:1||BIOREMEDIATION:1||Porphyrin:1||2,4,6TRICHLOROPHENOL:1||IMPEDANCE SPECTROSCOPY:1||NATURAL ORGANICMATTER:1||INSITU REMEDIATION:1||FATE:1||Acetone:1||nZVI:1||Chromate:1||HEXAVALENT CHROMIUM:1||ASPERGILLUSFUMIGATUS:1||RATIOS:1||MOUNTAINS:1||AREAS:1||PBDE MIXTURE:1||triazines:1||EFFICIENCIES:1||POLLUTANTS:1||POLYPHENOLS:1||,3TRIHYDROXYBIPHENYL:1||PUTIDA GJ31:1||BODY BURDEN:1||FUSION:1||POLYCHLORINATED PHENOLS:1||HAPs:1||animal feed:1||SERUM DIOXIN:1||ATMOSPHERIC PROCESSES:1||model:1||KINASEC ACTIVATION:1||MEMBRANE:1||ADAPTATION:1||degradation:1||FLUORENE:1||season:1||PARTICULATE MATTER:1||GRAMPOSITIVE BACTERIUM:1||PCDD/Fs (polychlorinated dibenzopdioxins and dibenzofurans):1||DGGE (denaturing gradient gel electrophoresis) analysis:1||passive air sampling:1||steel production:1||steel complex:1||RBBR:1||TEXTILE WASTEWATER:1||RISKASSESSMENT:1||TNTCONTAMINATED 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SAMPLES:1||GENECLUSTER:1||Toxicity:1||SYSTEM:1||COPLANAR PCBS:1||Bimetallic nanoparticles:1||Surface snow:1||CELLWALL:1||PAPER PULP:1||Biomass burning:1||ACTIVATEDSLUDGE SYSTEMS:1||SOURCE IDENTIFICATION:1||IRA743 resin bulk sampler:1||TAIWAN:1||OCPs:1||Ganoderma lucidum laccase:1||PLEUROTUSERYNGII:1||COLORATION:1||chlorodibenzopdioxins:1||FORESTFIRE:1||Masan Bay:1||HRGC/HRMS:1||maternal body burden:1||SOURCE DECAY:1||PEPTIDE:1||COEFFICIENT:1||very long chain bifunctional fatty acyl component:1||DIOXYGENASE:1||environmental level:1||REFUSE INCINERATION:1||FABRIC FILTER:1||COMBUSTION CONDITIONS:1||TRANSECT:1||GENETICALLYENGINEERED MICROORGANISMS:1||TERMINAL OXYGENASE COMPONENT:1||incinerator fly ash:1||plastic:1||IRONOXIDE CATALYST:1||bulk:1||PLANT:1||fine particle:1||NEWBEDFORD HARBOR:1||carbon monoxide:1||RETRIEVAL ALGORITHM:1||emission factors:1||WASTE:1||NATIONALHEALTH:1||NONDIABETIC ADULTS:1||HEALTHRISKS:1||4Fluorophenol:1||RHODOCOCCUSOPACUS:1||Pd/nFe:1||METALIONS:1||Fish:1||MAJOR UK CONURBATION:1||INDOOR AIR:1||ENDOCRINE DISRUPTING CHEMICALS:1||FUNGUS CORIOLOPSISPOLYZONA:1||DIPHENYL ETHER:1||2NDSPHERE COORDINATION:1||WHEAT BRAN:1||ELECTRONTRANSFER:1||TBBPA:1||dust:1||office:1||SIZE:1||CINCA RIVER:1||TIO2 NANOPARTICLES:1||COPPER NANOPARTICLES:1||Time trend:1||Elementary school student:1||ADULT MICE:1||TRANSITIONMETALS:1||Alginate bead:1||Oxygen release:1||Bioremediation:1||HEXACHLOROBENZENE:1||iron oxide nanoparticles:1||DIOXIDE:1||laccases:1||DIVERSITY:1||Incinerator:1||Indicator congener:1||COALTAR CREOSOTE:1||CA10:1||NHANES:1||CRYPTOCOCCUSNEOFORMANS:1||MEDIATED OXIDATION:1||General population:1||Deposition:1||Soil:1||Reductive dechlorination:1||Sphingomonas sp:1||FORMULATIONS:1||Steel complexes:1||EXTRACTION:1||SUPERCRITICALFLUID EXTRACTION:1||SOXHLET:1||HEALTH:1||LIGNIN MODELCOMPOUND:1||PHENOLICCOMPOUNDS:1||multicomponent nanoparticles:1||MAGNETICPROPERTIES:1||DITHIONITE:1||PHENYLENEDIAMINE:1||edible freshwater fish:1||ISOMERSPECIFIC DETERMINATION:1||daily intake:1||OPERATION RANCH HAND:1||HUMANMILK:1||DICHLORODIPHENYL DICHLOROETHENE DDE:1||RINGCLEAVAGE:1||DIBENZOPARADIOXINS:1||MSW INCINERATORS:1||URBAN AIR:1||NORTHAMERICAN ATMOSPHERE:1||microbial biocatalysts:1||diphenyl ether:1||Sphingomonas sp.:1||MASSSPECTROMETRY:1||dioxinlike PCBs:1||TRAMETESHIRSUTA:1||response surface methodology:1||Human health:1||DEPOSITION:1||BIOLOGICAL TREATMENT:1||ASH:1||GROWTH:1||carbon flux:1||ESI/LCMS:1||SATELLITE DATA:1||CO:1||biological removal:1||DEGRADING BACTERIUM:1||METHYLTRICLOSAN:1||RSCs:1||QUANTIFICATION:1||NONHODGKINSLYMPHOMA:1||Diabetes:1||Pseudonocardia benzenivorans:1||BACTERIALDEGRADATION:1||WASTEWATER TREATMENT:1||OXIDATIVE TRANSFORMATION:1||ONTARIO:1||SHIHWA:1||OTTAWA:1||GREATLAKES:1||MANGANESE PEROXIDASE:1||Natural organic coagulants:1||Grape seed extract:1||Syringaldehyde:1||AQUEOUSSOLUTIONS:1||GREEN RECOVERY:1||AUSTRALIA:1||Incinerator workers:1||Steel dust:1||Industrial wastes:1||MECHANISMS:1||Chemical contamination:1||Flame retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM ALGINATE:1||TDS:1||Dietary exposure:1||Zerovalent irons:1||Dechlorane plus:1||Polychlorinated biphenyls:1||Passive air sampling:1||manganese oxides:1||heavy metal ions:1||ADSORBENT:1||SYNTHETIC APPLICATIONS:1||Zinc Nanoparticles:1||PCDD/F FORMATION:1||Biotransformation:1||INCINERATOR FLYASH:1||Photocatalytic degradation:1||ENVIRONMENTAL CONCERN:1||Health risk:1||WET DEPOSITION:1||UASB REACTOR:1||Bulk deposition:1||PROFILES:1||CATALYZED OXIDATIVE POLYMERIZATION:1||CAPILLARYZONEELECTROPHORESIS:1||NATURALWATERS:1||PEPTIDES:1||ENVIRONMENTALSAMPLES:1||Pentachlorophenol:1||ELECTRONTRANSFERREACTIONS:1||TCE:1||2,2&apos:1||ANGULAR DIOXYGENATION:1||JAPANESE:1||cancer risk:1||polychlorinated dibenzopdioxins polychlorinated biphenyls:1||DIBENZOPDIOXIN:1||GENES:1||RHODOCOCCUSCHLOROPHENOLICUS:1||CEPACIA:1||PH01:1||industrial waste incinerator:1||oxidative stress:1||OCCUPATIONALEXPOSURE:1||VETERANS:1||HUMANS:1||AEROSOLS:1||VAPORPRESSURE:1||TEMPERATURE:1||STRESS:1||DENOVOSYNTHESIS:1||PARAMETERS:1||SAPONINS:1||AIRBORNE PARTICLES:1||TRENDS:1||bioremediation:1||CHLORINATED ETHENES:1||ORGANIC CONTAMINANTS:1||UK BACKGROUND AIR:1||SINTERING PLANTS:1||TSP:1||SIZE DISTRIBUTION:1||white rot fungus:1||dye decolorization:1||congenerspecific analysis:1||NUTRIENT TRANSPORT:1||human bloods:1||PLASMA:1||heavy metals:1||BIVALVES:1||isotope effect:1||GCMS:1||biomass burning:1||TRANSPORT:1||JAPAN:1||size dependent distribution of dioxin:1||gravitational SPLITT fractionation:1||marine sediment:1||INTERNAL EXPOSURE:1||CONSTRUCTION:1||PCN:1||CHLORINATED NAPHTHALENES:1||DYSFUNCTION:1||DDE:1||ENDOCRINEDISRUPTING CHEMICALS:1||SURFACE WATERS:1||Dechlorane Plus:1||Surface dust:1||INDUSTRIALAREA:1||Natural polyphenols:1||MALACHITE GREEN:1||MORINGAOLEIFERA:1||FLAVONOIDS:1||ALUMINUM:1||MT. QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX 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retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM 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QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE 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QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX MEDIATORS:2||WATERS:2||DISPERSION:2||Odor:2||OXIDE NANOPARTICLES:2||DEBROMINATION:2||SILVER NANOPARTICLES:2||Inventory:2||AROCLOR 1254:2||MIXTURE:2||polychlorinated dibenzofurans (PCDFs):2||TITANIUMDIOXIDE:2||MIXTURES:2||DEEP OCEAN:2||SWEDISH HUMANMILK:2||SERUM CONCENTRATIONS:2||Decolorization:2||Nanotoxicity:2||OUTDOOR AIR:2||THERMODYNAMIC PROPERTIES:2||LAURENTIAN GREATLAKES:2||ENVIRONMENTAL APPLICATIONS:2||PHENOLS:2||DIBENZOFURANS:2||FUNGAL LACCASES:2||AREA:2||ISLAND:2||polychlorinated dibenzopdioxins and dibenzofurans:2||ATMOSPHERIC TRANSPORT:2||polychlorinated biphenyl:2||INTERANNUAL VARIABILITY:2||TERRESTRIAL ECOSYSTEMS:2||BIOCONCENTRATION:2||ORGANICSOLVENTS:2||fly ash:2||SAMPLERS:2||SPHINGOMONASWITTICHII RW1:2||ABYSSAL OCEAN:2||MIXEDLAYER:2||carbon emission:2||Stormwater catch basin:2||WATER TREATMENT PLANTS:2||Bacterial viability:1||DLPCBs:1||PCDD/F LEVELS:1||Polybrominated diphenyl ethers (PBDEs):1||Dietary daily intake:1||STABILIZATION:1||INACTIVATION:1||Foods:1||SEAFOOD 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intake:1||OPERATION RANCH HAND:1||HUMANMILK:1||DICHLORODIPHENYL DICHLOROETHENE DDE:1||RINGCLEAVAGE:1||DIBENZOPARADIOXINS:1||MSW INCINERATORS:1||URBAN AIR:1||NORTHAMERICAN ATMOSPHERE:1||microbial biocatalysts:1||diphenyl ether:1||Sphingomonas sp.:1||MASSSPECTROMETRY:1||dioxinlike PCBs:1||TRAMETESHIRSUTA:1||response surface methodology:1||Human health:1||DEPOSITION:1||BIOLOGICAL TREATMENT:1||ASH:1||GROWTH:1||carbon flux:1||ESI/LCMS:1||SATELLITE DATA:1||CO:1||biological removal:1||DEGRADING BACTERIUM:1||METHYLTRICLOSAN:1||RSCs:1||QUANTIFICATION:1||NONHODGKINSLYMPHOMA:1||Diabetes:1||Pseudonocardia benzenivorans:1||BACTERIALDEGRADATION:1||WASTEWATER TREATMENT:1||OXIDATIVE TRANSFORMATION:1||ONTARIO:1||SHIHWA:1||OTTAWA:1||GREATLAKES:1||MANGANESE PEROXIDASE:1||Natural organic coagulants:1||Grape seed extract:1||Syringaldehyde:1||AQUEOUSSOLUTIONS:1||GREEN RECOVERY:1||AUSTRALIA:1||Incinerator workers:1||Steel dust:1||Industrial wastes:1||MECHANISMS:1||Chemical contamination:1||Flame retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM ALGINATE:1||TDS:1||Dietary exposure:1||Zerovalent irons:1||Dechlorane plus:1||Polychlorinated biphenyls:1||Passive air sampling:1||manganese oxides:1||heavy metal ions:1||ADSORBENT:1||SYNTHETIC APPLICATIONS:1||Zinc Nanoparticles:1||PCDD/F FORMATION:1||Biotransformation:1||INCINERATOR FLYASH:1||Photocatalytic degradation:1||ENVIRONMENTAL CONCERN:1||Health risk:1||WET DEPOSITION:1||UASB REACTOR:1||Bulk deposition:1||PROFILES:1||CATALYZED OXIDATIVE POLYMERIZATION:1||CAPILLARYZONEELECTROPHORESIS:1||NATURALWATERS:1||PEPTIDES:1||ENVIRONMENTALSAMPLES:1||Pentachlorophenol:1||ELECTRONTRANSFERREACTIONS:1||TCE:1||2,2&apos:1||ANGULAR