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HCID 32872생성일: 2026년 10월 27일

이소펜포스

아아이소펜포스(아이소펜포스) · 이소펜포스 · 아이소펜포스 · 2-((에톡시((1-메틸에틸)아미노)포스피노티오일)옥시)벤조산1-메틸에틸에스테르 · 40sd · Amaze · pyrfon · Pryfon

https://huagongshe.com/ko/chemical/32872

이소펜포스 분자 구조식

식별자 및 물리적 특성

CAS No.103982-06-5
분자식C15H24NO4PS
평균 분자량345.4 g/mol
단동위원소 질량345.11636642 g/mol
SMILESCCOP(=S)(NC(C)C)Oc1ccccc1C(=O)OC(C)C
InChIKeyHOQADATXFBOEGG-UHFFFAOYSA-N
PubChem CID32872
ChEMBLCHEMBL1882342
ChEBICHEBI:6009
EC No.246-814-1
DTXSIDDTXSID8032417
현지명이소펜포스

화학 및 물리적 성질

XLogP4.1
극성 표면적88.9
수소 결합 공여자 수1
수소 결합 수용자 수6
회전 가능 결합 수9
무거운 원자 수22
형식 전하0
복잡도403
LogP(분배 계수)log Kow= 4.12
냄새Characteristic
밀도1.131 @ 20 °C1.131 g/cm3 (20 ºC)
용해도Readily soluble in n-hexane, dichloromethane, 2-propanol, tolueneIn water, 22.1 mg/l @ 20 °C0.0221 mg/mL at 20 °C클로로포름 (약간 용해됨), DMSO (약간 용해됨)
끓는 점120 °C @ 0.01 mm Hgbp0.01 120°
DecompositionWhen heated to decomposition it emits toxic fumes of /phosphorus oxides, sulfur oxides, & nitrogen oxides/.DT50 for aqueous hydrolysis /is/ 2.8 yr (pH 4), >1 yr (pH 7), >1 yr (pH 9) (22 °C).
녹는점Less than -12 °C-12℃
증기압0.000003 [mmHg]3.00X10-6 mm Hg @ 25 °C2.2 x 10-4 Pa (20 °C)
헨리 상수Henry's Law constant= 4.15X10-8 atm cu-m/mol @ 20 °C1.2×102 mol/(m3Pa) at 25℃, Mackay et al. (2006)
Physical DescriptionIsofenphos is a colorless oil. Non corrosive. Used as an insecticide.Liquid[Merck Index] Colorless liquid[CAMEO]
Stability/Shelf LifePhotodegradation on soil surface in the laboratory is extremely rapid. Under natural light, photodegradation is not so fast.
Kovats Retention Index203320452060.120182048.12039.32038.62064206620622055.52063.82064.12070.92070.52046.520652035.8
저장 조건0-6°C
용해도18mg l-1(20°C)
pKa(산도 계수)-0.30±0.70(Predicted)
물리적 상태기름
색상무색
EPAIsofenphos (25311-71-1)

화학적 성질

Isofenphos is a colorless oil at room temperature. It is sparingly soluble in water, but soluble in cyclohexone, toluene, acetone, and diethyl ether. The US EPA has grouped isofenphos under RUP, which indicates that qualifi ed, certifi ed, and trained workers are required in the safety management of isofenphos. It is used on turf and ornamental trees and shrubs to control white grubs, mole crickets, and other insects, such as soil-dwelling insects, cabbage root fl ies, corn roundworms, and wire worms.

