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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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics in vivo
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Various peer-reviewed articles discussing toxicokinetic aspects of of sulphur (and compounds), public literature, some restrictions, acceptable for assessment
Data source
Referenceopen allclose all
- Reference Type:
- publication
- Title:
- Autoradiographic observations on the uptake of S35 in the genital organs of the female rat and rabbit after injection of labeled sodium sulfate.
- Author:
- Bostrom H, Odeblad E
- Year:
- 1 952
- Bibliographic source:
- Acta Endocrinol. (Copenh);10(1):89-96
- Reference Type:
- publication
- Title:
- On the enzymatic exchange of the sulfate group of chondroitinsulfuric acid in slices of cartilage.
- Author:
- Bostrom H, Mansson B
- Year:
- 1 952
- Bibliographic source:
- J.Biol.Chem.;196(2):483-8
- Reference Type:
- publication
- Title:
- On the metabolism of the sulfate group of chondroitinsulfuric acid.
- Author:
- Bostrom H
- Year:
- 1 952
- Bibliographic source:
- J.Biol.Chem.;196(2):477-81
- Reference Type:
- publication
- Title:
- Rate of excretion of radioactive sulphur and its concentration in some tissues of the rat after intraperitoneal administration of labeled sodium sulphate.
- Author:
- Dziewiatkowski D
- Year:
- 1 949
- Bibliographic source:
- J.Biol.Chem.;178:197-202
- Reference Type:
- publication
- Title:
- Metabolic acidosis after sulfur ingestion.
- Author:
- Blum JE, Coe FL
- Year:
- 1 977
- Bibliographic source:
- N.Engl.J.Med.;297(16):869-70
- Reference Type:
- publication
- Title:
- The oxidation of sulfide to thiosulfate by metalloprotein complexes and by ferritin.
- Author:
- Baxter CF, van Reen R
- Year:
- 1 958
- Bibliographic source:
- Biochim.Biophys.Acta;28(3):573-8
- Reference Type:
- publication
- Title:
- Some aspects of sulfide oxidation by rat-liver preparations.
- Author:
- Baxter CF, van Reen R
- Year:
- 1 958
- Bibliographic source:
- Biochim.Biophys.Acta;28(3):567-73.
- Reference Type:
- publication
- Title:
- Hepatic sulfite oxidase. The nature and function of the heme prosthetic groups.
- Author:
- Cohen HJ, Fridovich I
- Year:
- 1 971
- Bibliographic source:
- J.Biol.Chem.;246(2):367-73
- Reference Type:
- publication
- Title:
- Accidental sulfur poisoning in a group of Holstein heifers.
- Author:
- Gunn M, Baird J, Nimmo Wilkie J
- Year:
- 1 987
- Bibliographic source:
- Can.Vet.J.;28(4):188-92
- Reference Type:
- publication
- Title:
- A critical review of the literature on hydrogen sulphide toxicity.
- Author:
- Beauchamp R, Bus J, Popp J, Boreiko C, Andjelkovich D
- Bibliographic source:
- CRC Crit.Rev.Tox.;13(1):25-97
Materials and methods
- Objective of study:
- toxicokinetics
- Principles of method if other than guideline:
- In accordance with column 2 of REACH Annex VIII-X, an assessment of the toxicokinetic behaviour of the substance should be derived using all available studies. No quantitative data are available on the toxicokinetics of elemental sulfur via the oral, dermal and respiratory routes, neither in animals nor in humans and no specific key studies are identified. A number of peer-reviewed articles shed some qualitative light on elemental sulfur toxicokinetics.
- GLP compliance:
- no
Test material
- Reference substance name:
- Sulfur
- EC Number:
- 231-722-6
- EC Name:
- Sulfur
- Cas Number:
- 7704-34-9
- Molecular formula:
- S
- IUPAC Name:
- sulfur
- Details on test material:
- elemental sulphur (various forms, not always clearly specified)
Constituent 1
Test animals
- Species:
- other: rats, rabbits, dogs, cattle, humans
- Strain:
- other: various
- Sex:
- male/female
Administration / exposure
- Route of administration:
- other: oral, dermal and i.p.
Results and discussion
Toxicokinetic / pharmacokinetic studies
- Details on absorption:
- No quantitative data are available on absorption of elemental sulfur via the oral and inhalation route, neither in animals nor in humans.
- Details on distribution in tissues:
- Once absorbed as sulphide, 35S is distributed in rats as sulfates formed in the body, mostly in tissue containing mucopolysaccharides such as cartilage, trachea, intestinal mucosa, skin and genitals (Bostrom and Odeblad, 1952; Bostrom and Mansson, 1952; Bostrom, 1952).
- Details on excretion:
- Excretion of H2S by the lungs after parenteral administration of a solution of sulfide salts (sodium35S-sulfide) to dogs, rabbits or to rats is minimal and can be considered as negligible (Beauchamp et al, 1984). Urinary excretion of35S after intraperitoneal administration of sodium sulfate to rats was approximately 67% of the radioactivity within 24h, 85% after 120 h with a recovery of 10 % in the faeces within 120 h (Dziewiatkowski, 1949).
