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HCID 73282作成日：2026年10月27日

2-(2-クロロエトキシ)-N-[(4-メトキシ-6-メチル-1,3,5-トリアジン-2-イルアミノ)カルボニル]ベンゼンスルホンアミド

N-(6-メトキシ-4-メチル-1,3,5-トリアジン-2-イルアミノカルボニル)-2-(2-クロロエトキシ)ベンゼンスルホンアミド · 1-[2-(2-クロロエトキシ)フェニルスルホニル]-3-[(6-メトキシ-4-メチル-1,3,5-トリアジン)-2-イル]尿素 · 2-(2-クロロエトキシ)-N-[(4-メトキシ-6-メチル-1,3,5-トリアジン-2-イルアミノ)カルボニル]ベンゼンスルホンアミド · 1-[2-(2-クロロエトキシ)フェニルスルホニル]-3-(4-メトキシ-6-メチル-1,3,5-トリアジン-2-イル)尿素 · 1-(4-メチル-6-メトキシ-1,3,5-トリアジン-2-イル)-3-[2-(2-クロロエトキシ)フェニルスルホニル]尿素 · 1-(4-メチル-6-メトキシ-1,3,5-トリアジン-2-イル)-3-[[2-(2-クロロエトキシ)フェニル]スルホニル]尿素 · トリアスルフロン · トリアスルフロン標準品

https://huagongshe.com/ja/chemical/73282

2-(2-クロロエトキシ)-N-[(4-メトキシ-6-メチル-1,3,5-トリアジン-2-イルアミノ)カルボニル]ベンゼンスルホンアミド の分子構造式

識別子と物理属性

CAS No.82097-50-5
分子式C14H16ClN5O5S
平均分子量401.8 g/mol
単同位体質量401.0560675 g/mol
SMILESCOc1nc(C)nc(NC(=O)NS(=O)(=O)c2ccccc2OCCCl)n1
InChIKeyXOPFESVZMSQIKC-UHFFFAOYSA-N
PubChem CID73282
ChEMBLCHEMBL1896787
ChEBICHEBI:9673
EC No.617-298-9
DTXSIDDTXSID0024345
現地名2-(2-クロロエトキシ)-N-[(4-メトキシ-6-メチル-1,3,5-トリアジン-2-イルアミノ)カルボニル]ベンゼンスルホンアミド

化学・物理的性質

XLogP2.3
極性表面積141
水素結合供与体数2
水素結合受容体数8
回転可能結合数7
重原子数26
形式電荷0
複雑度560
農薬Pesticide -> EPA IRISHerbicidesActive substance -> EU Pesticides database: Not approvedEnvironmental transformation -> Pesticides (parent, predecessor)Pesticide (Triasulfuron) -> USDA PDB
LogP（分配係数）log Kow = 1.1 (pH 5.0), -0.59 (pH 6.9), -1.8 (pH 9.0) at 25 °C2.04
密度1.5 g/cu cm1.5218 (rough estimate)
Color/FormFine white powder
溶解度In water, 1.5 g/L (pH 7) at 20 °CIn water, 32 mg/L (pH 5), 815 mg/L (pH 7), 13,500 mg/L (pH 8.2) at 25 °CSolubility (g/L at 25 °C): Acetone 14, dichloromethane 36, ethyl acetate 4.3)Solubility (mg/L at 25 °C): ethanol 420, n-octanol 130, n-hexane 0.04, toluene 300DMSO (Slightly), Methanol (Slightly, Heated)
DecompositionHazardous decomposition products formed under fire conditions: Carbon oxides, nitrogen oxides (NOx), sulfur oxides, hydrogen chloride gas.
融点178.1 °C (decomposes)Melting point: 186 °C178°C
蒸気圧Vapor pressure: 7.5X10-13 mm Hg at 20 °CVapor pressure: 2.25X10-10 mm Hg at 25 °C (based on the Knudsen diffusivity (m sq/sec) measured value for triasulfuron's close analog Chlorsulfuron)<1.5X10-8 mm Hg at 25 °C (OECD Guideline Method 104)0Pa at 25℃
Stability/Shelf LifeStable under recommended storage conditions.
Ionization EfficiencyPositive2.172.7Agilent XCTElectrospray ionizationformic acid (5.3nM)
Dissociation ConstantspKa = 4.64
Other Experimental PropertiesHenry's Law constant = <2.5X10-10 atm-cu m/mole at 23 °C (estimated from vapor pressure and water solubility (pH 5)calculated value at pH7 and pH9 will be even lower due to higher water solubility
沸点150-260 °C
屈折率1.5630 (estimate)
貯蔵条件0-6°C
pKa（酸解離定数）4.34±0.10(Predicted)
BRN7151883
ヘンリー定数8.0×108 mol/(m3Pa) at 25℃, Ebert et al. (2023)
主な用途農業環境
InChI1S/C14H16ClN5O5S/c1-9-16-12(19-14(17-9)24-2)18-13(21)20-26(22,23)11-6-4-3-5-10(11)25-8-7-15/h3-6H,7-8H2,1-2H3,(H2,16,17,18,19,20,21)
InChIKeyXOPFESVZMSQIKC-UHFFFAOYSA-N
SMILESCOc1nc(C)nc(NC(=O)NS(=O)(=O)c2ccccc2OCCCl)n1
LogP（分配係数）1.6-2.6 at 25℃ and pH5-9
CAS データベース82097-50-5(CAS DataBase Reference)
EPAの化学物質情報Triasulfuron (82097-50-5)