안전 및 규제

GHS 분류DangerH301: Toxic if swallowed [Danger Acute toxicity, oral]H311: Toxic in contact with skin [Danger Acute toxicity, dermal]H400: Very toxic to aquatic life [Warning Hazardous to the aquatic environment, acute hazard]H410: Very toxic to aquatic life with long lasting effects [Warning Hazardous to the aquatic environment, long-term hazard]P262, P264, P270, P273, P280, P301+P316, P302+P352, P316, P321, P330, P361+P364, P391, P405, and P501 (click each P-code to see the statement)
규제 정보Isofenphos is listed in the dataset of EPA Human Health Benchmarks for Pesticides under the Safe Drinking Water Act (40 eCFR 141)2002/2076The New Jersey Worker and Community Right to Know Act requires public and private employers to provide information about hazardous substances at their workplaces. (N.J.S.A. 34:5A-1 et. seq.)
기타 안전 정보IMAP assessments - Benzoic acid, 2-[[ethoxy[(1-methylethyl)amino]phosphinothioyl]oxy]-, 1-methylethyl ester: Environment tier I assessmentIMAP assessments - Benzoic acid, 2-[[ethoxy[(1-methylethyl)amino]phosphinothioyl]oxy]-, 1-methylethyl ester: Human health tier I assessment
운송 라벨(DOT)Poison
화재 위험Excerpt from ERG Guide 152 [Substances - Toxic (Combustible)]:Combustible material: may burn but does not ignite readily. Containers may explode when heated. Those substances designated with a (P) may polymerize explosively when heated or involved in a fire. Runoff may pollute waterways. Substance may be transported in a molten form. (ERG, 2024)
건강 유해성Excerpt from ERG Guide 152 [Substances - Toxic (Combustible)]:Highly toxic, may be fatal if inhaled, ingested or absorbed through skin. Contact with molten substance may cause severe burns to skin and eyes. Avoid any skin contact. Fire may produce irritating, corrosive and/or toxic gases. Runoff from fire control or dilution water may be corrosive and/or toxic and cause environmental contamination. (ERG, 2024)
유해성 요약Not irritating to skin and mildly irritating to eyes of rabbitsNo evidence of delayed neuropathy in intramuscular injection study with hens[HSDB] No developmental effects in studies with rats at doses that caused cholinesterase inhibition in mothers

용도

용도

Isofenphos is an organophosphorus insecticide used in soil to control leaf-eating and soil-dwelling pests in vegetables, fruits, turf and field crops.

일반 설명

Colorless oil. Non corrosive. Used as an insecticide.

