ScholarWorks@Hanyang University ERICA Campus: Moon, Hyo-Bang

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Moon, Hyo-Bang (문효방)

COLLEGE OF ENGINEERING SCIENCES (ERICA 해양융합공학과)

Research Area: 잔류성유기오염물질, 환경분석, 위해도 평가, Persistent organic pollutants, Environmental analysis, Risk Assessment

Tel 031-400-5534
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Sediment:13||DEHP:10||Coprostanol:10||PCBs:9||Biomonitoring:9||PAHs:8||WWTP:8||Bioaccumulation:8||Phthalates:7||Nonylphenol:7||Daily intake:7||PBDE:6||Bisphenol A:6||Polychlorinated biphenyls:6||POLYCHLORINATEDBIPHENYLS:6||Marine mammals:6||Personal care products:6||OPFR:6||PFOS:6||PBDEs:6||PCDD/Fs:5||Toxicity:5||Urine:5||Effectdirected analysis:5||Health risk:5||Infant:5||HUMAN EXPOSURE:5||Time trend:5||PERSISTENT ORGANIC POLLUTANTS:5||Pregnant women:5||Sewage:5||Alternative:5||POPs:5||Synthetic musk:5||Fecal sterol:5||Plasticizer:5||Nontarget screening:5||TEQ:5||Ecological risk:4||Lead:4||DBDPE:4||Estimated daily intake:4||Risk:4||PCB:4||HHCB:4||POLYBROMINATED DIPHENYL ETHERS:4||Siloxane:4||Flame retardant:4||Regulation:4||Human exposure:4||Wastewater treatment plant:4||Indoor dust:4||GCQTOFMS:4||Children:4||Marine mammal:4||Methyl paraben:4||Organochlorine pesticides:4||Mercury:4||Masan Bay:4||Siloxanes:3||ESTROGENIC ACTIVITY:3||Thyroid hormones:3||Polybrominated diphenyl ethers:3||Ethyl paraben:3||Exposure:3||Exposure assessment:3||POLYCYCLIC AROMATICHYDROCARBONS:3||Mokpo:3||Multidimensional scaling (MDS):3||exposure:3||DIBENZOPDIOXINS:3||Lactation:3||ENDOCRINEDISRUPTING CHEMICALS:3||H4IIEluc bioassay:3||DEHT:3||BPA:3||BDE 209:3||BROMINATED FLAME RETARDANTS:3||Family exposure:3||BTBPE:3||BPS:3||Risk assessment:3||Riverine discharge:3||PFASs:3||COASTAL WATERS:3||Diet:3||Endocrine disruption:3||Dietary intake:3||DDT:3||CONTAMINATION:3||HPLCMS/MS:3||WASTEWATER:3||LCHRMS:3||road dust:3||Seafood:3||Temporal trend:3||Seawater:3||Environmental phenols:3||Phthalate:3||Sediment quality:3||Sediments:3||Flame retardants:3||Alternative plasticizers:3||Yellow Sea:3||Organophosphate flame retardants:3||TCPP:3||Placental transfer:3||Interspecies difference:2||CORD BLOOD:2||Flux:2||Dioxins:2||Combustion process:2||Sludge:2||Oxidative stress:2||Cyclic:2||Jinhae Bay:2||Breast milk:2||Adipose tissue:2||Cetacean:2||LCMS/MS:2||Surface sediment:2||Dust ingestion:2||Aryl hydrocarbon receptor:2||TBEP:2||TBT:2||PCDDs:2||PCDFs:2||TOTM:2||TOXICITY:2||GREATLAKES ATMOSPHERE:2||ENVIRONMENTAL CHEMICALS:2||PFAS:2||General population:2||Linear:2||PFUnDA:2||Benthic organism:2||Loading fluxes:2||Thyroid hormone:2||BREASTMILK:2||Toddler:2||MASSSPECTROMETRY:2||Total organic carbon:2||Effluent:2||Triclocarban:2||Trimester:2||Embryogenesis:2||Trophic position:2||BSAF:2||HEALTH:2||US POPULATION:2||Ulsan Bay:2||Atmospheric deposition:2||Marine sediment:2||Persistent organic pollutant:2||Endocrine