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EC number: 205-517-7 | CAS number: 141-98-0
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Short-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model and falling into its applicability domain, with adequate and reliable documentation / justification
- Justification for type of information:
- QSAR prediction:US EPA accepted QSAR method for chemicals properties assessment.
- Qualifier:
- according to guideline
- Guideline:
- other: QSAR model
- Principles of method if other than guideline:
- EPI Suite v 4.0/ECOSARv1.00
- GLP compliance:
- no
- Remarks:
- not applicable. QSAR model
- Analytical monitoring:
- not required
- Vehicle:
- no
- Test organisms (species):
- other: Mysid shrimp
- Details on test organisms:
- Scientific name: Americamysis bahia
Common name: Opossum shrimp, Mysid shrimp, Mysids - Test type:
- other: QSAR model
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 96 h
- Hardness:
- not applicable. QSAR model
- Test temperature:
- not applicable. QSAR model
- pH:
- not applicable. QSAR model
- Dissolved oxygen:
- not applicable. QSAR model
- Salinity:
- not applicable. QSAR model
- Nominal and measured concentrations:
- not applicable. QSAR model
- Details on test conditions:
- SMILES : O(C(=NCC)S)C(C)C
CHEM : Carbamothioic acid, ethyl-, O-(1-methylethyl) ester
CAS Number: 141-98-0
MOL FOR: C6 H13 N1 O1 S1
MOL WT : 147.24
Log Kow: 3.32 (KowWin estimate)
Wat Sol: 114.4 mg/L (WskowWin estimate) - Reference substance (positive control):
- not required
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 3.06 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Details on results:
- The ECOSAR QSAR model predicts that LC50 for fresh water species cited would to be 3.06 mg/l therefore that the substance is effectively moderately toxic to Mysid shrimp.
- Validity criteria fulfilled:
- yes
- Remarks:
- US EPA accepted QSAR method for chemicals properties assessment.
- Conclusions:
- The ECOSAR QSAR model predicts that LC50 for fresh water species cited would to be 3.06 mg/l therefore that the substance is effectively moderately toxic to Mysid shrimp.
- Executive summary:
The ECOSAR QSAR model predicts that LC50 for fresh water species cited would to be 3.06 mg/l therefore that the substance is effectively moderately toxic to Mysid shrimp.
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model and falling into its applicability domain, with adequate and reliable documentation / justification
- Justification for type of information:
- QSAR prediction: US EPA accepted QSAR method for chemicals properties assessment.
- Qualifier:
- according to guideline
- Guideline:
- other: QSAR model
- Principles of method if other than guideline:
- EPI Suite v 4.0/ECOSARv1.00
- GLP compliance:
- no
- Remarks:
- not applicable. QSAR model
- Analytical monitoring:
- not required
- Vehicle:
- no
- Test organisms (species):
- other: Daphnid species
- Test type:
- other: QSAR model
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Hardness:
- not applicable. QSAR model
- Test temperature:
- not applicable. QSAR model
- pH:
- not applicable. QSAR model
- Dissolved oxygen:
- not applicable. QSAR model
- Salinity:
- not applicable. QSAR model
- Nominal and measured concentrations:
- not applicable. QSAR model
- Details on test conditions:
- SMILES : O(C(=NCC)S)C(C)C
CHEM : Carbamothioic acid, ethyl-, O-(1-methylethyl) ester
CAS Number: 141-98-0
MOL FOR: C6 H13 N1 O1 S1
MOL WT : 147.24
Log Kow: 3.32 (KowWin estimate)
Wat Sol: 114.4 mg/L (WskowWin estimate) - Reference substance (positive control):
- not required
- Duration:
- 48 h
- Dose descriptor:
- LC50
- Effect conc.:
- 5.383 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Validity criteria fulfilled:
- yes
- Remarks:
- US EPA accepted QSAR method for chemicals properties assessment.