安全性と法規制

GHS 分類WarningH400: Very toxic to aquatic life [Warning Hazardous to the aquatic environment, acute hazard]P273, P391, and P501 (click each P-code to see the statement)H400 (100%): Very toxic to aquatic life [Warning Hazardous to the aquatic environment, acute hazard]
規制情報Commission Regulation (EU) No 1141/2010Triasulfuron is listed in the dataset of EPA Human Health Benchmarks for Pesticides under the Safe Drinking Water Act (40 eCFR 141)00/66/EC, 2010/77/EU, Reg (EU) 2015/408, Reg. (EU) 2015/1885, Reg. (EU) 2016/864, Reg. (EU) No 540/2011REACH registered substance: Triasulfuron (EC: 617-298-9)
FIFRA 要件Tolerances are established for residues of the herbicide triasulfuron [3-(6-methoxy-4-methyl-1,3,5-triazin-2-yl)-1-(2-(2-chloroethoxy)phenylsulfonyl)urea] in or on the following raw agricultural commodities:[Table#8503]
Hazard Classes and CategoriesAquatic Acute 1 (100%)Hazardous to the aquatic environment (acute) - category 1
Hazardous Reactivities and IncompatibilitiesIncompatible materials: Strong oxidizing agents
消火手順Suitable extinguishing media: Use water spray, alcohol-resistant foam, dry chemical or carbon dioxide.Advice for firefighters: Wear self-contained breathing apparatus for firefighting if necessary.
保管条件Keep container tightly closed in a dry and well-ventilated place.
清掃方法ACCIDENTAL RELEASE MEASURES: Personal precautions, protective equipment and emergency procedures: Use personal protective equipment. Avoid dust formation. Avoid breathing vapors, mist or gas. Ensure adequate ventilation. Evacuate personnel to safe areas. Avoid breathing dust. Environmental precautions: Prevent further leakage or spillage if safe to do so. Do not let product enter drains. Discharge into the environment must be avoided. Methods and materials for containment and cleaning up: Pick up and arrange disposal without creating dust. Sweep up and shovel. Keep in suitable, closed containers for disposal.
処分方法SRP: Recycle any unused portion of the material for its approved use or return it to the manufacturer or supplier. Ultimate disposal of the chemical must consider: the material's impact on air quality

用途

使用

Herbicide.