DIOXYGENATION:1||JAPANESE:1||cancer risk:1||polychlorinated dibenzopdioxins polychlorinated biphenyls:1||DIBENZOPDIOXIN:1||GENES:1||RHODOCOCCUSCHLOROPHENOLICUS:1||CEPACIA:1||PH01:1||industrial waste incinerator:1||oxidative stress:1||OCCUPATIONALEXPOSURE:1||VETERANS:1||HUMANS:1||AEROSOLS:1||VAPORPRESSURE:1||TEMPERATURE:1||STRESS:1||DENOVOSYNTHESIS:1||PARAMETERS:1||SAPONINS:1||AIRBORNE PARTICLES:1||TRENDS:1||bioremediation:1||CHLORINATED ETHENES:1||ORGANIC CONTAMINANTS:1||UK BACKGROUND AIR:1||SINTERING PLANTS:1||TSP:1||SIZE DISTRIBUTION:1||white rot fungus:1||dye decolorization:1||congenerspecific analysis:1||NUTRIENT TRANSPORT:1||human bloods:1||PLASMA:1||heavy metals:1||BIVALVES:1||isotope effect:1||GCMS:1||biomass burning:1||TRANSPORT:1||JAPAN:1||size dependent distribution of dioxin:1||gravitational SPLITT fractionation:1||marine sediment:1||INTERNAL EXPOSURE:1||CONSTRUCTION:1||PCN:1||CHLORINATED NAPHTHALENES:1||DYSFUNCTION:1||DDE:1||ENDOCRINEDISRUPTING CHEMICALS:1||SURFACE WATERS:1||Dechlorane Plus:1||Surface dust:1||INDUSTRIALAREA:1||Natural polyphenols:1||MALACHITE GREEN:1||MORINGAOLEIFERA:1||FLAVONOIDS:1||ALUMINUM:1||MT. QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX MEDIATORS:2||WATERS:2||DISPERSION:2||Odor:2||OXIDE NANOPARTICLES:2||DEBROMINATION:2||SILVER NANOPARTICLES:2||Inventory:2||AROCLOR 1254:2||MIXTURE:2||polychlorinated dibenzofurans (PCDFs):2||TITANIUMDIOXIDE:2||MIXTURES:2||DEEP OCEAN:2||SWEDISH HUMANMILK:2||SERUM CONCENTRATIONS:2||Decolorization:2||Nanotoxicity:2||OUTDOOR AIR:2||THERMODYNAMIC PROPERTIES:2||LAURENTIAN GREATLAKES:2||ENVIRONMENTAL APPLICATIONS:2||PHENOLS:2||DIBENZOFURANS:2||FUNGAL LACCASES:2||AREA:2||ISLAND:2||polychlorinated dibenzopdioxins and dibenzofurans:2||ATMOSPHERIC TRANSPORT:2||polychlorinated biphenyl:2||INTERANNUAL VARIABILITY:2||TERRESTRIAL ECOSYSTEMS:2||BIOCONCENTRATION:2||ORGANICSOLVENTS:2||fly ash:2||SAMPLERS:2||SPHINGOMONASWITTICHII RW1:2||ABYSSAL OCEAN:2||MIXEDLAYER:2||carbon emission:2||Stormwater catch basin:2||WATER TREATMENT PLANTS:2||Bacterial viability:1||DLPCBs:1||PCDD/F LEVELS:1||Polybrominated diphenyl ethers (PBDEs):1||Dietary daily intake:1||STABILIZATION:1||INACTIVATION:1||Foods:1||SEAFOOD CONSUMPTION:1||DUST INGESTION:1||HYDROTHERMAL SYNTHESIS:1||laccasemediator system:1||LIGNIN:1||Metabolic intermediates:1||BIOREMEDIATION:1||Porphyrin:1||2,4,6TRICHLOROPHENOL:1||IMPEDANCE SPECTROSCOPY:1||NATURAL ORGANICMATTER:1||INSITU REMEDIATION:1||FATE:1||Acetone:1||nZVI:1||Chromate:1||HEXAVALENT CHROMIUM:1||ASPERGILLUSFUMIGATUS:1||RATIOS:1||MOUNTAINS:1||AREAS:1||PBDE MIXTURE:1||triazines:1||EFFICIENCIES:1||POLLUTANTS:1||POLYPHENOLS:1||,3TRIHYDROXYBIPHENYL:1||PUTIDA GJ31:1||BODY BURDEN:1||FUSION:1||POLYCHLORINATED PHENOLS:1||HAPs:1||animal feed:1||SERUM DIOXIN:1||ATMOSPHERIC PROCESSES:1||model:1||KINASEC ACTIVATION:1||MEMBRANE:1||ADAPTATION:1||degradation:1||FLUORENE:1||season:1||PARTICULATE MATTER:1||GRAMPOSITIVE BACTERIUM:1||PCDD/Fs (polychlorinated dibenzopdioxins and dibenzofurans):1||DGGE (denaturing gradient gel electrophoresis) analysis:1||passive air sampling:1||steel production:1||steel complex:1||RBBR:1||TEXTILE WASTEWATER:1||RISKASSESSMENT:1||TNTCONTAMINATED 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SAMPLES:1||GENECLUSTER:1||Toxicity:1||SYSTEM:1||COPLANAR PCBS:1||Bimetallic nanoparticles:1||Surface snow:1||CELLWALL:1||PAPER PULP:1||Biomass burning:1||ACTIVATEDSLUDGE SYSTEMS:1||SOURCE IDENTIFICATION:1||IRA743 resin bulk sampler:1||TAIWAN:1||OCPs:1||Ganoderma lucidum laccase:1||PLEUROTUSERYNGII:1||COLORATION:1||chlorodibenzopdioxins:1||FORESTFIRE:1||Masan Bay:1||HRGC/HRMS:1||maternal body burden:1||SOURCE DECAY:1||PEPTIDE:1||COEFFICIENT:1||very long chain bifunctional fatty acyl component:1||DIOXYGENASE:1||environmental level:1||REFUSE INCINERATION:1||FABRIC FILTER:1||COMBUSTION CONDITIONS:1||TRANSECT:1||GENETICALLYENGINEERED MICROORGANISMS:1||TERMINAL OXYGENASE COMPONENT:1||incinerator fly ash:1||plastic:1||IRONOXIDE CATALYST:1||bulk:1||PLANT:1||fine particle:1||NEWBEDFORD HARBOR:1||carbon monoxide:1||RETRIEVAL ALGORITHM:1||emission factors:1||WASTE:1||NATIONALHEALTH:1||NONDIABETIC ADULTS:1||HEALTHRISKS:1||4Fluorophenol:1||RHODOCOCCUSOPACUS:1||Pd/nFe:1||METALIONS:1||Fish:1||MAJOR UK CONURBATION:1||INDOOR AIR:1||ENDOCRINE DISRUPTING CHEMICALS:1||FUNGUS CORIOLOPSISPOLYZONA:1||DIPHENYL ETHER:1||2NDSPHERE COORDINATION:1||WHEAT BRAN:1||ELECTRONTRANSFER:1||TBBPA:1||dust:1||office:1||SIZE:1||CINCA RIVER:1||TIO2 NANOPARTICLES:1||COPPER NANOPARTICLES:1||Time trend:1||Elementary school student:1||ADULT MICE:1||TRANSITIONMETALS:1||Alginate bead:1||Oxygen release:1||Bioremediation:1||HEXACHLOROBENZENE:1||iron oxide nanoparticles:1||DIOXIDE:1||laccases:1||DIVERSITY:1||Incinerator:1||Indicator congener:1||COALTAR CREOSOTE:1||CA10:1||NHANES:1||CRYPTOCOCCUSNEOFORMANS:1||MEDIATED OXIDATION:1||General population:1||Deposition:1||Soil:1||Reductive dechlorination:1||Sphingomonas sp:1||FORMULATIONS:1||Steel complexes:1||EXTRACTION:1||SUPERCRITICALFLUID EXTRACTION:1||SOXHLET:1||HEALTH:1||LIGNIN MODELCOMPOUND:1||PHENOLICCOMPOUNDS:1||multicomponent nanoparticles:1||MAGNETICPROPERTIES:1||DITHIONITE:1||PHENYLENEDIAMINE:1||edible freshwater fish:1||ISOMERSPECIFIC DETERMINATION:1||daily intake:1||OPERATION RANCH HAND:1||HUMANMILK:1||DICHLORODIPHENYL DICHLOROETHENE DDE:1||RINGCLEAVAGE:1||DIBENZOPARADIOXINS:1||MSW INCINERATORS:1||URBAN AIR:1||NORTHAMERICAN ATMOSPHERE:1||microbial biocatalysts:1||diphenyl ether:1||Sphingomonas sp.:1||MASSSPECTROMETRY:1||dioxinlike PCBs:1||TRAMETESHIRSUTA:1||response surface methodology:1||Human health:1||DEPOSITION:1||BIOLOGICAL TREATMENT:1||ASH:1||GROWTH:1||carbon flux:1||ESI/LCMS:1||SATELLITE DATA:1||CO:1||biological removal:1||DEGRADING BACTERIUM:1||METHYLTRICLOSAN:1||RSCs:1||QUANTIFICATION:1||NONHODGKINSLYMPHOMA:1||Diabetes:1||Pseudonocardia benzenivorans:1||BACTERIALDEGRADATION:1||WASTEWATER TREATMENT:1||OXIDATIVE TRANSFORMATION:1||ONTARIO:1||SHIHWA:1||OTTAWA:1||GREATLAKES:1||MANGANESE PEROXIDASE:1||Natural organic coagulants:1||Grape seed extract:1||Syringaldehyde:1||AQUEOUSSOLUTIONS:1||GREEN RECOVERY:1||AUSTRALIA:1||Incinerator workers:1||Steel dust:1||Industrial wastes:1||MECHANISMS:1||Chemical contamination:1||Flame retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM ALGINATE:1||TDS:1||Dietary exposure:1||Zerovalent irons:1||Dechlorane plus:1||Polychlorinated biphenyls:1||Passive air sampling:1||manganese oxides:1||heavy metal ions:1||ADSORBENT:1||SYNTHETIC APPLICATIONS:1||Zinc Nanoparticles:1||PCDD/F FORMATION:1||Biotransformation:1||INCINERATOR FLYASH:1||Photocatalytic degradation:1||ENVIRONMENTAL CONCERN:1||Health risk:1||WET DEPOSITION:1||UASB REACTOR:1||Bulk deposition:1||PROFILES:1||CATALYZED OXIDATIVE POLYMERIZATION:1||CAPILLARYZONEELECTROPHORESIS:1||NATURALWATERS:1||PEPTIDES:1||ENVIRONMENTALSAMPLES:1||Pentachlorophenol:1||ELECTRONTRANSFERREACTIONS:1||TCE:1||2,2&apos:1||ANGULAR DIOXYGENATION:1||JAPANESE:1||cancer risk:1||polychlorinated dibenzopdioxins polychlorinated biphenyls:1||DIBENZOPDIOXIN:1||GENES:1||RHODOCOCCUSCHLOROPHENOLICUS:1||CEPACIA:1||PH01:1||industrial waste incinerator:1||oxidative stress:1||OCCUPATIONALEXPOSURE:1||VETERANS:1||HUMANS:1||AEROSOLS:1||VAPORPRESSURE:1||TEMPERATURE:1||STRESS:1||DENOVOSYNTHESIS:1||PARAMETERS:1||SAPONINS:1||AIRBORNE PARTICLES:1||TRENDS:1||bioremediation:1||CHLORINATED ETHENES:1||ORGANIC CONTAMINANTS:1||UK BACKGROUND AIR:1||SINTERING PLANTS:1||TSP:1||SIZE DISTRIBUTION:1||white rot fungus:1||dye decolorization:1||congenerspecific analysis:1||NUTRIENT TRANSPORT:1||human bloods:1||PLASMA:1||heavy metals:1||BIVALVES:1||isotope effect:1||GCMS:1||biomass burning:1||TRANSPORT:1||JAPAN:1||size dependent distribution of dioxin:1||gravitational SPLITT fractionation:1||marine sediment:1||INTERNAL EXPOSURE:1||CONSTRUCTION:1||PCN:1||CHLORINATED NAPHTHALENES:1||DYSFUNCTION:1||DDE:1||ENDOCRINEDISRUPTING CHEMICALS:1||SURFACE WATERS:1||Dechlorane Plus:1||Surface dust:1||INDUSTRIALAREA:1||Natural polyphenols:1||MALACHITE GREEN:1||MORINGAOLEIFERA:1||FLAVONOIDS:1||ALUMINUM:1||MT. QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX 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retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM 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QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE 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QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX MEDIATORS:2||WATERS:2||DISPERSION:2||Odor:2||OXIDE NANOPARTICLES:2||DEBROMINATION:2||SILVER NANOPARTICLES:2||Inventory:2||AROCLOR 1254:2||MIXTURE:2||polychlorinated dibenzofurans (PCDFs):2||TITANIUMDIOXIDE:2||MIXTURES:2||DEEP OCEAN:2||SWEDISH HUMANMILK:2||SERUM CONCENTRATIONS:2||Decolorization:2||Nanotoxicity:2||OUTDOOR