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Diss Factsheets
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EC number: 202-713-4 | CAS number: 98-92-0
- 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:
- 43.75 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- other: other: According to EFSA Scientific Committee on Food - Scientific Panel on Dietetic Products, Nutrition and Allergies (2006) Tolerable Upper Intake Levels for Vitamins and Minerals, see section exposure related to observations in humans for details.
- Overall assessment factor (AF):
- 2
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 87.5 mg/m³
- Explanation for the modification of the dose descriptor starting point:
- Body weight (worker) 70 kg; respiratory volume 10.00 m3/person (8 h, light activity), absorption oral/inhalation factor 0.5
- AF for dose response relationship:
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
- AF for differences in duration of exposure:
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
- AF for other interspecies differences:
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
- AF for intraspecies differences:
- 2
- Justification:
- An uncertainty factor of 2 was used to account for vulunerable sub-groups, incl. children (EFSA, 2006).
- AF for the quality of the whole database:
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
- AF for remaining uncertainties:
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
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:
- 12.5 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- other: According to EFSA Scientific Committee on Food - Scientific Panel on Dietetic Products, Nutrition and Allergies (2006) Tolerable Upper Intake Levels for Vitamins and Minerals, see section exposure related to observations in humans for details.
- Overall assessment factor (AF):
- 2
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 25 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- 100 % dermal absorption
- AF for dose response relationship:
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
- AF for differences in duration of exposure:
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
- AF for other interspecies differences:
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
- AF for intraspecies differences:
- 2
- Justification:
- An uncertainty factor of 2 was used to account for vulunerable sub-groups, incl. children (EFSA, 2006).
- AF for the quality of the whole database:
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
- AF for remaining uncertainties:
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
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:
- high hazard (no threshold derived)
Additional information - workers
Derived DNELs are based on results obtained in human studies (see IUCLID section on exposure related to observations in humans for details). Nicotinamide does not produce the flushing response that has been used as the basis for the upper level for nicotinic acid. There has been only one reported case of hepatotoxicity in a patient receiving high-dose nicotinamide (however, nicotinamide has not been subject to extensive clinical trials [at 3 g per day or more] for use as a hypolipidaemic agent). No significant adverse effects have been reported in trials on the possible benefits of nicotinamide in patients with or at risk of diabetes, which have used doses up to the equivalent of 3 g per day, for periods up to 3 years. The NOAEL from these studies is approximately 25 mg/kg bw/day. This value represents the lowest reported dose in a number of recent trials of high quality, many of which used sensitive markers of hepatic function and glucose homeostasis, and included a range of age groups, with some subjects treated with up to 50 mg/kg bw/day. An uncertainty factor of 2 has been used to allow for the fact that adults may eliminate nicotinamide more slowly than the study groups, many of which were children, and that data for children would not reflect the full extent of intersubject variability that could occur in an older population. The upper level for nicotinamide is established at 12.5 mg/kg bw/day or approximately 900 mg/day for adults.
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 21.88 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- other: According to EFSA Scientific Committee on Food - Scientific Panel on Dietetic Products, Nutrition and Allergies (2006) Tolerable Upper Intake Levels for Vitamins and Minerals, see section exposure related to observations in humans for details.
- Overall assessment factor (AF):
- 2
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 43.75 mg/m³
- Explanation for the modification of the dose descriptor starting point:
- Body weight (general public) 70 kg, respiratory volume (24 h, basal activity), factor absportion oral/inhalation 0.5
- AF for dose response relationship:
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
- AF for differences in duration of exposure:
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
- AF for other interspecies differences:
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
- AF for intraspecies differences:
- 2
- Justification:
- An uncertainty factor of 2 was used to account for vulunerable sub-groups, incl. children (EFSA, 2006).
- AF for the quality of the whole database:
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
- AF for remaining uncertainties:
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
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:
- 12.5 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- other: According to EFSA Scientific Committee on Food - Scientific Panel on Dietetic Products, Nutrition and Allergies (2006) Tolerable Upper Intake Levels for Vitamins and Minerals, see section exposure related to observations in humans for details.
- Overall assessment factor (AF):
- 2
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 25 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- 100 % dermal absorption
- AF for dose response relationship:
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
- AF for differences in duration of exposure:
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
- AF for other interspecies differences:
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
- AF for intraspecies differences:
- 2
- Justification:
- An uncertainty factor of 2 was used to account for vulunerable sub-groups, incl. children (EFSA, 2006).
- AF for the quality of the whole database:
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
- AF for remaining uncertainties:
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
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:
- 12.5 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- other: According to EFSA Scientific Committee on Food - Scientific Panel on Dietetic Products, Nutrition and Allergies (2006) Tolerable Upper Intake Levels for Vitamins and Minerals, see section exposure related to observations in humans for details.
- Overall assessment factor (AF):
- 2
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 25 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- Not applicable
- AF for dose response relationship:
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
- AF for differences in duration of exposure:
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
- AF for other interspecies differences:
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
- AF for intraspecies differences:
- 2
- Justification:
- An uncertainty factor of 2 was used to account for vulunerable sub-groups, incl. children (EFSA, 2006).
- AF for the quality of the whole database:
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
- AF for remaining uncertainties:
- 1
- Justification:
- See section on exposure related to observations in humans for details, EFSA (2006)
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
General Population - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- high hazard (no threshold derived)
Additional information - General Population
Derived DNELs are based on results obtained in human studies (see IUCLID section on exposure related to observations in humans for details). Nicotinamide does not produce the flushing response that has been used as the basis for the upper level for nicotinic acid. There has been only one reported case of hepatotoxicity in a patient receiving high-dose nicotinamide (however, nicotinamide has not been subject to extensive clinical trials [at 3 g per day or more] for use as a hypolipidaemic agent). No significant adverse effects have been reported in trials on the possible benefits of nicotinamide in patients with or at risk of diabetes, which have used doses up to the equivalent of 3 g per day, for periods up to 3 years. The NOAEL from these studies is approximately 25 mg/kg bw/day. This value represents the lowest reported dose in a number of recent trials of high quality, many of which used sensitive markers of hepatic function and glucose homeostasis, and included a range of age groups, with some subjects treated with up to 50 mg/kg bw/day. An uncertainty factor of 2 has been used to allow for the fact that adults may eliminate nicotinamide more slowly than the study groups, many of which were children, and that data for children would not reflect the full extent of intersubject variability that could occur in an older population. The upper level for nicotinamide is established at 12.5 mg/kg bw/day or approximately 900 mg/day for adults.
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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