No available studies on human reproductive effects or effects on lactation
[REPROTOX] No clinical or histopathological evidence of delayed neurotoxicity in three studies with hens (at doses up to 2 mg/kg bw for 90 days and single oral doses up to 74 mg/kg bw after antidotal treatment)
Observations of delayed neurotoxic effects in one study with hens two weeks following (dosage of 100 mg/kg bw achieved with antidotal treatments)
[Reference #2] The average of two baseline respective cholinesterase activity determinations three days apart, with no exposures to enzyme inhibiting pesticides for at least 30 days, is recommended for each worker prior to exposure to cholinesterase inhibitors because of large inter-individual differences in published baseline values. To be established at least once a year. Removal from workplace exposures is recommended until the cholinesterase activity returns to within 20% of baseline. [TLVs and BEIs]
반응성 그룹Amines, Phosphines, and PyridinesEsters, Sulfate Esters, Phosphate Esters, Thiophosphate Esters, and Borate Esters
FIFRA 요건As the federal pesticide law FIFRA directs, EPA is conducting a comprehensive review of older pesticides to consider their health and environmental effects and make decisions about their future use. Under this pesticide reregistration program, EPA examines health and safety data for pesticide active ingredients initially registered before November 1, 1984, and determines whether they are eligible for reregistration. In addition, all pesticides must meet the new safety standard of the Food Quality Protection Act of 1996. Pesticides for which EPA had not issued Registration Standards prior to the effective date of FIFRA '88 were divided into three lists based upon their potential for human exposure and other factors, with List B containing pesticides of greater concern and List D pesticides of less concern. Isophenphos is found on List B. Case No: 2345Pesticide type: insecticide, herbicideCase Status: PreRED - OPP is reviewing data from the pesticide's producers regarding its human health and/or environmental effects, or OPP is determining the pesticide's eligibility for reregistration and developing the Reregistration Eligibility Decision (RED) document.Active ingredient (AI): isopropylsalicylate,O-ester with O-ethyl isopropylphosphoramidothioateData Call-in (DCI) Date(s): 05/10/91, 03/03/95, 10/13/95AI Status: The producers of the pesticide has made commitments to conduct the studies and pay the fees required for reregistration, and are meeting those commitments in a timely manner.
Reactivity ProfileOrganothiophosphates, such as ISOFENPHOS, are susceptible to formation of highly toxic and flammable phosphine gas in the presence of strong reducing agents such as hydrides. Partial oxidation by oxidizing agents may result in the release of toxic phosphorus oxides.
DOT Hazard ClassificationIsofenphosMarine pollutant
Air and Water ReactionsHydrolyzed by alkali solution.
Hazard Classes and CategoriesAcute Tox. 3 (97.6%)Acute Tox. 1 (92.9%)Aquatic Acute 1 (100%)Aquatic Chronic 1 (100%)Acute toxicity - category 3Hazardous to the aquatic environment (acute) - category 1Hazardous to the aquatic environment (chronic) - category 1Acute toxicity (Oral) - Category 1Acute toxicity (Dermal) - Category 2Acute toxicity (Inhalation: Dusts and mists) - Category 2Skin corrosion/irritation - Category 3Serious eye damage/eye irritation - Category 2BReproductive toxicity - Category 2Specific target organ toxicity - Single exposure - Category 1 (nervous system)Specific target organ toxicity - Repeated exposure - Category 1 (nervous system, testis)Hazardous to the aquatic environment (Long-term) - Category 1Acute Tox. 3 *Aquatic Chronic 1
소화Excerpt from ERG Guide 152 [Substances - Toxic (Combustible)]:SMALL FIRE: Dry chemical, CO2 or water spray.LARGE FIRE: Water spray, fog or regular foam. If it can be done safely, move undamaged containers away from the area around the fire. Dike runoff from fire control for later disposal. Avoid aiming straight or solid streams directly onto the product.FIRE INVOLVING TANKS, RAIL TANK CARS OR HIGHWAY TANKS: Fight fire from maximum distance or use unmanned master stream devices or monitor nozzles. Do not get water inside containers. Cool containers with flooding quantities of water until well after fire is out. Withdraw immediately in case of rising sound from venting safety devices or discoloration of tank. ALWAYS stay away from tanks in direct contact with flames. For massive fire, use unmanned master stream devices or monitor nozzlesif this is impossible, withdraw from area and let fire burn. (ERG, 2024)
응급 처치Excerpt from ERG Guide 152 [Substances - Toxic (Combustible)]:Refer to the "General First Aid" section. Specific First Aid: Removal of solidified molten material from skin requires medical assistance. (ERG, 2024)
노출 관리 및 개인 보호Biological Exposure Indices (BEI) [ACGIH] - Acetylcholinesterase activity in red blood cells = 70% of individual's baselineButylcholinesterase activity in serum or plasma = 60% of individual's baselineSample at end of shift[TLVs and BEIs]