AIR:2||THERMODYNAMIC PROPERTIES:2||LAURENTIAN GREATLAKES:2||ENVIRONMENTAL APPLICATIONS:2||PHENOLS:2||DIBENZOFURANS:2||FUNGAL LACCASES:2||AREA:2||ISLAND:2||polychlorinated dibenzopdioxins and dibenzofurans:2||ATMOSPHERIC TRANSPORT:2||polychlorinated biphenyl:2||INTERANNUAL VARIABILITY:2||TERRESTRIAL ECOSYSTEMS:2||BIOCONCENTRATION:2||ORGANICSOLVENTS:2||fly ash:2||SAMPLERS:2||SPHINGOMONASWITTICHII RW1:2||ABYSSAL OCEAN:2||MIXEDLAYER:2||carbon emission:2||Stormwater catch basin:2||WATER TREATMENT PLANTS:2||Bacterial viability:1||DLPCBs:1||PCDD/F LEVELS:1||Polybrominated diphenyl ethers (PBDEs):1||Dietary daily intake:1||STABILIZATION:1||INACTIVATION:1||Foods:1||SEAFOOD 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intake:1||OPERATION RANCH HAND:1||HUMANMILK:1||DICHLORODIPHENYL DICHLOROETHENE DDE:1||RINGCLEAVAGE:1||DIBENZOPARADIOXINS:1||MSW INCINERATORS:1||URBAN AIR:1||NORTHAMERICAN ATMOSPHERE:1||microbial biocatalysts:1||diphenyl ether:1||Sphingomonas sp.:1||MASSSPECTROMETRY:1||dioxinlike PCBs:1||TRAMETESHIRSUTA:1||response surface methodology:1||Human health:1||DEPOSITION:1||BIOLOGICAL TREATMENT:1||ASH:1||GROWTH:1||carbon flux:1||ESI/LCMS:1||SATELLITE DATA:1||CO:1||biological removal:1||DEGRADING BACTERIUM:1||METHYLTRICLOSAN:1||RSCs:1||QUANTIFICATION:1||NONHODGKINSLYMPHOMA:1||Diabetes:1||Pseudonocardia benzenivorans:1||BACTERIALDEGRADATION:1||WASTEWATER TREATMENT:1||OXIDATIVE TRANSFORMATION:1||ONTARIO:1||SHIHWA:1||OTTAWA:1||GREATLAKES:1||MANGANESE PEROXIDASE:1||Natural organic coagulants:1||Grape seed extract:1||Syringaldehyde:1||AQUEOUSSOLUTIONS:1||GREEN RECOVERY:1||AUSTRALIA:1||Incinerator workers:1||Steel dust:1||Industrial wastes:1||MECHANISMS:1||Chemical contamination:1||Flame retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM ALGINATE:1||TDS:1||Dietary exposure:1||Zerovalent irons:1||Dechlorane plus:1||Polychlorinated biphenyls:1||Passive air sampling:1||manganese oxides:1||heavy metal ions:1||ADSORBENT:1||SYNTHETIC APPLICATIONS:1||Zinc Nanoparticles:1||PCDD/F FORMATION:1||Biotransformation:1||INCINERATOR FLYASH:1||Photocatalytic degradation:1||ENVIRONMENTAL CONCERN:1||Health risk:1||WET DEPOSITION:1||UASB REACTOR:1||Bulk deposition:1||PROFILES:1||CATALYZED OXIDATIVE POLYMERIZATION:1||CAPILLARYZONEELECTROPHORESIS:1||NATURALWATERS:1||PEPTIDES:1||ENVIRONMENTALSAMPLES:1||Pentachlorophenol:1||ELECTRONTRANSFERREACTIONS:1||TCE:1||2,2&apos:1||ANGULAR DIOXYGENATION:1||JAPANESE:1||cancer risk:1||polychlorinated dibenzopdioxins polychlorinated biphenyls:1||DIBENZOPDIOXIN:1||GENES:1||RHODOCOCCUSCHLOROPHENOLICUS:1||CEPACIA:1||PH01:1||industrial waste incinerator:1||oxidative stress:1||OCCUPATIONALEXPOSURE:1||VETERANS:1||HUMANS:1||AEROSOLS:1||VAPORPRESSURE:1||TEMPERATURE:1||STRESS:1||DENOVOSYNTHESIS:1||PARAMETERS:1||SAPONINS:1||AIRBORNE PARTICLES:1||TRENDS:1||bioremediation:1||CHLORINATED ETHENES:1||ORGANIC CONTAMINANTS:1||UK BACKGROUND AIR:1||SINTERING PLANTS:1||TSP:1||SIZE DISTRIBUTION:1||white rot fungus:1||dye decolorization:1||congenerspecific analysis:1||NUTRIENT TRANSPORT:1||human bloods:1||PLASMA:1||heavy metals:1||BIVALVES:1||isotope effect:1||GCMS:1||biomass burning:1||TRANSPORT:1||JAPAN:1||size dependent distribution of dioxin:1||gravitational SPLITT fractionation:1||marine sediment:1||INTERNAL EXPOSURE:1||CONSTRUCTION:1||PCN:1||CHLORINATED NAPHTHALENES:1||DYSFUNCTION:1||DDE:1||ENDOCRINEDISRUPTING CHEMICALS:1||SURFACE WATERS:1||Dechlorane Plus:1||Surface dust:1||INDUSTRIALAREA:1||Natural polyphenols:1||MALACHITE GREEN:1||MORINGAOLEIFERA:1||FLAVONOIDS:1||ALUMINUM:1||MT. QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX MEDIATORS:2||WATERS:2||DISPERSION:2||Odor:2||OXIDE NANOPARTICLES:2||DEBROMINATION:2||SILVER NANOPARTICLES:2||Inventory:2||AROCLOR 1254:2||MIXTURE:2||polychlorinated dibenzofurans (PCDFs):2||TITANIUMDIOXIDE:2||MIXTURES:2||DEEP OCEAN:2||SWEDISH HUMANMILK:2||SERUM CONCENTRATIONS:2||Decolorization:2||Nanotoxicity:2||OUTDOOR AIR:2||THERMODYNAMIC PROPERTIES:2||LAURENTIAN GREATLAKES:2||ENVIRONMENTAL APPLICATIONS:2||PHENOLS:2||DIBENZOFURANS:2||FUNGAL LACCASES:2||AREA:2||ISLAND:2||polychlorinated dibenzopdioxins and dibenzofurans:2||ATMOSPHERIC TRANSPORT:2||polychlorinated biphenyl:2||INTERANNUAL VARIABILITY:2||TERRESTRIAL ECOSYSTEMS:2||BIOCONCENTRATION:2||ORGANICSOLVENTS:2||fly ash:2||SAMPLERS:2||SPHINGOMONASWITTICHII RW1:2||ABYSSAL OCEAN:2||MIXEDLAYER:2||carbon emission:2||Stormwater catch basin:2||WATER TREATMENT PLANTS:2||Bacterial viability:1||DLPCBs:1||PCDD/F LEVELS:1||Polybrominated diphenyl ethers (PBDEs):1||Dietary daily intake:1||STABILIZATION:1||INACTIVATION:1||Foods:1||SEAFOOD CONSUMPTION:1||DUST INGESTION:1||HYDROTHERMAL SYNTHESIS:1||laccasemediator system:1||LIGNIN:1||Metabolic intermediates:1||BIOREMEDIATION:1||Porphyrin:1||2,4,6TRICHLOROPHENOL:1||IMPEDANCE SPECTROSCOPY:1||NATURAL ORGANICMATTER:1||INSITU REMEDIATION:1||FATE:1||Acetone:1||nZVI:1||Chromate:1||HEXAVALENT CHROMIUM:1||ASPERGILLUSFUMIGATUS:1||RATIOS:1||MOUNTAINS:1||AREAS:1||PBDE MIXTURE:1||triazines:1||EFFICIENCIES:1||POLLUTANTS:1||POLYPHENOLS:1||,3TRIHYDROXYBIPHENYL:1||PUTIDA GJ31:1||BODY BURDEN:1||FUSION:1||POLYCHLORINATED PHENOLS:1||HAPs:1||animal feed:1||SERUM DIOXIN:1||ATMOSPHERIC PROCESSES:1||model:1||KINASEC ACTIVATION:1||MEMBRANE:1||ADAPTATION:1||degradation:1||FLUORENE:1||season:1||PARTICULATE MATTER:1||GRAMPOSITIVE BACTERIUM:1||PCDD/Fs (polychlorinated dibenzopdioxins and dibenzofurans):1||DGGE (denaturing gradient gel electrophoresis) analysis:1||passive air sampling:1||steel production:1||steel complex:1||RBBR:1||TEXTILE WASTEWATER:1||RISKASSESSMENT:1||TNTCONTAMINATED 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SAMPLES:1||GENECLUSTER:1||Toxicity:1||SYSTEM:1||COPLANAR PCBS:1||Bimetallic nanoparticles:1||Surface snow:1||CELLWALL:1||PAPER PULP:1||Biomass burning:1||ACTIVATEDSLUDGE SYSTEMS:1||SOURCE IDENTIFICATION:1||IRA743 resin bulk sampler:1||TAIWAN:1||OCPs:1||Ganoderma lucidum laccase:1||PLEUROTUSERYNGII:1||COLORATION:1||chlorodibenzopdioxins:1||FORESTFIRE:1||Masan Bay:1||HRGC/HRMS:1||maternal body burden:1||SOURCE DECAY:1||PEPTIDE:1||COEFFICIENT:1||very long chain bifunctional fatty acyl component:1||DIOXYGENASE:1||environmental level:1||REFUSE INCINERATION:1||FABRIC FILTER:1||COMBUSTION CONDITIONS:1||TRANSECT:1||GENETICALLYENGINEERED MICROORGANISMS:1||TERMINAL OXYGENASE COMPONENT:1||incinerator fly ash:1||plastic:1||IRONOXIDE CATALYST:1||bulk:1||PLANT:1||fine particle:1||NEWBEDFORD HARBOR:1||carbon monoxide:1||RETRIEVAL ALGORITHM:1||emission factors:1||WASTE:1||NATIONALHEALTH:1||NONDIABETIC ADULTS:1||HEALTHRISKS:1||4Fluorophenol:1||RHODOCOCCUSOPACUS:1||Pd/nFe:1||METALIONS:1||Fish:1||MAJOR UK CONURBATION:1||INDOOR AIR:1||ENDOCRINE DISRUPTING CHEMICALS:1||FUNGUS CORIOLOPSISPOLYZONA:1||DIPHENYL ETHER:1||2NDSPHERE COORDINATION:1||WHEAT BRAN:1||ELECTRONTRANSFER:1||TBBPA:1||dust:1||office:1||SIZE:1||CINCA RIVER:1||TIO2 NANOPARTICLES:1||COPPER NANOPARTICLES:1||Time trend:1||Elementary school student:1||ADULT MICE:1||TRANSITIONMETALS:1||Alginate bead:1||Oxygen release:1||Bioremediation:1||HEXACHLOROBENZENE:1||iron oxide nanoparticles:1||DIOXIDE:1||laccases:1||DIVERSITY:1||Incinerator:1||Indicator congener:1||COALTAR CREOSOTE:1||CA10:1||NHANES:1||CRYPTOCOCCUSNEOFORMANS:1||MEDIATED OXIDATION:1||General population:1||Deposition:1||Soil:1||Reductive dechlorination:1||Sphingomonas sp:1||FORMULATIONS:1||Steel complexes:1||EXTRACTION:1||SUPERCRITICALFLUID EXTRACTION:1||SOXHLET:1||HEALTH:1||LIGNIN MODELCOMPOUND:1||PHENOLICCOMPOUNDS:1||multicomponent nanoparticles:1||MAGNETICPROPERTIES:1||DITHIONITE:1||PHENYLENEDIAMINE:1||edible freshwater fish:1||ISOMERSPECIFIC DETERMINATION:1||daily intake:1||OPERATION RANCH HAND:1||HUMANMILK:1||DICHLORODIPHENYL DICHLOROETHENE DDE:1||RINGCLEAVAGE:1||DIBENZOPARADIOXINS:1||MSW INCINERATORS:1||URBAN AIR:1||NORTHAMERICAN ATMOSPHERE:1||microbial biocatalysts:1||diphenyl ether:1||Sphingomonas sp.:1||MASSSPECTROMETRY:1||dioxinlike PCBs:1||TRAMETESHIRSUTA:1||response surface methodology:1||Human health:1||DEPOSITION:1||BIOLOGICAL TREATMENT:1||ASH:1||GROWTH:1||carbon flux:1||ESI/LCMS:1||SATELLITE DATA:1||CO:1||biological removal:1||DEGRADING BACTERIUM:1||METHYLTRICLOSAN:1||RSCs:1||QUANTIFICATION:1||NONHODGKINSLYMPHOMA:1||Diabetes:1||Pseudonocardia benzenivorans:1||BACTERIALDEGRADATION:1||WASTEWATER TREATMENT:1||OXIDATIVE TRANSFORMATION:1||ONTARIO:1||SHIHWA:1||OTTAWA:1||GREATLAKES:1||MANGANESE PEROXIDASE:1||Natural organic coagulants:1||Grape seed extract:1||Syringaldehyde:1||AQUEOUSSOLUTIONS:1||GREEN RECOVERY:1||AUSTRALIA:1||Incinerator workers:1||Steel dust:1||Industrial wastes:1||MECHANISMS:1||Chemical contamination:1||Flame retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM ALGINATE:1||TDS:1||Dietary exposure:1||Zerovalent irons:1||Dechlorane plus:1||Polychlorinated biphenyls:1||Passive