disruptors:2||Vertical profile:2||HUMAN BLOOD:2||WATER:2||CHECK:2||Wastewater:2||HUMAN SERUM:2||Placenta:2||Zebrafish:2||Plasticizers:2||Alternatives:2||Epigenetics:2||Polycyclic aromatic hydrocarbons:2||Hazard ratio:2||Precipitation:2||F53B:2||Prioritization:2||Mokpo coastal water:2||dietary intake:2||Accumulation profiles:2||Inventory:2||Debromination:2||environmental pollution:2||Mussel:2||House dust:2||floor dust:2||CHINA:2||NEWYORK:2||Bisphenol F:2||Dechlorane:2||RISKASSESSMENT:2||NORTH CHINA:2||human health1. IntroductionA large number of studies have demonstrated thatmany toxic organic contaminants are present in themarine environment:2||Bisphenols:2||lifetime cancer risk:2||Neurodevelopment:2||Nontarget analysis:2||River water:2||Nonylphenol ethoxylates:2||INVITRO:2||AHTN:2||OBESITY:2||OCPs:2||Feeding habit:2||Baby food:2||AhR agonists:2||Finless porpoises:2||Crassostrea gigas:2||ORGANOTIN COMPOUNDS:2||OXIDATIVE STRESS:2||SPRAGUEDAWLEY RATS:2||Industrial area:2||Industrial complex:2||Organic UV filters:2||Industry:2||Organic wastewater compounds:2||seafood:2||sediment:2||Seasonal exposure:2||Insulin resistance:2||Sediment core:2||Sediment elutriate:2||target hazardous quotient (THQ):2||the highest concen:2||Freshwater fish:1||Fukushima:1||Fullscan screening analysis:1||GALLATE:1||GC/MS/MS:1||GENEEXPRESSION:1||GLUCOSETOLERANCE TEST:1||GOBIOCYPRISRARUS:1||GRIDDED FIELD OBSERVATIONS:1||Genderspecific difference:1||Global methylation:1||Global survey:1||Global transport:1||Global trend:1||Glucose:1||Growth:1||Growth velocity:1||Guidelines:1||Gut microbial dysbiosis:1||H4IIE:1||H4IIEluc transactivation bioassay:1||HALOGENATED BYPRODUCTS:1||HAZARD ASSESSMENT:1||HBCDD:1||HONGKONG:1||HORMONES:1||HOUSEDUST:1||HPG axis:1||HUMAN BREASTMILK:1||HUMAN GUT MICROBIOTA:1||HUMAN URINE:1||HYDROXYANISOLE:1||Halowax:1||Hand cream:1||Harbor:1||Heavy metals:1||Hexachlorobenzene:1||Hg:1||Highresolution mass spectrometry:1||Historical record:1||Homemade baby food:1||Homes:1||Human biomonitoring:1||Human serum:1||Hypothalamuspituitarygonad axis:1||ICC:1||IMMATURE RAINBOWTROUT:1||IMMUNOTOXICITY:1||INHOUSE DUST:1||INUTERO:1||INDEXES:1||INDIVIDUALS:1||INTESTINAL METHANOGENESIS:1||IRONMETABOLISM:1||Identification:1||Immunotoxicity:1||Imprinted gene:1||In silico modeling:1||In vitro metabolism:1||Indoor air:1||Innate amounts:1||Interspecies:1||Intervention:1||Intestinal damage:1||Intestinal microbial metabolites:1||Inventories:1||Invertebrate:1||Japanese medaka:1||Kindergarten:1||Kinetic assay:1||Kongsfjorden:1||Korea:1||Korean population:1||LEPTIN:1||LEPTIN LEVELS:1||LIQUIDCHROMATOGRAPHY:1||LUNG:1||Lactational exposure:1||Lactational transfer:1||Lake Shihwa:1||Larimichthys crocea:1||Larimichthys polyactis:1||Legislative action:1||Liver:1||Liver microsomes:1||Longrange transport:1||Low molecular weight phthalates:1||MALE