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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 700-918-8 | CAS number: -
- 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:
- DMEL (Derived Minimum Effect Level)
- Value:
- 3.25 mg/m³
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:
- DMEL (Derived Minimum Effect Level)
- Value:
- 234 mg/kg bw/day
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
Workers - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- no hazard identified
Additional information - workers
Long-term - systemic - inhalation
Hazard assessment of the target substance is based on the most hazardous and critical constituent, benzene.
In accordance with REACH guidance (Appendix R.8-13), a science-based Binding Occupational Exposure Limit value (BOELV) can be used in place of a formal DN(M)EL provided no new scientific information exists which challenges the validity of the BOELV. While information regarding the NOAEC for effects on human bone marrow post-date the BOELV, a DNEL based on these bone marrow (threshold) findings would be higher (and hence offer less protection) than the BOELV. The BOELV will therefore be used as the basis of the DN(M)EL for long-term systemic effects associated with benzene, including haematotoxicity and carcinogenicity.
Relevant dose descriptor
Binding exposure limit value for benzene (BOELVbenzene 3.25 mg/m3) is used without modifications.
DNEL chronic systemic by inhalation route = 3.25 mg/m³
Long-term - systemic - dermal
Hazard assessment of the target substance is based on the most hazardous and critical constituent, benzene.
Relevant dose descriptor
The dermal NOAEL is extrapolated from the BOELVbenzene(3.25 mg/m3).
Modification of the dose descriptor according to ECHA Guidance R.8 (November 2012) Example B. 4.
Route of exposure (inhalation vs dermal); benzene bioavailability via inhalation is assumed to be 50 % while dermal absorption is only 0.1 % (Modjtahedi and Maibach, 2008).
Corrected dermal NOAEL = BOELVbenzene* wRV8h* ABSinh-human/ ABSoral-human
ABS - absorption
wRV8h-worker
respiratory volume (wRV) is 50% greater than the resting standard
respiratory volume of
0.2 L/min/kg bw; wRV8-hour=
(0.2 L/min/kg bw x 1.5 x 60 min x 8 h) / 1000 = 0.144 m3/kg bw
Corrected dermal NOAEL= 3.25* 0.144 * (50/0.1) = 234 mg/kg bw/day
Assessment factors
As the Binding exposure limit value (BOELV) is based on worker life-time exposure no assessment factor is needed.
DNEL worker chronic systemic by dermal route = 234 mg/kg bw/day
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DMEL (Derived Minimum Effect Level)
- Value:
- 3.25 µg/m³
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:
- DMEL (Derived Minimum Effect Level)
- Value:
- 234 µg/kg bw/day
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
General Population - Hazard via oral route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DMEL (Derived Minimum Effect Level)
- Value:
- 0.234 µg/kg bw/day
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
General Population - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- no hazard identified
Additional information - General Population
Long-term - systemic - inhalation
Hazard assessment of the target substance is based on the most hazardous component i.e. benzene. The value, DMEL 3.25 µg/m3, is based on the approach used by WHO (2000) which combined estimates of excess risk for leukaemia calculated by Crump (1994) for four models into a geometric mean estimate. The same four models were used for the derivation of this DMEL but estimates of excess risk for acute myelogenous or acute monocytic leukaemia (AMML) calculated by Crump (1994) were used instead of those for leukaemia. For three of the four models, excess risk estimates calculated by Crump (1994) were used. A more recent estimate of excess risk was available for one model (TCEQ, 2007) and this was used instead of the estimate calculated by Crump (1994). The value of 3.25 µg/m3 (1 ppb) is protective against haematotoxicity, genotoxicity and carcinogenicity and results in a geometric mean excess lifetime risk of AMLL of 0.9 x 10-5.
Relevant dose descriptor
DMEL benzene (3.25 µg/m3) is used without modifications.
DMEL chronic systemic by inhalation route =3.25 µg/m3
Long-term - systemic - dermal
Hazard assessment of the target substance is based on the most hazardous component, benzene.
Relevant dose descriptor
The dermal NOAEL is extrapolated from the inhalation DMELbenzene(3.25 µg/m3).
Modification of the dose descriptor according to ECHA Guidance R.8 (November 2012) Example B. 4.
Route of exposure (inhalation vs oral); bioavailability via inhalation is assumed to be 50 % while dermal absorption is only 0.1 % (Modjtahedi and Maibach, 2008).
Corrected dermal NOAEL = DMELbenzene* wRV8-h* ABSinh-rat/ ABSoral-human
ABS - absorption
wRV8-h-worker
respiratory volume (wRV) is 50% greater than the resting standard
respiratory volume of
0.2 L/min/kg bw; wRV8-hour=
(0.2 L/min/kg bw x 1.5 x 60 min x 8 h) / 1000 = 0.144 m3/kg bw
Corrected dermal NOAEL= 3.25 * 0.144 * (50/0.1) = 234 µg/kg bw/day
Assessment factors
As the DMEL is based on general population life-time exposure no assessment factor is needed.
DMEL chronic systemic by dermal route = 234 µg/kg bw/day
Long-term - systemic - oral
Hazard assessment of the target substance is based on the most hazardous component, benzene.
Relevant dose descriptor
The oral NOAEL is extrapolated from the inhalation DMELbenzene(3.25 µg/m3).
Modification of the dose descriptor according to ECHA Guidance R.8 (November 2012) Example B. 4.
Route of exposure (inhalation vs oral); bioavailability via inhalation is assumed to be 50 % while oral absorption is assumed to be 100 %.
Corrected oral NOAEL = DMELbenzene* wRV8-h* ABSinh-human/ ABSoral-human
ABS - absorption
wRV8-h-worker
respiratory volume (wRV) is 50% greater than the resting standard
respiratory volume of
0.2 L/min/kg bw; wRV8-hour=
(0.2 L/min/kg bw x 1.5 x 60 min x 8 h) / 1000 = 0.144 m3/kg bw
Corrected oral NOAEL= 3.25 * 0.144 * (50/100) = 0.234 µg/kg bw/day
Assessment factors
As the inhalation DMEL is based on general population life-time exposure no assessment factor is needed.
DMEL worker chronic systemic by oral route = 0.234 µg/kg bw/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.
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