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EC number: 248-660-0 | CAS number: 27794-93-0
- 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
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:
- 9.7 mg/m³
- Most sensitive endpoint:
- effect on fertility
DNEL related information
- Overall assessment factor (AF):
- 25
- Modified dose descriptor starting point:
- NOAEC
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 9.7 mg/m³
- Most sensitive endpoint:
- effect on fertility
DNEL related information
- Overall assessment factor (AF):
- 25
- Modified dose descriptor starting point:
- NOAEC
Local effects
Acute/short term exposure
DNEL related information
Workers - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 2.75 mg/kg bw/day
- Most sensitive endpoint:
- effect on fertility
DNEL related information
- Overall assessment factor (AF):
- 25
- Modified dose descriptor starting point:
- NOAEL
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 2.75 mg/kg bw/day
- Most sensitive endpoint:
- effect on fertility
DNEL related information
- Overall assessment factor (AF):
- 25
- Modified dose descriptor starting point:
- NOAEL
Local effects
Long term exposure
- Most sensitive endpoint:
- skin irritation/corrosion
Acute/short term exposure
- Most sensitive endpoint:
- skin irritation/corrosion
Workers - Hazard for the eyes
Additional information - workers
The DNELs for workers are based on the NOAEL obtained in a 3 -generation oral (dietary) reproductive toxicity study in rats. The NOAEL was ≥275 mg/kg bw/day. The possibility of using the NOAEL from the two-year carcinogenicity study in rats as the starting point for the DNEL calculation was explored. However, this calculation gave higher DNELs and therefore was less sensitive.
The DNELs are based on a NOAEL for the active acid, and as such are applicable to ATMP acid, as well as sodium, potassium and ammonium salts. With regard to the ammonium salt, there are no repeated dose toxicity data on this salt of ATMP. However, administration of this salt can be assumed to lead to the systemic effects observed following the independent administration of ATMP and ammonia (and salts). Therefore the repeated dose toxicity of ammonia is of relevance. In a 13 week repeated-dose feeding study in rats given ammonium sulfate up to 1,975 mg/kg bw/day, no effects were observed on body weight, food consumption or hematological and clinical parameters. However, increased kidney weights (in males and females) and increased liver weights (females) were observed at the highest dose without histopathological changes. The NOAEL was 1,975 mg/kg bw/day for females and 886 mg/kg bw/day for males (diarrhea). Therefore the ammonium salt is not expected to be more toxic than ATMP acid, sodium or potassium salts, and the derived DNELs are adequate to protect against the potential adverse effects of all salts of ATMP.
ATMP ammonium salt is not classified for human health. Aqueous ammonia is subject to formal specific concentration limits for hazard classification according to the CLP regulations. However in ATMP salt preparations the pH falls into a neutral pH range and the proportion of free ammonia in salt products is very small, being dominated by the highly soluble form NH4+which is of low bioavailability. As explained in the ammonia category SIAR, “As pH decreases, the concentration of ammonium ion increases with respect to decreases of unionized ammonia concentrations. However, the toxicity of the unionized ammonia is considered several orders of magnitude greater than the more abundant ammonium ion”. Some relevant toxicity data are available for relevant ammonia salts which would under normal conditions have pH in the neutral range; the pH of the tested substances is not reported but is assumed to be the same.
The NOAEL from oral repeated dose studies with ammonium salts (assumed to have pH in the neutral range) is 250 mg/kg bw/d (based on increased alkaline phosphatase and decreased total protein in blood). There are no effects on reproduction or foetal development. There is an existing inhalatory OEL for ammonia of 14 mg/m3.General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 2.39 mg/m³
- Most sensitive endpoint:
- effect on fertility
DNEL related information
- Overall assessment factor (AF):
- 50
- Modified dose descriptor starting point:
- NOAEC
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 2.39 mg/m³
- Most sensitive endpoint:
- effect on fertility
DNEL related information
- Overall assessment factor (AF):
- 50
- Modified dose descriptor starting point:
- NOAEC
Local effects
Acute/short term exposure
DNEL related information
General Population - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 1.38 mg/kg bw/day
- Most sensitive endpoint:
- effect on fertility
DNEL related information
- Overall assessment factor (AF):
- 50
- Modified dose descriptor starting point:
- NOAEL
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 1.38 mg/kg bw/day
- Most sensitive endpoint:
- effect on fertility
DNEL related information
- Overall assessment factor (AF):
- 50
- Modified dose descriptor starting point:
- NOAEL
Local effects
Long term exposure
- Most sensitive endpoint:
- skin irritation/corrosion
Acute/short term exposure
- Most sensitive endpoint:
- skin irritation/corrosion
General Population - Hazard via oral route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 1.38 mg/kg bw/day
- Most sensitive endpoint:
- effect on fertility
DNEL related information
- Overall assessment factor (AF):
- 50
- Modified dose descriptor starting point:
- NOAEL
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 1.38 mg/kg bw/day
- Most sensitive endpoint:
- effect on fertility
DNEL related information
- Overall assessment factor (AF):
- 50
- Modified dose descriptor starting point:
- NOAEL
General Population - Hazard for the eyes
Additional information - General Population
The DNELs for workers are based on the NOAEL obtained in a 3 -generation oral (dietary) reproductive toxicity study in rats. The NOAEL was≥275 mg/kg bw/day. The possibility of using the NOAEL from the two-year carcinogenicity study in rats as the starting point for the DNEL calculation was explored. However, this calculation gave higher DNELs and therefore was less sensitive.
The DNELs are based on a NOAEL for the active acid, and as such are applicable to ATMP acid, as well as sodium, potassium and ammonium salts. With regard to the ammonium salt, there are no repeated dose toxicity data on this salt of ATMP. However, administration of this salt can be assumed to lead to the systemic effects observed following the independent administration of ATMP and ammonia (and salts). Therefore the repeated dose toxicity of ammonia is of relevance.In a 13 week repeated-dose feeding study in rats given ammonium sulfate up to 1,975 mg/kg bw/day, no effects were observed on body weight, food consumption or hematological and clinical parameters. However, increased kidney weights (in males and females) and increased liver weights (females) were observed at the highest dose without histopathological changes. The NOAEL was 1,975 mg/kg bw/day for females and 886 mg/kg bw/day for males (diarrhea). Therefore the ammonium salt is not expected to be more toxic than ATMP acid, sodium or potassium salts, and the derived DNELs are adequate to protect against the potential adverse effects of all salts of ATMP.
ATMP ammonium salt is not classified for human health. Aqueous ammonia is subject to formal specific concentration limits for hazard classification according to the CLP regulations. However in ATMP salt preparations the pH falls into a neutral pH range and the proportion of free ammonia in salt products is very small, being dominated by the highly soluble form NH4+which is of low bioavailability. As explained in the ammonia category SIAR, “As pH decreases, the concentration of ammonium ion increases with respect to decreases of unionized ammonia concentrations. However, the toxicity of the unionized ammonia is considered several orders of magnitude greater than the more abundant ammonium ion”. Some relevant toxicity data are available for relevant ammonia salts which would under normal conditions have pH in the neutral range; the pH of the tested substances is not reported but is assumed to be the same.
The NOAEL from oral repeated dose studies with ammonium salts (assumed to have pH in the neutral range) is 250 mg/kg bw/d (based on increased alkaline phosphatase and decreased total protein in blood). There are no effects on reproduction or foetal development. There is an existing inhalatory OEL for ammonia of 14 mg/m3.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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