potential migration in air, soil or water
effects on animal, aquatic and plant life
and conformance with environmental and public health regulations. If it is possible or reasonable use an alternative chemical product with less inherent propensity for occupational harm/injury/toxicity or environmental contamination.
Product: Offer surplus and non-recyclable solutions to a licensed disposal company. Contact a licensed professional waste disposal service to dispose of this material. Contaminated packaging: Dispose of as unused product.
Preventive MeasuresACCIDENTAL RELEASE MEASURES: Personal precautions, protective equipment and emergency procedures: Use personal protective equipment. Avoid dust formation. Avoid breathing vapors, mist or gas. Ensure adequate ventilation. Evacuate personnel to safe areas. Avoid breathing dust. Environmental precautions: Prevent further leakage or spillage if safe to do so. Do not let product enter drains. Discharge into the environment must be avoided.Precautions for safe handling: Avoid contact with skin and eyes. Avoid formation of dust and aerosols. Provide appropriate exhaust ventilation at places where dust is formed.Appropriate engineering controls: Handle in accordance with good industrial hygiene and safety practice. Wash hands before breaks and at the end of workday.Gloves must be inspected prior to use. Use proper glove removal technique (without touching glove's outer surface) to avoid skin contact with this product. Dispose of contaminated gloves after use in accordance with applicable laws and good laboratory practices. Wash and dry hands.SRP: Local exhaust ventilation should be applied wherever there is an incidence of point source emissions or dispersion of regulated contaminants in the work area. Ventilation control of the contaminant as close to its point of generation is both the most economical and safest method to minimize personnel exposure to airborne contaminants. Ensure that the local ventilation moves the contaminant away from the worker.
Allowable TolerancesTolerances are established for residues of the herbicide triasulfuron [3-(6-methoxy-4-methyl-1,3,5-triazin-2-yl)-1-(2-(2-chloroethoxy)phenylsulfonyl)urea] in or on the following raw agricultural commodities:[Table#8502]
Personal Protective Equipment (PPE)Eye/face protection: Safety glasses with side-shields conforming to EN 166. Use equipment for eye protection tested and approved under appropriate government standards such as NIOSH (US) or EN 166(EU).Handle with gloves.Body Protection: Complete suit protecting against chemicals. The type of protective equipment must be selected according to the concentration and amount of the dangerous substance at the specific workplace.Respiratory protection: For nuisance exposures use type P95 (US) or type P1 (EU EN 143) particle respirator. For higher level protection use type OV/AG/P99 (US) or type ABEK-P2 (EU EN 143) respirator cartridges. Use respirators and components tested and approved under appropriate government standards such as NIOSH (US) or CEN (EU).
体内負荷Triasulfuron geometric mean concentrations in urine for the US population from years 2003-2008 were below the detection limit of 0.07 ug/L(1).
標的器官Hepatic
生態毒性値LC50Species: Colinus virginianus (Northern Bobwhite Quail) age 14 daysdiet >5000 ppm for 8 days /94.5% purity/Species: Anas platyrhynchos (Mallard Duck) diet >5000 ppm for 8 days /94.5% purity/LD50Species: Anas platyrhynchos (Mallard Duck) oral via capsule >2150 mg/kg /94.5% purity/Species: Colinus virginianus (Northern Bobwhite Quail) age 175 daysoral via capsule >2150 mg/kg /94.5% purity/For more Ecotoxicity Values (Complete) data for Triasulfuron (17 total), please visit the HSDB record page.
