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EC number: 203-874-3 | CAS number: 111-48-8
- 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:
- 17.6 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):
- 25
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 441 mg/m³
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
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:
- 25 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 100
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 2 500 mg/kg bw/day
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
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)
Workers - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- low hazard (no threshold derived)
Additional information - workers
Short term exposure worker (systemic effects)
It is not possible to derive a DNEL for acute effects based on the available data. The acute toxicity of Thiodiglycol is low with respect to the oral and dermal routes of exposure. There is no risk to be expected from inhalative vapor exposure since IRT showed no effects.
Short term exposure worker (local effects)
Thiodiglycol is in accordance with EU Classification, Labelling and Packaging of Substances and Mixtures (CLP) Regulation (EC) No. 1272/2008 classified as eye irritant (cat. 2). The performed guideline test is not providing dose-response data that could be used for the derivation of a DNEL.
According to the REACH guidance on information requirements and chemical safety assessment, Part E: Risk Characterisation, a qualitative risk characterisation should be performed for this endpoint. In order to guarantee "adequately control of risks", it is necessary to stipulate risk management measures that prevent exposure.
Long term exposure worker (systemic effects)
Inhalatory and dermal
The DNELs for inhalatory and dermal long term exposure are derived from the NOAEL obtained in an oral repeated dose study (Angerhofer et al., 1997). In this 90-day gavage study (doses: 0, 50, 500, 5000 mg/kg bw/day), effects on body and kidney weight (without a histopathological correlate) as well as altered parameters of the urine analysis were observed in males and females at 5000 mg/kg bw/day. A dose level of 500 mg/kg bw/day is considered as NOAEL.
Exposure by inhalation
Modification into a correct starting point:
Relevant dose descriptor (NOAEL): 500 mg/kg bw/d
Standard respiratory volume of the rat (sRVrat) for 8 hours: 0.38 m³/kg bw
Oral absorption of the rat / inhalation absorption of humans (ABSoral-rat / ABSinh-human): 0.5
Standard respiratory volume of humans (sRVhuman) for 8 hours: 6.7 m³
Worker respiratory volume (wRV) for 8 hours with light physical activity: 10 m³
Corrected inhalatory NOAEC for workers
= 500 mg/kg bw/d * (1 / 0.38 m³/kg bw) * 0.5 * (6.7 m³/10 m³)
= 441 mg/m³
Use of assessment factors: 25
Interspecies: no allometric scaling factor is applied because an oral-to-inhalation route extrapolation is performed.
Intraspecies AF (worker): 5
Exposure duration AF: 2
Remaining differences AF: 2.5
In conclusion, long term systemic inhalation DNEL, workers = 17.6 mg/m³.
Dermal exposure
Modification into a correct starting point:
In in vitro experiments using pig skin, the percutaneous absorption was 20% after application of radiolabelled thiodiglycol in acetone solution (Reifenrath et al., 2002).
Corrected dermal NOAEL for workers
= 500 mg/kg bw/d * (1 / 0.2)
= 2500 mg/kg bw
Step 3: Use of assessment factors: 100
Interspecies AF, allometric scaling (rat to human): 4
Intraspecies AF (worker): 5
Exposure duration AF: 2
Remaining differences AF: 2.5
In conclusion, long term systemic dermal DNEL, workers = 25 mg/kg bw/day.
Long term exposure worker (local effects)
Thiodiglycol is in accordance with EU Classification, Labelling and Packaging of Substances and Mixtures (CLP) Regulation (EC) No. 1272/2008 classified as eye irritant (cat. 2). The available data are not suitable for the derivation of a DNEL.
According to the REACH guidance on information requirements and chemical safety assessment, Part E: Risk Characterisation, a qualitative risk characterisation should be performed for this endpoint. In order to guarantee "adequately control of risks", it is necessary to stipulate risk management measures that prevent exposure.
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 4.3 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- Overall assessment factor (AF):
- 50
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 217 mg/m³
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
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
General Population - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 12.5 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- Overall assessment factor (AF):
- 200
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 2 500 mg/kg bw/day
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
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)
General Population - Hazard via oral route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 2.5 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- Overall assessment factor (AF):
- 200
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 500 mg/kg bw/day
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
DNEL related information
General Population - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- low hazard (no threshold derived)
Additional information - General Population
Short term exposure general population (systemic effects)
It is not possible to derive a DNEL for acute effects based on the available data. The acute toxicity of Thiodiglycol is low with respect to the oral and dermal routes of exposure. There is no risk to be expected from inhalative vapor exposure since IRT showed no effects.
Short term exposure general population (local effects)
Thiodiglycol is in accordance with EU Classification, Labelling and Packaging of Substances and Mixtures (CLP) Regulation (EC) No. 1272/2008 classified as eye irritant (cat. 2). The performed guideline test is not providing dose-response data that could be used for the derivation of a DNEL.
Long term exposure general population (systemic effects)
Inhalatory, dermal and oral
The DNELs for inhalatory, dermal and oral long term exposure are derived from the NOAEL obtained in an oral repeated dose study (Angerhofer et al., 1997). In this 90-day gavage study (doses: 0, 50, 500, 5000 mg/kg bw/day), effects on body and kidney weight (without a histopathological correlate) as well as altered parameters of the urine analysis were observed in males and females at 5000 mg/kg bw/day. A dose level of 500 mg/kg bw/day is considered as NOAEL.
Exposure by inhalation
Modification into a correct starting point:
Relevant dose descriptor (NOAEL): 500 mg/kg bw/d
Standard respiratory volume of the rat (sRVrat) for 24 hours: 1.15 m³/kg bw
Oral absorption of the rat / inhalation absorption of humans (ABSoral-rat / ABSinh-human): 0.5
Corrected inhalatory NOAEC for general population
= 500 mg/kg bw/d * (1 / 1.15 m³/kg bw/d) * 0.5
= 217 mg/m³
Use of assessment factors: 50
Interspecies: no allometric scaling factor is applied because an oral-to-inhalation route extrapolation is performed.
Intraspecies AF (general population): 10
Exposure duration AF: 2
Remaining differences AF: 2.5
In conclusion, long term systemic inhalation DNEL, general population = 4.3 mg/m³.
Dermal exposure
Modification into a correct starting point:
In in vitro experiments using pig skin,the percutaneous absorption was 20% after application of radiolabelled thiodiglycol in acetone solution (Reifenrath et al., 2002).
Corrected dermal NOAEL for general population
= 500 mg/kg bw/d * (1 / 0.2)
= 2500 mg/kg bw
Use of assessment factors: 200
Interspecies AF, allometric scaling (rat to human): 4
Intraspecies AF (general population): 10
Exposure duration AF: 2
Remaining differences AF: 2.5
In conclusion, long term systemic dermal DNEL, general population = 12.5 mg/kg bw/day.
Oral exposure
Modification into a correct starting point:
No modification of starting point necessary (NOAEL = 500 mg/kg bw/d)
Use of assessment factors: 200
Interspecies AF, allometric scaling (rat to human): 4
Intraspecies AF (general population): 10
Exposure duration AF: 2
Remaining differences AF: 2.5
In conclusion, long term systemic oral DNEL, general population = 2.5 mg/kg bw/day.
Long term exposure general population (local effects)
Thiodiglycol is in accordance with EU Classification, Labelling and Packaging of Substances and Mixtures (CLP) Regulation (EC) No. 1272/2008 classified as eye irritant (cat. 2). The available data are not suitable for the derivation of a DNEL.
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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