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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 200-830-5 | CAS number: 75-00-3
- 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:
- 37.7 mg/m³
- Most sensitive endpoint:
- developmental toxicity / teratogenicity
- Route of original study:
- By inhalation
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Dose descriptor starting point:
- NOAEC
- Value:
- 4 015 mg/m³
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 2 825 mg/m³
- Explanation for the modification of the dose descriptor starting point:
The calculation of the DNEL is based on an inhalation NOAEC observed in a developmental toxicity study in mice (OECD 414; 1986).
Conversion of an inhalatory mouse NOAEC into a corrected inhalatory NOAEC in case of differences between experimental and human exposure condition has to be performed.
Corrected starting point for the inhalative route for workers:
= NOAEC (inhalation) * exposure condition mouse / exposure condition human
= 4015 mg/m³ * (6h/day / 8h/day) * (6.7 m³ (8h) /10 m³ (8h) )* (7 days exposure mouse/5 days exposure worker)
= 4015 mg/m³ * 0.75 * 0.67 m³ * 1.4 = 2825 mg/m³
Thus, the corrected starting point for workers was 2825 mg/m³ for inhalation.
- Justification:
- The dose descriptor starting point is based on a NOAEC.
- Justification:
- The DNEL is based on a subacute study.
- Justification:
- AF not used for inhalation route.
- Justification:
- Default value according to ECHA REACH Guidance.
- Justification:
- Default value for workers according to ECHA REACH Guidance.
- Justification:
- The DNEL is based on high-quality studies.
- Justification:
- No remaining uncertainties as the lowest NOAEC was used.
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
DNEL related information
Workers - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 5.01 mg/kg bw/day
- Most sensitive endpoint:
- developmental toxicity / teratogenicity
- Route of original study:
- By inhalation
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Dose descriptor starting point:
- NOAEC
- Value:
- 4 015 mg/m³
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 2 631 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
The calculation of the DNEL is based on an inhalation NOAEC observed in a developmental toxicity study in mice (OECD 414; 1986).
Conversion of an inhalatory mouse NOAEC into a corrected dermal NOAEL in case of differences between experimental and human exposure condition and interspecies differences between mouse and human has to be performed.
Corrected starting point for the inhalative route for workers:
To correct the interspecies difference between rat and human the no observed effect level has to be corrected as follows:
Corrected starting point for the inhalative route for workers:
= NOAEC (inhalation) * sRV(mouse) * exposure condition mouse / exposure condition human * (ABSinh-mouse/ABSdermal-human) * (7 days exposure mouse/5 days exposure worker)
= 4015 mg/m³ * 0.624 m³/kg bw* (6h/day / 8h/day) * (1/1) * 1.4 = 2631 mg/kg bw/day
It is assumed that dermal absorption and inhalation absorption rates are equal.
(ABSdermal-human = dermal absorption in humans, ABSinh-mouse = inhalation absorption rate in mice)
Thus, the corrected starting point for workers is 2631 mg/kg bw/day for dermal exposure.
- Justification:
- The dose descriptor starting point is based on a NOAEL.
- Justification:
- The DNEL is based on a subacute study.
- Justification:
- Default value for mice according to ECHA REACH Guidance.
- Justification:
- Default value according to ECHA REACH Guidance.
- Justification:
- Default value for workers according to ECHA REACH Guidance.
- Justification:
- The DNEL is based on high-quality studies.
- Justification:
- No remaining uncertainties.
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- medium hazard (no threshold derived)
Acute/short term exposure
- Hazard assessment conclusion:
- medium hazard (no threshold derived)
Workers - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- medium 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:
- 6.7 mg/m³
- Most sensitive endpoint:
- developmental toxicity / teratogenicity
- Route of original study:
- By inhalation
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Dose descriptor starting point:
- NOAEC
- Value:
- 4 015 mg/m³
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 1 004 mg/m³
- Explanation for the modification of the dose descriptor starting point:
The calculation of the DNEL is based on an inhalation NOAEC observed in a developmental toxicity study in mice (OECD 414; 1986).
Conversion of an inhalatory mouse NOAEC into a corrected inhalatory NOAEC in case of differences between experimental and human exposure condition has to be performed.
Corrected starting point for the inhalative route for workers:
= NOAEC (inhalation) * exposure condition mouse / exposure condition human
= 4015 mg/m³ * (6h/day / 24h/day)
= 4015 mg/m³ * 0.25 = 1004 mg/m³
Thus, the corrected starting point for workers was 1004 mg/m³ for inhalation.