air sampling:1||manganese oxides:1||heavy metal ions:1||ADSORBENT:1||SYNTHETIC APPLICATIONS:1||Zinc Nanoparticles:1||PCDD/F FORMATION:1||Biotransformation:1||INCINERATOR FLYASH:1||Photocatalytic degradation:1||ENVIRONMENTAL CONCERN:1||Health risk:1||WET DEPOSITION:1||UASB REACTOR:1||Bulk deposition:1||PROFILES:1||CATALYZED OXIDATIVE POLYMERIZATION:1||CAPILLARYZONEELECTROPHORESIS:1||NATURALWATERS:1||PEPTIDES:1||ENVIRONMENTALSAMPLES:1||Pentachlorophenol:1||ELECTRONTRANSFERREACTIONS:1||TCE:1||2,2&apos:1||ANGULAR DIOXYGENATION:1||JAPANESE:1||cancer risk:1||polychlorinated dibenzopdioxins polychlorinated biphenyls:1||DIBENZOPDIOXIN:1||GENES:1||RHODOCOCCUSCHLOROPHENOLICUS:1||CEPACIA:1||PH01:1||industrial waste incinerator:1||oxidative stress:1||OCCUPATIONALEXPOSURE:1||VETERANS:1||HUMANS:1||AEROSOLS:1||VAPORPRESSURE:1||TEMPERATURE:1||STRESS:1||DENOVOSYNTHESIS:1||PARAMETERS:1||SAPONINS:1||AIRBORNE PARTICLES:1||TRENDS:1||bioremediation:1||CHLORINATED ETHENES:1||ORGANIC CONTAMINANTS:1||UK BACKGROUND AIR:1||SINTERING PLANTS:1||TSP:1||SIZE DISTRIBUTION:1||white rot fungus:1||dye decolorization:1||congenerspecific analysis:1||NUTRIENT TRANSPORT:1||human bloods:1||PLASMA:1||heavy metals:1||BIVALVES:1||isotope effect:1||GCMS:1||biomass burning:1||TRANSPORT:1||JAPAN:1||size dependent distribution of dioxin:1||gravitational SPLITT fractionation:1||marine sediment:1||INTERNAL EXPOSURE:1||CONSTRUCTION:1||PCN:1||CHLORINATED NAPHTHALENES:1||DYSFUNCTION:1||DDE:1||ENDOCRINEDISRUPTING CHEMICALS:1||SURFACE WATERS:1||Dechlorane Plus:1||Surface dust:1||INDUSTRIALAREA:1||Natural polyphenols:1||MALACHITE GREEN:1||MORINGAOLEIFERA:1||FLAVONOIDS:1||ALUMINUM:1||MT. QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX 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retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM 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QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE 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QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX MEDIATORS:2||WATERS:2||DISPERSION:2||Odor:2||OXIDE NANOPARTICLES:2||DEBROMINATION:2||SILVER NANOPARTICLES:2||Inventory:2||AROCLOR 1254:2||MIXTURE:2||polychlorinated dibenzofurans (PCDFs):2||TITANIUMDIOXIDE:2||MIXTURES:2||DEEP OCEAN:2||SWEDISH HUMANMILK:2||SERUM CONCENTRATIONS:2||Decolorization:2||Nanotoxicity:2||OUTDOOR AIR:2||THERMODYNAMIC PROPERTIES:2||LAURENTIAN GREATLAKES:2||ENVIRONMENTAL APPLICATIONS:2||PHENOLS:2||DIBENZOFURANS:2||FUNGAL LACCASES:2||AREA:2||ISLAND:2||polychlorinated dibenzopdioxins and dibenzofurans:2||ATMOSPHERIC TRANSPORT:2||polychlorinated biphenyl:2||INTERANNUAL VARIABILITY:2||TERRESTRIAL ECOSYSTEMS:2||BIOCONCENTRATION:2||ORGANICSOLVENTS:2||fly ash:2||SAMPLERS:2||SPHINGOMONASWITTICHII RW1:2||ABYSSAL OCEAN:2||MIXEDLAYER:2||carbon emission:2||Stormwater catch basin:2||WATER TREATMENT PLANTS:2||Bacterial viability:1||DLPCBs:1||PCDD/F LEVELS:1||Polybrominated diphenyl ethers (PBDEs):1||Dietary daily intake:1||STABILIZATION:1||INACTIVATION:1||Foods:1||SEAFOOD 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intake:1||OPERATION RANCH HAND:1||HUMANMILK:1||DICHLORODIPHENYL DICHLOROETHENE DDE:1||RINGCLEAVAGE:1||DIBENZOPARADIOXINS:1||MSW INCINERATORS:1||URBAN AIR:1||NORTHAMERICAN ATMOSPHERE:1||microbial biocatalysts:1||diphenyl ether:1||Sphingomonas sp.:1||MASSSPECTROMETRY:1||dioxinlike PCBs:1||TRAMETESHIRSUTA:1||response surface methodology:1||Human health:1||DEPOSITION:1||BIOLOGICAL TREATMENT:1||ASH:1||GROWTH:1||carbon flux:1||ESI/LCMS:1||SATELLITE DATA:1||CO:1||biological removal:1||DEGRADING BACTERIUM:1||METHYLTRICLOSAN:1||RSCs:1||QUANTIFICATION:1||NONHODGKINSLYMPHOMA:1||Diabetes:1||Pseudonocardia benzenivorans:1||BACTERIALDEGRADATION:1||WASTEWATER TREATMENT:1||OXIDATIVE TRANSFORMATION:1||ONTARIO:1||SHIHWA:1||OTTAWA:1||GREATLAKES:1||MANGANESE PEROXIDASE:1||Natural organic coagulants:1||Grape seed extract:1||Syringaldehyde:1||AQUEOUSSOLUTIONS:1||GREEN RECOVERY:1||AUSTRALIA:1||Incinerator workers:1||Steel dust:1||Industrial wastes:1||MECHANISMS:1||Chemical contamination:1||Flame retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM ALGINATE:1||TDS:1||Dietary exposure:1||Zerovalent irons:1||Dechlorane plus:1||Polychlorinated biphenyls:1||Passive air sampling:1||manganese oxides:1||heavy metal ions:1||ADSORBENT:1||SYNTHETIC APPLICATIONS:1||Zinc Nanoparticles:1||PCDD/F FORMATION:1||Biotransformation:1||INCINERATOR FLYASH:1||Photocatalytic degradation:1||ENVIRONMENTAL CONCERN:1||Health risk:1||WET DEPOSITION:1||UASB REACTOR:1||Bulk deposition:1||PROFILES:1||CATALYZED OXIDATIVE POLYMERIZATION:1||CAPILLARYZONEELECTROPHORESIS:1||NATURALWATERS:1||PEPTIDES:1||ENVIRONMENTALSAMPLES:1||Pentachlorophenol:1||ELECTRONTRANSFERREACTIONS:1||TCE:1||2,2&apos:1||ANGULAR DIOXYGENATION:1||JAPANESE:1||cancer risk:1||polychlorinated dibenzopdioxins polychlorinated biphenyls:1||DIBENZOPDIOXIN:1||GENES:1||RHODOCOCCUSCHLOROPHENOLICUS:1||CEPACIA:1||PH01:1||industrial waste incinerator:1||oxidative stress:1||OCCUPATIONALEXPOSURE:1||VETERANS:1||HUMANS:1||AEROSOLS:1||VAPORPRESSURE:1||TEMPERATURE:1||STRESS:1||DENOVOSYNTHESIS:1||PARAMETERS:1||SAPONINS:1||AIRBORNE PARTICLES:1||TRENDS:1||bioremediation:1||CHLORINATED ETHENES:1||ORGANIC CONTAMINANTS:1||UK BACKGROUND AIR:1||SINTERING PLANTS:1||TSP:1||SIZE DISTRIBUTION:1||white rot fungus:1||dye decolorization:1||congenerspecific analysis:1||NUTRIENT TRANSPORT:1||human bloods:1||PLASMA:1||heavy metals:1||BIVALVES:1||isotope effect:1||GCMS:1||biomass burning:1||TRANSPORT:1||JAPAN:1||size dependent distribution of dioxin:1||gravitational SPLITT fractionation:1||marine sediment:1||INTERNAL EXPOSURE:1||CONSTRUCTION:1||PCN:1||CHLORINATED NAPHTHALENES:1||DYSFUNCTION:1||DDE:1||ENDOCRINEDISRUPTING CHEMICALS:1||SURFACE WATERS:1||Dechlorane Plus:1||Surface dust:1||INDUSTRIALAREA:1||Natural polyphenols:1||MALACHITE GREEN:1||MORINGAOLEIFERA:1||FLAVONOIDS:1||ALUMINUM:1||MT. QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX MEDIATORS:2||WATERS:2||DISPERSION:2||Odor:2||OXIDE NANOPARTICLES:2||DEBROMINATION:2||SILVER NANOPARTICLES:2||Inventory:2||AROCLOR 1254:2||MIXTURE:2||polychlorinated dibenzofurans (PCDFs):2||TITANIUMDIOXIDE:2||MIXTURES:2||DEEP OCEAN:2||SWEDISH HUMANMILK:2||SERUM CONCENTRATIONS:2||Decolorization:2||Nanotoxicity:2||OUTDOOR AIR:2||THERMODYNAMIC PROPERTIES:2||LAURENTIAN GREATLAKES:2||ENVIRONMENTAL APPLICATIONS:2||PHENOLS:2||DIBENZOFURANS:2||FUNGAL LACCASES:2||AREA:2||ISLAND:2||polychlorinated dibenzopdioxins and dibenzofurans:2||ATMOSPHERIC TRANSPORT:2||polychlorinated biphenyl:2||INTERANNUAL VARIABILITY:2||TERRESTRIAL ECOSYSTEMS:2||BIOCONCENTRATION:2||ORGANICSOLVENTS:2||fly ash:2||SAMPLERS:2||SPHINGOMONASWITTICHII RW1:2||ABYSSAL OCEAN:2||MIXEDLAYER:2||carbon emission:2||Stormwater catch basin:2||WATER TREATMENT PLANTS:2||Bacterial viability:1||DLPCBs:1||PCDD/F LEVELS:1||Polybrominated diphenyl ethers (PBDEs):1||Dietary daily intake:1||STABILIZATION:1||INACTIVATION:1||Foods:1||SEAFOOD CONSUMPTION:1||DUST INGESTION:1||HYDROTHERMAL SYNTHESIS:1||laccasemediator system:1||LIGNIN:1||Metabolic intermediates:1||BIOREMEDIATION:1||Porphyrin:1||2,4,6TRICHLOROPHENOL:1||IMPEDANCE SPECTROSCOPY:1||NATURAL ORGANICMATTER:1||INSITU REMEDIATION:1||FATE:1||Acetone:1||nZVI:1||Chromate:1||HEXAVALENT CHROMIUM:1||ASPERGILLUSFUMIGATUS:1||RATIOS:1||MOUNTAINS:1||AREAS:1||PBDE MIXTURE:1||triazines:1||EFFICIENCIES:1||POLLUTANTS:1||POLYPHENOLS:1||,3TRIHYDROXYBIPHENYL:1||PUTIDA GJ31:1||BODY BURDEN:1||FUSION:1||POLYCHLORINATED PHENOLS:1||HAPs:1||animal feed:1||SERUM DIOXIN:1||ATMOSPHERIC PROCESSES:1||model:1||KINASEC ACTIVATION:1||MEMBRANE:1||ADAPTATION:1||degradation:1||FLUORENE:1||season:1||PARTICULATE MATTER:1||GRAMPOSITIVE BACTERIUM:1||PCDD/Fs (polychlorinated dibenzopdioxins and dibenzofurans):1||DGGE (denaturing gradient gel electrophoresis) analysis:1||passive air sampling:1||steel production:1||steel complex:1||RBBR:1||TEXTILE WASTEWATER:1||RISKASSESSMENT:1||TNTCONTAMINATED 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SAMPLES:1||GENECLUSTER:1||Toxicity:1||SYSTEM:1||COPLANAR PCBS:1||Bimetallic nanoparticles:1||Surface snow:1||CELLWALL:1||PAPER PULP:1||Biomass burning:1||ACTIVATEDSLUDGE SYSTEMS:1||SOURCE IDENTIFICATION:1||IRA743 resin bulk sampler:1||TAIWAN:1||OCPs:1||Ganoderma lucidum laccase:1||PLEUROTUSERYNGII:1||COLORATION:1||chlorodibenzopdioxins:1||FORESTFIRE:1||Masan Bay:1||HRGC/HRMS:1||maternal body burden:1||SOURCE DECAY:1||PEPTIDE:1||COEFFICIENT:1||very long chain bifunctional fatty acyl component:1||DIOXYGENASE:1||environmental level:1||REFUSE INCINERATION:1||FABRIC FILTER:1||COMBUSTION CONDITIONS:1||TRANSECT:1||GENETICALLYENGINEERED MICROORGANISMS:1||TERMINAL OXYGENASE COMPONENT:1||incinerator fly ash:1||plastic:1||IRONOXIDE CATALYST:1||bulk:1||PLANT:1||fine particle:1||NEWBEDFORD