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Chlorotoluron
CHLORTOLURON · c2242 · tolurex · TORO(R) · dicuran · Dikurin · cga15646 · highuron
Identifikatoren & physikalische Daten
| CAS No. | 15545-48-9 |
|---|---|
| Summenformel | C10H13ClN2O |
| Durchschnittliche Molmasse | 212,67 g/mol |
| Monoisotopische Masse | 212,0716407 g/mol |
| SMILES | Cc1ccc(NC(=O)N(C)C)cc1Cl |
| InChIKey | JXCGFZXSOMJFOA-UHFFFAOYSA-N |
| PubChem CID | 27375 |
| ChEMBL | CHEMBL1900581 |
| ChEBI | CHEBI:81981 |
| EC No. | 239-592-2 |
| DTXSID | DTXSID8052853 |
| Lokaler Name | Chlorotoluron |
Chemische & physikalische Eigenschaften
| XLogP | 2,4 |
|---|---|
| Polarare Oberfläche (TPSA) | 32,3 |
| H-Brücken-Donoren | 1 |
| H-Brücken-Akzeptoren | 1 |
| Frei drehbare Bindungen | 1 |
| Schwere Atome | 14 |
| Formalladung | 0 |
| Komplexität | 208 |
| LogP (Verteilungskoeffizient) | Log Kow = 2.412.5 |
| Geruch | ODORLESS |
| Dichte | 140 g/cu cm1.4 g/cm³1.2426 (rough estimate) |
| Color/Form | COLORLESS CRYSTALSwhite powder |
| Löslichkeit | IT IS SOLUBLE IN MOST ORGANIC SOLVENTSIn acetone 5%, ethyl acetate 2%, benzene 2.4%, isopropanol 1.5%, methylene chloride 4.3% w/vIn water, 70 mg/L at 25 °CIn acetone 54, dichloromethane 51, ethanol 48, toluene 3.0, hexane 0.06, n-octanol 24, ethyl acetate 21 (all in g/L at 25 °C)Solubility in water, g/100ml at 25 °C: 0.0074 (very poor)Chloroform: slightly solubleMethanol: slightly soluble70.43mg/L(20 ºC) |
| Corrosivity | Noncorrosive |
| Schmelzpunkt | 147-148 °C148.1 °C148.3° |
| Dampfdruck | 3.6X10-8 MM HG @ 20 °CVapor pressure at 20 °C: negligible |
| Physical Description | COLOURLESS CRYSTALS OR WHITE POWDER. |
| Stability/Shelf Life | Stable under normal conditions in neutral media. Hydrolyzed by strong acids and alkalis. |
| Kovats Retention Index | 1627.4 |
| Collision Cross Section | 145.96 Ų [M+H]+ [CCS Type: TW]147.5 Ų [M+H]+ [CCS Type: DTMethod: single field calibrated] |
| Siedepunkt | 367.8±42.0 °C(Predicted) |
| Brechungsindex | 1.6000 (estimate) |
| Flammpunkt | 2 °C |
| Lagerbedingungen | APPROX 4°C |
| Aggregatzustand | Solid |
| pKa (Säurekonstante) | 14.43±0.70(Predicted) |
| Farbe | Off-white to light yellow |
| Merck | 13,2191 |
| BRN | 2647688 |
| Henry-Konstante | 7.0×104 mol/(m3Pa) at 25℃, HSDB (2015) |
| Hauptanwendungen | agriculturecleaning productscosmeticsenvironmentalfood and beveragespersonal care |
| InChI | 1S/C10H13ClN2O/c1-7-4-5-8(6-9(7)11)12-10(14)13(2)3/h4-6H,1-3H3,(H,12,14) |
| InChIKey | JXCGFZXSOMJFOA-UHFFFAOYSA-N |
| SMILES | CN(C)C(=O)Nc1ccc(C)c(Cl)c1 |
| CAS Datenbank | 15545-48-9(CAS DataBase Reference) |
| NIST chemische Informationen | Chlortoluron(15545-48-9) |
| EPA chemische Informationen | Chlorotoluron (15545-48-9) |
Sicherheit & Vorschriften
| GHS-Einstufung | WarningH351: Suspected of causing cancer [Warning Carcinogenicity]H361d ***: Suspected of damaging the unborn child [Warning Reproductive toxicity]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]P203, P273, P280, P318, P391, P405, and P501 (click each P-code to see the statement) |
|---|---|
| Regulatorische Informationen | Chemical: Urea, N'-(3-chloro-4-methylphenyl)-N,N-dimethyl-05/53/EC, Reg. (EU) 2017/1511, Reg. (EU) 2018/1262, Reg. (EU) 2019/1589, Reg. (EU) 2020/1511, Reg. (EU) 2021/1449, Reg. (EU) 2022/1480, Reg. (EU) 2023/1757, Reg. (EU) No 533/2013, Reg. (EU) No 540/2011Chlorotoluron: Does not have an individual approval but may be used as a component in a product covered by a group standard. It is not approved for use as a chemical in its own right. |
| Brandgefahren | Combustible. Gives off irritating or toxic fumes (or gases) in a fire. |
| EG-Einstufung | Symbol: Xn, NR: 40-63-50/53S: (2)-26-36/37-46-60-61 |