비화재 누출 대응Excerpt from ERG Guide 152 [Substances - Toxic (Combustible)]:ELIMINATE all ignition sources (no smoking, flares, sparks or flames) from immediate area. Do not touch damaged containers or spilled material unless wearing appropriate protective clothing. Stop leak if you can do it without risk. Prevent entry into waterways, sewers, basements or confined areas. Cover with plastic sheet to prevent spreading. Absorb or cover with dry earth, sand or other non-combustible material and transfer to containers. DO NOT GET WATER INSIDE CONTAINERS. (ERG, 2024)
Isolation and EvacuationExcerpt from ERG Guide 152 [Substances - Toxic (Combustible)]:IMMEDIATE PRECAUTIONARY MEASURE: Isolate spill or leak area in all directions for at least 50 meters (150 feet) for liquids and at least 25 meters (75 feet) for solids.SPILL: Increase the immediate precautionary measure distance, in the downwind direction, as necessary.FIRE: If tank, rail tank car or highway tank is involved in a fire, ISOLATE for 800 meters (1/2 mile) in all directionsalso, consider initial evacuation for 800 meters (1/2 mile) in all directions. (ERG, 2024)
Allowable TolerancesAll food tolerances for Isofenphos have been revoked (effective January 1999).
Personal Protective Equipment (PPE)Excerpt from ERG Guide 152 [Substances - Toxic (Combustible)]:Wear positive pressure self-contained breathing apparatus (SCBA). Wear chemical protective clothing that is specifically recommended by the manufacturer when there is NO RISK OF FIRE. Structural firefighters' protective clothing provides thermal protection but only limited chemical protection. (ERG, 2024)
환경 거동TERRESTRIAL FATE: Based on a classification scheme(1), Koc values from 633 to 1,474 on four soils(2) indicate that isofenphos is expected to have low mobility in soil(SRC). Volatilization of isofenphos from moist soil surfaces is not expected to be an important fate process(SRC) given a Henry's Law constant of 4.15X10-8 atm-cu m/mole(3). Isofenphos is not expected to volatilize from dry soil surfaces(SRC) based upon a vapor pressure of 3.00X10-6 mm Hg(4). Isophenophos degrades on soil exposed to light with a half-life of 72 days(2). In a week-long incubation study using 6 soils with a history of isofenphos use and 19 soils with no previous use, an increased rate of mineralization in the soils with previous use history (35.9 +/- 2.4% of the parent mineralized to CO2) was found compared with the nonhistory soils (2.4+/-1.0%)(2). In a 4-week incubation study, 62.8% of the parent was recovered from a soil with no history of use and only 12.9% from a soil that was previously treated with isofenphos(2). Mineralization of the aromatic ring was evident(2). Isofenphos oxygen analog (also called isofenphos oxon) was identified as degradation product(2).TERRESTRIAL FATE: In turf plots in Georgia and Minnesota and soil plots in Georgia and California, isofenphos dissipated from the upper 6 inches of soil with first-order half-lives of 7 to 81 days and DT50s (the time in which 50% of the pesticide dissipates from the surface of the soil) ranging from 10 to 63 days(1). In California, a rapid initial dissipation (half-life = 7 days) was followed by a plateau and a secondary dissipation half-life of >63 days(1). When both isofenphos and the structurally-similar oxon analog are considered together, the dissipation half-lives range from 21 to 170 days(1). The studies only tracked isofenphos and the formation of its oxygen analog, but did not evaluate the formation of other degradates (including volatiles) or incorporation/ binding within the soil(1). The pesticide use history was unknown in the Georgia turf and soil plots(1). Isofenphos use was not reported in the previous 5 years on the other sites(1). Supplemental field studies covering 23 sites reported dissipation half-lives ranging from less than 2 weeks to more than 1 year, depending on factors such as formulation, location, and number of applications(1). Isofenphos and its oxygen analog were not detected below 12 inches in the Georgia and Minnesota turf studies or below 6 inches in the Georgia bareground study(1). Isofenphos was detected to 18 inches and the oxygen analog to 30 inches in the California bareground study(1). The soils in the California study had a much lower organic matter content (<0.5%) than did the other three sites(1). The results suggest that while isofenphos is not highly mobile through the soil profile, under certain conditions it may move into the subsurface(1).AQUATIC FATE: Based on a classification scheme(1), Koc values from 633 to 1,474 on four soils(2) indicate that isofenphos is expected to adsorb to suspended solids and sediment(SRC). Volatilization from water surfaces is not expected(SRC) based upon a Henry's Law constant of 4.15X10-8 atm-cu m/mole(3). According to a classification scheme(4), BCF values in fish tissues of 94.5 (fillet), 469 (viscera), and 277 (whole body)(2), suggests bioconcentration in aquatic organisms is high(SRC). Isophenphos is stable to hydrolysis