Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 200-664-3 | CAS number: 67-68-5
- 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
Immunotoxicity
Administrative data
Description of key information
Key value for chemical safety assessment
Effect on immunotoxicity: via inhalation route
Endpoint conclusion
- Dose descriptor:
- NOAEC
- 2 800 mg/m³
Additional information
As part of a 13-week inhalation toxicity study (Kenny, 2000, see section 7.5.3), four satellite groups of Sprague-Dawley rats (5/sex/group) were exposed snout-only, 6 h/day, 7 d/week, for 28 days to mean analyzed chamber concentrations of 0, 0.310, 0.964 and 2.783 mg DMSO/l. To act as a positive control, a further group of satellite animals were injected i.p. with cyclophosphamide at a dose of 50 mg/kg 2 days prior to termination. The study was designed to comply with OECD/US EPA OPPTS guidelines and GLP regulations. Sheep Red Blood Cell (SRBC)-specific antibody secreting cells (ASCs) were enumerated using a modification of the Jerne Plaque Forming Cell (PFC) assay. Inhalation exposure to DMSO led to an apparent increase in the number of antibody secreting cells in male rats, compared with controls. Changes in the total number of antibody secreting cells in the spleen (PFC/spleen) and also changes in the relative numbers of antibody secreting cells, associated with changes in other spleen cell populations (PFC/10e6 cells) were measured. Since DMSO increased both PFC/10e6 cells and PFC/spleen in male rats, the effect is likely to be a genuine enhancement, not simply a broad spectrum increase in spleen cell numbers. It is worth noting that there was a high degree of inter-animal variation in the PFC response. This is almost certainly linked to the genetic background of the Sprague-Dawley rats, which are an outbred population. The adaptive immune response is known to have strong genetic linkage and work from other sources has shown that whilst outbred species are popular models in toxicology they have an inherent variability in immune responses. Based in the high variability observed in male rats, the lack of effects in female rats and the lack of effect on the other end-points relevant for immunotoxicity (spleen and thymus weights, lymphocyte count) reported in the 13-week study, these data doesn't desmonstrate any effects of toxicological significance on the immune system (Kenny, 2000; reliability 1).
Autoimmune strain MRL/lpr, CH3/lpr, and male BXSB mice were placed on a continuous treatment with 3% DMSO (8-10 g/kg bw/d) in the drinking water, commencing at 1 to 2 months of age, before spontaneous disease development could be detected. DMSO provides significant protection against the development of murine autoimmune lymphoproliferative disease (Morton & Siegel, 1986).
Mice were injected i.p. daily with 1.3-2.5 g/kg 100% DMSO or sterile saline for 5 weeks. All mice were immunized twice with sheep red blood cells (days 13 and 24), and bled twice by caudal incision (days 20 and 29). Haematocrits were significantly decreased but still within the normal range. The primary and secondary antibody response to sheep red blood cells, leukocytes counts, body weight, and the size of the heart, lungs, spleen, thymus, and kidneys were not affected. DMSO treatment resulted in significant liver enlargement (Caren et al., 1985).
Justification for classification or non-classification
Based on the available data, no classification for repeated toxicity has to be applied for DMSO according to EU Directive 67/584/EEC and EU regulation (EC) No 1272/2008 (CLP).
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.