HARBOR:1||carbon monoxide:1||RETRIEVAL ALGORITHM:1||emission factors:1||WASTE:1||NATIONALHEALTH:1||NONDIABETIC ADULTS:1||HEALTHRISKS:1||4Fluorophenol:1||RHODOCOCCUSOPACUS:1||Pd/nFe:1||METALIONS:1||Fish:1||MAJOR UK CONURBATION:1||INDOOR AIR:1||ENDOCRINE DISRUPTING CHEMICALS:1||FUNGUS CORIOLOPSISPOLYZONA:1||DIPHENYL ETHER:1||2NDSPHERE COORDINATION:1||WHEAT BRAN:1||ELECTRONTRANSFER:1||TBBPA:1||dust:1||office:1||SIZE:1||CINCA RIVER:1||TIO2 NANOPARTICLES:1||COPPER NANOPARTICLES:1||Time trend:1||Elementary school student:1||ADULT MICE:1||TRANSITIONMETALS:1||Alginate bead:1||Oxygen release:1||Bioremediation:1||HEXACHLOROBENZENE:1||iron oxide nanoparticles:1||DIOXIDE:1||laccases:1||DIVERSITY:1||Incinerator:1||Indicator congener:1||COALTAR CREOSOTE:1||CA10:1||NHANES:1||CRYPTOCOCCUSNEOFORMANS:1||MEDIATED OXIDATION:1||General population:1||Deposition:1||Soil:1||Reductive dechlorination:1||Sphingomonas sp:1||FORMULATIONS:1||Steel complexes:1||EXTRACTION:1||SUPERCRITICALFLUID EXTRACTION:1||SOXHLET:1||HEALTH:1||LIGNIN MODELCOMPOUND:1||PHENOLICCOMPOUNDS:1||multicomponent nanoparticles:1||MAGNETICPROPERTIES:1||DITHIONITE:1||PHENYLENEDIAMINE:1||edible freshwater fish:1||ISOMERSPECIFIC DETERMINATION:1||daily intake:1||OPERATION RANCH HAND:1||HUMANMILK:1||DICHLORODIPHENYL DICHLOROETHENE DDE:1||RINGCLEAVAGE:1||DIBENZOPARADIOXINS:1||MSW INCINERATORS:1||URBAN AIR:1||NORTHAMERICAN ATMOSPHERE:1||microbial biocatalysts:1||diphenyl ether:1||Sphingomonas sp.:1||MASSSPECTROMETRY:1||dioxinlike PCBs:1||TRAMETESHIRSUTA:1||response surface methodology:1||Human health:1||DEPOSITION:1||BIOLOGICAL TREATMENT:1||ASH:1||GROWTH:1||carbon flux:1||ESI/LCMS:1||SATELLITE DATA:1||CO:1||biological removal:1||DEGRADING BACTERIUM:1||METHYLTRICLOSAN:1||RSCs:1||QUANTIFICATION:1||NONHODGKINSLYMPHOMA:1||Diabetes:1||Pseudonocardia benzenivorans:1||BACTERIALDEGRADATION:1||WASTEWATER TREATMENT:1||OXIDATIVE TRANSFORMATION:1||ONTARIO:1||SHIHWA:1||OTTAWA:1||GREATLAKES:1||MANGANESE PEROXIDASE:1||Natural organic coagulants:1||Grape seed extract:1||Syringaldehyde:1||AQUEOUSSOLUTIONS:1||GREEN RECOVERY:1||AUSTRALIA:1||Incinerator workers:1||Steel dust:1||Industrial wastes:1||MECHANISMS:1||Chemical contamination:1||Flame retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM ALGINATE:1||TDS:1||Dietary exposure:1||Zerovalent irons:1||Dechlorane plus:1||Polychlorinated biphenyls:1||Passive air sampling:1||manganese oxides:1||heavy metal ions:1||ADSORBENT:1||SYNTHETIC APPLICATIONS:1||Zinc Nanoparticles:1||PCDD/F FORMATION:1||Biotransformation:1||INCINERATOR FLYASH:1||Photocatalytic degradation:1||ENVIRONMENTAL CONCERN:1||Health risk:1||WET DEPOSITION:1||UASB REACTOR:1||Bulk deposition:1||PROFILES:1||CATALYZED OXIDATIVE POLYMERIZATION:1||CAPILLARYZONEELECTROPHORESIS:1||NATURALWATERS:1||PEPTIDES:1||ENVIRONMENTALSAMPLES:1||Pentachlorophenol:1||ELECTRONTRANSFERREACTIONS:1||TCE:1||2,2&apos:1||ANGULAR DIOXYGENATION:1||JAPANESE:1||cancer risk:1||polychlorinated dibenzopdioxins polychlorinated biphenyls:1||DIBENZOPDIOXIN:1||GENES:1||RHODOCOCCUSCHLOROPHENOLICUS:1||CEPACIA:1||PH01:1||industrial waste incinerator:1||oxidative stress:1||OCCUPATIONALEXPOSURE:1||VETERANS:1||HUMANS:1||AEROSOLS:1||VAPORPRESSURE:1||TEMPERATURE:1||STRESS:1||DENOVOSYNTHESIS:1||PARAMETERS:1||SAPONINS:1||AIRBORNE PARTICLES:1||TRENDS:1||bioremediation:1||CHLORINATED ETHENES:1||ORGANIC CONTAMINANTS:1||UK BACKGROUND AIR:1||SINTERING PLANTS:1||TSP:1||SIZE DISTRIBUTION:1||white rot fungus:1||dye decolorization:1||congenerspecific analysis:1||NUTRIENT TRANSPORT:1||human bloods:1||PLASMA:1||heavy metals:1||BIVALVES:1||isotope effect:1||GCMS:1||biomass burning:1||TRANSPORT:1||JAPAN:1||size dependent distribution of dioxin:1||gravitational SPLITT fractionation:1||marine sediment:1||INTERNAL EXPOSURE:1||CONSTRUCTION:1||PCN:1||CHLORINATED NAPHTHALENES:1||DYSFUNCTION:1||DDE:1||ENDOCRINEDISRUPTING CHEMICALS:1||SURFACE WATERS:1||Dechlorane Plus:1||Surface dust:1||INDUSTRIALAREA:1||Natural polyphenols:1||MALACHITE GREEN:1||MORINGAOLEIFERA:1||FLAVONOIDS:1||ALUMINUM:1||MT. QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX 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retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM 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QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE 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QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX MEDIATORS:2||WATERS:2||DISPERSION:2||Odor:2||OXIDE NANOPARTICLES:2||DEBROMINATION:2||SILVER NANOPARTICLES:2||Inventory:2||AROCLOR 1254:2||MIXTURE:2||polychlorinated dibenzofurans (PCDFs):2||TITANIUMDIOXIDE:2||MIXTURES:2||DEEP OCEAN:2||SWEDISH HUMANMILK:2||SERUM CONCENTRATIONS:2||Decolorization:2||Nanotoxicity:2||OUTDOOR AIR:2||THERMODYNAMIC PROPERTIES:2||LAURENTIAN GREATLAKES:2||ENVIRONMENTAL APPLICATIONS:2||PHENOLS:2||DIBENZOFURANS:2||FUNGAL LACCASES:2||AREA:2||ISLAND:2||polychlorinated dibenzopdioxins and dibenzofurans:2||ATMOSPHERIC TRANSPORT:2||polychlorinated biphenyl:2||INTERANNUAL VARIABILITY:2||TERRESTRIAL ECOSYSTEMS:2||BIOCONCENTRATION:2||ORGANICSOLVENTS:2||fly ash:2||SAMPLERS:2||SPHINGOMONASWITTICHII RW1:2||ABYSSAL OCEAN:2||MIXEDLAYER:2||carbon emission:2||Stormwater catch basin:2||WATER TREATMENT PLANTS:2||Bacterial viability:1||DLPCBs:1||PCDD/F LEVELS:1||Polybrominated diphenyl ethers (PBDEs):1||Dietary daily intake:1||STABILIZATION:1||INACTIVATION:1||Foods:1||SEAFOOD 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intake:1||OPERATION RANCH HAND:1||HUMANMILK:1||DICHLORODIPHENYL DICHLOROETHENE DDE:1||RINGCLEAVAGE:1||DIBENZOPARADIOXINS:1||MSW INCINERATORS:1||URBAN AIR:1||NORTHAMERICAN ATMOSPHERE:1||microbial biocatalysts:1||diphenyl ether:1||Sphingomonas sp.:1||MASSSPECTROMETRY:1||dioxinlike PCBs:1||TRAMETESHIRSUTA:1||response surface methodology:1||Human health:1||DEPOSITION:1||BIOLOGICAL TREATMENT:1||ASH:1||GROWTH:1||carbon flux:1||ESI/LCMS:1||SATELLITE DATA:1||CO:1||biological removal:1||DEGRADING BACTERIUM:1||METHYLTRICLOSAN:1||RSCs:1||QUANTIFICATION:1||NONHODGKINSLYMPHOMA:1||Diabetes:1||Pseudonocardia benzenivorans:1||BACTERIALDEGRADATION:1||WASTEWATER TREATMENT:1||OXIDATIVE TRANSFORMATION:1||ONTARIO:1||SHIHWA:1||OTTAWA:1||GREATLAKES:1||MANGANESE PEROXIDASE:1||Natural organic coagulants:1||Grape seed extract:1||Syringaldehyde:1||AQUEOUSSOLUTIONS:1||GREEN RECOVERY:1||AUSTRALIA:1||Incinerator workers:1||Steel dust:1||Industrial wastes:1||MECHANISMS:1||Chemical contamination:1||Flame retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM ALGINATE:1||TDS:1||Dietary exposure:1||Zerovalent irons:1||Dechlorane plus:1||Polychlorinated biphenyls:1||Passive air sampling:1||manganese oxides:1||heavy metal ions:1||ADSORBENT:1||SYNTHETIC APPLICATIONS:1||Zinc Nanoparticles:1||PCDD/F FORMATION:1||Biotransformation:1||INCINERATOR FLYASH:1||Photocatalytic degradation:1||ENVIRONMENTAL CONCERN:1||Health risk:1||WET DEPOSITION:1||UASB REACTOR:1||Bulk deposition:1||PROFILES:1||CATALYZED OXIDATIVE POLYMERIZATION:1||CAPILLARYZONEELECTROPHORESIS:1||NATURALWATERS:1||PEPTIDES:1||ENVIRONMENTALSAMPLES:1||Pentachlorophenol:1||ELECTRONTRANSFERREACTIONS:1||TCE:1||2,2&apos:1||ANGULAR DIOXYGENATION:1||JAPANESE:1||cancer risk:1||polychlorinated dibenzopdioxins polychlorinated biphenyls:1||DIBENZOPDIOXIN:1||GENES:1||RHODOCOCCUSCHLOROPHENOLICUS:1||CEPACIA:1||PH01:1||industrial waste incinerator:1||oxidative stress:1||OCCUPATIONALEXPOSURE:1||VETERANS:1||HUMANS:1||AEROSOLS:1||VAPORPRESSURE:1||TEMPERATURE:1||STRESS:1||DENOVOSYNTHESIS:1||PARAMETERS:1||SAPONINS:1||AIRBORNE PARTICLES:1||TRENDS:1||bioremediation:1||CHLORINATED ETHENES:1||ORGANIC CONTAMINANTS:1||UK BACKGROUND AIR:1||SINTERING PLANTS:1||TSP:1||SIZE DISTRIBUTION:1||white rot fungus:1||dye decolorization:1||congenerspecific analysis:1||NUTRIENT TRANSPORT:1||human bloods:1||PLASMA:1||heavy metals:1||BIVALVES:1||isotope effect:1||GCMS:1||biomass burning:1||TRANSPORT:1||JAPAN:1||size dependent distribution of dioxin:1||gravitational SPLITT fractionation:1||marine sediment:1||INTERNAL EXPOSURE:1||CONSTRUCTION:1||PCN:1||CHLORINATED NAPHTHALENES:1||DYSFUNCTION:1||DDE:1||ENDOCRINEDISRUPTING CHEMICALS:1||SURFACE WATERS:1||Dechlorane Plus:1||Surface dust:1||INDUSTRIALAREA:1||Natural polyphenols:1||MALACHITE GREEN:1||MORINGAOLEIFERA:1||FLAVONOIDS:1||ALUMINUM:1||MT. QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX MEDIATORS:2||WATERS:2||DISPERSION:2||Odor:2||OXIDE NANOPARTICLES:2||DEBROMINATION:2||SILVER NANOPARTICLES:2||Inventory:2||AROCLOR 1254:2||MIXTURE:2||polychlorinated dibenzofurans (PCDFs):2||TITANIUMDIOXIDE:2||MIXTURES:2||DEEP OCEAN:2||SWEDISH HUMANMILK:2||SERUM CONCENTRATIONS:2||Decolorization:2||Nanotoxicity:2||OUTDOOR AIR:2||THERMODYNAMIC PROPERTIES:2||LAURENTIAN GREATLAKES:2||ENVIRONMENTAL APPLICATIONS:2||PHENOLS:2||DIBENZOFURANS:2||FUNGAL