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EC number: 231-901-9 | CAS number: 7778-39-4
- 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
Additional information
Arsenic acid (AA) is an inorganic compound of arsenic (As). There are no proprietary data investigating the stability of AA unless a range of publications dealing with the abiotic fate of As are available in the literature. This section aims to provide a concise overview of the abiotic fate of As in water and atmosphere compartments. As is a naturally occurring element but As also enters into environment through releases from human activities.
Stability in contact with water
There are no existing studies investigating the hydrolysis of AA in aqueous media. The hydrolysis information requirement is waived since the information requirement is not applicable to AA which does not exhibit hydrolysable moieties. As (+5) is a thermodynamically stable form of As. In water and under aerobic conditions, AA exists as a mixture of arsenate ions based on its pKa:
H3AsO4 <-> H+ + H2AsO4 - (pKa1=2.22)
H2AsO4 - <-> H+ + HAsO42 - (pKa2=6.98)
HAsO42 - <-> H+ + AsO43- (pKa3=11.53)
Considering the influence of pH alone, the protonated form H3AsO4 is the dominant form of arsenate at very low pH. Under most environmental conditions (pH 5 - 9), H2AsO4 - and HAsO42 - are the dominant forms of arsenate ions.
As (+3) as arsine is usually present and sometimes dominates in low oxygen waters (e.g. bottom water). Some arsenate and arsenite species can interchange oxidation states depending on Eh, pH and biotransformation. The relevant abundance of oxidised and reduced species of As is significantly influenced by iron and manganese oxides.
As (-3) and As (0) occur only under strong reducing conditions (low Eh and anaerobic conditions).
Stability in contact with light
As enters into the atmosphere mainly through the release of As2O3 or less frequently as volatile organic compounds (arsine). Trivalent As species and arsine undergo oxidation into As (+5) forms. Photolysis in atmosphere is not considered as a significant breakdown process or As compounds.
The rates of photochemical decomposition in water of arsenite, DMA and MMA have been studied in both distilled water and seawater. All species were found to degrade rapidly in aerated distilled water. Half-life values for the degradation of DMA, MMA and arsenite were 9.2, 11.5 and 0.9 min for aerated distilled water and 25, 19 and 8 min for de-aerated distilled water. In seawater, the photochemical decomposition rate is slower with 20% of DMA converted to MMA after 300 min.
Photolysis
It has no influence on the behaviour and transformation of arsenate in waters.
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