Huagongshe화공사 화학 정보 인쇄 보고서 · 연구 참고용
디클로로아세톤
디클로로아세톤 · 1,1-다이클로로아세톤 · 1,1-디클로로아세톤 · 1,1-Dichloropropanone · 1,1-DICHLORO-2-PROPANONE · 1,1-DCA · 1,1-DICHLOROPROPAN-2-ONE · 2-Propanone, 1,1-dichloro-

식별자 및 물리적 특성
| CAS No. | 30605-38-0 |
|---|---|
| 분자식 | C3H4Cl2O |
| 평균 분자량 | 126.97 g/mol |
| 단동위원소 질량 | 125.96392011 g/mol |
| SMILES | CC(=O)C(Cl)Cl |
| InChIKey | CSVFWMMPUJDVKH-UHFFFAOYSA-N |
| PubChem CID | 10567 |
| ChEMBL | CHEMBL3188688 |
| EC No. | 208-175-7 |
| DTXSID | DTXSID7021576 |
| 현지명 | 디클로로아세톤 |
화학 및 물리적 성질
| XLogP | 1.3 |
|---|---|
| 극성 표면적 | 17.1 |
| 수소 결합 공여자 수 | 0 |
| 수소 결합 수용자 수 | 1 |
| 회전 가능 결합 수 | 1 |
| 무거운 원자 수 | 6 |
| 형식 전하 | 0 |
| 복잡도 | 59.8 |
| 물질 분류 | Volatile Organic Compound (VOC) |
| SpringerMaterials Properties | Schoenflies notation |
| 밀도 | 1.304 g/cu cm at 18 °C1.327 g/mL at 25 °C(lit.) |
| 용해도 | Sol in ethyl alcoholmiscible in ethyl ether클로로포름(약간 용해됨), 메탄올(약간 용해됨) |
| 끓는 점 | 120 °C117-118 °C(lit.) |
| Decomposition | When heated to decomposition it emits toxic vapors of /hydrogen chloride/. |
| 증기압 | 27 mm Hg at 25 °C |
| Other Experimental Properties | Boiling with sodium carbonate gives acrylic acid |
| 굴절률 | n20/D 1.446(lit.) |
| 인화점 | 99-100 °F |
| 저장 조건 | Flammables area |
| 물리적 상태 | 기름 |
| 색상 | 무색 |
| Merck | 14,3051 |
| BRN | 1740214 |
| 헨리 상수 | 3.3×10-1 mol/(m3Pa) at 25℃, Burkholder et al. (2019) |
| 안정성 | 휘발성 물질 |
| 주요 응용 | 환경 |
| InChI | InChI=1S/C3H4Cl2O/c1-2(6)3(4)5/h3H,1H3 |
| InChIKey | CSVFWMMPUJDVKH-UHFFFAOYSA-N |
| SMILES | C(Cl)(Cl)C(=O)C |
| EPA | 1,1-Dichloropropanone (513-88-2) |
화학적 성질
CLEAR COLOURLESS TO YELLOW LIQUID
안전 및 규제
| GHS 분류 | DangerH226 (97.4%): Flammable liquid and vapor [Warning Flammable liquids]P210, P233, P240, P241, P242, P243, P260, P264, P264+P265, P270, P273, P280, P301+P316, P301+P317, P301+P330+P331, P302+P361+P354, P303+P361+P353, P304+P340, P305+P351+P338, P305+P354+P338, P316, P317, P321, P330, P337+P317, P363, P370+P378, P391, P403+P235, P405, and P501 (click each P-code to see the statement)Aggregated GHS information provided per 76 reports by companies from 8 notifications to the ECHA C&L Inventory. Each notification may be associated with multiple companies. |
|---|---|
| 규제 정보 | Chemical: 2-Propanone, 1,1-dichloro-Status: Active Update: 01-03-2016 https://echa.europa.eu/registration-dossier/-/registered-dossier/171401,1-Dichloroacetone: Does not have an individual approval but may be used under an appropriate group standard |
| Hazard Classes and Categories | Flam. Liq. 3 (97.4%) |
| 처리 방법 | SRP: The most favorable course of action is to use an alternative chemical product with less inherent propensity for occupational exposure or environmental contamination. 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 qualitypotential migration in soil or watereffects on animal, aquatic, and plant lifeand conformance with environmental and public health regulations. |
| 환경 거동 | TERRESTRIAL FATE: Based on a classification scheme(1), an estimated Koc value of 6.0(SRC), determined from a structure estimation method(2), indicates that 1,1-dichloroacetone is expected to have very high mobility in soil(SRC). Volatilization of 1,1-dichloroacetone from moist soil surfaces is expected to be an important fate process(SRC) given an estimated Henry's Law constant of 6.15X10-6 atm-cu m/mole(SRC), using a fragment constant estimation method(3). 1,1-Dichloroacetone is not expected to volatilize from dry soil surfaces(SRC) based upon a vapor pressure of 27 mm Hg(4). Biodegradation data were not available(SRC, 2008).AQUATIC FATE: Based on a classification scheme(1), an estimated Koc value of 6.0(SRC), determined from a structure estimation method(2), indicates that 1,1-dichloroacetone is not expected to adsorb to suspended solids and sediment(SRC). Volatilization from water surfaces is expected(3) based upon an estimated Henry's Law constant of 6.1X10-6 atm-cu m/mole(SRC), developed using a fragment constant estimation method(4). Using this Henry's Law constant and an estimation method(3), volatilization half-lives for a model river and model lake are 7 days and 53 days, respectively(SRC). According to a classification scheme(5), an estimated BCF of 3(SRC), from an estimated log Kow of 0.20(5) and a regression-derived equation(6), suggests the potential for bioconcentration in aquatic organisms is very high(SRC). Biodegradation data were not available(SRC, 2008). |