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EC number: 231-843-4 | CAS number: 7758-94-3
- 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:
- insufficient hazard data available (further information necessary)
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
- Most sensitive endpoint:
- acute toxicity
- Route of original study:
- By inhalation
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- insufficient hazard data available (further information necessary)
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
- Most sensitive endpoint:
- irritation (respiratory tract)
DNEL related information
Workers - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 2.8 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 0.5
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 1.4
- Explanation for the modification of the dose descriptor starting point:
- Extrapolation from 50 % oral bioavailability to 10 % dermal bioavailability, since no dermal study is available. Corrected dermal DNEL = 0.28 mg Fe/kg bw/day*(50 %/10 %) = 1.4 mg Fe/kg bw/day.
- AF for dose response relationship:
- 1
- Justification:
- not required (NOAEL in humans)
- AF for differences in duration of exposure:
- 1
- Justification:
- not required (chronic human data)
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- not required (human data)
- AF for other interspecies differences:
- 1
- Justification:
- not required (human data)
- AF for intraspecies differences:
- 0.5
- Justification:
- default factor for workers
- AF for the quality of the whole database:
- 1
- Justification:
- not required
- AF for remaining uncertainties:
- 1
- Justification:
- not required
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
- Most sensitive endpoint:
- acute toxicity
- Route of original study:
- Dermal
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
- Most sensitive endpoint:
- skin irritation/corrosion
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
Workers - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- medium hazard (no threshold derived)
Additional information - workers
- U.S. EPA United States Environmental Protection Agency (1993) Reregistration Eligibility Document (RED) Iron Salts. Self-published, document reference EPA-738-F-93-002, OPPTS, Washington, DC, U.S.A.
The long-term inhalation DNEL for systemic and local effects is not assessed, since from the sole reliable repeated inhalation study (Johansson 1992) no systemic data are available. The scientific discussion is ongoing.
The acute/short term inhalation DNEL for systemic effects is not derived, since low hazard was concluded based on an ineffective concentration of 1100 mg/m³, indicating a much greater LC50 value (Robbins 1991) for Fe2(SO4)3 as reported in the US EPA (1993) Registration Eligibility Document.
The acute/short term inhalation DNEL for local effects is not derived, since low hazard was identified based on respiratory irritating properties of iron salts reported in ACGIH (1999) documentation for worker protection.
The long-term dermal DNEL for systemic effects is derived basing on the assessment of The Expert Group on Vitamins and Minerals. The Expert Group on Vitamins and Minerals has assessed in their report in 2003 the toxicity of iron in food, drinks and supplement. After a close evaluation of the available data and taking into account the toxicokinetic information they have come up with a guidance value of approximately 17 mg/day of supplementary orally taken iron (equivalent to 0.28 mg/kg bw/day for a 60 kg adult). This ”would not be expected to produce adverse effects in the majority of people. This is derived by dividing the lower end of the range found to have an effect by an uncertainty factor of 3 to allow for extrapolation from a LOAEL to a NOAEL. This is based on data referring to ferrous iron (Fe II), which is the form of iron used in supplements currently available in this country. No additional uncertainty factor is needed for inter-individual variation because the assessment is based on studies on large numbers of people. A safe upper level for total iron has not been estimated, as gastrointestinal effects are associated with iron in supplements rather than in foods.” The value of 0.28 mg/kg bw for the general population is therefore deemed a more reliable DNEL (oral, long-term, general population). As in the not-standard approach 50 % bioavailability of iron salts via the oral and 10 % via the dermal route (based on toxicokinetic considerations) is assumed and as the intraspecies variability in workers is regarded to be lower than in the general population this value is multiplied by a factor of 2 in order to derive a DNEL (dermal, long-term, workers) of 0.28*(50%/10%)* 2 = 2.8 mg/kg bw/d.
Table: DNELs for specific iron salts calculated based on iron content threshold values
Iron salt species |
Factor for relative iron content |
DNEL (dermal, long-term, worker) [mg/kg bw/d] |
Fe |
1 |
2.80 |
FeCl3 |
2.90 |
8.15 |
FeCl3 x 6 H2O |
4.84 |
13.55 |
FeCl2 |
2.27 |
6.35 |
Fe2(SO4)3 |
3.58 |
10.00 |
FeSO4 |
2.72 |
7.60 |
FeSO4 x 7 H2O |
4.98 |
13.95 |
FeClSO4 |
3.36 |
9 |
The acute/short term dermal DNEL for systemic effects is not derived, since no hazard was identified based on acute dermal toxicity, where LD50 > 2000 mg/kg bw for FeCl2 was reported in Choi (2004) study.
The long and acute/short term dermal DNELs for local effects are not derived, since low hazard was identified based on irritating properties to skin of the soluble iron salts.
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- insufficient hazard data available (further information necessary)
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- insufficient hazard data available (further information necessary)
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
DNEL related information
General Population - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 1.4 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 1
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 1.4 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- Extrapolation from 50 % oral bioavailability to 10 % dermal bioavailability, since no dermal study is available. Corrected dermal DNEL = 0.28 mg Fe/kg bw/day*(50 %/10 %) = 1.4 mg Fe/kg bw/day.
