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Diss Factsheets
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EC number: 219-371-7 | CAS number: 2425-79-8
- 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:
- 4.7 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 75
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 352.6 mg/m³
- Explanation for the modification of the dose descriptor starting point:
- The oral NOAEL of 200 mg/kg bw/d, derived from the subacute OECD407-study, is converted to a NOAEC by dividing by 0.38 and multiplying by 0.67 according to ECHA Guidance taking into account differences in respiratory volume (rat/humans) and light-work activity by workers: NOAEC 200 * 0.67/ 0.38 = 352.6 mg/m3. As inhalatory and oral absorption are both considered 100%, no adjustment for absorption is applied.
- AF for dose response relationship:
- 1
- Justification:
- NOAEC is used as a starting point
- AF for differences in duration of exposure:
- 6
- Justification:
- AF based on a sub-acute study according to OECD407
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- AF not used for inhalation route according to ECHA guidance
- AF for other interspecies differences:
- 2.5
- Justification:
- Default factor for other interspecies differences
- AF for intraspecies differences:
- 5
- Justification:
- For workers the default factor of 5 is applied, according to ECHA guidance
- AF for the quality of the whole database:
- 1
- Justification:
- Underlying OECD407 study is rated Klimisch 1 performed under GLP without deviations
- AF for remaining uncertainties:
- 1
- Justification:
- No further uncertainties have to be taken into account
Acute/short term exposure
- Hazard assessment conclusion:
- high hazard (no threshold derived)
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- high hazard (no threshold derived)
Acute/short term exposure
- Hazard assessment conclusion:
- high 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:
- 6.66 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):
- 300
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 2 000 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- The oral NOAEL of 200 mg/kg bw/d, derived from the subacute OECD407-study, is converted to a dermal NOAL by applying a factor of 10 according to ECHA Guidance taking into account differences in absorption rate of the substance (10% dermal versus 100% oral): NOAEL(dermal) = 200 * 100/10 = 2000 mg/m3.
- AF for dose response relationship:
- 1
- Justification:
- NOAEL is used as a starting point.
- AF for differences in duration of exposure:
- 6
- Justification:
- AF based on a sub-acute study according to OECD407
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- AF according to ECHA guidance as rats were used in the OECD407 study.
- AF for other interspecies differences:
- 2.5
- Justification:
- Default factor for other interspecies differences
- AF for intraspecies differences:
- 5
- Justification:
- For workers the default factor of 5 is applied, according to ECHA guidance
- AF for the quality of the whole database:
- 1
- Justification:
- Underlying OECD407 study is rated Klimisch 1 performed under GLP without deviations
- AF for remaining uncertainties:
- 1
- Justification:
- No further uncertainties have to be taken into account
Acute/short term exposure
- Hazard assessment conclusion:
- high hazard (no threshold derived)
- Most sensitive endpoint:
- sensitisation (skin)
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- high hazard (no threshold derived)
- Most sensitive endpoint:
- sensitisation (skin)
Acute/short term exposure
- Hazard assessment conclusion:
- high hazard (no threshold derived)
- Most sensitive endpoint:
- sensitisation (skin)
Workers - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- medium hazard (no threshold derived)
Additional information - workers
WORKER
Acute DNELs:
Production of epoxy resins is in excess of 10 t/y. According to the REACH "Guidance on information requirements and chemical safety assessment, Part B: Hazard Assessment", above 10 t/y, the establishment of acute toxicity DNEL is unnecessary in most cases, as the DNEL based on long-term exposure is normally sufficient to ensure that adverse effects do not occur. Thus, acute DNELs should default to the long term systemic DNELs.
For local effects, a DNEL was not quantifiable; however, as epoxy resins are classified as skin sensitizers, local effects must be assessed qualitatively and risk management measures applied as necessary. The potential for respiratory sensitization is unknown; however, given its skin sensitization potential, this endpoint also is assessed qualitatively.
Long-term DNELs:
DNELs are based on the oral 28-day study in rats (key study selected) entitled "A 28-Day Oral Gavage Toxicity Study of Butanediol Diglycidylether in Sprague Dawley Rats (WIL-749003)” with the most sensitive endpoint selected as repeated dose toxicity.
Starting Dose for DNEL calculation:
NOAEL: 200 mg/kg/day
Absorption Information:
Oral absorption was considered to be 100% based on experimental data.
Inhalation absorption was considered to be 100% based on consideration of the molecular weight and log Kow values.
Dermal absorption was considered to be 10% based on the physicochemical properties of epoxy resins and the lack of observed systemic effects following dermal exposure.
Modified dose for DNEL Calculation:
Worker – Inhalation = 200 mg/kg/day x 1/0.38 x 6.7/10 (no adjustment for absorption) = 352.6 mg/m3
Worker – Dermal = 200 mg/kg/day x 100%/10% (adjustment for absorption) = 2,000 mg/kg/day
Assessment Factors (AF) were selected as described in line with ECHA guidance documents.
Final DNELs:
Worker – Inhalation = 4.7 mg/m3
Worker – Dermal = 6.66 mg/kg/day
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 1.16 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 150
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 173.9 mg/m³
- Explanation for the modification of the dose descriptor starting point:
- The oral NOAEL of 200 mg/kg bw/d, derived from the subacute OECD407-study, is converted to a NOAEC by dividing by 1.15 according to ECHA Guidance taking into account differences in respiratory volume (rat/humans) by consumers: NOAEC 200 / 1.15 = 173.9 mg/m3. As inhalatory and oral absorption are both considered 100%, no adjustment for absorption is applied.