| Special Reports | Collected Data on Herbicide ToxicologyVerlag Chemie GmBH, Postfach 1260/1280, 6940 Weinheim, Fed Rep of Germany, 4th instalment 2: 272 pages (1983). A loose-leaf collection published by the pesticides Committee of the German Research Association. A statement of the criteria involved in toxicological assessment of pesticides is followed by monographs on several herbicides, their applications, their toxicity to animals and man, and their metabolism or transformation in plants, soil and water. Each monograph is completed by a toxicological evaluation and a bibliography. The 4th supplement offers new or updated information on chlortoluron.Geissbuhler HHow Safe are PesticidesExperientia 38 (8): 890-5 (1982). The safety of the pesticides, chlortoluron and atrazine, is discussed in relation to use, exposure, pollution, etc. |
| Chemical Dangers | On combustion, forms toxic fumes. Reacts with strong acids and strong bases. |
| Packaging and Labelling | Do not transport with food and feedstuffs. |
| Hazard Classes and Categories | Carc. 2 (100%)Repr. 2 (89.4%)Repr. 2 (12.8%)Aquatic Acute 1 (100%)Aquatic Chronic 1 (100%)Carcinogenicity - category 2Reproductive toxicity - category 2Hazardous to the aquatic environment (acute) - category 1Hazardous to the aquatic environment (chronic) - category 1Aquatic Chronic 1 |
| Brandbekämpfung | Use water spray, foam, dry powder, carbon dioxide. |
| Erste-Hilfe-Maßnahmen | Fresh air, rest.Remove contaminated clothes. Rinse and then wash skin with water and soap.First rinse with plenty of water for several minutes (remove contact lenses if easily possible), then refer for medical attention.Rinse mouth. |
| Sichere Lagerung | Provision to contain effluent from fire extinguishing. Store in an area without drain or sewer access. Separated from strong bases, strong acids and food and feedstuffs. |
| Entsorgungsverfahren | SRP: At the time of review, criteria for land treatment or burial (sanitary landfill) disposal practices are subject to significant revision. Prior to implementing land disposal of waste residue (including waste sludge), consult with environmental regulatory agencies for guidance on acceptable disposal practices. |
| Verschüttetes entsorgen | Personal protection: particulate filter respirator adapted to the airborne concentration of the substance. Do NOT let this chemical enter the environment. Sweep spilled substance into covered containers. Carefully collect remainder. |
| Preventive Measures | Avoid contact with skin, clothing and eyes. |
| Eye Prevention | Wear safety goggles. |
| Inhalation Risk | A harmful concentration of airborne particles can be reached quickly when dispersed. |
| Skin Prevention | Protective gloves. |
| Ingestion Prevention | Do not eat, drink, or smoke during work. Wash hands before eating. |
| Inhalation Prevention | Use local exhaust or breathing protection. |
| Effects of Long Term Exposure | Tumours have been detected in experimental animals but may not be relevant to humans. |
| Wechselwirkungen | Levels of cytochrome p450s and rates of monooxygenase activities were studied in microsomes prepared from wheat cell suspension cultures. Cytochrome contents and enzymatic activities, namely, the enzymatic systems responsible for chlorotoluron ring-methy1 hydroxy1ation and N-demethylation, were enhanced after pretreatment of cells with 2,4-D, procloraz, mecoprop, chlorotoluron, and oxime ether safeners. Effects of various agrochemicals were also determined on chlorotoluron ring-methyl hydroxylase and N-demethylase, following their direct addition to microsomal preparations. Plant growth regulators and fungicide, as well as piperonyl butoxide decreased both activities, tetcyclacis, and procloraz being marked1y inhibitory. Naphthalic anhydride, oxime ether safeners, dich1ormid, and tridiphane had only weak effects. The substrate specificities of chlorotoluron ring-methyl hydroxylase and N-demethylase were also investigated using structural analogues of the herbicide. Diuron was the strongest inhibitor among the tested phenylureas. Other herbicides that can be metabolized by wheat affected both activities to different extents. However, diclofop enhanced only chlorotoluron N-demethylase. |
| Ökotoxizitätswerte | LC50 trout more than 100 mg/l |