環境中動態TERRESTRIAL FATE: Based on a classification scheme(1), measured Koc ranges of 7-25(2) and 51.6-190.6(3) in a variety of soils, indicate that triasulfuron is expected to have very high to moderate mobility in soil(SRC). The pKa of triasulfuron is 4.64(4), indicating that this compound will exist partially in anion form at pH 5 and almost entirely in the anion form at pH 7-9 in the environment(SRC) and anions generally do not adsorb more strongly to soils containing organic carbon and clay than their neutral counterparts(5). Some studies indicate adsorption in soil can be effected by humic acids and pH(6,7) while other studies found that adsorption of triasulfuron was not pH dependent(8). Volatilization of non-ionized triasulfuron from moist soil surfaces is not expected to be an important fate process(SRC) given an estimated Henry's Law constant of <2.5X10-10 atm-cu m/mole(SRC), derived from its vapor pressure, <1.5X10-8 mm Hg(4), and water solubility, 32-13500 mg/L at pH5-8.2(4). Triasulfuron in anion form will not volatilize. Triasulfuron is not expected to volatilize from dry soil surfaces(SRC) based upon its vapor pressure(SRC). Triasulfuron did not volatilize from soil or plant surfaces during photolytic degradation tests(2). Triasulfuron was found to be not readily biodegradable in sediment-water degradation studies with biodegradation half-lives ranging from 30-245 days(2). Measured half-lives of triasulfuron in microbially active soils (pH 6.5 or 7.2) were found to be four times faster than those in sterile soil(9). Triasulfuron is susceptible to aqueous hydrolysis in moist acidic soilshydrolysis half-life is about 30 days at pH 5 and 20 °C(3). Triasulfuron absorbs at wavelengths >290 nm(3) and is susceptible to direct photolysis by sunlight on soil surfaces(2). Reported half-lives in field dissipation studies ranged from 3-48 days (mean of 19 days), 8-59 days and 10-87 days(8). and 10-87 days(3).FIELD STUDY: Herbicides are essential in agricultural systems for maintaining crop yields, as weeds compromise grain production. Furthermore, the application of organic amendments to soil is an increasingly frequent agricultural practice for avoiding irreversible soil degradation. However, this practice could modify the behaviour of the herbicides applied, with implications for their absorption by weeds. This study evaluated the dissipation, persistence and mobility of the herbicides triasulfuron and prosulfocarb in a sandy clay loam soil unamended and amended with green compost (GC) in a field experiment using single or combined commercial formulations of both herbicides. The study was carried out in experimental plots (eight treatments x three replicates) corresponding to unamended soil and soil amended with GC, untreated and treated with the herbicide formulations Logran Tr, Auros Tr and Auros Plus Tr over 100 days. The half-life (DT50) of triasulfuron applied individually was 19.4 days, and increased in the GC-amended soil (46.7 days) due to its higher adsorption by this soil, although non-significant differences between DT50 values were found when it was applied in combination with prosulfocarb. Prosulfocarb dissipated faster than triasulfuron under all the conditions assayed, but non-significant differences were observed for the different treatments. The analysis of the herbicides at different soil depths (0-50 cm) after their application confirmed the leaching of both herbicides to deeper soil layers under all conditions, although larger amounts of residues were found in the 0-10 and 10-20 cm layers. The application of GC to the soil increased the persistence of both herbicides, and prevented the rapid leaching of triasulfuron in the soil, but the leaching of prosulfocarb was not inhibited. The influence of single or combined formulations was observed for triasulfuron, but not for prosulfocarb. The results obtained highlight the interest of obtaining field data to design rational joint applications of GC and herbicides to prevent the possible decrease in their effectiveness for weeds or the risk of water contamination.AQUATIC FATE: Based on a classification scheme(1), measured Koc ranges of 7-25(2) and 51.6-190.6(3) indicate that triasulfuron is not expected to adsorb to suspended solids and sediment(SRC). A pKa of 4.64(4) indicates this compound will exist partially in anion form at pH 5 and almost entirely in the anion form at pH 7-9 in the environment(SRC), and volatilization of the anion form from water surfaces is not expected to be an important fate process(SRC). Volatilization from water surfaces is also not expected of the non-ionized form(3) based upon an estimated