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

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Moon, Hyo-Bang (문효방)

COLLEGE OF SCIENCE AND CONVERGENCE TECHNOLOGY (DEPARTMENT OF MARINE SCIENCE AND CONVERGENCE ENGINEERING)

Research Area: 환경분석화학, 해양오염, Environmental Analytical Chemistry, Marine Pollution

Tel 031-400-5534
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Coprostanol:10||Sediment:9||PAHs:9||WWTP:9||PBDEs:9||PCBs:8||DEHP:8||PCDD/Fs:8||POPs:7||Nonylphenol:7||POLYCHLORINATEDBIPHENYLS:7||Bioaccumulation:7||Bisphenol A:6||Polychlorinated biphenyls:6||Masan Bay:6||Phthalates:6||PBDE:6||Wastewater treatment plant:6||Daily intake:6||PFOS:6||Infant:5||Sediments:5||HUMAN EXPOSURE:5||Alternative:5||Pregnant women:5||TEQ:5||Plasticizer:5||Marine mammals:5||OPFR:5||Toxicity:5||Synthetic musk:5||PERSISTENT ORGANIC POLLUTANTS:5||Fecal sterol:5||Sewage:5||GCQTOFMS:4||Human exposure:4||Time trend:4||Risk:4||POLYBROMINATED DIPHENYL ETHERS:4||DBDPE:4||Mercury:4||Temporal trend:4||Indoor dust:4||Organochlorine pesticides:4||Seafood:4||Seawater:4||Biomonitoring:4||Personal care products:4||Marine mammal:4||Health risk:4||Flame retardant:4||Estimated daily intake:4||PCB:4||Regulation:4||BTBPE:3||HHCB:3||ORGANOTIN COMPOUNDS:3||ENDOCRINEDISRUPTING CHEMICALS:3||Lactation:3||Mokpo:3||DecaBDE:3||Limanda yokohamae:3||Vertical profiles:3||Polybrominated diphenyl ethers:3||Siloxane:3||Siloxanes:3||Multidimensional scaling (MDS):3||Thyroid hormones:3||DEHT:3||Crassostrea gigas:3||CONTAMINATION:3||Sludge:3||COASTAL WATERS:3||Dietary intake:3||WASTEWATER:3||BDE 209:3||exposure:3||Flame retardants:3||Lead:3||Riverine discharge:3||ESTROGENIC ACTIVITY:3||TCPP:3||POLYCYCLIC AROMATICHYDROCARBONS:3||Phthalate:3||Methyl paraben:3||Placental transfer:3||BROMINATED FLAME RETARDANTS:3||DIBENZOPDIOXINS:3||Organophosphate flame retardants:3||Urine:3||Children:3||Sediment quality:3||OXIDATIVE STRESS:2||Feeding habit:2||BPA:2||SPRAGUEDAWLEY RATS:2||Atmospheric deposition:2||Organic contaminants:2||Organic wastewater compounds:2||Finless porpoises:2||Industrial area:2||Industrial complex:2||Industry:2||Sediment core:2||Sediment elutriate:2||BPS:2||Insulin resistance:2||Oxidative stress:2||Breast milk:2||Interspecies difference:2||proteomics:2||road dust:2||seafood:2||seasonal variation:2||seawater:2||sediment:2||Inventories:2||Inventory:2||South Korea:2||Jinhae Bay:2||target hazardous quotient (THQ):2||the highest concen:2||Alternative plasticizers:2||Korea:2||Surface sediment:2||LCHRMS:2||Environmental phenols:2||PCDFs:2||TBEP:2||TBT:2||Flux:2||Fluxes:2||Food Contamination:2||CORD BLOOD:2||TOTM:2||PFAS:2||TOXICITY:2||Dioxins:2||Benthic organism:2||PFUnDA:2||BREASTMILK:2||Cyclic:2||Linear:2||Thyroid hormone:2||Loading fluxes:2||BSAF:2||Cetacean:2||Toddler:2||MASSSPECTROMETRY:2||Dust ingestion:2||GREATLAKES ATMOSPHERE:2||Total organic