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EC number: 201-188-9 | CAS number: 79-24-3
- 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:
- DNEL (Derived No Effect Level)
- Value:
- 8.4 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- Overall assessment factor (AF):
- 18
- Modified dose descriptor starting point:
- LOAEC
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 17 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- Overall assessment factor (AF):
- 9
- Modified dose descriptor starting point:
- LOAEC
Local effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 25 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- Overall assessment factor (AF):
- 6
- Dose descriptor:
- NOAEC
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 50 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- Overall assessment factor (AF):
- 3
- Dose descriptor starting point:
- NOAEC
Workers - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 350 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- Overall assessment factor (AF):
- 72
- Modified dose descriptor starting point:
- NOAEL
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 2 100 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- Overall assessment factor (AF):
- 12
- Modified dose descriptor starting point:
- NOAEL
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:
- no hazard identified
Additional information - workers
Worker DNELs for Nitroethane
The major use of nitroethane is as a chemical intermediate for the manufacture of other chemicals. Nitroethane is also used as a solvent for polymers in coatings and inks. The predominant route of occupational exposure for nitroethane is inhalation. Products containing nitroethane are not widely used by consumers. The following DNELs were derived using ECETOC guidance document entitled, “Guidance on Assessment Factors to Derive DNELs”, Final draft. March 17th2010.
Inhalation DNEL: Long-term worker exposures, systemic effects.
The LOAEC of 100 ppm (300 mg/m3) was taken from a sub-chronic inhalation study.
Time adjustment for 6 hr/day exposure = (6 h/d)/(8 h/d)
Adjustment for respiration rate (8 hr) = (6.7 m3)/(10 m3)
Allometric scaling factor (rat) = 1 (not applicable when setting an inhalation DNEL from an inhalation animal study)
Remaining differences = 1
LOAEL to NOAEL = 3 (based on severity of the effects)
Sub-chronic to chronic = 2
Intraspecies variation for the worker population = 3
Inhalation DNEL/long-term, systemic effects = (300 mg/m3)(6/8)(6.7/10)(1/2)(1/3)(1/3) = 8.4 mg/m3
Inhalation DNEL: Acute/Short-term worker exposures, systemic effects
The LOAEC of 100 ppm (300 mg/m3) was taken from a sub-chronic inhalation study to derive an inhalation DNEL/worker population.
Time adjustment for 6 hr/8 hr day exposure = (6 h/d)/(8 h/d)
Adjustment for respiration rate = 6.7 m3/10m3
Allometric scaling factor (rat) = 1 (Not applicable when setting an inhalation DNEL from an inhalation animal study)
Remaining Differences = 1
LOAEL to NOAEL = 3 (based on slight severity of the effects)
Sub-chronic to acute = N/A
Intraspecies variation for the worker population = 3
Inhalation DNEL/short-term, systemic effects = (300 mg/m3)(6/8)(6.7/10)(1/3)(1/3) = 17 mg/m3
Inhalation DNEL: Long-term worker exposures, local effects:
The NOAEC of 100 ppm (300 mg/m3) was taken from a sub-acute inhalation study
Time adjustment for 6 hr/day exposure = (6 hr/day)/(8h/day)
Adjustment for respiration rate (8 hr) = (6.7 m3)/(10 m3)
Allometric scaling factor (rat) = 1 (not appropriate for local effects)
Remaining differences = 1
Sub-chronic to chronic = 2
Intraspecies variation for the worker population = 3
Inhalation DNEL/long-term, local effects = (300 mg/m3)(6/8)(6.7/10)(1/2)(1/3) = 25 mg/m3
Inhalation DNEL: Acute/short-term worker exposures, local effects
The NOAEC of 100 ppm (300 mg/m3) was taken from a sub-chronic inhalation study
Time adjustment for 6 hr/day exposure = (6 hr/day)/(8h/day)
Adjustment for respiration rate (8 hr) = (6.7 m3)/(10 m3)
Allometric scaling factor (rat) = 1 (not appropriate for local effects)
Remaining differences = 1
Sub-chronic to acute = N/A
Intraspecies variation for the worker population = 3
Inhalation DNEL/short-term, local effects = (300 mg/m3)(6/8)(6.7/10)(1/3) = 50 mg/m3
Dermal DNELs:
Dermal DNELs for acute short-term local effects and long-term exposure local effects were not derived for nitroethane. No dermal studies examining the systemic toxicity of nitroethane were found. Instead a route-to-route extrapolation is used from a repeat dose oral study using 1-nitropropane as a surrogate for read across. No classification or labelling is required for skin and eye irritation or dermal toxicity since it is not irritating to the skin and the dermal LD50 is greater than 2000. Pharmacokinetic studies in monkeys indicate that 1-nitropropane is poorly absorbed from the skin (~0.12% in 72 hrs). Also, nitroethane is not readily absorbed through the skin and volatilizes quickly from the skin's surface. Therefore, no acute dermal DNELs for local effects are necessary for this compound.
