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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 233-032-0 | CAS number: 10024-97-2
- 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
Endpoint summary
Administrative data
Description of key information
Nitrous oxide is not expected to induce adverse effects in the haematopoietic system at occupational concentrations and under occupational exposure scenarios.
Since nitrous oxide is a gas, the oral and dermal route is not relevant for the assessment of repeated dose toxicity.
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: inhalation - systemic effects
Link to relevant study records
- Endpoint:
- sub-chronic toxicity: inhalation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 413 (90-Day (Subchronic) Inhalation Toxicity Study
- Deviations:
- yes
- Remarks:
- Limited haematology and pathology
- GLP compliance:
- no
- Limit test:
- no
- Species:
- mouse
- Strain:
- Swiss Webster
- Sex:
- male/female
- Route of administration:
- inhalation: gas
- Type of inhalation exposure:
- whole body
- Vehicle:
- air
- Duration of treatment / exposure:
- 14 weeks
- Frequency of treatment:
- 4 h/d, 5 d/w
- Dose / conc.:
- 5 000 ppm
- Remarks:
- (0.5%)
- Dose / conc.:
- 50 000 ppm
- Remarks:
- (5%)
- Dose / conc.:
- 500 000 ppm
- Remarks:
- (50%)
- No. of animals per sex per dose:
- 27
- Control animals:
- yes, concurrent vehicle
- Observations and examinations performed and frequency:
- BODY WEIGHT: Yes
- Time schedule for examinations: twice weekly
HAEMATOLOGY: Yes
CLINICAL CHEMISTRY: Yes - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes
HISTOPATHOLOGY: Yes - Other examinations:
- Liver microsomal cytochrome P-450 content and the rates of defluorination of enflurane and methoxyflurane were determined.
- Mortality:
- no mortality observed
- Description (incidence):
- All animals survived to the scheduled necropsy.
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- Treatment related decreases in body weight were observed at 500 000 ppm with a depression of 77 and 63% in body weight gain in males and females respectively. This depression in weight gain was statistically significant (p<0.025 and p<0.01, respectively).
- Haematological findings:
- no effects observed
- Description (incidence and severity):
- No treatment related changes were observed in any of the parameter measured.
- Clinical biochemistry findings:
- no effects observed
- Description (incidence and severity):
- No treatment related changes were observed in any of the parameter measured.
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Description (incidence and severity):
- No treatment related changes were observed in any of the parameter measured. No impairment of the testis weight was observed.
- Histopathological findings: non-neoplastic:
- no effects observed
- Description (incidence and severity):
- No histological changes in the liver, kidneys or adrenal gland were detected.
- Other effects:
- no effects observed
- Description (incidence and severity):
- Neither the hepatic microsomal cytochrome P-450 content nor the rates of anesthetic defluorination were increased. No enzyme induction or inhibition could be observed.
- Key result
- Dose descriptor:
- NOAEC
- Effect level:
- 50 000 ppm
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- body weight and weight gain
- Remarks on result:
- other: corresponds to 90909 mg/m3
- Critical effects observed:
- no
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEC
- 90 909 mg/m³
- Study duration:
- subacute
- Experimental exposure time per week (hours/week):
- 20
- Species:
- mouse
Repeated dose toxicity: inhalation - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
Repeated dose: oral and dermal route
Since nitrous oxide is a gas, the oral and dermal route is not relevant for the assessment of repeated dose toxicity.
Repeated dose: via inhalation
Animal studies reflecting exposure duration and concentrations relevant for the workplace are not available. Occupational exposure to nitrous oxide without waste gas scavenging usually ranges between 400 and 3000 ppm (ACGIH report, 2001). Whilst using concentrations of 5000 ppm and more, the study of Rice et al. (1985) is considered the only relevant investigation for the assessment of systemic effects after long-term exposure to nitrous oxide.
Swiss Webster mice (15/sex/gp) were exposed to nitrous oxide via whole body inhalation at concentrations of 0, 5000, 50 000 or 500 000 ppm [0, 0.5, 5, 50%] for 4h/d, 5d/wk over 14 wks. At necropsy limited histopathology and haematology / biochemistry parameters were measured. All animals survived to the scheduled necropsy. The study failed to demonstrate exposure related haematopoietic changes. There was no change in the white blood cell count nor was granulocytopenia or thrombocytopenia observed. The lack of effect suggests that either the strain of mouse was insensitive to nitrous oxide, or more likely that continuous exposure is necessary to induce leucocytopenia, as previous demonstrated following continuous exposure to nitrous oxide at high concentrations (20-80%). Furthermore, no treatment related changes in organ weights, biochemical or histopathological parameters were observed. Treatment related decreases in body weight were observed in high dose group animals, with a depression of 77 and 63% in body weight gain in males and females respectively. This depression in weight gain was statistically significant (p<0.025 and p<0.01, respectively). The objective of the study was to demonstrate the maximum tolerated concentration of nitrous oxide, which was deemed to be 50% (500000 ppm). In terms of establishing a NOAEL, based on the results of this study and the data presented, 50000 ppm (5%) was deemed to be the NOAEL, based on statistically significant reductions in body weight gains observed at the LOAEL (500000 ppm [50%]) (Rice et al, 1985).
Effects on the haematopoietic system observed in man and laboratory animals (MAK value documentation, 1993) occur only at high concentrations usually used for anaesthesia and are therefore not relevant for the hazard assessment at the workplace. They were included in the dossier for the sake of completeness.
After exposure of rats to 10 000 ppm nitrous oxide for 5 weeks (6 hours/day, 5 days/week), the number of mast cells in the peripheral blood and bone marrow was increased. After 9 weeks normal values were found once more. Exposure for 6 months resulted initially in a reversible polycythaemia and, after 5 months, in an increase in the number of reticulocytes. The meaning of these results is not clear. No leukocytopenia was observed (Cleaton-Jones et al. 1975, 1977).
After up to two weeks continuous exposure to 500 000 ppm there was a significant reduction in the leukocyte and lymphocyte counts, in the number of nucleated mature bone marrow cells, pluripotent stem cells and granulocyte precursors in the bone marrow of splenectomized mice (Suzuki et al. 1990).
In rats exposed intermittently (21 to 35 days, no other information) to nitrous oxide concentrations of 200 000 ppm the only effect observed was a decrease in the lymphocyte count. With continuous administration, the leukocyte, reticulocyte and lymphocyte counts were reduced after 35 days. After day 10, changes in the bone marrow occurred. The same effects in the bone marrow were seen after as little as three days intermittent or continuous exposure to 400000 ppm (Kripke et al. 1977).
Continuous exposure of rats to nitrous oxide concentrations of 800 000 ppm for 2, 4 and 6 days led to a decrease in the white blood cells counts and to changes in the histology of the bone marrow (Green and Eastwood 1963). No NOAEC was described.
Taken together, nitrous oxide is not expected to induce adverse effects in the haematopoietic system at occupational concentrations and under occupational exposure scenarios.
General remark
1 mL/m3 (ppm) = 1.83 mg/m3
Justification for classification or non-classification
Classification, Labeling, and Packaging Regulation (EC) No 1272/2008
The criteria for classification for specific target organ toxicity after repeated exposure according to Regulation (EC) No 1272/2008, as amended for fifteenth time in Regulation (EU) No 2020/1182, are not met.
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.