| Umweltverhalten | TERRESTRIAL FATE: Measured Koc values ranging from 1 to 3467(1) were obtained in a study of seventeen soils from Australiagenerally, measured Koc values averaged from 150-420(2-4) with adsorption dependent on the percentage of organic matter present in the soil(1). Based on a recommended classification scheme(5), these values indicate that chlortoluron will generally have moderate mobility in soil(SRC). Absorption follows an L-isotherm indicating a decrease in site availability as the solution concentration of this compound increases(6). Biodegradation is expected to be the major fate process for chlortoluron in soil(7-9). In an outdoor lysimeter experiment, half-lives of 49 days and 52 days were reported for a silty loam and silty sand soil, respectively(7). Major metabolites of monomethyl chlortoluron(8) and N-demethylated chlortoluron(7) indicate that degradation of chlortoluron proceeds via cleavage of the C-N bond(10). Biodegradation may be slightly attenuated in soils containing higher concentrations of organic matter as sorption may have a protective effect(11). Volatilization of chlortoluron will not be important from moist or dry soil surfaces(SRC) based on an estimated value for its Henry's Law constant(12,13,SRC), and its measured vapor pressure, 3.6X10-8 mm Hg(12), respectively. Half-lives from 4-16 weeks have been determined for chlortoluron in soil(14).AQUATIC FATE: Based on a recommended classification scheme(1), measured Koc values averaging 150-420(2-4) indicate that chlortoluron may adsorb to suspended solids and sediment(SRC) in the water column. Based on results from soil studies(5-7), biodegradation may be an important fate process for this compound in water(SRC). Half-lives from 4-16 weeks have been determined for chlortoluron in soil(5)monomethyl chlortoluron(6) and N-demethylated chlortoluron(5) were the major metabolites of this process. Chlortoluron should not volatilize from water surfaces(8,SRC) based on an estimated Henry's Law constant of 1.4X10-10 atm-cu m/mole(SRC), calculated from experimental values for vapor pressure(9) and water solubility(10). An estimated BCF value of 40(11,SRC), from an experimental log Kow(11), suggests that chlortoluron will not bioconcentrate in aquatic organisms(SRC) according to a recommended classification scheme(12).ATMOSPHERIC FATE: According to a suggested classification scheme(1), an experimental vapor pressure of 3.6X10-8 mm Hg at 25 °C(2,SRC) indicates that chlortoluron will exist solely in the particulate phase in the ambient atmosphere. Particulate-phase chlortoluron may be physically removed from the air by wet and dry deposition(SRC). |
| Expositionspfade | The substance can be absorbed into the body by inhalation of its aerosol and by ingestion. |
| Plant Concentrations | No residue can be detected in the seed of winter wheat 120 days after treatment in spring. |
| Signs and Symptoms | Redness. |
| ICSC Environmental Data | The substance is very toxic to aquatic organisms. This substance does enter the environment under normal use. Great care, however, should be taken to avoid any additional release, for example through inappropriate disposal. |
| Soil Adsorption/Mobility | An average organic matter-water distribution of 60 was measured for seven soils (organic matter range 1.09-5.92%pH range 5.9-7.5)(1). Seventeen soils from Australia had a range of organic matter-water distribution values for this compound from 25-85, giving Koc values ranging from 1-3467 (organic matter range 0.19-6.62pH range 4.8-8.4)(2). Leaching was studied following field application of chlortoluron to a sandy soilafter 10 cm of rain had fallen, >2 mg/kg, 1 mg/kg, 0.5 mg/kg, and a trace remained in the 0-2.5, 2.5-5, 5-7.5, and 7.5-10 cm depth, respectively(2). Chlortoluron has measured Koc values ranging from 146-346 for eight Czechoslovakian soils (mean=228), with higher values corresponding to soils with a greater content of organic matter(3). Koc values of 271 and 419 were measured for a loamy sand and a mucky peat soil, respectively, at 25 °C(4). According to a recommended classification scheme(5), these estimated Koc values suggest that chlortoluron has moderate mobility in soil(SRC). Adsorption of chlortoluron corresponds to an L-isotherm indicating that as the solution concentration increases, there is a decrease in site availability(6). Chlortoluron, applied at a rate of 2.0 kg/ha to sandy soil monoliths containers, had a measured Koc of 160 and 113 in the A and B horizons, respectively(7). The addition of liquid manure, increasing the organic carbon content, resulted in reduced mobility(7). |