- AF for dose response relationship:
- 1
- Justification:
- NOAEC is used as a starting point
- AF for differences in duration of exposure:
- 6
- Justification:
- AF based on a sub-acute study according to OECD407
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- AF not used for inhalation route according to ECHA guidance
- AF for other interspecies differences:
- 2.5
- Justification:
- Default factor for other interspecies differences
- AF for intraspecies differences:
- 10
- Justification:
- For consumers the default factor of 10 is applied, according to ECHA guidance
- AF for the quality of the whole database:
- 1
- Justification:
- Underlying OECD407 study is rated Klimisch 1 performed under GLP without deviations
- AF for remaining uncertainties:
- 1
- Justification:
- No further uncertainties have to be taken into account
Acute/short term exposure
- Hazard assessment conclusion:
- high hazard (no threshold derived)
- Most sensitive endpoint:
- sensitisation (respiratory tract)
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- high hazard (no threshold derived)
- Most sensitive endpoint:
- sensitisation (respiratory tract)
Acute/short term exposure
- Hazard assessment conclusion:
- high hazard (no threshold derived)
- Most sensitive endpoint:
- sensitisation (respiratory tract)
DNEL related information
General Population - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 3.33 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 600
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 2 000 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- The oral NOAEL of 200 mg/kg bw/d, derived from the subacute OECD407-study, is converted to a dermal NOAL by applying a factor of 10 according to ECHA Guidance taking into account differences in absorption rate of the substance (10% dermal versus 100% oral): NOAEL(dermal) = 200 * 100/10 = 2000 mg/m3.
- AF for dose response relationship:
- 1
- Justification:
- NOAEL is used as a starting point.
- AF for differences in duration of exposure:
- 6
- Justification:
- AF based on a sub-acute study according to OECD407
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- AF according to ECHA guidance as rats were used in the OECD407 study.
- AF for other interspecies differences:
- 2.5
- Justification:
- Default factor for other interspecies differences
- AF for intraspecies differences:
- 10
- Justification:
- For consumers the default factor of 10 is applied, according to ECHA guidance
- AF for the quality of the whole database:
- 1
- Justification:
- Underlying OECD407 study is rated Klimisch 1 performed under GLP without deviations
- AF for remaining uncertainties:
- 1
- Justification:
- No further uncertainties have to be taken into account
Acute/short term exposure
- Hazard assessment conclusion:
- high hazard (no threshold derived)
- Most sensitive endpoint:
- sensitisation (skin)
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- high hazard (no threshold derived)
- Most sensitive endpoint:
- sensitisation (skin)
Acute/short term exposure
- Hazard assessment conclusion:
- high hazard (no threshold derived)
- Most sensitive endpoint:
- sensitisation (skin)
General Population - Hazard via oral route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.33 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):
- 600
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 200 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:
- NOAEL is used as a starting point.
- AF for differences in duration of exposure:
- 6
- Justification:
- AF based on a sub-acute study according to OECD407
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- AF according to ECHA guidance as rats were used in the OECD407 study.
- AF for other interspecies differences:
- 2.5
- Justification:
- Default factor for other interspecies differences
- AF for intraspecies differences:
- 10
- Justification:
- For consumers the default factor of 10 is applied, according to ECHA guidance
- AF for the quality of the whole database:
- 1
- Justification:
- Underlying OECD407 study is rated Klimisch 1 performed under GLP without deviations
- AF for remaining uncertainties:
- 1
- Justification:
- No further uncertainties have to be taken into account
Acute/short term exposure
- Hazard assessment conclusion:
- medium hazard (no threshold derived)
DNEL related information
General Population - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- medium hazard (no threshold derived)
Additional information - General Population
GENERAL POPULATION
Acute DNELs:
General population: Production of epoxy resins is in excess of 10 t/y. According to the REACH "Guidance on information requirements and chemical safety assessment, Part B: Hazard Assessment", above 10 t/y, the establishment of acute toxicity DNEL is unnecessary in most cases, as the DNEL based on long-term exposure is normally sufficient to ensure that adverse effects do not occur. Thus, acute DNELs should default to the long term systemic DNELs.
For local effects, a DNEL was not quantifiable; however, as epoxy resins are classified as skin sensitizers, local effects must be assessed qualitatively. The potential for respiratory sensitization is unknown; however, given its skin sensitization potential, this endpoint also is assessed qualitatively.
Long-term DNELs:
DNELs are based on the oral 28-day study in rats (key study selected) entitled "A 28-Day Oral Gavage Toxicity Study of Butanediol
Diglycidylether in Sprague Dawley Rats (WIL-749003)” with the most sensitive endpoint selected as repeated dose toxicity.
Starting Dose for DNEL calculation:
NOAEL: 200 mg/kg/day
Absorption Information:
Oral absorption was considered to be 100% based on experimental data.
Inhalation absorption was considered to be 100% based on consideration of the molecular weight and log Kow values.
Dermal absorption was considered to be 10% based on the physicochemical properties of epoxy resins and the lack of observed systemic effects following dermal exposure.
Modified dose for DNEL Calculation:
General Population – Oral = 200 mg/kg/day (no adjustment for absorption) = 200 mg/kg/day
General Population – Inhalation = 200 mg/kg/day x 1/1.15 (no adjustment for absorption) = 173.9 mg/m3
General Population– Dermal = 200 mg/kg/day x 100%/10% (adjustment for absorption) = 2,000 mg/kg/day
Assessment Factors (AF) were selected as described in line with ECHA guidance documents.
Final DNELs:
General Population – Oral = 0.33 mg/kg/day
General Population – Inhalation = 1.18 mg/m3
General Population– Dermal = 3.33 mg/kg/day
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.