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Diss Factsheets
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EC number: 203-483-8 | CAS number: 107-35-7
- 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:
- no hazard identified
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:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
- Explanation for the modification of the dose descriptor starting point:
Due to no systemic toxicity and the fact that Taurine (with high water solubility and a log P value well below 0) may be too hydrophilic to cross the lipid rich environment of the stratum corneum it is highly improbable that an acute dermal toxicity study would result in any toxicity. In absence of further information concerning route specific effects through dermal exposure, no acute dermal DNELs are considered applicable. This is in line with ECHA's guidance document on information requirements and chemical safety assessment, part R8 that a DNEL for acute toxicity should only be derived if an acute toxicity hazard (leading to C&L) has been identified and there is potential for high peak exposures. This is not the case.
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:
- no hazard identified
Additional information - workers
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
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:
- no hazard identified
DNEL related information
- Dose descriptor starting point:
- NOAEL
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:
- no hazard identified
DNEL related information
- Explanation for the modification of the dose descriptor starting point:
A GLP-and OECD-compliant neurotoxicity study was conducted (please see chapter 7.9.1). Based on these results no compound-related effects were reported at any dose with respect to locomotor activity testing or FOB parameters (including home cage, handling, open field, sensory, neuromuscular, or physiological observations). EFSA (2009) concluded that the results of this study are sufficient to address the behavioral concerns previously raised, and provide evidence for a NOAEL of 1,000 mg/kg body weight/day in the original toxicity study (i.e., WIL, 2001). A NOAEL of 1 ,656 mg/kg body weight was determined based on a lack of adverse physiological or behavioral effects following this 13 week exposure via drinking water in the follow-up neurological study.
Exposure to taurine is unavoidable as it is a natural constituent of the body and is present in foods of animal origin. Spitze et al. (2003) determined the taurine content of a variety of foodstuffs. Animal muscle tissue, particularly fish flesh, contained high concentrations of taurine. The mean daily exposure to taurine from omnivore diets has been estimated to range from 9–40 (lowest range values) to up to 200–400 mg/person per day (top range values) (Rana and Sanders, 1986; Laidlaw et al., 1990; Hayes and Trautwein, 1994).
The EFSA FEEDAP Panel estimated the Observed Safe Limit (OSL) in humans to be 6 g/person per day (corresponding to 100 mg/kg bw per day). Exposure resulting from the consumption of foodstuffs and "energy drinks" together would amount to about one-third of the OSL.
The highest, as well as the most recent, of the top range estimates is 400 mg/person per day (Hayes and Trautwein, 1994), equal to 6.7 mg/kg bw per day for a 60-kg person. This value is 150 times lower than the NOAEL of 1000 mg/kg bw per day in laboratory animals and 15 times lower than the human OSL (100 mg/kg bw per day).
Furthermore, taurine is used in more than 30 clinical investigations in humans in conditions including diabetes, epilepsy, congestive heart failure, hypertension, liver disease and cystic fibrosis, concluding that “No adverse health effects attributable to taurine have been reported over a period of 30 years. In many cases taurine has proved medically beneficial.”
Literature:
Hayes KC and Trautwein EA, 1994. Modern nutrition in health and disease. In: Taurine. Lea & Febiger, Philadelphia, 477–485 (cited in the SCF opinion 1999).
Laidlaw SA, Grosvenor M and Koppele JD, 1990. The taurine content of common foodstuffs. Journal of Parenteral and Enteral Nutrition, 14, 183–188.
Spitze AR, Wong DL, Rogers QR and Fascetti AJ, 2003. Taurine concentrations in animal feed ingredients; cooking influences taurine content. Journal of Animal Physiology and Animal Nutrition, 87, 251–262.
Rana SK and Sanders TAB, 1986. Taurine concentrations in the diet, plasma and breast milk of vegans compared with omnivores.British Journal of Nutrition, 56, 17–27.
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
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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