Henry's Law constant of <2.5X10-10 atm-cu m/mole(SRC), derived from its vapor pressure, <1.5X10-8 mm Hg(4), and water solubility, 32-13500 mg/L at pH5-8.2(4). According to a classification scheme(5), an estimated BCF of 1(SRC), from its log Kow of 1.10(4) and a regression-derived equation(6), suggests the potential for bioconcentration in aquatic organisms is low(SRC). Triasulfuron was found to be not readily biodegradable in sediment-water degradation studies with biodegradation half-lives ranging from 30-245 days(2). The USDA Pesticide Properties Database lists the hydrolysis rate of triasulfuron as "Stable" at pH 7-9 (20 °C) and 0.023/day (half-life of 30 days) at pH 5 (20 °C)(3). Hydrolysis half-lives at 25 °C were 7.78 days (pH 4), 13.8 days (pH 5), 27.1 days (pH 6), 492 days (pH 7) and 387 days (pH 9)(7). Triasulfuron absorbs at wavelengths >290 nm(2) and, therefore, may be susceptible to direct photolysis by sunlight(SRC). At 10 ppm in aqueous solution at 20 °C, triasulfuron had a 3 hour photo-stability half-life when irradiated with a mercury vapor lamp(2).ATMOSPHERIC FATE: According to a model of gas/particle partitioning of semivolatile organic compounds in the atmosphere(1), triasulfuron, which has a vapor pressure of <1.5X10-8 mm Hg at 25 °C(2), is expected to exist solely in the particulate phase in the ambient atmosphere. Particulate-phase triasulfuron may be removed from the air by wet and dry deposition(SRC). Triasulfuron absorbs at wavelengths >290 nm(3) and, therefore, may be susceptible to direct photolysis by sunlight(SRC). Triasulfuron photodegrades in aqueous solution exposed to sunlight(4).
毒性の概要IDENTIFICATION AND USE: Triasulfuron is a fine white powder. it is used as a selective herbicide pre- and post-emergence for the control of annual broad-leaved weeds in wheat, barley, and triticale. HUMAN STUDIES: There are no data available. ANIMAL STUDIES: In rats fed triasulfuron for 90 days reduced body weight and kidney toxicity observed at 10,000 ppm. In mice fed triasulfuron for 2 years, centrilobular hepatocytomegaly was observed in male mice receiving 1000, 5000, and 10,000 ppm and in females receiving 10,000 ppm. Increased centrilobular degeneration, focal accumulation of inflammatory cells, microgranulomas, and pigment depositions were also observed in the liver of 10,000-ppm males. In dogs, fed triasulfuron in the diet for 1 year, effects seen at 5000 ppm include liver vacuolization, Kupffer cell pigment, lymphoid hyperplasia, anemia, increased relative spleen, kidney (females), pituitary (females), and liver weights, and increased severity of prostate cystic hyperplasia in males. In developmental study in rats, reductions in body weight were noted in F1a and F2a pups. No developmental effects were observed in rabbits. The genotoxicity of trisulfuron was demonstrated in the wing spot test of Drosophila melanogaster. ECOTOXICITY STUDIES: For aquatic organisms triasulfuron photoproducts were less toxic than the parent compound.
生態毒性抜粋/AQUATIC SPECIES/ The present study aimed to compare the sensitivity of larvae of the gilthead seabream (Sparus aurata), a valuable fish species of the Spanish South Atlantic littoral, with the extensively used Microtox test on a commercial herbicide formulation containing terbutryn (59.4%) and triasulfuron (0.6%). To this purpose, mortality displayed by endogenous feeding S. aurata larvae exposed during 72 hr post-hatching to nominal concentrations of the commercial formulation and bioluminescence of the marine bacterium Vibrio fischeri were compared. Histomorphological changes were also studied. Clearly, the S. aurata assay was the more sensitive indicator of toxicity for this herbicide. The 72-hr concentration lethal to 50% of the individuals (LC(50)) found for yolk sac larvae was 1.41 mg/L. This value was more than one order of magnitude below the 15-min EC(50) found for V. fischeri (15.94 mg/L). Growth of the larvae was not significantly affected by a terbutryn-triasulfuron mixture at concentrations up to 1.56 mg/L, the maximum at which there was some proportion of survival./AQUATIC SPECIES/ The toxicological effects of the sulfonylurea herbicide triasulfuron and