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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 231-722-6 | CAS number: 7704-34-9
- 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
Carcinogenicity
Administrative data
Description of key information
In accordance with section 1 of REACH Annex XI, a carcinogenicity study does not need to be conducted. Sulfur is not mutagenic (the structure of sulfur raises no chemical alert for mutagenicity or other general reactivity with genetic material) and did not cause hyperplasia and/or pre-neoplastic lesions in the sub-chronic repeated dose toxicity study.
In general, sulfur is an essential element in the metabolism of all living organisms, thus chronic exposure to sulfur is the natural state. More specifically, sulfur is unreactive and insoluble. Systemic effects were absent after subacute and subchronic oral exposure and subacute dermal exposure. Additionally, in vitro and in vivo tests have demonstrated no evidence of genotoxicity. Sulfur is only metabolised by intestinal bacteria; there are indications of absorption of metabolites but which are most likely endogenous to the body (e.g. well known to be intermediary or end products of mammalian metabolic reactions). The expectation that no carcinogenic effects will occur as a consequence of sulfur exposure is supported by the long-standing use of sulfur in topically applied, pharmaceutical formulations and as a pesticide and the absence of carcinogenic effects.
The US-EPA (1991) draws the same conclusion. According to the US-EPA human risks, if any, from both dietary and occupational exposure to sulfur are considered to be very low because of the general knowledge of the chemical, its ubiquitous natural occurrence and its low acute toxicity as well as its long history of use including some pharmaceutical applications. It is therefore considered unnecessary to conduct carcinogenicity studies with elemental sulfur.
Key value for chemical safety assessment
Carcinogenicity: via oral route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Carcinogenicity: via inhalation route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Carcinogenicity: via dermal route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Justification for classification or non-classification
In the absence of experimental carcinogenicity data and taking account of the lack of mutagenic activity, classification is not necessary for carcinogenicity under EU CLP Regulation (EC No. 1272/2008),
Additional information
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.