Metabolite characterisation studies
- Metabolites identified:
- yes
- Details on metabolites:
- In non-ruminant animals, including man, ingested elemental sulfur is probably converted first to hydrogen sulfide, by colonic bacteria, absorbed and then converted to sulfate (Blum and Coe, 1977) which enters then the normal sulfate body-pool, and, in the liver and the kidney into thiosulfate by an enzymatic activity associated with the mitochondria (Baxter and van Reen, 1958). The enzyme system which is most probably involved is the cytochrome oxidase system which uses molecular oxygen. Cohen and Fridovich (1971) demonstrated by spectral similarity that the sulfite oxidase activity associated with the microsomal fraction of bovine liver is due to a cytochrome b type oxidase. Ferritin seems to convert H2S into thiosulfate in the intestinal mucosa (Baxter and van Reen, 1958).
The absorbed sulfur compounds are incorporated into endogenous sulfur-containing molecules.
In ruminants, sulfur is rapidly reduced in the rumen to sulfite and hydrogen sulphide, some of the hydrogen sulfide is oxidised to sulfate (Gunn, Baird and Nimmo Wilkie, 1987). While some of the hydrogen sulfide is incorporated into microbial protein before being absorbed in the form of essential amino-acids methionine and cysteine, excessive sulfur production within the rumen results in a build-up of toxic hydrogen sulfide gas (H2S). Since the liver efficiently removes sulfide absorbed into the portal vasculature, toxicity of H2S in ruminants is apparently due to eructation (i.e., ejection of gas or air through the mouth from the stomach) and inhalation of H2S produced in the rumen. It is not possible with the available literature to quantify this process. Once H2S has been absorbed, it is metabolised by three different pathways:
1. Oxidation to sulfate and thiosulfate;
2. Methylation to methanethiol and dimethyl sulfide;
3. Reaction with metallo- and disulfide-containing proteins.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): low bioaccumulation potential based on study results
In non ruminant animals (and humans), once absorbed, sulfur gets distributed mostly in tissue containing mucopolysaccharides such as cartilage, trachea, intestinal mucosa, skin and genitals. Majority of sulfur gets excreted via urine and faeces.
In ruminants, sulfur is rapidly reduced in the rumen to sulfite and hydrogen sulphide, with some of the hydrogen sulfide being oxidised to sulfate. Once absorbed, H2S is metabolised by three different pathways:
1. Oxidation to sulfate and thiosulfate;
2. Methylation to methanethiol and dimethyl sulfide;
3. Reaction with metallo- and disulfide-containing proteins. - Executive summary:
No quantitative data are available on absorption of elemental sulfur via the oral and inhalation route, neither in animals nor in humans.
Once absorbed as sulphide, radiolabelled sulphur (35S) is distributed in rats as sulfates formed in the body, mostly in tissue containing mucopolysaccharides such as cartilage, trachea, intestinal mucosa, skin and genitals.
Excretion of H2S by the lungs after parenteral administration of a solution of sulfide salts (sodium 35S-sulfide) to dogs, rabbits or to rats is minimal and can be considered as negligible. Urinary excretion of 35S after intraperitoneal administration of sodium sulfate to rats was approximately 67% of the radioactivity within 24h, 85% after 120 h with a recovery of 10 % in the faeces within 120 h.
In non-ruminant animals, including man, ingested elemental sulfur is probably converted first to hydrogen sulfide, by colonic bacteria, absorbed and then converted to sulfate which enters then the normal sulfate body-pool, and, in the liver and the kidney into thiosulfate by an enzymatic activity associated with the mitochondria. The enzyme system which is most probably involved is the cytochrome oxidase system which uses molecular oxygen. It has been demonstrated by spectral similarity that the sulfite oxidase activity associated with the microsomal fraction of bovine liver is due to a cytochrome b type oxidase. Ferritin seems to convert H2S into thiosulfate in the intestinal mucosa.
The absorbed sulfur compounds are incorporated into endogenous sulfur-containing molecules.
In ruminants, sulfur is rapidly reduced in the rumen to sulfite and hydrogen sulphide, some of the hydrogen sulfide is oxidised to sulfate. While some of the hydrogen sulfide is incorporated into microbial protein before being absorbed in the form of essential amino-acids methionine and cysteine, excessive sulfur production within the rumen results in a build-up of toxic hydrogen sulfide gas (H2S). Since the liver efficiently removes sulfide absorbed into the portal vasculature, toxicity of H2S in ruminants is apparently due to eructation (i.e., ejection of gas or air through the mouth from the stomach) and inhalation of H2S produced in the rumen. It is not possible with the available literature to quantify this process. Once H2S has been absorbed, it is metabolised by three different pathways:
1. Oxidation to sulfate and thiosulfate;
2. Methylation to methanethiol and dimethyl sulfide;
3. Reaction with metallo- and disulfide-containing proteins.
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