- AF for dose response relationship:
- 1
- Justification:
- not required (NOAEL in humans)
- AF for differences in duration of exposure:
- 1
- Justification:
- not required (chronic human data)
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- not required (human data)
- AF for other interspecies differences:
- 1
- Justification:
- not required (human data)
- AF for intraspecies differences:
- 1
- Justification:
- not required (data from general population)
- AF for the quality of the whole database:
- 1
- Justification:
- not required
- AF for remaining uncertainties:
- 1
- Justification:
- not required
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
- Most sensitive endpoint:
- acute toxicity
- Route of original study:
- Dermal
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
- Most sensitive endpoint:
- skin irritation/corrosion
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
General Population - Hazard via oral route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.28 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 1
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 0.28 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- no route-to-route extrapolation performed
- AF for dose response relationship:
- 1
- Justification:
- not required (NOAEL in humans)
- AF for differences in duration of exposure:
- 1
- Justification:
- not required (chronic human data)
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- not required (human data)
- AF for other interspecies differences:
- 1
- Justification:
- not required (human data)
- AF for intraspecies differences:
- 1
- Justification:
- not required (human data)
- AF for the quality of the whole database:
- 1
- Justification:
- not required
- AF for remaining uncertainties:
- 1
- Justification:
- not required
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 20 mg/kg bw/day
- Most sensitive endpoint:
- acute toxicity
- Route of original study:
- Oral
DNEL related information
General Population - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- medium hazard (no threshold derived)
Additional information - General Population
- U.S. EPA United States Environmental Protection Agency (1993) Reregistration Eligibility Document (RED) Iron Salts. Self-published, document reference EPA-738-F-93-002, OPPTS, Washington, DC, U.S.A.
The long-term inhalation DNEL for systemic and local effects is not assessed, since from the sole reliable repeated inhalation study (Johansson 1992) no systemic data are available. The scientific discussion is ongoing.
The acute/short term inhalation DNEL for systemic effects is not derived, since low hazard was concluded based on an ineffective concentration of 1100 mg/m³, indicating a much greater LC50 value (Robbins 1991) for Fe2(SO4)3 as reported in the US EPA (1993) Registration Eligibility Document.
The acute/short term inhalation DNEL for local effects is not derived, since low hazard was identified based on respiratory irritating properties of iron salts reported in ACGIH (1999) documentation for worker protection.
The long-term dermal and oral DNELs for systemic effects are derived basing on the assessment of The Expert Group on Vitamins and Minerals. The Expert Group on Vitamins and Minerals has assessed in their report in 2003 the toxicity of iron in food, drinks and supplement. After a close evaluation of the available data and taking into account the toxicokinetic information they have come up with a guidance value of approximately 17 mg/day of supplementary iron (equivalent to 0.28 mg/kg bw/day for a 60 kg adult). This
“would not be expected to produce adverse effects in the majority of people. This is derived by dividing the lower end of the range found to have an effect by an uncertainty factor of 3 to allow for extrapolation from a LOAEL to a NOAEL. This is based on data referring to ferrous iron (Fe II), which is the form of iron used in supplements currently available in this country. No additional uncertainty factor is needed for inter-individual variation because the assessment is based on studies on large numbers of people. A safe upper level for total iron has not been estimated, as gastrointestinal effects are associated with iron in supplements rather than in foods.”
The value of 0.28 mg/kg bw for the general population is therefore deemed a more reliable DNEL(oral, long-term, general population).
As in the not-standard approach 50 % bioavailability of iron salts via the oral and 10 % via the dermal route (based on toxicokinetic considerations) is assumed, therefore the value multiplied by 5 applies as the DNEL(dermal, long-term, general population).
Table: DNELs for specific iron salts calculated based on iron content threshold values
Iron salt species |
Factor for relative iron content |
DNEL(dermal, long-term, general population) [mg/kg bw/d] |
DNEL(oral, long-term, general population) [mg/kg bw/d] |
Fe |
1 |
1.4 |
0.28 |
FeCl3 |
2.90 |
4.05 |
0.81 |
FeCl3 x 6 H2O |
4.84 |
6.8 |
1.36 |
FeCl2 |
2.27 |
3.2 |
0.64 |
Fe2(SO4)3 |
3.58 |
5.00 |
1.00 |
FeSO4 |
2.72 |
3.8 |
0.76 |
FeSO4 x 7 H2O |
4.98 |
6.95 |
1.39 |
FeClSO4 |
3.36 |
4.7 |
0.94 |
The acute/short term dermal DNEL for systemic effects is not derived, since no hazard was identified based on acute dermal toxicity, where LD50 > 2000 mg/kg bw for FeCl2 reported in Choi (2004) study.
The long and acute/short term dermal DNELs for local effects are not derived, since low hazard was identified based on irritating properties to skin of the soluble iron salts.
The acute/short term oral DNEL for systemic effects is taken from The Expert Group on Vitamins and Minerals (EVM 2003) assessment. Here is considered that acute toxic doses apply for infants (under the age of six years) 20 mg/kg for gastrointestinal irritation, with systemic effects not occurring below 60 mg/kg bw. Therefore the lowest dose is considered as critical value for the acute/short term oral local effects in the most sensitive population group (infants).
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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