its photoproducts were assessed on four aquatic organisms. Toxicity varied with tested organism and with triasulfuron irradiation time. Triasulfuron and its photoproducts had no significant effects on the crustacean (Cladocera) Daphnia magna (causing 50% effective concentration [EC50] [48 hr] = 49 +/- 1 mg/L) and the marine bacteria Vibrio fischeri (EC50 [30 min] > 100 mg/L). In contrast, primary producers (the duckweed Lemna minor, the microalgae Pseudokirchneriella subcapitata, and Chlorella vulgaris) were very sensitive to triasulfuron (EC50s < 11 microg/L). For these organisms, triasulfuron photoproducts were less toxic than the parent compound but the residual toxicity observed still represented a potential environmental hazard.
Ongoing Test StatusEPA has released the Interactive Chemical Safety for Sustainability (iCSS) Dashboard. The iCSS Dashboard provides an interactive tool to explore rapid, automated (or in vitro high-throughput) chemical screening data generated by the Toxicity Forecaster (ToxCast) project and the federal Toxicity Testing in the 21st century (Tox21) collaboration. /The title compound was tested by ToxCast and/or Tox21 assays/[USEPAICSS Dashboard ApplicationAvailable from, as of August 9, 2018: http://actor.epa.gov/dashboard/]
EPA IRIS InformationTriasulfuronHepatic1 x 10 ^-2 mg/kg-day
Soil Adsorption/MobilitySoil adsorption studies using 9 soils (organic content 0.6-25%, pH 6.2-7.8) determined a Koc range of 7-25(1). Using three Italian soils (organic matter 1.3, 4.4 and 6.3%), measured Kd values were 0.46, 1.13 and 6.43 respectively(2)these correspond to Koc values of 48, 61 and 173 respectively(SRC). Triasulfuron Koc values of 9.2 and 9.6 were determined in a loam soil and a clay loam soil, respectively(3). The USDA Pesticide Properties Database list a Koc range of 51.6 to 190.6 for triasulfuron with a recommended value of 105(4). According to a classification scheme(5), these Koc values suggest that triasulfuron is expected to have very high to moderate mobility in soil. The content of humic acids and soil pH can effect the soil adsorption of triasulfuron(2,6), although some laboratory studies found that adsorption of triasulfuron and its metabolite (triazine amine) was not pH dependent(7). Mobility tests in three alkaline cropping soils in Australia found triasulfuron to be mobile as leaching exceeded an 80 cm soil depth(8).
Artificial Pollution SourcesTriasulfuron's production may result in its release to the environment through various waste streamsits use as a herbicide to control broad-leaved weeds pre- and post-emergence in wheat, barley and triticale(1) will result in its direct release to the environment(SRC).
Environmental BiodegradationAEROBIC: Laboratory studies in 4 soils at 20 °C found triasulfuron dissipation half-lives of 33-76 days with triazine amine as a metabolite(1). A dissipation half-life of 49 days was observed in laboratory tests at 10 °C(1). In 6 soils at 25 °C in laboratory tests, 90% triasulfuron dissipation occurred in 127-349 days(1). A review of reliable field studies from 17 sites (US, Switzerland, France, Canada, Germany and Brazil) determined a triasulfuron dissipation half-life range of 3-48 days (one exception, 83 days), a mean dissipation half-life of 19 days and 90 percentile of 38 days(1)90% dissipation ranged from 53-300 days with a mean of 70 days(1). Triasulfuron was classified as having moderate to medium persistance based on studies which indicated biphasic kinetics with half lives of 15-48 days at 20 °C and 8-59 days in Europoean field studies(2). The USDA Pesticide Properties Database lists a triasulfuron field dissipation half-life of 10-87 days(3).ANAEROBIC: Laboratory studies at 20 °C found a triasulfuron dissipation half-life of about 280 days under anaerobic conditions(1).
Carcinogen ClassificationNo indication of carcinogenicity to humans (not listed by IARC).
水環境危害等級（WGK）2
RTECS 番号DB1554000
輸送番号（UN）UN3077 9/PG 3
毒性LD50 in rats (mg/kg): >5000 orally>2000 dermallyLC50 (4 hr) in rats: >5185 mg/m3 by inhalation (Amrein, Gerber)
税関コード29350090
危険文句（R）50/53
危険表示N
安全措置（S）60-61
貯蔵分類11 - Combustible Solids
有害物質データ82097-50-5(Hazardous Substances Data)