carbon:2||DDT:2||General population:2||Triclocarban:2||Trimester:2||ENVIRONMENT:2||Trophic position:2||ENVIRONMENTAL CHEMICALS:2||Persistent organic pollutant:2||US POPULATION:2||Accumulation profiles:2||Ulsan Bay:2||Marine sediment:2||Placenta:2||WATER:2||Wastewater:2||H4IIEluc bioassay:2||Ecological risk:2||Effectdirected analysis:2||Effluent:2||Embryogenesis:2||Yellow Sea:2||HEALTH:2||Zebrafish:2||Polycyclic aromatic hydrocarbons:2||HONGKONG:2||,4,4&apos:2||bivalves:2||Endocrine disruption:2||HUMAN BLOOD:2||2,2&apos:2||HUMAN SERUM:2||Mokpo coastal water:2||PCDDs:2||CHECK:2||Mussel:2||Epigenetics:2||Hazard ratio:2||RISKASSESSMENT:2||Ethyl paraben:2||NEWYORK:2||Exposure:2||dietary intake:2||Exposure assessment:2||AhR agonists:2||DLPCBs:2||NORTH CHINA:2||environmental pollution:2||Bisphenol F:2||fish:2||Neurodevelopment:2||floor dust:2||Baby food:2||CHINA:2||River water:2||Nonylphenol ethoxylates:2||Adipose tissue:2||OBESITY:2||OCPs:2||Bivalve:2||Debromination:2||human health1. IntroductionA large number of studies have demonstrated thatmany toxic organic contaminants are present in themarine environment:2||Combustion process:2||lifetime cancer risk:2||INVITRO:2||Dechlorane:2||Fecal sterols:2||First morning void:1||Fish consumption:1||Fluoranthene:1||Fluorotelomer alcohol:1||Fluorotelomer iodides:1||Food consumption:1||Fractionation:1||Free cortisol:1||Freshwater: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||Geologic Sediments:1||Global methylation:1||Global survey:1||Global transport:1||Global trend:1||Glucose:1||Growth:1||Growth velocity:1||Guidelines:1||H4IIEluc transactivation bioassay:1||HALOGENATED BYPRODUCTS:1||HARBOR:1||HAZARD ASSESSMENT:1||HORMONES:1||HOUSEDUST:1||HPG axis:1||HPLCMS/MS:1||HUMAN BREASTMILK:1||HUMAN GUT MICROBIOTA:1||HUMAN URINE:1||HYDROXYANISOLE:1||Halowax:1||Harbor:1||Heavy metals:1||Hexachlorobenzene:1||Hg:1||Historical record:1||Homemade baby food:1||Homes:1||Human serum:1||Humans:1||Hypothalamuspituitarygonad axis:1||ICC:1||IMMATURE RAINBOWTROUT:1||IMMUNOTOXICITY:1||IMPOSEX:1||INHOUSE DUST:1||INUTERO:1||INDEXES:1||INDIVIDUALS:1||INTESTINAL METHANOGENESIS:1||IRONMETABOLISM:1||Identification:1||Immunotoxicity:1||Imposex Level:1||Imprinted gene:1||In vitro metabolism:1||Innate amounts:1||Interspecies:1||Intervention:1||Invertebrate:1||Japanese medaka:1||Kinetic assay:1||Korean Coastal Water: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||Macrobenthic Community:1||Male:1||Management:1||Marine pollution:1||Mass discharge: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||Middle Aged:1||Minke whale:1||Minke whales:1||Mitochondria:1||Mitochondrial 16S rRNA:1||Motherchild pairs:1||Multiomics:1||Multipollutant approach:1||Mussel watch:1||Mussels:1||Mytilus edulis:1||NATIONALHEALTH:1||NBFR:1||NIST:1||NONDIABETIC ADULTS:1||NONMONOTONIC DOSE RESPONSES:1||NONYLPHENOL:1||NUCELLALAPILLUS:1||Neonates:1||Nontarget:1||Nontarget