Dermal DNEL: Long-term worker exposures, systemic effects.
A NOAEL from an oral 28 day study in rats exposed to 1-nitropropanewas used as a surrogate for read across to nitroethane to derive a dermal DNEL chronic /long-term exposure systemic effects.
Dose Modification:
Percutaneous absorption from non-human primate = 0.12%
Therefore: 30 mg/kg/day ÷.0012 = 25’000 mg/kg/day
Assessment factors:
Allometric scaling from rat to human = 4
Remaining differences = 1
Intraspecies adjustment factor for worker population = 3
Exposure duration (From sub-acute study to Chronic) = 6
Dermal DNEL/long-term, systemic effects = 25’000 mg/kg/day/4*3*6 = 350 mg/kg/day
Worker Dermal DNEL: Acute/short-term worker exposure, systemic effects
A NOAEL from an oral 28 day study in rats exposed to 1-nitropropane was used as a surrogate for read across to nitroethane to derive a dermal DNEL acute/short term exposure systemic effects.
Dose Modification:
Percutaneous absorption from non-human primate = 0.12%
Therefore: 30 mg/kg/day ÷ 0.0012 = 25’000 mg/kg/day
Assessment factors:
Allometric scaling from rat to human = 4
Remaining differences = 1
Intraspecies adjustment factor for worker population = 3
Exposure Duration (Subacute study) = N/A
Dermal DNEL/short-term, systemic effects = 25’000 mg/kg/day/4*3 = 2’100 mg/kg/day
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 2 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- Overall assessment factor (AF):
- 30
- Modified dose descriptor starting point:
- LOAEC
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 5 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- Overall assessment factor (AF):
- 75
- Modified dose descriptor starting point:
- LOAEC
Local effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 5 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- Overall assessment factor (AF):
- 10
- Dose descriptor:
- NOAEC
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 15 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- Overall assessment factor (AF):
- 5
- Dose descriptor starting point:
- NOAEC
General Population - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 210 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- Overall assessment factor (AF):
- 120
- Modified dose descriptor starting point:
- NOAEL
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 1 250 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- Overall assessment factor (AF):
- 20
- Modified dose descriptor starting point:
- NOAEL
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:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
General Population - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- no hazard identified
Additional information - General Population
General Population DNELs for Nitroethane
The major use of nitroethane is as a chemical intermediate for the manufacture of other chemicals. Nitroethane is used as a solvent for polymers in coatings and inks. The predominant route of occupational exposure for nitroethane is inhalation. Products containing nitroethane are not widely used by consumers. The following DNELs were derived using ECETOC guidance document entitled, “Guidance on Assessment Factors to Derive DNELs”, Final draft. March 17th 2010.
Inhalation DNEL: Long-term general population exposure, systemic effects.
The LOAEC of 100 ppm (300 mg/m3) was taken from a sub-chronic inhalation study.
Time adjustment for 6 hr/day exposure = (6 h/d)/(24 h/d)
Adjustment from 5 days/week to 7 days/week = (5 days/7 days)
Allometric scaling factor (rat) = 1 (not applicable when setting an inhalation DNEL from an inhalation animal study)
Remaining differences = 1
LOAEL to NOAEL = 3 (based on slight severity of the effects)
Sub-chronic to chronic = 2
Intraspecies variation for the general population = 5
Inhalation DNEL/long-term, systemic= (300 mg/m3)(6/24)(5/7)(1/2)(1/3)(1/5) =2 mg/m3
Inhalation DNEL: Acute/Short-term general population exposure, systemic effects
The LOAEC of 100 ppm (300 mg/m3) was taken from a sub-chronic inhalation study to derive an inhalation DNEL/general population.