| Artificial Pollution Sources | Chlortoluron's production and use (not marketed in U.S.)(1) as a herbicide(2) would result in its release directly to the environment(SRC). |
| Environmental Biodegradation | Degradation of chlortoluron proceeds through the cleavage of the C-N bond as demonstrated using both soil and microbial culture studies(1). Chlortoluron had a half-life in soil of 4-6 weeks(2). The only metabolite identified in this study was monomethyl chlortoluron(2). A half-life of between 6-18 weeks was reported for chlortoluron(3). In biometer experiments, half-lives of 93 days and 40 days were measured for chlortoluron in a silty sand and silty loam soil, respectively(4). However, the disappearance of this compound in an outdoor lysimeter experiment was slower in silty loam (49 days, fallow land38 days, barley field) than in silty sand(52 days, fallow land14 days, barley field)(4). The main metabolite of chlortoluron degradation was N-dimethylated chlortoluron(4). Chlortoluron, applied as either a suspendible concentrate or wettable powder, had a calculated half-life of 96 days for both conditions in one soil (pH 5.1organic carbon 4.1%silt 16%water holding capacity 27%)a second soil (pH 7.0organic carbon 1.6%silt 11% water holding capacity 16.6%) had calculated half-lives of 82 and 84 days for a suspendible concentrate and wettable powder, respectively(5).Chlortoluron at 5 and 100 umol/kg soil was incubated at 25 °C in both a sandy loam and a mucky peat(1). Degradation was slow and there was no indication of a lag phase. The percentage of total applied 14C activity evolved as 14CO2 from the soil varied from 0.21 to 0.14% in peat and sand, respectively, at the 5 umol/kg soil herbicide concentration and from 0.25 to 0.38% in peat and sand, respectively, at the 100 umol/kg soil herbicide concentration(1). The higher rate for the sandy soil at 100 umol/kg soil concentration was believed due to the protective effect of sorption (in the peat soil) on the degradation process(1). A half-life of chlortoluron in soil was estimated at 25 °C as 2306 and 4730 days for peat and sand soils, respectively, at a herbicide concentration of 5 umol/kg soil(1). A half-life of 1949 and 1335 days for peat and sand soils, respectively, was estimated for a herbicide concentration of 100 umol/kg soil(1). These half-lives were derived from the rate of 14CO2 production under laboratory conditions(1). |
| Sediment/Soil Concentrations | IN TEMPERATE CLIMATES, AN INITIAL SOIL APPLICATION OF 6 KG AI/HA HAD T/2 OF 30 TO 40 DAYS. |
| Environmental Bioconcentration | An estimated BCF value of 40 was calculated for chlortoluron(SRC), using an experimental log Kow of 2.41(1,SRC) and a recommended regression-derived equation(2). According to a classification scheme, this BCF value suggests that bioconcentration in aquatic organisms is moderate, not high(3). Winter wheat grown in soil containing 4.7 mg chlortoluron/kg dry soil had bioconcentration factors of 21 and 22 for root material and for shoots, respectively (bioconcentration factor is the concentration of 14C from the chlortoluron in the plant versus the soil)(4). |
| Wassergefährdungsklasse (WGK) | 3 |
| TSCA-Inventar-Status | TSCA listed |
| UN-Transportnummer | UN 3077 |
| RTECS-Nr. | YS7230000 |
| R-Sätze (R) | 40-50/53-63-36-20/21/22-11 |
| Toxizität | rat,LC50,inhalation,1300mg/m3 (1300mg/m3),"Wirksubstanzen der Pflanzenschutz und Schadlingsbekampfungsmittel," Perkow, W., Berlin, Verlag Paul Parey, 1971-1976Vol. -, Pg. -, 1971/1976. |
| Gefahrensymbole | XnN,N,Xn,F |
| Sicherheitshinweise (S) | 26-36/37-46-60-61-16 |
| Lagerklasse | 11 - Combustible Solids |
| Gefahrstoffdaten | 15545-48-9(Hazardous Substances Data) |
| Gefahrenklasse | Aquatic Acute 1Aquatic Chronic 1Carc. 2Repr. 2 |
Anwendungen & Verwendung
Verwenden
Herbicide.