screening:1||Nonylphenols:1||NyAlesund:1||OMEGA3FATTYACIDS:1||ORAL GAVAGE:1||ORGANIC CONTAMINANTS:1||ORGANIC POLLUTANTS:1||ORGANICCHEMICALS:1||ORGANOCHLORINE COMPOUNDS:1||ORGANOCHLORINE PESTICIDES:1||ORGANOCHLORINES:1||Obesogen:1||Occurrence:1||OctaBDE:1||Octanolwater partition coefficient (Kow):1||Organochlorine:1||Organochlorine compounds:1||Organochlorine pesticide mixtures:1||Organochlorine pesticides (OCPs):1||Organochlorines: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||PCBS:1||PCDD:1||PCDF:1||PCN:1||PERFLUORINATED COMPOUNDS:1||PERFLUOROOCTANE SULFONATE:1||PERSONAL CARE PRODUCTS:1||PERSONALCARE PRODUCTS:1||PERSPECTIVE: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||Partitioning:1||Pb:1||Pelagic: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||Pesticide:1||Pesticides:1||Pharmaceutical:1||Pharmaceuticals and personal care products:1||Phenolic:1||Photodegradation process:1||Phthalate metabolites:1||Physiologicallybased pharmacokinetic model:1||Plasticizers:1||Pollution history:1||Polychaete:1||Polychlorinated biphenyls (PCBs):1||Polycyclic Hydrocarbons, Aromatic:1||Polycyclic aromatic hydrocarbon:1||Polyfluoroalkyl substances:1||Ponderal index:1||Porpoises:1||Postpartum depression:1||Potential toxicity:1||Premenopausal women:1||Precipitation:1||Prenatal exposure:1||Prioritization:1||Probabilistic risk estimation:1||Productbased exposure:1||Propyl paraben:1||Purified water:1||Pusan [South Korea]:1||QuEChERS:1||RAINBOWTROUT:1||RATLIVER:1||RECEPTOR:1||REMOVAL:1||RESIDUES:1||RESISTANCE:1||RISK:1||RIVER:1||RIVER DELTA:1||ROCK SHELL:1||Realtime PCR:1||Receipt:1||Receptorbased exposure:1||Relative Penis Le:1||Relative exposure contribution:1||Repeated measurement:1||Repeatedly collected urines:1||Reproduction:1||Reproductive Output:1||Reproductive Success:1||Risk assessment:1||Risk management:1||Rivers:1||SAFETY ASSESSMENT:1||SALMOGAIRDNERI:1||SALMON SALMOSALAR:1||SEAFOOD CONSUMPTION:1||SEASONALVARIATION:1||SEDIMENT:1||SEDIMENTS:1||SENSITIVITY:1||SERUM:1||SERUM CONCENTRATIONS:1||SEWAGE POLLUTION: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||Saccharin:1||Safety limit:1||Salinity:1||Seafood consumption:1||Sebastes schlegeli:1||Sediment contamination:1||Sentinel:1||Sex difference:1||Sex hormone:1||Sex steroid:1||ShapiroWilk test:1||Shark:1||Silicone:1||Snow core:1||Soil:1||Soilair exchange:1||Source identification:1||Spatial distribution:1||Species identification:1||SpragueDawley rat:1||Stable isotope:1||Standard criteria:1||Stockholm Convention:1||Streamwater:1||Suburban Area:1||Sulfide:1||Suspect:1||Synthetic musk compounds:1||TANDEM MASSSPECTROMETRY:1||TBBPA:1||TBEOP:1||TDCPP:1||TEMPORAL TRENDS:1||TEQs:1||THAISCLAVIGERA:1||TIMECOURSE VARIATION:1||TOC:1||TOM:1||TOXIC POLLUTANTS:1||TRACE ORGANIC CONTAMINANTS:1||TRACKING:1||TREATMENT PLANTS:1||TRENDS:1||TRIBUTYLTIN:1||TRIBUTYLTIN