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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
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EC number: 200-835-2 | CAS number: 75-05-8
- 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
Toxicological Summary
- Administrative data
- Workers - Hazard via inhalation route
- Workers - Hazard via dermal route
- Workers - Hazard for the eyes
- Additional information - workers
- General Population - Hazard via inhalation route
- General Population - Hazard via dermal route
- General Population - Hazard via oral route
- General Population - Hazard for the eyes
- Additional information - General Population
Administrative data
Workers - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- other toxicological threshold
- Value:
- 70 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- By inhalation
DNEL related information
- DNEL derivation method:
- other: Commission Directive 2006/15/EC established a list of indicative occupational exposure limit (IOEL) values
- Dose descriptor starting point:
- NOAEL
- Value:
- 342 mg/m³
- Explanation for the modification of the dose descriptor starting point:
Expert review and IOEL method
Acute/short term exposure
- Hazard assessment conclusion:
- other toxicological threshold
- Value:
- 102 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- By inhalation
DNEL related information
- DNEL derivation method:
- other: UK HSE STEL: 2011
- Explanation for the modification of the dose descriptor starting point:
Reliable animal data indicate that acetonitrile is not a skin irritant, is not acutely toxic by the dermal route, and is not a skin sensitizer. Local effects are therefore unlikely. However a STEL of 60 ppm (102 mg/m3) is set UK HSE EH40/2005 Workplace exposure limits, 2nd Edition 2011. This may be reflective of early US ACGIH published values for a STEL and is reasonably assumed to be protective of workers for short term exposure.
Local effects
Long term exposure
- Hazard assessment conclusion:
- other toxicological threshold
- Value:
- 70 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- DNEL derivation method:
- other: Commission Directive 2006/15/EC established a list of indicative occupational exposure limit (IOEL) values
Acute/short term exposure
- Hazard assessment conclusion:
- other toxicological threshold
- Value:
- 102 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
Workers - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- other toxicological threshold
- Value:
- 20 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- By inhalation
DNEL related information
- DNEL derivation method:
- other: Commission Directive 2006/15/EC established a list of indicative occupational exposure limit (IOEL) values for 8 h inhalation exposure
- Dose descriptor starting point:
- other: Commission Directive 2006/15/EC established a list of indicative occupational exposure limit (IOEL) values for 8 h inhalation exposure
- Value:
- 70 mg/m³
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 10 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
The IOEL TWA converted to mg/kg dose over 8 h, breathing 10 m3, then adjusted for 50% dermal absorption
- AF for dose response relationship:
- 1
- Justification:
- IOEL converted
- AF for differences in duration of exposure:
- 1
- Justification:
- Chronic study
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- Worker IOEL converted
- AF for other interspecies differences:
- 1
- Justification:
- IOEL conversion
- AF for intraspecies differences:
- 1
- Justification:
- Worker IOEL converted
- AF for the quality of the whole database:
- 1
- Justification:
- Complete
- AF for remaining uncertainties:
- 1
- Justification:
- Worker IOEL converted
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
Workers - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- low hazard (no threshold derived)
Additional information - workers
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 2.4 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- By inhalation
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 25
- Dose descriptor starting point:
- NOAEC
- Value:
- 340 mg/m³
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 60 mg/m³
- Explanation for the modification of the dose descriptor starting point:
A NOAEC in a chronic mouse study is used to calculate a modified dose descriptor. In the chronic mouse study, exposure was for six hours a day for five days a week. To convert this to 24 hour exposure for the general popluation, the NOAEC needs to be corrected by a factor of 0.25 (6/24) and 0.714 (5/7).
The modified dose descriptor is therefore 336 mg/m^3 * 0.25 * 0.714, which is 60 mg/m^3
- AF for dose response relationship:
- 1
- Justification:
- Default value: A modified NOAEC from a chronic mouse study is used as the starting point.
- AF for differences in duration of exposure:
- 1
- Justification:
- Since the repeated dose study was a chronic study, no assessment factor for duration of exposure is required.
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- This is not required for inhalation as this is accounted for in the calculation
- AF for other interspecies differences:
- 2.5
- Justification:
- Default value for toxiokinetic and toxicodynamics interspecies differences.
- AF for intraspecies differences:
- 10
- Justification:
- Default value for the general population.
