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EC number: 215-481-4 | CAS number: 1327-53-3
- 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
Read across approach
Diarsenic trioxide is readily soluble in water (17.8 g/L at 20°C). Upon dissolution in water, it reacts acidically to trivalent arsenite ions which are not subject to any relevant degree of oxidation for up to 72 hours (Klawonn, 2010). Read-across from toxicological data on inorganic arsenites to diarsenic trioxide is justified without restrictions. However, it is also known that in the human body, inorganic arsenic compounds are converted apart from As(III) also to As(V). Upon becoming systemically available, As(V) is rapidly partly converted to As(III). As(III) species are considered to be more toxic and bioactive than As(V) species. The difference in toxicological potency between As(III) and As(V) cannot be quantified exactly and may vary between routes of exposure and/or type of toxicological effects. Generally, risk assessments are conducted for "inorganic arsenic compounds" as a group, and do not differentiate between various species. Following a conservative approach, the toxicity of diarsenic trioxide is therefore considered to be determined by the release of soluble inorganic species (trivalent arsenites and pentavalent arsenates) which do not differ substantially in potency and may be interconverted both in the environment and in the body. Consequently, it is justified to apply read across to soluble inorganic arsenic compounds to evaluate the systemic effects, including acute toxicity, of diarsenic trioxide.
The acute toxicity of arsenic compounds has been studied to great extent in animal studies and there are also many case reports of acute effects in humans. The focus of such investigations has been on oral exposure. Because of the enormous amount of data, reference is made to available reviews, such as the "Toxicological Profile for Arsenic (ATSDR, 2007), or to peer-reviewed factual databases, such as the Hazardous Substance Databank (HSDB) and the Registry of Toxic Effects of Chemical Substances (RTECS).
Oral
For diarsenic trioxide, reported oral LD50s in animals are in the range from ca. 10-214 mg/kg, which is in agreement with the existing harmonized classification as Acute Tox 2 - H300 according to Regulation (EC) No 1272/2008. Human case reports of accidental or deliberate poisoning support the conclusion that diarsenic trioxide is acutely toxic via the oral route.
Inhalation
Acute inhalation exposure of humans to diarsenic trioxide usually does not take place to a significant extent and does not usually lead to lethality, but irritation of skin and mucous membranes has been observed (in agreement with the existing harmonised classification as Skin Corr. 1B). After evaluation of all available data (existing reviews, literature searches in factual and bibliographic databases) a reliable standard toxicity descriptor value, such as a LC50(4h), cannot be established for diarsenic trioxide. A standard acute inhalation toxicity study (e.g. OECD TG 403 or comparable guideline) is not available. Some animal studies are available which used intratracheal injection as the route of exposure, but are not focused on lethality as an endpoint, but rather on local lung effects, lung clearance issues or carcinogenicity. Due to the well-known toxicological profile of arsenic compounds, including diarsenic trioxide, and specifically because of the carcinogenic potential, strict measures are already in place to exclude or minimise as far as possible any exposure of humans to such compounds.
Dermal
Adverse effects from dermal exposure to inorganic or organic arsenicals have not been extensively investigated. No studies were located regarding death in humans after dermal exposure to inorganic arsenicals. In rats, no deaths resulted from dermal exposure to arsenate or arsenite at doses up to 1000 mg As/kg (e.g. Gaines, 1960). These data indicate that dermal exposure to inorganic arsenic compounds is very unlikely to result in lethality. According to reliable reviews, the dermal absorption of inorganic arsenic compounds is considered to be low (<10%), rendering this route of exposure to be of limited relevance. The chemical nature of arsenic metal, together with its poor solubility, renders its potential for uptake through skin low. This is also the case for any expected transformation/dissolution products, i.e. dissolved arsenic in ionic form. Uptake of arsenic through the skin has been determined to occur at rates below 2%, when applied in dissolved form as radiolabelled arsenic acid to human skin in vitro (Wester et al., 1993).With regards to this low dermal absorption, we can consider this route of exposure to be of limited relevance.
Due to the well-known toxicological profile of arsenic compounds, including diarsenic trioxide, and specifically because of the carcinogenic potential, strict measures are already in place to exclude or minimise as far as possible any exposure of humans to such compounds. Therefore, and for animal welfare reasons, it is not justified to conduct further toxicological studies in experimental animals.
Key value for chemical safety assessment
Acute toxicity: via oral route
Link to relevant study records
- Endpoint:
- acute toxicity: oral
- Type of information:
- other: cited in secondary literature
- Adequacy of study:
- weight of evidence
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- other: Cited in peer reviewed factual database (RTECS). Primary bibliographic source unavailable.
- Principles of method if other than guideline:
- Not available. Cited in peer reviewed factual database (RTECS). Primary bibliographic source unavailable.
- Species:
- mouse
- Route of administration:
- oral: unspecified
- Key result
- Sex:
- not specified
- Dose descriptor:
- LD50
- Effect level:
- 145 mg/kg bw
- Based on:
- not specified
- Clinical signs:
- other: Behavioral: Ataxia; Gastrointestinal: Hypermotility, diarrhea
- Interpretation of results:
- Toxicity Category III
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Endpoint:
- acute toxicity: oral
- Type of information:
- other: cited in secondary literature
- Adequacy of study:
- weight of evidence
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- other: Cited in peer reviewed factual database (RTECS). Primary bibliographic source unavailable.