TBT:1||TRICLOSAN:1||TRIPHENYLTIN:1||TROUT ONCORHYNCHUSMYKISS:1||TUMOR PROMOTION:1||Tap water:1||Temporal trends:1||Temporal variability:1||Threshold:1||Threshold value:1||Tidal power plant:1||Time Factors:1||Time of flight:1||Tissue distribution:1||Tokyo Bay:1||Tolerable daily intake:1||Total Organic Carbon Content:1||Trace metals:1||Transplacental:1||Trend:1||Tributyltin (TBT):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 dilution:1||Urinary excretion:1||VTG:1||Variability:1||Vertical profile:1||Vibrio fischeri:1||WEIGHTLOSS:1||Wastewater indicator:1||Wastewater treatment plant (WWTP):1||Water Pollutants, Chemical:1||Water purifier:1||Whale:1||Whales:1||Withinsubject variation:1||Women of reproductive age:1||Young children:1||Zebraflsh:1||alternative:1||ambient temperature:1||aquatic pollution:1||aquatic toxicity data:1||aryl hydrocarbon receptormediatedactivity:1||benthic community:1||benzo(a)pyrene:1||biomagnification:1||body weight:1||breast milk:1||brominated flameretardants (BFRs):1||bulk sample:1||cPAH:1||cadmium:1||central limit theorem:1||cephalopods:1||cetaceans:1||chemical levels:1||chemical pollutant:1||combustion processes:1||congener distribution:1||coprostanol:1||crustaceans:1||cumulative risk:1||decaBDE:1||delta C13:1||delta N15:1||deposition flux:1||depositional flux:1||dioxinlike:1||ewaste:1||early life stages:1||environmental contamination:1||environmental legislation:1||female:1||female workers:1||flame retardant:1||food co:1||food consumption:1||free cortisol:1||fullscan screening:1||gastropods:1||gene expression:1||geographic origin:1||haplotype:1||hazard assessment:1||health risk:1||hierarchical clustering analysis:1||house dust:1||house dust mite allergens:1||human health:1||industrial wastewater:1||lead:1||major clinical study:1||manganese:1||marbled sole:1||marine ecosystems:1||marine environmental contamination:1||marine sediment:1||marinemammals:1||maternal serum:1||medaka:1||mediation effect:1||mercury:1||minke whales:1||mitochondrial DNA:1||multidimensional scaling:1||multidimensional scaling (MDS):1||mussel:1||mussel culture:1||newborns:1||nonferrous:1||nonylphenol:1||normal distribution:1||organic pollutant:1||phenanthrene: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||precipitation:1||pregnant women:1||priority:1||proteome:1||radiation:1||risk assessment:1||sediment elutriate:1||sediment pollution:1||sediment quality:1||sediment toxicity:1||sediments:1||settled house dust:1||sewage:1||shrimp:1||species identification:1||total organic carbon (TOC):1||transcription:1||transfer ratio:1||umbilical cord serum:1||xenobiotics:1||관리:1||기준:1||양식장:1||퇴적물:1||,3,3&apos:1||해수:1||,4,4 &apos:1||,5,5&apos:1||,6,6&apos:1||decabromodiphenyl ether (BDE 209):1||deoxyguanosine (8OHdG):1||tetrabromodiphenyl ether (BDE 47):1||tetrabromodiphenyl ether (BDE47):1||1HYDROXYPYRENE