REPRODUCTIVESYSTEM:1||MDS:1||MEHP:1||MESSENGERRNA:1||METABOLIC SYNDROME:1||METABOLISM:1||METABOLITES:1||METHYLMERCURY:1||MODEL ASSESSMENT:1||MULTIPLE COMPOUNDS:1||Malondialdehyde:1||Management:1||Marian Cove:1||Marine pollution:1||Mass discharge:1||Mass inventory:1||Mass mortalities:1||Maternal:1||Maternal blood:1||Meconium:1||Medaka:1||Melamine:1||Mercury and lead exposures:1||Metabolic activity:1||Metabolic syndrome:1||Metal stable isotopes:1||Methyl mercury:1||Microenvironment:1||Micropollutants:1||Minke whale:1||Minke whales:1||Mitochondria:1||Mitochondrial 16S rRNA:1||Mitochondrial signaling pathways:1||Motherchild pairs:1||Multiomics:1||Multipollutant approach:1||NATIONALHEALTH:1||NBFR:1||NIST:1||NONDIABETIC ADULTS:1||NONMONOTONIC DOSE RESPONSES:1||NONYLPHENOL:1||Nationwide monitoring:1||Neonates:1||Neonicotinoid insecticide:1||Nontarget:1||NyÅlesund:1||NyAlesund:1||OMEGA3FATTYACIDS:1||ORAL GAVAGE:1||ORGANIC POLLUTANTS:1||ORGANICCHEMICALS:1||ORGANOCHLORINE COMPOUNDS:1||ORGANOCHLORINE PESTICIDES:1||ORGANOCHLORINES:1||Obesogen:1||Occurrence:1||Ocean current:1||Ocean dumping:1||Octanolwater partition coefficient (Kow):1||Organic contaminants:1||Organochlorine:1||Organochlorine compounds:1||Organochlorine pesticide mixtures:1||Organochlorine pesticides (OCPs):1||Organochlorines:1||Organophosphate ester:1||Organophosphate esters:1||Organophosphates:1||Organophosphorus flame retardants:1||Organophosphorus flame retardants (PFRs):1||Oxygen consumption:1||PAPER:1||PAPER PRODUCTS:1||PARTICLESIZE DISTRIBUTIONS:1||PASSIVE AIR SAMPLERS:1||PBDD/Fs as byproducts, in waste incineration:1||PBDD/Fs toxicity, bioaccumulative, activating AhR:1||PBDDs and dibenzofurans:1||PBDES:1||PBPK:1||PCAMLR:1||PCBS:1||PCDD:1||PCDF:1||PCN:1||PERFLUORINATED COMPOUNDS:1||PERFLUOROOCTANE SULFONATE:1||PERSONAL CARE PRODUCTS:1||PERSONALCARE PRODUCTS:1||PERSPECTIVE:1||PFASsFamilyHouse dustDietSerumExposure assessmentRisk assessment:1||PFNA:1||PFOA:1||PHTHALATEESTERS:1||PLACENTAL TISSUE SAMPLES:1||PMHs:1||POLYCHLORINATED BIPHENYL 153:1||POLYCHLORINATEDBIPHENYLS PCBS:1||POSTNATAL EXPOSURE:1||PRENATAL EXPOSURE:1||PROSPECTIVE COHORT:1||Parabens:1||Partition coefficient:1||Partitioning:1||Pb:1||Pelagic:1||Per And Polyfluoroalkyl Substances:1||Perchlorate:1||Perfluorinated:1||Perfluorinated alkyl substances:1||Perfluorinated compounds:1||Perfluoroalkyl acids (PFAAs):1||Perfluoroalkyl and polyfluoroalkyl substances:1||Perfluoroalkyl substances:1||Perfluorooctanesulfonic acid:1||Perfluorooctanoic acid:1||Perinatal exposure:1||Persistent organic pollutants:1||Persistent toxic substances:1||Personalized exploration:1||Pesticide:1||Pesticides:1||Pharmaceutical:1||Phenolic:1||Photodegradation process:1||Phthalate metabolites:1||Physiologicallybased pharmacokinetic model:1||Polar environment:1||Pollution history:1||Polychlorinated biphenyls (PCBs):1||Polycyclic aromatic