- Justification:
- The dose descriptor starting point is based on a NOAEL.
- Justification:
- The DNEL is based on a subacute study.
- Justification:
- AF not used used for inhalation route.
- Justification:
- Default value according to ECHA REACH Guida
- Justification:
- Default value general population.
- Justification:
- The DNEL is based on a high-quality data set.
- Justification:
- No remaining uncertainties.
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
DNEL related information
General Population - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 1.79 mg/kg bw/day
- Most sensitive endpoint:
- developmental toxicity / teratogenicity
- Route of original study:
- By inhalation
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Dose descriptor starting point:
- NOAEC
- Value:
- 4 015 mg/m³
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 1 877 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
The calculation of the DNEL is based on an inhalation NOAEC observed in a developmental toxicity study in mice (OECD 414; 1986).
Conversion of an inhalatory mouse NOAEC into a corrected dermal NOAEL in case of differences between experimental and human exposure condition and interspecies differences between mouse and human has to be performed.
Corrected starting point for the inhalative route for workers:
To correct the interspecies difference between rat and human the no observed effect level has to be corrected as follows:
Corrected starting point for the inhalative route for workers:
= NOAEC (inhalation) * sRV(mouse) * exposure condition mouse / exposure condition human * (ABSinh-mouse/ABSdermal-human) * (7 days exposure mouse/5 days exposure worker)
= 4015 mg/m³ * 1.87 m³/kg bw* (6h/day / 24h/day) * (1/1) = 1877 mg/kg bw/day
It is assumed that dermal absorption and inhalation absorption rates are equal.
(ABSdermal-human = dermal absorption in humans, ABSinh-mouse = inhalation absorption rate in mice)
Thus, the corrected starting point for general population is 1877 mg/kg bw/day for dermal exposure.
- Justification:
- The dose descriptor starting point is based on a NOAEL.
- Justification:
- The DNEL is based on a subacute study.
- Justification:
- Default value for mice according to ECHA REACH Guidance.
- Justification:
- Default value according to ECHA REACH Guidance
- Justification:
- Default value for general population according to ECHA REACH Guidance.
- Justification:
- The DNEL is base on a set of high-quality studies.
- Justification:
- No remaining uncertaintie.
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- medium hazard (no threshold derived)
Acute/short term exposure
- Hazard assessment conclusion:
- medium hazard (no threshold derived)
General Population - Hazard via oral route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 1.79 mg/kg bw/day
- Most sensitive endpoint:
- developmental toxicity / teratogenicity
- Route of original study:
- By inhalation
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Dose descriptor starting point:
- NOAEC
- Value:
- 4 015 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 1 877 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
The calculation of the DNEL is based on an inhalation NOAEC observed in a developmental toxicity study in mice (OECD 414; 1986).
Conversion of an inhalatory mouse NOAEC into a corrected dermal NOAEL in case of differences between experimental and human exposure condition and interspecies differences between mouse and human has to be performed.
Corrected starting point for the inhalative route for workers:
To correct the interspecies difference between rat and human the no observed effect level has to be corrected as follows:
Corrected starting point for the inhalative route for workers:
= NOAEC (inhalation) * sRV(mouse) * exposure condition mouse / exposure condition human * (ABSinh-mouse/ABSdermal-human) * (7 days exposure mouse/5 days exposure worker)
= 4015 mg/m³ * 1.87 m³/kg bw* (6h/day / 24h/day) * (1/1) = 1877 mg/kg bw/day
It is assumed that oral absorption and inhalation absorption rates are equal.
(ABSdermal-human = dermal absorption in humans, ABSinh-mouse = inhalation absorption rate in mice)
Thus, the corrected starting point forgeneral population is 1877 mg/kg bw/dayfordermal exposure.
- Justification:
- The dose descriptor starting point is based on a NOAEL.
- Justification:
- The DNEL is based on a subactue study.
- Justification:
- Default value for mice according to ECHA REACH Guidance.
- Justification:
- Default value according to ECHA REACH Guidance.
- Justification:
- Default value for general population according to ECHA REACH Guidance.
- Justification:
- The DNEL is based on a set of high-quality studies.
- Justification:
- no remaining uncertainties
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
General Population - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- medium hazard (no threshold derived)
Additional information - General Population
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.