Time adjustment for 6 hr/8 hr day exposure = (6 h/d)/(24 h/d)
Allometric scaling factor (rat) = 1 (Not applicable when setting an inhalation DNEL from an inhalation animal study)
Remaining differences = 1
LOAEL to NOAEL = 3 (based on slight severity of the effects)
Sub-chronic to acute = N/A
Intraspecies variation for the general population = 5
Inhalation DNEL/short-term, systemic = (300 mg/m3)(6/24)(1/5)(1/3) =5 mg/m3
Inhalation DNEL: Long-term general population exposure, local effects:
The NOAEC of 100 ppm (300 mg/m3) was taken from a sub-chronic inhalation study
Time adjustment for 6 hr/day exposure = (6 hr/day)/(24 h/day)
Adjustment from 5 days/week to 7 days/week = (5 day/7 days)
Allometric Scaling factor (rat) = 1 (not appropriate for local effects)
Remaining Differences = 1
Sub-chronic to chronic = 2
Intraspecies variation for the general population = 5
Inhalation DNEL general population = (300 mg/m3)(6/24)(5/7)(1/2)(1/5) =5 mg/m3
Inhalation DNEL: Acute/short-term exposure, local effects
The NOAEC of 100 ppm (300 mg/m3) was taken from a sub-chronic inhalation study
Time adjustment for 6 hr/day exposure = (6 hr/day)/(24 h/day)
Allometric scaling factor (rat) = 1 (not appropriate for local effects)
Remaining differences = 1
Sub-chronic to acute = N/A
Intraspecies variation for the general population = 5
Inhalation DNEL/short-term, local effects = (300 mg/m3)(6/24)(1/5) =15 mg/m3
Dermal DNELs:
Dermal DNELs for acute short-term local effects and long-term exposure local effects were not derived for nitroethane. No dermal studies examining the systemic toxicity of nitroethane were found. Instead a route-to-route extrapolation is used from a repeat dose oral study using 1-nitropropane as a surrogate for read across. No classification or labelling is required for skin and eye irritation or dermal toxicity since it is not irritating to the skin and the dermal LD50 is greater than 2000. Pharmacokinetic studies in monkeys indicate that 1-nitropropane is poorly absorbed from the skin (~0.12% in 72 hrs). Also, nitroethane is not readily absorbed through the skin and volatilizes quickly from the skin's surface. Therefore, no acute dermal DNELs for local effects are necessary for this compound.
Dermal DNEL: Long-term general population exposure, systemic effects.
A NOAEL from an oral 28 day study in rats exposed to 1-nitropropanewas used as a surrogate for read across to nitroethane to derive a dermal DNEL chronic /long-term exposure systemic effects.
Dose Modification:
Percutaneous absorption from non-human primate = 0.12%
Therefore: 30 mg/kg/day ÷.0012 = 25’000 mg/kg/day
Assessment factors:
Allometric scaling from rat to human = 4
Remaining differences = 1
Intraspecies adjustment factor for general population = 5
Exposure duration (from sub-acute study to chronic) = 6
Dermal DNEL/short-term, systemic = 25’000 mg/kg/day/4*5*6 =210 mg/kg/day
Dermal DNEL: Acute/Short-term general population exposure, systemic effects
Read across to nitroethane to derive a dermal DNEL acute/short term exposure systemic effects.
Dose Modification:
Percutaneous absorption from non-human primate = 0.12%
Therefore: 30 mg/kg/day ÷ 0.0012 = 25’000 mg/kg/day
Assessment factors:
Allometric scaling from rat to human = 4
Remaining differences = 1
Intraspecies adjustment factor for the general population = 5
Exposure duration (sub-acute study) = N/A
Dermal DNEL/short-term, systemic = 25’000 mg/kg/day/4*5 =1’250 mg/kg/day
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