hydrocarbon:1||Polyfluoroalkyl substances:1||Ponderal index:1||Porpoises:1||Postpartum depression:1||Potential toxicity:1||Power plant:1||Premenopausal women:1||Prenatal exposure:1||Probabilistic risk estimation:1||Productbased exposure:1||Propyl paraben:1||Purified water:1||QSAR modeling:1||QuEChERS:1||RAINBOWTROUT:1||RATLIVER:1||RECEPTOR:1||REMOVAL:1||RESIDUES:1||RESISTANCE:1||RISK:1||RIVER:1||RIVER DELTA:1||ROSmediated pathways:1||Realtime PCR:1||Receipt:1||Receptorbased exposure:1||Relative exposure contribution:1||Repeated measurement:1||Repeatedly collected urines:1||Reproduction:1||Rivers:1||SAFETY ASSESSMENT:1||SALMOGAIRDNERI:1||SALMON SALMOSALAR:1||SEAFOOD CONSUMPTION:1||SEASONALVARIATION:1||SEDIMENT:1||SENSITIVITY:1||SERUM:1||SERUM CONCENTRATIONS:1||SEWAGETREATMENT:1||SODIUM/IODIDE SYMPORTER:1||SOURCE APPORTIONMENT:1||SOUTH CHINA:1||SOUTHKOREA:1||SPATIALDISTRIBUTION:1||STABILIZERS:1||STIMULATING HORMONE:1||SULFONATE:1||SUNSCREENS:1||SURFACE:1||SURVIVAL:1||Safety limit:1||Salinity:1||Seal:1||Sebastes schlegeli:1||Sentinel:1||Serum:1||Sex difference:1||Sex hormone:1||Sex steroid:1||ShapiroWilk test:1||Shark:1||Silicone:1||Skin care:1||Snow core:1||Soil:1||Soilair exchange:1||Source identification:1||Spatial distribution:1||Spatiotemporal distribution:1||Species identification:1||Species sensitivity distribution:1||SpragueDawley rat:1||Stable isotope:1||Standard criteria:1||Stockholm Convention:1||Streamwater:1||Sulfide:1||Suspect:1||Synthetic musk compounds:1||TANDEM MASSSPECTROMETRY:1||TBBPA:1||TBEOP:1||TDCPP:1||TEMPORAL TRENDS:1||TEQs:1||TIMECOURSE VARIATION:1||TOC:1||TOF:1||TOM:1||TOXIC POLLUTANTS:1||TRACE ORGANIC CONTAMINANTS:1||TRACKING:1||TREATMENT PLANTS:1||TRENDS:1||TRIBUTYLTIN TBT:1||TRICLOSAN:1||TRIPHENYLTIN:1||TROUT ONCORHYNCHUSMYKISS:1||TUMOR PROMOTION:1||Tap water:1||Teenage girls:1||Temporal trends:1||Terephthalate:1||Threshold:1||Threshold value:1||Tidal power plant:1||Time of flight:1||Timeactivity diary:1||Tissue distribution:1||Tokyo Bay:1||Tolerable daily intake:1||Toxicological mechanisms:1||Trace metals:1||Transformation product:1||Transplacental:1||Trend:1||Triclosan:1||Trophic magnification factor:1||Trophic transfer:1||Type 2 diabetes:1||URBANRURAL TRANSECT:1||URINE:1||UV FILTERS:1||UV328:1||UVFILTERS:1||Umbilical cord blood:1||Urbanization:1||Urinary biomarkers:1||Urinary concentrations:1||Urinary dilution:1||Urinary excretion:1||VTG:1||Variability:1||Vertical profiles:1||Vibrio fischeri:1||WEIGHTLOSS:1||Wastewater indicator:1||Water purifier:1||Whale:1||Whales:1||Withinsubject variation:1||Women of reproductive age:1||Young children:1||Zebraflsh:1||acute aquatic toxicity:1||alternative:1||aquatic pollution:1||aquatic toxicity data:1||aryl hydrocarbon receptormediatedactivity:1||benthic organism:1||benthos:1||benzo(a)pyrene:1||benzothiazole:1||bioaccumulation:1||biomagnification:1||breast