- Conclusions:
- The ECOSAR QSAR model predicts that LC50 for fresh water species cited would to be 5.383 mg/l therefore that the substance is effectively moderately toxic to Daphnid.
- Executive summary:
The ECOSAR QSAR model predicts that LC50 for fresh water species cited would to be 5.383 mg/l therefore that the substance is effectively moderately toxic to Daphnid.
Daphnid , 48-hr LC50 = 5.383 mg/L (ppm)
Referenceopen allclose all
Overview of QSARs estimations on short-term aquatic toxicity of O-isopropyl ethylthiocarbamate (IPETC ) to Mysid shrimp
Method
|
Results |
Remarks |
Reference |
QSAR estimate |
Mysid Shrimp, 96 -hr, LC50= 3.060 mg/L (ppm) Mysid Shrimp (SW), 30-day, ChV (chronic value) = 0.179 mg/L (ppm)
|
Reliable with restrictions, QSAR estimated data |
ECOSAR Program (v1.00) |
Mysid Shrimp, 96 -hr, LC50= 3.060 mg/L (ppm)
Mysid Shrimp (SW), 30-day, ChV (chronic value) = 0.179 mg/L (ppm)
Overview of QSARs estimations on short-term aquatic toxicity of
O-isopropyl ethylthiocarbamate (IPETC ) to Daphnid
Method
|
Results |
Remarks |
Reference |
QSAR estimate |
Daphnid , 48-hr LC50 = 5.383mg/L (ppm)
Daphnid, 30-day, ChV (chronic value) = 0.769mg/L (ppm)
|
Reliable with restrictions, QSAR estimated data |
ECOSAR Program (v1.00) |
The ECOSAR QSAR model predicts that LC50 for fresh water species cited would to be 5.383 mg/l therefore that the substance is effectively moderately toxic to Daphnid.
Daphnid , 48-hr LC50 = 5.383mg/L (ppm)
Daphnid, 30-day, ChV (chronic value) = 0.769mg/L (ppm)
Description of key information
The ECOSAR QSAR model predicts that LC50 for fresh water species cited would to be 5.383 mg/l therefore that the substance is effectively moderately toxic to Daphnid.
The ECOSAR QSAR model predicts that LC50 for fresh water species cited would to be 3.06 mg/l therefore that the substance is effectively moderately toxic to Mysid shrimp.
The available data for marine water short-term to aquatic invertebrate are limited and to obtaine the value for PNECs for saltwaters is taken account a assesment factor 10 to extrapolate to LC50 following the “Guidance on Information Requirement and Chemical Safety Assessment R.10: Characterisation of dose [concentration]- response for environment”and “Table R.10-5 Assessment factors proposed for deriving PNEC water for saltwater for different data sets”, to account for the possibility that greater taxonomic diversity in the marine environment makes it likely that some marine taxa may be more sensitive than the most sensitive freshwater taxa.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 5.383 mg/L
Marine water invertebrates
Marine water invertebrates
- Effect concentration:
- 0.538 mg/L
Additional information
The ECOSAR QSAR model predicts that LC50 for fresh water species cited would to be 5.383 mg/l therefore that the substance is effectively moderately toxic to Daphnid.
The ECOSAR QSAR model predicts that LC50 for fresh water species cited would to be 3.06 mg/l therefore that the substance is effectively moderately toxic to Mysid shrimp.
The available data for marine water short-term to aquatic invertebrate are limited and to obtaine the value for PNECs for saltwaters is taken account a assesment factor 10 to extrapolate to LC50 following the “Guidance on Information Requirement and Chemical Safety Assessment R.10: Characterisation of dose [concentration]- response for environment”and “Table R.10-5 Assessment factors proposed for deriving PNEC water for saltwater for different data sets”, to account for the possibility that greater taxonomic diversity in the marine environment makes it likely that some marine taxa may be more sensitive than the most sensitive freshwater taxa.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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