- Principles of method if other than guideline:
- Not available. Cited in peer reviewed factual database (RTECS). Primary bibliographic source unavailable.
- Species:
- rat
- Route of administration:
- oral: unspecified
- Key result
- Sex:
- not specified
- Dose descriptor:
- LD50
- Effect level:
- 763 mg/kg bw
- Based on:
- not specified
- Clinical signs:
- other: Behavioral: Ataxia; Gastrointestinal: Hypermotility, diarrhea
- Interpretation of results:
- Toxicity Category IV
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Endpoint:
- acute toxicity: oral
- Type of information:
- other: cited in secondary literature
- Adequacy of study:
- weight of evidence
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- other: Cited in peer reviewed factual database (RTECS). Primary bibliographic source unavailable.
- Principles of method if other than guideline:
- Not available. Cited in peer reviewed factual database (RTECS). Primary bibliographic source unavailable.
- Species:
- mouse
- Route of administration:
- oral: unspecified
- Key result
- Sex:
- not specified
- Dose descriptor:
- LD50
- Effect level:
- 144 mg/kg bw
- Based on:
- not specified
- Interpretation of results:
- Toxicity Category III
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Endpoint:
- acute toxicity: oral
- Data waiving:
- other justification
- Justification for data waiving:
- other:
Referenceopen allclose all
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 10 mg/kg bw
Acute toxicity: via inhalation route
Link to relevant study records
- Endpoint:
- acute toxicity: inhalation
- Data waiving:
- other justification
- Justification for data waiving:
- other:
- Clinical signs:
- other:
Reference
Endpoint conclusion
- Endpoint conclusion:
- no study available
Acute toxicity: via dermal route
Link to relevant study records
- Endpoint:
- acute toxicity: dermal
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- secondary literature
- Reason / purpose for cross-reference:
- data waiving: supporting information
- Qualifier:
- according to guideline
- Guideline:
- other: No guideline was followed
- GLP compliance:
- not specified
- Test type:
- other: single dermal dose
- Limit test:
- yes
- Specific details on test material used for the study:
- Calcium arsenate and lead arsenate
- Species:
- rat
- Strain:
- Sherman
- Sex:
- female
- Details on test animals or test system and environmental conditions:
- The rats used in these studies were reared in a separate building of the laboratory where the tests were made. They were at least 90 days old and had minimum body weights of 175 and 200 g for the males and females, respectively. The animals were individually caged during the study and fed Purina Laboratory Chow. None of them was fasted prior to dosage. The survivors were held for daily observation until they appeared to have recovered completely or for a minimum of 14 days.
- Type of coverage:
- open
- Vehicle:
- other: 95% ethyl alcohol
- Details on dermal exposure:
- In this study the test substances were suspended in 95% ethyl alcohol prior testing. The fur of the rats was clipped over the top of the shoulder and forward part of the back with an Ang-Ra No. 2 animal clipper to provide a clean area of about 3.0 X 4.5 cm for application of the test substance. The clipped area of unbroken skin was bathed with a 1:1 solution of acetone and 95% ethyl alcohol to remove dirt and excess oils.
The formulations of the test substances were applied slowly to prevent run-off, using a 1-ml pipette. The rats were observed at least once each hour during the first day after dosage, and twice a day thereafter, for symptoms of poisoning and time of death. The LD50 values were determined by the method of Litchfield and Wilcoson (1949). - Duration of exposure:
- 14 d
- Doses:
- 0.0016 mL/kg bw
- No. of animals per sex per dose:
- 20 females
- Control animals:
- not specified
- Key result
- Dose descriptor:
- LD50
- Effect level:
- > 2 400 mg/kg bw
- Based on:
- test mat.
- Remarks on result:
- other: calcium arsenate
- Key result
- Dose descriptor:
- LD50
- Effect level:
- 2 400 mg/kg bw
- Based on:
- test mat.
- Remarks on result:
- other: lead arsenate
- Interpretation of results:
- study cannot be used for classification
- Conclusions:
- Under the study conditions, the LD50s of the tested substances were > 2400 mg/kg bw after single dermal application.
- Executive summary:
A 14-day acute dermal toxicity study was conducted to determine the potential toxic effects of calcium arsenate and lead arsenate when applied as a single dermal dose to adult rats. 20 Sherman strain female rats were used. The substances were suspended in 95% ethyl alcohol and tested separately at the dose of 0.0016 mL/kg bw. Under the study conditions, the LD50s of the tested substances were > 2400 mg/kg bw after single dermal application (Gaines, 1960).
- Endpoint:
- acute toxicity: dermal
- Data waiving:
- other justification
- Justification for data waiving:
- other:
Referenceopen allclose all
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
Justification for classification or non-classification
Diarsenic trioxide is classified as Acute Tox 2 - H300 (Fatal if swallowed) according to Regulation (EC) No 1272/2008 based on a large database of human and animal data. LD50s (oral) reported for diarsenic trioxide in peer-reviewed factual databases are in the range from ca. 10-214 mg/kg. There are no guideline-conform studies on acute toxicity following inhalation or dermal exposure to As2O3, and the conduct of such animal studies is not justifiable for animal welfare reasons in consideration of the irritating/corrosive nature of As2O3.
Further, based on the known toxicological profile of arsenic compounds strict risk reduction measures are usually in place to protect against long term effects, specifically against carcinogenicity. In conclusion, further classifications for acute toxicity via the dermal or oral route are not justified.
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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