at pHs 5 and 7 and degrades slowly at pH 9 with a half-life of 131 days(2). Isophenophos is stable to photolysis in water(2). Using non- sterilized, filtered river water at pH 7.3, isofenphos degraded in 97 and 175 days at 22 and 6 °C, respectively(5). In seawater at pH 8.1, isofenphos degraded in 118 and 224 days at 22 and 6 °C, respectively(5). In filtered estuarine water (pH 7.8, salinity 20 g/l) from the Ebre River, Spain, the degradation half-life for isofenphos ranged from 9.8-11.9 days(6).ATMOSPHERIC FATE: According to a model of gas/particle partitioning of semivolatile organic compounds in the atmosphere(1), isofenphos, which has a vapor pressure of 3.00X10-6 mm Hg at 25 °C(2), will exist in both the vapor and particulate phases in the ambient atmosphere(SRC). Vapor-phase isofenphos is degraded in the atmosphere by reaction with photochemically-produced hydroxyl radicals(SRC)the half-life for this reaction in air is estimated to be 1.4 hrs(SRC), calculated from its rate constant of 2.75X10-10 cu cm/molecule-sec at 25 °C(SRC) that was derived using a structure estimation method(3). Particulate-phase isofenphos may be removed from the air by wet and dry deposition(SRC).
식품 조사 수치In Canada between 1992-1994, isofenphos was found in 1 of 105 broccoli (fresh) samples and 1 of 211 cauliflower (fresh) samples at concns <0.05 ppm(1). In Canada between 1989-1991, isofenphos was found in 1 of 1,044 samples of potato (fresh) and 2 of 187 samples of broccoli (fresh) at concns of 0.05 ppm(2).
유해 작용Neurotoxin - Predominantly motorOther Poison - Organophosphate
Soil Adsorption/MobilityThe Koc of isofenphos ranged from 633 to 1,474 on four soils(1). According to a classification scheme(2), these Koc values suggest that isofenphos is expected to have low mobility in soil(SRC).
Atmospheric ConcentrationsURBAN/SUBURBAN: The concn of isofenphos in ambient air from Kitakyushu, Japan was 10 ng/cu m in July 1991 and 0.73 ng/cu m in April 1992(1).
Human Toxicity Excerpts... A unique case of attempted suicide /was reported/ by intramuscular injection of the organophosphate isofenphos which resulted in a muscarinic and nicotinic syndrome lasting 15 days and requiring prolonged mechanical ventilation and hospitalization. The patient, who demonstrated no signs of delayed polyneuropathy on hospital day 25, subsequently died of pneumonia. Toxicological investigations showed isofenphos plasma decay and confirmed the intramuscular route of poisoning. It appears that continuous isofenphos absorption resulted in the prolonged intoxication observed in this patient.Late progressive polyneuropathy followed by pyramidal findings in a 20-year old agricultural laborer who ingested Isofenphos solution during his work, is presented. The patient was confined to a wheelchair within 6 weeks, regained walking ability within 6 months, and a 23 months' follow up revealed slight additional clinical improvement with minimal progression of the pyramidal signs. The neuropathic clinical manifestations, the EMG and the nerve conduction studies were compatible with a pathology of a distal, mainly axonal, mainly motor neuropathy.The organophosphate pesticide, isofenphos, is associated with human myeloid leukemia. In this study we describe metabolic changes in K562 myeloid blast cells from exposure to varying concentrations of isofenphos using the stable [1,2-13C(2)]glucose isotope as the single tracer and biological mass spectrometry. Isofenphos (1, 10, 100 microg/ml/72 hr) treated K562 cells showed increases of 10.7, 33.8 and 39.7% in lactate production as well as a 14.2% increase (1 microg/ml/72 hr) in 13C incorporation into nucleic acid ribose from glucose. Concomitantly, we observed a decrease in glucose oxidation and the synthesis of glutamate, palmitate and stearate from glucose. Our results demonstrate that this organophosphate pesticide exerts a leukemogenic effect by the recruitment of glucose carbons for nucleic acid synthesis thus promoting proliferation simultaneous with poor differentiation. The imbalanced metabolic phenotype with a severe defect in glucose oxidation, lipid and amino acid synthesis concurrent with de novo synthesis of nucleic acids in response to isofenphos treatment conforms to the invasive proliferating phenotype observed in TGF-beta treated lung epithelial carcinoma cells.
Artificial Pollution SourcesIsofenphos' former(1) production may have resulted in its release to the environment through various waste streamsits former use as an insecticide on crops and turf grass(2) resulted in its direct release to the environment(SRC).