milk:1||cPAH:1||cadmium:1||central limit theorem:1||cetaceans:1||combustion processes:1||coprostanol:1||cumulative risk:1||cyclic:1||delta C13:1||delta N15:1||dioxinlike:1||ewaste:1||ecological risk:1||ecological risk assessment:1||female workers:1||fish:1||free cortisol:1||fullscan screening:1||geographic origin:1||haplotype:1||hazard assessment:1||hierarchical clustering analysis:1||house dust:1||house dust mite allergens:1||human health:1||industrial wastewater:1||lead:1||linear:1||luc bioassay:1||manganese:1||marbled sole:1||marine ecosystems:1||marinemammals:1||maternal serum:1||medaka:1||mediation effect:1||mercury:1||minke whales:1||mitochondrial DNA:1||multidimensional scaling:1||newborns:1||nonferrous:1||nonylphenol:1||normal distribution:1||octanol/water partition coefficient (Kow):1||organic pollutant:1||phosphate chemicals:1||phthalates:1||plasticizer:1||polybrominated diphenyl ethers:1||polybrominated diphenyl ethers (PBDEs):1||polychlorinated biphenyls:1||polychlorinated dibenzopdioxins:1||polychlorinated dibenzofurans:1||polymorphism:1||population structure:1||pregnant women:1||proteome:1||proteomics:1||radiation:1||readacross assessment:1||rubber additives:1||seasonal variation:1||seawater:1||sediment quality:1||settled house dust:1||sewage:1||shrimp:1||siloxane:1||siloxanes:1||source:1||species identification:1||species sensitivity factor:1||temporal trend:1||total organic carbon (TOC):1||transcription:1||transfer ratio:1||umbilical cord serum:1||관리:1||기준:1||양식장:1||퇴적물:1||1HYDROXYPYRENE CONCENTRATIONS:1||해수:1||2,2 ',4,4 'tetrabromodiphenyl ether (BDE47):1||2,2',3,3',4,4',5,5',6,6'decabromodiphenyl ether (BDE 209):1||2,2',4,4'tetrabromodiphenyl ether (BDE 47):1||2NAPHTHOL:1||4HB:1||6PPDquinone:1||8Hydroxy2 'deoxyguanosine (8OHdG):1||8OHdG:1||A BPA:1||A CONTAMINATION:1||A multipollutant approach:1||ACCUMULATION:1||ACIDESTERS PARABENS:1||AChE inhibition:1||ADIPONECTIN:1||ADIPOSETISSUE:1||ADIPOSITY:1||AGRICULTURAL SOILS:1||ANALOGS:1||ANTIFOULING PAINTS:1||ASIAN COUNTRIES:1||ASSOCIATION:1||Adiponectin:1||Adjustment:1||Adolescents:1||Adult male zebrafish:1||Adverse health effect:1||Aggregate exposure:1||AhRmediated activity:1||AhRmediated potency:1||Air cleaner captured dust:1||Albumintocreatinine ratio (ACR):1||Alternative plasticizer:1||Amino acid:1||Aquaculture:1||Aquaculture products:1||Aquatic biota:1||Arctic:1||Association:1||Atmospheric deposition flux:1||BAN:1||BDE153:1||BDE47:1||BDE99:1||BEHTBP:1||BENZOATE PRESERVATIVES PARABENS:1||BHT:1||BINDING:1||BIOACCUMULATION:1||BIODEGRADATION:1||BIOMARKER:1||BIOSOLIDS:1||BISPHENOLA:1||BOB 47:1||BPA ratio:1||BPF:1||BREASTCANCER CELLS:1||BTs:1||BUTYLATED HYDROXYTOLUENE:1||BUTYLTIN COMPOUNDS:1||BUVS:1||BaP:1||Babyfood:1||Bayley scales of infant development (BSID):1||Behavior:1||Benign diseases:1||Benthic:1||Benthic community:1||Benthos:1||Benzophenones:1||Bioaccumulation