LACCASES:2||AREA:2||ISLAND:2||polychlorinated dibenzopdioxins and dibenzofurans:2||ATMOSPHERIC TRANSPORT:2||polychlorinated biphenyl:2||INTERANNUAL VARIABILITY:2||TERRESTRIAL ECOSYSTEMS:2||BIOCONCENTRATION:2||ORGANICSOLVENTS:2||fly ash:2||SAMPLERS:2||SPHINGOMONASWITTICHII RW1:2||ABYSSAL OCEAN:2||MIXEDLAYER:2||carbon emission:2||Stormwater catch basin:2||WATER TREATMENT PLANTS:2||Bacterial viability:1||DLPCBs:1||PCDD/F LEVELS:1||Polybrominated diphenyl ethers (PBDEs):1||Dietary daily intake:1||STABILIZATION:1||INACTIVATION:1||Foods:1||SEAFOOD CONSUMPTION:1||DUST INGESTION:1||HYDROTHERMAL SYNTHESIS:1||laccasemediator system:1||LIGNIN:1||Metabolic intermediates:1||BIOREMEDIATION:1||Porphyrin:1||2,4,6TRICHLOROPHENOL:1||IMPEDANCE SPECTROSCOPY:1||NATURAL ORGANICMATTER:1||INSITU REMEDIATION:1||FATE:1||Acetone:1||nZVI:1||Chromate:1||HEXAVALENT CHROMIUM:1||ASPERGILLUSFUMIGATUS:1||RATIOS:1||MOUNTAINS:1||AREAS:1||PBDE MIXTURE:1||triazines:1||EFFICIENCIES:1||POLLUTANTS:1||POLYPHENOLS:1||,3TRIHYDROXYBIPHENYL:1||PUTIDA GJ31:1||BODY BURDEN:1||FUSION:1||POLYCHLORINATED PHENOLS:1||HAPs:1||animal feed:1||SERUM DIOXIN:1||ATMOSPHERIC PROCESSES:1||model:1||KINASEC ACTIVATION:1||MEMBRANE:1||ADAPTATION:1||degradation:1||FLUORENE:1||season:1||PARTICULATE MATTER:1||GRAMPOSITIVE BACTERIUM:1||PCDD/Fs (polychlorinated dibenzopdioxins and dibenzofurans):1||DGGE (denaturing gradient gel electrophoresis) analysis:1||passive air sampling:1||steel production:1||steel complex:1||RBBR:1||TEXTILE WASTEWATER:1||RISKASSESSMENT:1||TNTCONTAMINATED 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SAMPLES:1||GENECLUSTER:1||Toxicity:1||SYSTEM:1||COPLANAR PCBS:1||Bimetallic nanoparticles:1||Surface snow:1||CELLWALL:1||PAPER PULP:1||Biomass burning:1||ACTIVATEDSLUDGE SYSTEMS:1||SOURCE IDENTIFICATION:1||IRA743 resin bulk sampler:1||TAIWAN:1||OCPs:1||Ganoderma lucidum laccase:1||PLEUROTUSERYNGII:1||COLORATION:1||chlorodibenzopdioxins:1||FORESTFIRE:1||Masan Bay:1||HRGC/HRMS:1||maternal body burden:1||SOURCE DECAY:1||PEPTIDE:1||COEFFICIENT:1||very long chain bifunctional fatty acyl component:1||DIOXYGENASE:1||environmental level:1||REFUSE INCINERATION:1||FABRIC FILTER:1||COMBUSTION CONDITIONS:1||TRANSECT:1||GENETICALLYENGINEERED MICROORGANISMS:1||TERMINAL OXYGENASE COMPONENT:1||incinerator fly ash:1||plastic:1||IRONOXIDE CATALYST:1||bulk:1||PLANT:1||fine particle:1||NEWBEDFORD HARBOR:1||carbon monoxide:1||RETRIEVAL ALGORITHM:1||emission factors:1||WASTE:1||NATIONALHEALTH:1||NONDIABETIC ADULTS:1||HEALTHRISKS:1||4Fluorophenol:1||RHODOCOCCUSOPACUS:1||Pd/nFe:1||METALIONS:1||Fish:1||MAJOR UK CONURBATION:1||INDOOR AIR:1||ENDOCRINE DISRUPTING CHEMICALS:1||FUNGUS CORIOLOPSISPOLYZONA:1||DIPHENYL ETHER:1||2NDSPHERE COORDINATION:1||WHEAT BRAN:1||ELECTRONTRANSFER:1||TBBPA:1||dust:1||office:1||SIZE:1||CINCA RIVER:1||TIO2 NANOPARTICLES:1||COPPER NANOPARTICLES:1||Time trend:1||Elementary school student:1||ADULT MICE:1||TRANSITIONMETALS:1||Alginate bead:1||Oxygen release:1||Bioremediation:1||HEXACHLOROBENZENE:1||iron oxide nanoparticles:1||DIOXIDE:1||laccases:1||DIVERSITY:1||Incinerator:1||Indicator congener:1||COALTAR CREOSOTE:1||CA10:1||NHANES:1||CRYPTOCOCCUSNEOFORMANS:1||MEDIATED OXIDATION:1||General population:1||Deposition:1||Soil:1||Reductive dechlorination:1||Sphingomonas sp:1||FORMULATIONS:1||Steel complexes:1||EXTRACTION:1||SUPERCRITICALFLUID EXTRACTION:1||SOXHLET:1||HEALTH:1||LIGNIN MODELCOMPOUND:1||PHENOLICCOMPOUNDS:1||multicomponent nanoparticles:1||MAGNETICPROPERTIES:1||DITHIONITE:1||PHENYLENEDIAMINE:1||edible freshwater fish:1||ISOMERSPECIFIC DETERMINATION:1||daily intake:1||OPERATION RANCH HAND:1||HUMANMILK:1||DICHLORODIPHENYL DICHLOROETHENE DDE:1||RINGCLEAVAGE:1||DIBENZOPARADIOXINS:1||MSW INCINERATORS:1||URBAN AIR:1||NORTHAMERICAN ATMOSPHERE:1||microbial biocatalysts:1||diphenyl ether:1||Sphingomonas sp.:1||MASSSPECTROMETRY:1||dioxinlike PCBs:1||TRAMETESHIRSUTA:1||response surface methodology:1||Human health:1||DEPOSITION:1||BIOLOGICAL TREATMENT:1||ASH:1||GROWTH:1||carbon flux:1||ESI/LCMS:1||SATELLITE DATA:1||CO:1||biological removal:1||DEGRADING BACTERIUM:1||METHYLTRICLOSAN:1||RSCs:1||QUANTIFICATION:1||NONHODGKINSLYMPHOMA:1||Diabetes:1||Pseudonocardia benzenivorans:1||BACTERIALDEGRADATION:1||WASTEWATER TREATMENT:1||OXIDATIVE TRANSFORMATION:1||ONTARIO:1||SHIHWA:1||OTTAWA:1||GREATLAKES:1||MANGANESE PEROXIDASE:1||Natural organic coagulants:1||Grape seed extract:1||Syringaldehyde:1||AQUEOUSSOLUTIONS:1||GREEN RECOVERY:1||AUSTRALIA:1||Incinerator workers:1||Steel dust:1||Industrial wastes:1||MECHANISMS:1||Chemical contamination:1||Flame retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM ALGINATE:1||TDS:1||Dietary exposure:1||Zerovalent irons:1||Dechlorane plus:1||Polychlorinated biphenyls:1||Passive air sampling:1||manganese oxides:1||heavy metal ions:1||ADSORBENT:1||SYNTHETIC APPLICATIONS:1||Zinc Nanoparticles:1||PCDD/F FORMATION:1||Biotransformation:1||INCINERATOR FLYASH:1||Photocatalytic degradation:1||ENVIRONMENTAL CONCERN:1||Health risk:1||WET DEPOSITION:1||UASB REACTOR:1||Bulk deposition:1||PROFILES:1||CATALYZED OXIDATIVE POLYMERIZATION:1||CAPILLARYZONEELECTROPHORESIS:1||NATURALWATERS:1||PEPTIDES:1||ENVIRONMENTALSAMPLES:1||Pentachlorophenol:1||ELECTRONTRANSFERREACTIONS:1||TCE:1||2,2&apos:1||ANGULAR DIOXYGENATION:1||JAPANESE:1||cancer risk:1||polychlorinated dibenzopdioxins polychlorinated biphenyls:1||DIBENZOPDIOXIN:1||GENES:1||RHODOCOCCUSCHLOROPHENOLICUS:1||CEPACIA:1||PH01:1||industrial waste incinerator:1||oxidative stress:1||OCCUPATIONALEXPOSURE:1||VETERANS:1||HUMANS:1||AEROSOLS:1||VAPORPRESSURE:1||TEMPERATURE:1||STRESS:1||DENOVOSYNTHESIS:1||PARAMETERS:1||SAPONINS:1||AIRBORNE PARTICLES:1||TRENDS:1||bioremediation:1||CHLORINATED ETHENES:1||ORGANIC CONTAMINANTS:1||UK BACKGROUND AIR:1||SINTERING PLANTS:1||TSP:1||SIZE DISTRIBUTION:1||white rot fungus:1||dye decolorization:1||congenerspecific analysis:1||NUTRIENT TRANSPORT:1||human bloods:1||PLASMA:1||heavy metals:1||BIVALVES:1||isotope effect:1||GCMS:1||biomass burning:1||TRANSPORT:1||JAPAN:1||size dependent distribution of dioxin:1||gravitational SPLITT fractionation:1||marine sediment:1||INTERNAL EXPOSURE:1||CONSTRUCTION:1||PCN:1||CHLORINATED NAPHTHALENES:1||DYSFUNCTION:1||DDE:1||ENDOCRINEDISRUPTING CHEMICALS:1||SURFACE WATERS:1||Dechlorane Plus:1||Surface dust:1||INDUSTRIALAREA:1||Natural polyphenols:1||MALACHITE GREEN:1||MORINGAOLEIFERA:1||FLAVONOIDS:1||ALUMINUM:1||MT. QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX 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retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM 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QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE 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QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX MEDIATORS:2||WATERS:2||DISPERSION:2||Odor:2||OXIDE NANOPARTICLES:2||DEBROMINATION:2||SILVER NANOPARTICLES:2||Inventory:2||AROCLOR 1254:2||MIXTURE:2||polychlorinated dibenzofurans (PCDFs):2||TITANIUMDIOXIDE:2||MIXTURES:2||DEEP OCEAN:2||SWEDISH HUMANMILK:2||SERUM CONCENTRATIONS:2||Decolorization:2||Nanotoxicity:2||OUTDOOR AIR:2||THERMODYNAMIC PROPERTIES:2||LAURENTIAN GREATLAKES:2||ENVIRONMENTAL APPLICATIONS:2||PHENOLS:2||DIBENZOFURANS:2||FUNGAL LACCASES:2||AREA:2||ISLAND:2||polychlorinated dibenzopdioxins and dibenzofurans:2||ATMOSPHERIC TRANSPORT:2||polychlorinated biphenyl:2||INTERANNUAL VARIABILITY:2||TERRESTRIAL ECOSYSTEMS:2||BIOCONCENTRATION:2||ORGANICSOLVENTS:2||fly ash:2||SAMPLERS:2||SPHINGOMONASWITTICHII RW1:2||ABYSSAL OCEAN:2||MIXEDLAYER:2||carbon emission:2||Stormwater catch basin:2||WATER TREATMENT PLANTS:2||Bacterial viability:1||DLPCBs:1||PCDD/F LEVELS:1||Polybrominated diphenyl ethers (PBDEs):1||Dietary daily intake:1||STABILIZATION:1||INACTIVATION:1||Foods:1||SEAFOOD 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intake:1||OPERATION RANCH HAND:1||HUMANMILK:1||DICHLORODIPHENYL DICHLOROETHENE DDE:1||RINGCLEAVAGE:1||DIBENZOPARADIOXINS:1||MSW INCINERATORS:1||URBAN AIR:1||NORTHAMERICAN ATMOSPHERE:1||microbial biocatalysts:1||diphenyl ether:1||Sphingomonas sp.:1||MASSSPECTROMETRY:1||dioxinlike PCBs:1||TRAMETESHIRSUTA:1||response surface methodology:1||Human health:1||DEPOSITION:1||BIOLOGICAL TREATMENT:1||ASH:1||GROWTH:1||carbon flux:1||ESI/LCMS:1||SATELLITE DATA:1||CO:1||biological removal:1||DEGRADING BACTERIUM:1||METHYLTRICLOSAN:1||RSCs:1||QUANTIFICATION:1||NONHODGKINSLYMPHOMA:1||Diabetes:1||Pseudonocardia benzenivorans:1||BACTERIALDEGRADATION:1||WASTEWATER TREATMENT:1||OXIDATIVE TRANSFORMATION:1||ONTARIO:1||SHIHWA:1||OTTAWA:1||GREATLAKES:1||MANGANESE PEROXIDASE:1||Natural organic coagulants:1||Grape seed extract:1||Syringaldehyde:1||AQUEOUSSOLUTIONS:1||GREEN RECOVERY:1||AUSTRALIA:1||Incinerator workers:1||Steel dust:1||Industrial wastes:1||MECHANISMS:1||Chemical