- AF for the quality of the whole database:
- 1
- Justification:
- Default value: good quality database
- AF for remaining uncertainties:
- 1
- Justification:
- Default for remaining uncertainties.
Acute/short term exposure
- Hazard assessment conclusion:
- other toxicological threshold
- Value:
- 22 mg/m³
- Most sensitive endpoint:
- irritation (respiratory tract)
- Route of original study:
- By inhalation
DNEL related information
- DNEL derivation method:
- other: Acute Exposure Guidance levels published by EPA.
- Overall assessment factor (AF):
- 3
- Dose descriptor starting point:
- NOAEC
- Value:
- 66 mg/m³
- Modified dose descriptor starting point:
- other: Human volunteer study
- Explanation for the modification of the dose descriptor starting point:
Not required as taken from human volunteer study (4 h exposure)
- AF for dose response relationship:
- 1
- Justification:
- Based on human volunteers
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- based on human volunteers
- AF for other interspecies differences:
- 1
- Justification:
- Study conducted in humans; no assessment factor required.
- AF for intraspecies differences:
- 1
- Justification:
- Based on human volunteers
- AF for the quality of the whole database:
- 1
- Justification:
- Human exeperience and chronic inhalation studies in animals
- AF for remaining uncertainties:
- 3
- Justification:
- Limited number of subjects in trial
Local effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- other toxicological threshold
- Value:
- 22 mg/m³
- Most sensitive endpoint:
- irritation (respiratory tract)
DNEL related information
- DNEL derivation method:
- other: Acute Exposure Guidance levels 2 published by US EPA.
- Overall assessment factor (AF):
- 3
- Dose descriptor starting point:
- NOAEC
- Value:
- 66 mg/m³
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- Human volunteers
- AF for other interspecies differences:
- 1
- Justification:
- Study conducted in humans; no assessment factor required.
- AF for intraspecies differences:
- 1
- Justification:
- study in human volunteers
- AF for the quality of the whole database:
- 1
- Justification:
- Human volunteers and chronic rodent inhaltion values
- AF for remaining uncertainties:
- 3
- Justification:
- Limited number of subjects in trial
General Population - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 1.2 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- By inhalation
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 25
- Dose descriptor starting point:
- NOAEC
- Value:
- 342 mg/m³
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 30 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
NOAEC from chronic mouse inhaltion exposure study, converted to equivalent rat exposure level for 24 h over 7 days per week.
- AF for dose response relationship:
- 1
- Justification:
- inhalation
- AF for differences in duration of exposure:
- 1
- Justification:
- chronic study
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- as guidance
- AF for other interspecies differences:
- 2.5
- Justification:
- standard residual
- AF for intraspecies differences:
- 10
- Justification:
- Standard for general population
- AF for the quality of the whole database:
- 1
- Justification:
- Complete
- AF for remaining uncertainties:
- 1
- Justification:
- No further AF required; assumed 100% obsorption
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
General Population - Hazard via oral route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.4 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- By inhalation
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 25
- Dose descriptor starting point:
- NOAEC
- Value:
- 70 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 10 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
The mouse 200 ppm NOAEC (6 h per day, 5 days per week) was converted to a continuous exposure. This was multiplied by 1.15 m3/kg bw. This was then divided by 7, to convert from the mouse to human.
- AF for dose response relationship:
- 1
- AF for differences in duration of exposure:
- 1
- Justification:
- Chronic study
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- ECHA values used
- AF for other interspecies differences:
- 2.5
- Justification:
- ECHA values
- AF for intraspecies differences:
- 10
- Justification:
- Genral population ECHA default
- AF for the quality of the whole database:
- 1
- Justification:
- Full data base
- AF for remaining uncertainties:
- 1
- Justification:
- Full data base
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.6 mg/kg bw/day
- Most sensitive endpoint:
- acute toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 500
- Dose descriptor starting point:
- other: LD10
- Value:
- 300 mg/kg bw/day
- AF for dose response relationship:
- 10
- Justification:
- The mouse LD 10 was divided by 10 to estimate the NOAEL
- AF for other interspecies differences:
- 10
- AF for intraspecies differences:
- 5
General Population - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- low hazard (no threshold derived)
Additional information - General Population
No uses which expose the genral population to acetonitrile are supported.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.