CONCENTRATIONS:1||2,2 &apos:1||2NAPHTHOL:1||4HB:1||8Hydroxy2 &apos:1||8OHdG:1||A BPA:1||A CONTAMINATION:1||A multipollutant approach:1||ACCUMULATION:1||ACIDESTERS PARABENS:1||ACPbased PCR:1||ADIPONECTIN:1||ADIPOSETISSUE:1||ADIPOSITY:1||ADJACENT:1||AGRICULTURAL SOILS:1||AHTN:1||ALKYLPHENOLS:1||ANALOGS:1||ANTIFOULING PAINT:1||ANTIFOULING PAINTS:1||ASIAN COUNTRIES:1||ASSOCIATION:1||Acetaminophen:1||Adiponectin:1||Adjustment:1||Adverse health effect:1||Aggregate exposure:1||Albumintocreatinine ratio (ACR):1||Amino acid:1||Antibiotics:1||Aquaculture:1||Aquaculture products:1||Aquatic biota:1||Aquatic ecosystem:1||Arctic:1||Artificial sweeteners:1||Aryl hydrocarbon receptor:1||Asian dust event:1||Aspartame:1||Association:1||Atmospheric deposition flux:1||BAN:1||BAY: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||BiP:1||Bioaccumulation potentials:1||Bioconcentration:1||Bioconcentration factor (BCF):1||Biomagnification:1||Bird:1||Bisphenol A (BPA):1||Bisphenol S (BPS):1||Bisphenols:1||Bivalvia: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||Butyltin Compound: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||CHOP:1||CHROMATOGRAPHY:1||CHROMATOGRAPHYMASS SPECTROMETRY:1||CHROMATOGRAPHYMASSSPECTROMETRY:1||COASTAL ENVIRONMENT:1||COI sequencing:1||CORROSIONINHIBITION:1||Cancer risk:1||Carbon isotope:1||Cashier:1||Cetacean animals:1||Cetaceans:1||Child:1||Child behavior checklist (CBCL):1||Child, Preschool:1||Chloralkali:1||Chlordane:1||Chlorinated dibenzopdioxins and dibenzofurans:1||Chlorobenzenes:1||Chronic kidney disease (CKD):1||Climate change:1||Coal Combustion: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||DERIVATIVES:1||DEUTERIUMLABELED DEHP:1||DI(2ETHYLHEXYL)PHTHALATE DEHP:1||DIABETESMELLITUS:1||DIETARYINTAKE:1||DINCH:1||DIOXINLIKE:1||DIPHENYL ETHERS PBDES:1||DISEASE:1||DNA microarray system:1||DP:1||DYSFUNCTION:1||Danio rerio:1||Dated sediment:1||Decamethylcyclopentasilane:1||Dechlorane Plus:1||Decreasing trend:1||Dermal exposure:1||Developmental origins of health and disease (DOHaD):1||Diabetes:1||Diastereoisomer:1||Diesel Exhaust:1||Diet:1||Dietary exposure:1||Digestive Gland:1||Dioxinlike PCBs:1||Direct assessment:1||Distribution levels:1||DnBP:1||Dodecamethylcyclohexasilane:1||Dolphins:1||Domestic pollution:1||Dust:1||Ewaste:1||EC50:1||ENDOCRINEDISRUPTING COMPOUNDS:1||ENVIRONMENTALPOLLUTANTS:1||EQUIVALENCY FACTORS TEFS:1||ER stress:1||EXPOSURE:1||Emission:1||Emission flux:1||Endocrine disrupting chemicals (EDCs):1||Endocrine disruptors:1||Endocrinedisrupting chemical:1||Environmental pollutant:1||Environmental pollution:1||Exposure pathway:1||F–53B:1||F53B:1||FATE:1||FATTYACIDS:1||FECAL STEROLS:1||FISH:1||FISH CONSUMPTION:1||FLUOROTELOMER ALCOHOLS:1||FOOD:1||FOODWEB:1||FOSA:1||Fetal growth:1||Fetus:1||Fibroids:1||Finless porpoise:1||Firefighters:1||

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