contamination:1||Flame retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM ALGINATE:1||TDS:1||Dietary exposure:1||Zerovalent irons:1||Dechlorane plus:1||Polychlorinated biphenyls:1||Passive air sampling:1||manganese oxides:1||heavy metal ions:1||ADSORBENT:1||SYNTHETIC APPLICATIONS:1||Zinc Nanoparticles:1||PCDD/F FORMATION:1||Biotransformation:1||INCINERATOR FLYASH:1||Photocatalytic degradation:1||ENVIRONMENTAL CONCERN:1||Health risk:1||WET DEPOSITION:1||UASB REACTOR:1||Bulk deposition:1||PROFILES:1||CATALYZED OXIDATIVE POLYMERIZATION:1||CAPILLARYZONEELECTROPHORESIS:1||NATURALWATERS:1||PEPTIDES:1||ENVIRONMENTALSAMPLES:1||Pentachlorophenol:1||ELECTRONTRANSFERREACTIONS:1||TCE:1||2,2&apos:1||ANGULAR DIOXYGENATION:1||JAPANESE:1||cancer risk:1||polychlorinated dibenzopdioxins polychlorinated biphenyls:1||DIBENZOPDIOXIN:1||GENES:1||RHODOCOCCUSCHLOROPHENOLICUS:1||CEPACIA:1||PH01:1||industrial waste incinerator:1||oxidative stress:1||OCCUPATIONALEXPOSURE:1||VETERANS:1||HUMANS:1||AEROSOLS:1||VAPORPRESSURE:1||TEMPERATURE:1||STRESS:1||DENOVOSYNTHESIS:1||PARAMETERS:1||SAPONINS:1||AIRBORNE PARTICLES:1||TRENDS:1||bioremediation:1||CHLORINATED ETHENES:1||ORGANIC CONTAMINANTS:1||UK BACKGROUND AIR:1||SINTERING PLANTS:1||TSP:1||SIZE DISTRIBUTION:1||white rot fungus:1||dye decolorization:1||congenerspecific analysis:1||NUTRIENT TRANSPORT:1||human bloods:1||PLASMA:1||heavy metals:1||BIVALVES:1||isotope effect:1||GCMS:1||biomass burning:1||TRANSPORT:1||JAPAN:1||size dependent distribution of dioxin:1||gravitational SPLITT fractionation:1||marine sediment:1||INTERNAL EXPOSURE:1||CONSTRUCTION:1||PCN:1||CHLORINATED NAPHTHALENES:1||DYSFUNCTION:1||DDE:1||ENDOCRINEDISRUPTING CHEMICALS:1||SURFACE WATERS:1||Dechlorane Plus:1||Surface dust:1||INDUSTRIALAREA:1||Natural polyphenols:1||MALACHITE GREEN:1||MORINGAOLEIFERA:1||FLAVONOIDS:1||ALUMINUM:1||MT. QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX MEDIATORS:2||WATERS:2||DISPERSION:2||Odor:2||OXIDE NANOPARTICLES:2||DEBROMINATION:2||SILVER NANOPARTICLES:2||Inventory:2||AROCLOR 1254:2||MIXTURE:2||polychlorinated dibenzofurans (PCDFs):2||TITANIUMDIOXIDE:2||MIXTURES:2||DEEP OCEAN:2||SWEDISH HUMANMILK:2||SERUM CONCENTRATIONS:2||Decolorization:2||Nanotoxicity:2||OUTDOOR AIR:2||THERMODYNAMIC PROPERTIES:2||LAURENTIAN GREATLAKES:2||ENVIRONMENTAL APPLICATIONS:2||PHENOLS:2||DIBENZOFURANS:2||FUNGAL LACCASES:2||AREA:2||ISLAND:2||polychlorinated dibenzopdioxins and dibenzofurans:2||ATMOSPHERIC TRANSPORT:2||polychlorinated biphenyl:2||INTERANNUAL VARIABILITY:2||TERRESTRIAL ECOSYSTEMS:2||BIOCONCENTRATION:2||ORGANICSOLVENTS:2||fly ash:2||SAMPLERS:2||SPHINGOMONASWITTICHII RW1:2||ABYSSAL OCEAN:2||MIXEDLAYER:2||carbon emission:2||Stormwater catch basin:2||WATER TREATMENT PLANTS:2||Bacterial viability:1||DLPCBs:1||PCDD/F LEVELS:1||Polybrominated diphenyl ethers (PBDEs):1||Dietary daily intake:1||STABILIZATION:1||INACTIVATION:1||Foods:1||SEAFOOD CONSUMPTION:1||DUST INGESTION:1||HYDROTHERMAL SYNTHESIS:1||laccasemediator system:1||LIGNIN:1||Metabolic intermediates:1||BIOREMEDIATION:1||Porphyrin:1||2,4,6TRICHLOROPHENOL:1||IMPEDANCE SPECTROSCOPY:1||NATURAL ORGANICMATTER:1||INSITU REMEDIATION:1||FATE:1||Acetone:1||nZVI:1||Chromate:1||HEXAVALENT CHROMIUM:1||ASPERGILLUSFUMIGATUS:1||RATIOS:1||MOUNTAINS:1||AREAS:1||PBDE MIXTURE:1||triazines:1||EFFICIENCIES:1||POLLUTANTS:1||POLYPHENOLS:1||,3TRIHYDROXYBIPHENYL:1||PUTIDA GJ31:1||BODY BURDEN:1||FUSION:1||POLYCHLORINATED PHENOLS:1||HAPs:1||animal feed:1||SERUM DIOXIN:1||ATMOSPHERIC PROCESSES:1||model:1||KINASEC ACTIVATION:1||MEMBRANE:1||ADAPTATION:1||degradation:1||FLUORENE:1||season:1||PARTICULATE MATTER:1||GRAMPOSITIVE BACTERIUM:1||PCDD/Fs (polychlorinated dibenzopdioxins and dibenzofurans):1||DGGE (denaturing gradient gel electrophoresis) analysis:1||passive air sampling:1||steel production:1||steel complex:1||RBBR:1||TEXTILE WASTEWATER:1||RISKASSESSMENT:1||TNTCONTAMINATED 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SAMPLES:1||GENECLUSTER:1||Toxicity:1||SYSTEM:1||COPLANAR PCBS:1||Bimetallic nanoparticles:1||Surface snow:1||CELLWALL:1||PAPER PULP:1||Biomass burning:1||ACTIVATEDSLUDGE SYSTEMS:1||SOURCE IDENTIFICATION:1||IRA743 resin bulk sampler:1||TAIWAN:1||OCPs:1||Ganoderma lucidum laccase:1||PLEUROTUSERYNGII:1||COLORATION:1||chlorodibenzopdioxins:1||FORESTFIRE:1||Masan Bay:1||HRGC/HRMS:1||maternal body burden:1||SOURCE DECAY:1||PEPTIDE:1||COEFFICIENT:1||very long chain bifunctional fatty acyl component:1||DIOXYGENASE:1||environmental level:1||REFUSE INCINERATION:1||FABRIC FILTER:1||COMBUSTION CONDITIONS:1||TRANSECT:1||GENETICALLYENGINEERED MICROORGANISMS:1||TERMINAL OXYGENASE COMPONENT:1||incinerator fly ash:1||plastic:1||IRONOXIDE CATALYST:1||bulk:1||PLANT:1||fine particle:1||NEWBEDFORD HARBOR:1||carbon monoxide:1||RETRIEVAL ALGORITHM:1||emission factors:1||WASTE:1||NATIONALHEALTH:1||NONDIABETIC ADULTS:1||HEALTHRISKS:1||4Fluorophenol:1||RHODOCOCCUSOPACUS:1||Pd/nFe:1||METALIONS:1||Fish:1||MAJOR UK CONURBATION:1||INDOOR AIR:1||ENDOCRINE DISRUPTING CHEMICALS:1||FUNGUS CORIOLOPSISPOLYZONA:1||DIPHENYL ETHER:1||2NDSPHERE COORDINATION:1||WHEAT BRAN:1||ELECTRONTRANSFER:1||TBBPA:1||dust:1||office:1||SIZE:1||CINCA RIVER:1||TIO2 NANOPARTICLES:1||COPPER NANOPARTICLES:1||Time trend:1||Elementary school student:1||ADULT MICE:1||TRANSITIONMETALS:1||Alginate bead:1||Oxygen release:1||Bioremediation:1||HEXACHLOROBENZENE:1||iron oxide nanoparticles:1||DIOXIDE:1||laccases:1||DIVERSITY:1||Incinerator:1||Indicator congener:1||COALTAR CREOSOTE:1||CA10:1||NHANES:1||CRYPTOCOCCUSNEOFORMANS:1||MEDIATED OXIDATION:1||General population:1||Deposition:1||Soil:1||Reductive dechlorination:1||Sphingomonas sp:1||FORMULATIONS:1||Steel complexes:1||EXTRACTION:1||SUPERCRITICALFLUID EXTRACTION:1||SOXHLET:1||HEALTH:1||LIGNIN MODELCOMPOUND:1||PHENOLICCOMPOUNDS:1||multicomponent nanoparticles:1||MAGNETICPROPERTIES:1||DITHIONITE:1||PHENYLENEDIAMINE:1||edible freshwater fish:1||ISOMERSPECIFIC DETERMINATION:1||daily intake:1||OPERATION RANCH HAND:1||HUMANMILK:1||DICHLORODIPHENYL DICHLOROETHENE DDE:1||RINGCLEAVAGE:1||DIBENZOPARADIOXINS:1||MSW INCINERATORS:1||URBAN AIR:1||NORTHAMERICAN ATMOSPHERE:1||microbial biocatalysts:1||diphenyl ether:1||Sphingomonas sp.:1||MASSSPECTROMETRY:1||dioxinlike PCBs:1||TRAMETESHIRSUTA:1||response surface methodology:1||Human health:1||DEPOSITION:1||BIOLOGICAL TREATMENT:1||ASH:1||GROWTH:1||carbon flux:1||ESI/LCMS:1||SATELLITE DATA:1||CO:1||biological removal:1||DEGRADING BACTERIUM:1||METHYLTRICLOSAN:1||RSCs:1||QUANTIFICATION:1||NONHODGKINSLYMPHOMA:1||Diabetes:1||Pseudonocardia benzenivorans:1||BACTERIALDEGRADATION:1||WASTEWATER TREATMENT:1||OXIDATIVE TRANSFORMATION:1||ONTARIO:1||SHIHWA:1||OTTAWA:1||GREATLAKES:1||MANGANESE PEROXIDASE:1||Natural organic coagulants:1||Grape seed extract:1||Syringaldehyde:1||AQUEOUSSOLUTIONS:1||GREEN RECOVERY:1||AUSTRALIA:1||Incinerator workers:1||Steel dust:1||Industrial wastes:1||MECHANISMS:1||Chemical contamination:1||Flame retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM ALGINATE:1||TDS:1||Dietary exposure:1||Zerovalent irons:1||Dechlorane plus:1||Polychlorinated biphenyls:1||Passive air sampling:1||manganese oxides:1||heavy metal ions:1||ADSORBENT:1||SYNTHETIC APPLICATIONS:1||Zinc Nanoparticles:1||PCDD/F FORMATION:1||Biotransformation:1||INCINERATOR FLYASH:1||Photocatalytic degradation:1||ENVIRONMENTAL CONCERN:1||Health risk:1||WET DEPOSITION:1||UASB REACTOR:1||Bulk deposition:1||PROFILES:1||CATALYZED OXIDATIVE POLYMERIZATION:1||CAPILLARYZONEELECTROPHORESIS:1||NATURALWATERS:1||PEPTIDES:1||ENVIRONMENTALSAMPLES:1||Pentachlorophenol:1||ELECTRONTRANSFERREACTIONS:1||TCE:1||2,2&apos:1||ANGULAR DIOXYGENATION:1||JAPANESE:1||cancer risk:1||polychlorinated dibenzopdioxins polychlorinated biphenyls:1||DIBENZOPDIOXIN:1||GENES:1||RHODOCOCCUSCHLOROPHENOLICUS:1||CEPACIA:1||PH01:1||industrial waste incinerator:1||oxidative stress:1||OCCUPATIONALEXPOSURE:1||VETERANS:1||HUMANS:1||AEROSOLS:1||VAPORPRESSURE:1||TEMPERATURE:1||STRESS:1||DENOVOSYNTHESIS:1||PARAMETERS:1||SAPONINS:1||AIRBORNE PARTICLES:1||TRENDS:1||bioremediation:1||CHLORINATED ETHENES:1||ORGANIC CONTAMINANTS:1||UK BACKGROUND AIR:1||SINTERING PLANTS:1||TSP:1||SIZE DISTRIBUTION:1||white rot fungus:1||dye decolorization:1||congenerspecific analysis:1||NUTRIENT TRANSPORT:1||human bloods:1||PLASMA:1||heavy metals:1||BIVALVES:1||isotope effect:1||GCMS:1||biomass burning:1||TRANSPORT:1||JAPAN:1||size dependent distribution of dioxin:1||gravitational SPLITT fractionation:1||marine sediment:1||INTERNAL EXPOSURE:1||CONSTRUCTION:1||PCN:1||CHLORINATED NAPHTHALENES:1||DYSFUNCTION:1||DDE:1||ENDOCRINEDISRUPTING CHEMICALS:1||SURFACE WATERS:1||Dechlorane Plus:1||Surface dust:1||INDUSTRIALAREA:1||Natural polyphenols:1||MALACHITE GREEN:1||MORINGAOLEIFERA:1||FLAVONOIDS:1||ALUMINUM:1||MT. QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSITION:4||Triclosan:4||DIOXINS:4||LAND:4||Ganoderma