Environmental BiodegradationAEROBIC: Isofenphos degrades slowly (half-life of 352 days) under aerobic soil conditions(1). Although isofenophos is persistent when first applied to soils, microbial adaptations enhance degradation in subsequent years(1). In a week-long incubation study using 6 soils with a history of isofenphos use and 19 soils with no previous use, an increased rate of mineralization in the soils with previous use history (35.9 +/- 2.4% of the parent mineralized to CO2) was found compared with the nonhistory soils (2.4+/-1.0%)(1). In a 4-week incubation study, 62.8% of the parent was recovered from a soil with no history of use and only 12.9% from a soil that was previously treated with isofenphos(1). Mineralization of the aromatic ring was evident(1). Isofenphos oxygen analog (also called isofenphos oxon) was identified as degradation product(1). If both isofenphos and the structurally similar isofenphos oxon are considered together, the aerobic soil metabolism half-life is on the order of 3 years(1). Isofenphos oxon accumulated only in a nonhistory soil(1). Repeated annual treatments of isofenphos increased the enhanced degradation activity in soil(1). Enhanced degradation activity was still apparent in soils more than 162 weeks after the last treatment(1). Exposure of soil to salicylic acid, a secondary hydrolysis product, resulted in enhanced degradation of isofenphos(1). The formation of salicylic acid in soil may be a key factor in triggering the susceptibility of isofenphos to enhanced degradation(1). It is not clear whether the presence of other organophosphates may trigger enhanced degradation(1).AEROBIC: Using non-sterile, filtered river water at pH 7.3, isofenphos degraded in 97 and 175 days at 22 and 6 °C, respectively(1). In seawater at pH 8.1, isofenphos degraded in 118 and 224 days at 22 and 6 °C, respectively(1). In filtered estuarine water (pH 7.8, salinity 20 g/l) from the Ebre River, Spain, the degradation half-life for isofenphos ranged from 9.8-11.9 days(2).ANAEROBIC: Isofenphos is stable under anaerobic aquatic conditions(1). In an anaerobic aquatic metabolism study, the distribution of applied isofenphos residues increased from 30% to >60% in the pond water and decreased from 69% to <30% in the sediment after 1 year (isofenphos comprised 90% of the residues)(1). This data suggests, at least in stagnant waters, a significant portion of applied isofenphos will remain in the water column(1).
Sediment/Soil ConcentrationsSEDIMENT: In Florida, isofenphos was not detected (limits of detection ranging from 1.2 to 36 mg/kg, dry weight) in 68 sediment samples taken from lakes, estuaries, streams and outflows(1).
Environmental BioconcentrationBCFs of 94.5 (fillet), 469 (viscera), and 277 (whole body) in fish tissues were measured for isofenphos(1). According to a classification scheme(2), these BCF values suggests the potential for bioconcentration in aquatic organisms is high(SRC).
Volatilization from Water/SoilThe Henry's Law constant for isofenphos is 4.15X10-8 atm-cu m/mole(1). This Henry's Law constant indicates that isofenphos is expected to be essentially nonvolatile from water surfaces(2). Isofenphos is not expected to volatilize from dry soil surfaces(SRC) based upon a vapor pressure of 3.00X10-6 mm Hg(3).
Non-Human Toxicity ExcerptsNot irritating to skin, slightly irritating to eyes (rabbits).In 1990 an outbreak of ataxia occurred in over 700 pigs in the north of England. /Follow up/ studies demonstrated that the disorder was associated with the consumption of feed from a particular supplier and that one component (wheat screenings) was common to the batch of feed with which the ataxia was associated. An analysis of the feed demonstrated the presence of an organophosphorus pesticide, later identified as isofenphos, a pesticide not approved for use in the United Kingdom. The wheat screenings had been imported from France and the warehouse in which they had been stored was contaminated with isofenphos, which is approved for restricted use in France. Isofenphos is known to cause delayed neuropathy. The dose to which the pigs were theoretically exposed would be expected to have resulted in neuropathy (manifested as ataxia).The neuropathic potential of acute and repeated exposures of the phosphoramidates tabun (GA) and isofenphos (IFP), of diisopropyl fluorophosphate (DFP) and paraoxon (PO) were examined in the hen with treatments for up to 90 days via intramuscular injections of the highest tolerated doses with atropine protection. Plasma acetylcholinesterase (AChE), non-specific butyrylcholinesterase (BChE) and creatine kinase (CK) activities were measured in order to monitor whether the compounds were present at biologically active concentrations. Locomotor behavior was observed and tissues from the peripheral and central nervous systems were examined for signs of organophosphate-induced delayed neuropathy (OPIDN). No behavioral or histological evidence of OPIDN was observed after treatments with GA, IFP, PO, saline or atropine sulfate. DFP-treated birds displayed locomotor and neuropathological signs of OPIDN with a no effect level (NOEL) between 25 and 50 micrograms/kg.
수질 위해 등급(WGK)2
RTECS 번호VO4395500
운송 번호(UN)3018
독성LD50 orally in rats, mice (mg/kg): 30-40, 90-130 (Homeyer)
관세 코드29299090
위험 문구(R)24/25-50/53-52/53-36-20/21/22-11
위험 표시T,N,Xn,F
안전 문구(S)36/37-45-60-61-26-16
포장분류I
위험 등급6.1(a)
기존화학 물질KE-13447
유해 물질 데이터25311-71-1(Hazardous Substances Data)
함량 및 규제정보물질구분: 유독물질혼합물(제품)함량정보: 이소펜포스 및 이를 1% 이상 함유한 혼합물
유해화학물질 필터링97-1-230