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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 200-641-8 | CAS number: 67-03-8
- 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:
- 11 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
- Dose descriptor starting point:
- NOAEC
- Value:
- 1 000 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 881 mg/m³
- Explanation for the modification of the dose descriptor starting point:
DNEL for inhalation exposure
The relevant NOAEL for inhalation DNELs is 1000 mg/kg bw/d for Thiamine hydrochloride based on the 28-day repeated dose toxicity study (OECD422). Route-to-route extrapolation is considered using a default factor of 2 (according to the Guidance Document on Information Requirements, Chapter R8 assuming that oral absorption was at least 50 % and that 100 % of the applied dose would be absorbed by inhalation).
Worker
The NOAEL of 1000 mg Thiamine hydrochloride/kg bw/d is converted into corrected inhalatory NOAEC using the equation provided in the Guidance Document on Information Requirement, Chapter R8.
NOAEC = oral NOAEL*(1/(0.38 m3/kg/d))*(ABSoral rat/ABSinh human)*(6.7 m3(8h)/10 m3(8h))
It is calculated to 881 mg/m3.
Using assessment factors of (i) 5 for intraspecies extrapolation, (ii) 1 for duration exposure, and (iii) 2.5 for the remaining species differences (AF = 12.5), this results in a DNEL of 70 mg/m3for short-term exposure for workers.
Using assessment factors of (i) 5 for intraspecies extrapolation, (ii) 6 for duration exposure, and (iii) 2.5 for the remaining species differences (AF = 75), this results in a DNEL of 11 mg/m3for long-term exposure for workers.
- AF for dose response relationship:
- 1
- Justification:
- The starting point is a NOAEL
- AF for differences in duration of exposure:
- 6
- Justification:
- Subacute to chronic
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- NA for inhalation
- AF for other interspecies differences:
- 1
- Justification:
- Addressed by modification of starting point
- AF for intraspecies differences:
- 5
- Justification:
- Default value for workers
- AF for the quality of the whole database:
- 1
- Justification:
- Data available on the test substance appropriate for the tonnage band
- AF for remaining uncertainties:
- 1
- Justification:
- Default value
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:
- 3.3 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
- Dose descriptor starting point:
- NOAEL
- Value:
- 1 000 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 1 000 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
DNEL for dermal exposure
Based on the general assumption that dermal absorption will not be higher than oral absorption, the relevant NOAEL for dermal DNELs is 1000 mg/kg bw/d for Thiamine hydrochloride based on the 28-day repeated dose toxicity study (OECD422) via the oral route.
Worker
Using a dermal NOAEL of 1000 mg/kg bw/day and taking into account assessment factors for (i) interspecies variation of 4, (ii) remaining species differences of 2.5, (iii) exposure duration of 6, and (iv) intraspecies variation of 5 (AF = 300), the systemic DNEL worker for long-term exposure via the dermal route is3.3 mg/kg bw/day.
- AF for dose response relationship:
- 1
- Justification:
- A clear NOAEL was obtained
- AF for differences in duration of exposure:
- 6
- Justification:
- subacute to chronic
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- default for rat
- AF for other interspecies differences:
- 1
- Justification:
- default value
- AF for intraspecies differences:
- 5
- Justification:
- default value for workers
- AF for the quality of the whole database:
- 1
- Justification:
- appropriate for the tonnage band
- AF for remaining uncertainties:
- 2.5
- Justification:
- any remaining difference
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
Workers - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- low 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:
- 2.8 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
- Dose descriptor starting point:
- NOAEC
- Value:
- 1 000 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 434 mg/m³
- Explanation for the modification of the dose descriptor starting point:
DNEL for inhalation exposure
The relevant NOAEL for inhalation DNELs is 1000 mg/kg bw/d for Thiamine hydrochloride based on the 28-day repeated dose toxicity study (OECD422). Route-to-route extrapolation is considered using a default factor of 2 (according to the Guidance Document on Information Requirements, Chapter R8 assuming that oral absorption was at least 50 % and that 100 % of the applied dose would be absorbed by inhalation).
General Population
The NOAEL of 1000 mgThiamine hydrochloride/kg bw/d is converted into corrected inhalatory NOAEC using the equation provided in the Guidance Document on Information Requirements, Chapter R8.
NOAEC = oral NOAEL*(1/(1.15 m3/kg/d))*(ABSoral rat/ABSinh human)
It is calculated to 434 mg/m3.
Using assessment factors of (i) 10 for intraspecies extrapolation, (ii) 6 for duration exposure, and (iii) 2.5 for the remaining species differences (AF = 150), this results in a DNEL of2.8 mg/m3for long-term exposure.
- AF for dose response relationship:
- 1
- Justification:
- The starting point is a NOAEL
- AF for differences in duration of exposure:
- 6
- Justification:
- Subacute to chronic
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- NA for inhalation
- AF for other interspecies differences:
- 1
- Justification:
- Addressed by modification of starting point
- AF for intraspecies differences:
- 10
- Justification:
- Default value for general population
- AF for the quality of the whole database:
- 1
- Justification:
- Data available on the test substance appropriate for the tonnage band
- AF for remaining uncertainties:
- 1
- Justification:
- Default value
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:
- 1.6 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
- Dose descriptor starting point:
- NOAEL
- Value:
- 1 000 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 1 000 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
DNEL for dermal exposure
Based on the general assumption that dermal absorption will not be higher than oral absorption, the relevant NOAEL for dermal DNELs is 1000 mg/kg bw/d for Thiamine hydrochloride based on the 28-day repeated dose toxicity study (OECD422) via the oral route.
General Population
Using a dermal NOAEL of 1000 mg/kg bw/day and taking into account assessment factors for (i) interspecies variation of 4, (ii) remaining species differences of 2.5, (iii) exposure duration of 6, and (iv) intraspecies variation of 10 (AF = 600), the systemic DNEL worker for long-term exposure via the dermal route is1.6 mg/kg bw/day.
- AF for dose response relationship:
- 1
- Justification:
- A clear NOAEL was obtained
- AF for differences in duration of exposure:
- 6
- Justification:
- subacute to chronic
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- default value
- AF for other interspecies differences:
- 2.5
- Justification:
- default value
- AF for intraspecies differences:
- 5
- Justification:
- default value for workers
- AF for the quality of the whole database:
- 1
- Justification:
- appropriate for the tonnage band
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:
- DNEL (Derived No Effect Level)
- Value:
- 1.6 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
- Dose descriptor starting point:
- NOAEL
- Value:
- 1 000 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 1 000 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
DNEL for oral exposure
For Worker a DNEL for oral exposure is not considered necessary as workers are not supposed to eat at their work environment.
The relevant NOAEL for oral DNELs is 1000 mg/kg bw/d for Thiamine hydrochloride based on the 28-day repeated dose toxicity study (OECD422) via the oral route.
General Population
Using assessment factors of (i) 10 for intraspecies extrapolation, (ii) 6 for duration exposure, (iii) 4 for extrapolation from rat to human, and (iv) 2.5 for the remaining species differences (AF = 600), this results in a DNEL of1.6 mg/kg bw/dfor long-term exposure.
- AF for dose response relationship:
- 1
- Justification:
- A clear NOAEL was obtained
- AF for differences in duration of exposure:
- 6
- Justification:
- subacute to chronic
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Default value
- AF for other interspecies differences:
- 2.5
- Justification:
- Default value
- AF for intraspecies differences:
- 10
- Justification:
- Default value for general population
- AF for the quality of the whole database:
- 1
- Justification:
- appropriate for the tonnage band
- AF for remaining uncertainties:
- 1
- Justification:
- Default value
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
General Population - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- low 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.