lucidum:4||IMMOBILIZED LACCASE:4||Laccase:4||DESTRUCTION:4||HUMAN ADIPOSETISSUE:4||WASTE INCINERATORS:4||CO2:4||LONGRANGE TRANSPORT:4||PCDDs:4||POLYCHLORINATED DIBENZOFURANS:4||Persistent organic pollutants:4||ATMOSPHERE:4||1,2,3,4TETRACHLORODIBENZOPDIOXIN:4||PHANEROCHAETECHRYSOSPORIUM:4||POLYCHLORINATEDBIPHENYLS PCBS:4||MODELS:4||WHITEROT FUNGUS:4||Bacillus pumilus:4||EXCHANGE:4||Organochlorine pesticides:3||RURAL TRENDS:3||GANODERMALUCIDUM:3||dibenzofuran:3||BUDGET:3||particle size:3||gas/particle partitioning:3||PCDD:3||ASSESS URBAN:3||IMPACT:3||reforestation:3||HYDROCARBONS:3||BENZENES:3||ESTUARINE SEDIMENTS:3||SYNTHETIC DYES:3||VOLATILE ORGANICCOMPOUNDS:3||CARBON NANOTUBES:3||Sphingomonas wittichii RW1:3||SOLIDWASTE INCINERATORS:3||GAS:3||BACILLUSPUMILUS:3||HUMAN EXPOSURE:3||INHOUSE DUST:3||AQUEOUSSOLUTION:3||SPATIALDISTRIBUTION:3||TOXIC EQUIVALENCY FACTORS:3||PASSIVE AIR SAMPLERS:3||biosorption:3||AROMATICCOMPOUNDS:3||ADSORPTION:3||MUNICIPAL WASTE INCINERATOR:3||CONSUMPTION:3||DECABROMODIPHENYL ETHER:3||WORKERS:3||CARBON:3||ACID:3||soil:3||CARBONTETRACHLORIDE:3||Biodegradation:3||BIOTRANSFORMATION:3||biotransformation:3||MEDIATORS:3||TOXICITY:3||DNADAMAGE:3||human blood:3||AZO DYES:3||SOUTH CHINA:3||ACCUMULATION:3||FURANS:3||VEGETATION:3||stack gas:3||DEHALOGENATION:3||ODORS:3||RATE CONSTANTS:3||South Korea:3||DECOLORIZATION:3||ENZYMES:3||PAHS:2||PDIOXINS:2||SPLITT:2||Urban:2||GRANULAR IRON:2||NANOSCALE ZEROVALENT IRON:2||CONTAMINATION:2||ISOMERS:2||HUMICACID:2||2,4DICHLOROPHENOL:2||NITRATE REDUCTION:2||CONGENERS:2||UNITEDKINGDOM:2||IRON:2||HISTORICAL EMISSION INVENTORY:2||TEMPORAL TRENDS:2||REDUCTION:2||MICROBIALDEGRADATION:2||LIVERTUMORS:2||polybrominated diphenyl ethers:2||forest fire:2||PCDD/PCDF:2||MSW INCINERATION:2||FACILITIES:2||laccase:2||VICINITY:2||ANTICYCLONIC EDDY:2||GASEXCHANGE:2||size characterization:2||PYCNOPORUSCINNABARINUS:2||TEXTILE DYES:2||GASES:2||AROMATICHYDROCARBONS PAHS:2||CHLORINATED PHENOLS:2||CHEMICALS:2||BREASTMILK:2||ATMOSPHERIC PCBS:2||INDUSTRY:2||SEASONALVARIATIONS:2||HORMONE LEVELS:2||ECOSYSTEMS:2||protein:2||MIDLATITUDE FOREST:2||NITRATE:2||CANADA:2||Reduced sulfur compounds:2||AQUATIC ENVIRONMENT:2||DIETARYINTAKE:2||GRAPHENE OXIDE:2||GLOBAL DISTRIBUTION MODEL:2||PAHs:2||PERFORMANCE LIQUIDCHROMATOGRAPHY:2||INDUCTION:2||PILOT INCINERATOR:2||SPAIN:2||AQUEOUS SUSPENSIONS:2||TRACER:2||forest fires:2||COMPLEX:2||OLFACTOMETRY:2||GULLS LARUSARGENTATUS:2||BIMETALLIC NANOPARTICLES:2||TCE DECHLORINATION:2||ENZYMATICSYNTHESIS:2||IDENTIFICATION:2||TRICHLOROETHYLENE:2||STRAIN RW1:2||Sphingomonas sp PH07:2||ORGANOCHLORINATED COMPOUNDS:2||PESTICIDES:2||CORIOLUSVERSICOLOR:2||CELLS:2||genetic instability:2||MITOSIS:2||INFANTS:2||ACTIVATEDSLUDGE:2||forest carbon uptake:2||biomass expansion factor:2||PCDD/F:2||PHOTOLYSIS:2||incinerators:2||reactive black 5:2||Volatile organic compounds:2||VOC:2||REACTIVITY:2||POWDER ELECTRODES:2||TEQ:2||FOOD:2||SOILS:2||PURIFICATION:2||p53:2||mitotic arrest:2||INVIVO:2||polychlorinated dibenzopdioxins (PCDDs):2||FLUXES:2||TRANSLOCATION:2||ADVANCED OXIDATION PROCESSES:2||Longrange atmospheric transport:2||BEHAVIOR:2||Seasonal variation:2||2Phenoxyphenol:2||Emission factor:2||KINETICS:2||TISSUES:2||air:2||SEDIMENT:2||OXIDATIVE STRESS:2||breast milk:2||dioxin:2||STORAGE:2||atmospheric carbon dioxide:2||forest biomass:2||forest management:2||PHOTODEGRADATION:2||1,2,3,4TCDD:2||HYDRODECHLORINATION:2||EXTRACELLULAR LACCASE:2||REDOX 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retardants:1||indoor air:1||society and environment:1||FE:1||RADIOACTIVE CESIUM:1||ACID SOLUTIONS:1||ENANTIOMERSPECIFIC ACCUMULATION:1||Dibenzofuran degradation:1||INVITRO:1||Dioxins:1||SPONTANEOUS BEHAVIOR:1||POTENTIAL ROLE:1||NANO ZEROVALENT IRON:1||Carboxymethyl cellulose:1||ENCAPSULATION:1||Coupling processes:1||Advanced oxidation processes:1||ORGANICMATTER:1||POLYMERIZATION:1||NANOSIZED ZEROVALENT IRON:1||Biomineralization:1||GREEN RUSTS:1||brominated diphenyl ethers (BDEs):1||online MEKCESIMS:1||ATMOSPHERIC PARTICLES:1||DETERMINANTS:1||ANTARCTICA:1||HEXACHLOROCYCLOHEXANES:1||iron sulfides:1||margin of exposure:1||SINK:1||ATMOSPHERIC O2:1||recombinant bioluminescent bacteria:1||cellular toxicity:1||LUX:1||ATCC39723:1||STRAINS:1||BIOSORPTION:1||LIVE:1||WOOD:1||WET:1||human milk:1||FORMULAFED INFANTS:1||hybrid QTOF MS:1||transmembrane lipids:1||Sarcina ventriculi:1||CHLOROPHENOL REACTIONS:1||DIOXINS/DIBENZOFURANS:1||BACILLUSPUMILUS PH01:1||PBDEs (polybrominated diphenyl ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM 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QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE 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ethers):1||volatile PAHs:1||DEVICES SPMDS:1||goethite:1||incineration:1||back trajectory:1||AEROSOL:1||dye decolourization:1||human serum:1||DIOXINLIKE:1||TEXTILE EFFLUENT:1||single root:1||soilplant system:1||plantation:1||OZONE:1||bioconversion of benzene:1||TOXICOLOGY:1||ESTERS:1||MOPITT:1||bioaugmentation:1||dioxins:1||RISK ASSESSMENT:1||Acids:1||TIME TRENDS:1||P,P&apos:1||6FLUORO SUBSTITUENT:1||Polybrominated diphenyl ethers:1||Indoor air:1||INHALATION EXPOSURE:1||ELECTRON TRANSFER:1||Cationic dyes:1||Himalayas:1||Snow:1||TIBETAN PLATEAU:1||ALPINE GLACIER:1||LINKED CHITOSAN RESIN:1||PNITROPHENOL:1||WORLD:1||Malachite green:1||TRIPHENYLMETHANE DYES:1||SYSTEMS:1||HEAVYMETALS:1||ANAEROBIC MICROBIAL CONSORTIUM:1||ENVIRONMENTS:1||Environmental Protection Agency:1||HBCD:1||bromine compound:1||car:1||dust exposure:1||high risk population:1||SUSPENSIONS:1||Reductive debromination:1||PHYSICOCHEMICAL PROPERTIES:1||POLYCHLORINATED BIPHENYL:1||Dechlorane compounds:1||CALCIUM ALGINATE:1||TDS:1||Dietary exposure:1||Zerovalent irons:1||Dechlorane plus:1||Polychlorinated biphenyls:1||Passive air sampling:1||manganese oxides:1||heavy metal ions:1||ADSORBENT:1||SYNTHETIC APPLICATIONS:1||Zinc Nanoparticles:1||PCDD/F FORMATION:1||Biotransformation:1||INCINERATOR FLYASH:1||Photocatalytic degradation:1||ENVIRONMENTAL CONCERN:1||Health risk:1||WET DEPOSITION:1||UASB REACTOR:1||Bulk deposition:1||PROFILES:1||CATALYZED OXIDATIVE POLYMERIZATION:1||CAPILLARYZONEELECTROPHORESIS:1||NATURALWATERS:1||PEPTIDES:1||ENVIRONMENTALSAMPLES:1||Pentachlorophenol:1||ELECTRONTRANSFERREACTIONS:1||TCE:1||2,2&apos:1||ANGULAR DIOXYGENATION:1||JAPANESE:1||cancer risk:1||polychlorinated dibenzopdioxins polychlorinated biphenyls:1||DIBENZOPDIOXIN:1||GENES:1||RHODOCOCCUSCHLOROPHENOLICUS:1||CEPACIA:1||PH01:1||industrial waste incinerator:1||oxidative stress:1||OCCUPATIONALEXPOSURE:1||VETERANS:1||HUMANS:1||AEROSOLS:1||VAPORPRESSURE:1||TEMPERATURE:1||STRESS:1||DENOVOSYNTHESIS:1||PARAMETERS:1||SAPONINS:1||AIRBORNE PARTICLES:1||TRENDS:1||bioremediation:1||CHLORINATED ETHENES:1||ORGANIC CONTAMINANTS:1||UK BACKGROUND AIR:1||SINTERING PLANTS:1||TSP:1||SIZE DISTRIBUTION:1||white rot fungus:1||dye decolorization:1||congenerspecific analysis:1||NUTRIENT TRANSPORT:1||human bloods:1||PLASMA:1||heavy metals:1||BIVALVES:1||isotope effect:1||GCMS:1||biomass burning:1||TRANSPORT:1||JAPAN:1||size dependent distribution of dioxin:1||gravitational SPLITT fractionation:1||marine sediment:1||INTERNAL EXPOSURE:1||CONSTRUCTION:1||PCN:1||CHLORINATED NAPHTHALENES:1||DYSFUNCTION:1||DDE:1||ENDOCRINEDISRUPTING CHEMICALS:1||SURFACE WATERS:1||Dechlorane Plus:1||Surface dust:1||INDUSTRIALAREA:1||Natural polyphenols:1||MALACHITE GREEN:1||MORINGAOLEIFERA:1||FLAVONOIDS:1||ALUMINUM:1||MT. QOMOLANGMA EVEREST:1||WIDELY USED BIOCIDE:1||OPTIMIZATION:1||EAF DUST:1||Heavy metals:1||Indoor environment:1||Dust:1||concentration (composition):1||health impact:1||occupational exposure:1||body burden:1||controlled study:1||kindergarten:1||limit of detection:1||ACTIVATED CARBON:1||SEWAGESLUDGE:1||COASTAL WATERS:1||DIBENZOPDIOXINS:29||Korea:23||PCDD/Fs:18||DEGRADATION:16||POLYCHLORINATEDBIPHENYLS:14||POLYCYCLIC AROMATICHYDROCARBONS:13||PERSISTENT ORGANIC POLLUTANTS:11||EXPOSURE:11||PCBS:10||PCBs:10||ORGANOCHLORINE PESTICIDES:10||ZEROVALENT IRON:10||AIR:10||POLYBROMINATED DIPHENYL ETHERS:8||SAMPLES:8||EMISSIONS:8||SOIL:8||ENVIRONMENT:7||FLYASH:7||BIPHENYLS:7||DECHLORINATION:7||SP STRAIN RW1:6||KOREA:6||COMBUSTION:6||PCDD/FS:6||PARTICLES:6||CHLORINATED DIOXINS:6||ORGANICCOMPOUNDS:6||AMBIENT AIR:6||WATER:6||REDUCTIVE DECHLORINATION:6||PATTERNS:6||PBDEs:6||ESCHERICHIACOLI:5||PCDFs:5||FISH:5||PCDDS:5||PCDFS:5||biodegradation:5||incinerator:5||BIODEGRADATION:5||SEPARATION:5||METABOLISM:5||FLUEGAS:5||BROMINATED FLAME RETARDANTS:5||TRANSFORMATION:5||TRAMETESVERSICOLOR:5||PCB:5||Human serum:5||BIOMASS:5||REMOVAL:5||PBDES:5||CHINA:5||HUMAN BLOOD:5||FLAME RETARDANTS:4||PCDF:4||EMISSION:4||OXIDATION:4||NANOPARTICLES:4||WASTEWATER:4||ZEROVALENT IRON:4||URBAN:4||DRY DEPOSIT