potentials:1||Bioconcentration:1||Bioconcentration factor (BCF):1||Biomagnification:1||Bird:1||Bisphenol A (BPA):1||Bisphenol S (BPS):1||Bivalve:1||Blacktailed gull eggs:1||Blood lipids:1||Body burden:1||Body mass change:1||Breastmilk:1||Brominated dibenzopdioxins and dibenzofurans:1||Brominated flame retardant:1||Brominatedflame retardant:1||Bulk samples:1||CANADA:1||CANCER:1||CARDIOVASCULARDISEASE:1||CD28 EXPRESSION:1||CD8(+) CD28():1||CELLS:1||CHAIN PERFLUORINATED ACIDS:1||CHEMICALS:1||CHIMINHCITY:1||CHILDREN:1||CHINESE SURFACE SOIL:1||CHLOROHYDROXY DERIVATIVES:1||CHROMATOGRAPHY:1||CHROMATOGRAPHYMASS SPECTROMETRY:1||CHROMATOGRAPHYMASSSPECTROMETRY:1||COI sequencing:1||CORROSIONINHIBITION:1||Cancer risk:1||Carbon isotope:1||Cashier:1||Cetacean animals:1||Cetaceans:1||Chemical tracer:1||Chemicals of concern:1||Child behavior checklist (CBCL):1||Chloralkali:1||Chlordane:1||Chlorinated dibenzopdioxins and dibenzofurans:1||Chlorobenzenes:1||Chronic kidney disease (CKD):1||Climate change:1||Coal:1||Coastal sediment:1||Cohort study:1||Combustion activities:1||Common dolphin:1||Common dolphins:1||Congener:1||Cord:1||Correction factor:1||Correlation:1||Cosmetic:1||Cosmetics:1||Creatinine:1||Cresyl diphenyl phosphate (CDP):1||Cyanuric acid:1||Cytochrome:1||Cytochrome P450:1||Cytochrome c oxidase subunit I:1||D5:1||DECHLORANE PLUS:1||DEHTP:1||DERIVATIVES:1||DEUTERIUMLABELED DEHP:1||DI(2ETHYLHEXYL)PHTHALATE DEHP:1||DIABETESMELLITUS:1||DIETARYINTAKE:1||DINCH:1||DIPHENYL ETHERS PBDES:1||DISEASE:1||DLPCBs:1||DNA microarray system:1||DP:1||DPMI:1||DYSFUNCTION:1||Danio rerio:1||Dated sediment:1||DecaBDE:1||Decamethylcyclopentasilane:1||Dechlorane Plus:1||Decreasing trend:1||Dermal application:1||Dermal exposure:1||Developmental origins of health and disease (DOHaD):1||Diabetes:1||Diastereoisomer:1||Dietary exposure:1||Dilution factor:1||Dioxinlike PCBs:1||Dioxinlike compounds:1||Direct assessment:1||Distribution levels:1||DnBP:1||Dodecamethylcyclohexasilane:1||Dolphins:1||Domestic pollution:1||Dust:1||Ewaste:1||EDC:1||ENDOCRINEDISRUPTING COMPOUNDS:1||ENVIRONMENT:1||ENVIRONMENTALPOLLUTANTS:1||EQUIVALENCY FACTORS TEFS:1||EXPOSURE:1||East Sea:1||Ecological risk assessment:1||Embryolarva:1||Emerging PAHs:1||Emerging contaminants:1||Emission:1||Emission flux:1||Endocrine disrupting chemicals (EDCs):1||Endocrinedisrupting chemical:1||Environmental pollutant:1||Exposure pathway:1||Exposure sources:1||FATE:1||FATTYACIDS:1||FISH:1||FISH CONSUMPTION:1||FLUOROTELOMER ALCOHOLS:1||FOOD:1||FOODWEB:1||FOSA:1||Family:1||Fecal sterols:1||Fetal growth:1||Fetus:1||Fibroids:1||Finless porpoise:1||Firefighters:1||First morning void:1||Fish consumption:1||Fluorotelomer alcohol:1||Fluorotelomer iodides:1||Fluxes:1||Food consumption:1||Fractionation:1||Free cortisol:1||Freshwater:1||

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