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Diss Factsheets
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EC number: 418-570-8 | CAS number: 25383-07-7
- 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:
- 5.3 mg/m³
- Most sensitive endpoint:
- developmental toxicity / teratogenicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 12.5
- Modified dose descriptor starting point:
- other: NOEC
- Value:
- 65.8 mg/m³
- Explanation for the modification of the dose descriptor starting point:
- No adequate experimental effect data are available on the relevant route of exposure for the population under consideration.
- AF for dose response relationship:
- 1
- Justification:
- Default assessment factor when the starting point for the DNEL calculation is a NOAEL.
- AF for differences in duration of exposure:
- 1
- Justification:
- The NOAEC derives fron a one-generation reproduction study.
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- Allometric scalic is not appropriate for inhalaiton route.
- AF for other interspecies differences:
- 2.5
- Justification:
- Default assessment factor for other interspecies differences.
- AF for intraspecies differences:
- 5
- Justification:
- Default assessment factor for intraspecies differences between workers.
- AF for the quality of the whole database:
- 1
- Justification:
- Default assessment factor for good/standard quality of the database.
- AF for remaining uncertainties:
- 1
- Justification:
- There are no remaining uncertainties.
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
- Most sensitive endpoint:
- developmental toxicity / teratogenicity
- Route of original study:
- Oral
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
DNEL related information
Workers - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 1 mg/kg bw/day
- Most sensitive endpoint:
- developmental toxicity / teratogenicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 50
- Modified dose descriptor starting point:
- other: NOEL
- Value:
- 50 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- No adequate experimental effect data are available on the relevant route of exposure for the population under consideration.
- AF for dose response relationship:
- 1
- Justification:
- Default assessment factor when the starting point for the DNEL calculation is a NOAEL.
- AF for differences in duration of exposure:
- 1
- Justification:
- The NOAEC derives fron a one-generation reproduction study.
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Allometric scaling factor for rats as compared to humans.
- AF for other interspecies differences:
- 2.5
- Justification:
- Default assessment factor for other interspecies differences.
- AF for intraspecies differences:
- 5
- Justification:
- Default assessment factor for intraspecies differences between workers.
- AF for the quality of the whole database:
- 1
- Justification:
- Default assessment factor for good/standard quality of the database.
- AF for remaining uncertainties:
- 1
- Justification:
- There are no remaining uncertainties.
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
- Most sensitive endpoint:
- developmental toxicity / teratogenicity
- Route of original study:
- Oral
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
- Most sensitive endpoint:
- skin irritation/corrosion
Workers - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- no hazard identified
Additional information - workers
Phenethylammonium salt of fosfomycin is not classified for any acute toxicity effects according to toxicological data available and according to Regulation (EC) n. 1272/2008.
The substance is not harmful after oral and dermal acute exposure and it resulted not irritant to the skin and to the eyes inin vivotest systems.
Moreover, it did not result sensitizing.
According to two in vitro test systems, Phenethylammonium salt of fosfomycin resulted not genotoxic.
In the 28-day oral repeated-dose toxicity study in rats, a NOAEL of 150 mg/kg bw/day has been identified (mid-dose tested). At the higher dose tested (500 mg/kg bw/day), some effects like salivation after gavage, fur loss, lacrimation and/or eyelid swelling, chromodacryorrhea, abdomen dilation and poor conditions were observed. Reversibility of the above-mentioned clinical changes was ascertained.
At the end of the treatment period, a few changes were seen that were considered related to the test article administration. These were on the whole slight increases in mean weights of liver and kidneys in males and females of the intermediate and high dose groups, (usually being statistically significant), a slight decrease in absolute values of testes in males and in spleen in females of the high dose group. At the end of recovery, the only change seen was an evident decrease in weights of tests in the group previously treated with 500 mg/kg/day, while other organs affected at the end of the treatment period showed complete recovery.
In the oral one-generation study performed with rats, the NOEL of 50 mg/kg bw/day was observed in parent females and in offspring. The NOAEL of 100 mg/kg bw/day was, instead, observed in parent females and in offspring.
As no acute effects are expected for Phenethylammonium salt of fosfomycin, no acute DNEL were derived as no/low hazard has been identified.
The only local effects after repeated exposure were fur loss and chromodacryorrhea in female rats during the oral 28-day repeated toxicity study. Although the relevance of these effects after inhalation and dermal exposure is unclear, DNELs were derived from a precautionary and conservative point of view.
Although inhalation exposure is considered to be negligible (see toxicokinetics summary and CSR Section 9), the DNEL after long-term inhalation exposure has been derived from a precautionary and conservative point of view.
Long-term systemic DNELs have been derived starting from the NOEL of the one-generation study with rats.
Details of the derivations are reported above.
General Population - Hazard via inhalation route
Systemic effects
Acute/short term exposure
DNEL related information
Local effects
Acute/short term exposure
DNEL related information
General Population - Hazard via dermal route
Systemic effects
Acute/short term exposure
DNEL related information
General Population - Hazard via oral route
Systemic effects
Acute/short term exposure
DNEL related information
General Population - Hazard for the eyes
Additional information - General Population
Phenethylammonium salt of fosfomycin is an intermediate intended only to industrial use. No exposure is foreseen for consumers and humans via environment (see CSR Section 9).
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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