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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
Toxicity to aquatic algae and cyanobacteria
Administrative data
Link to relevant study record(s)
Description of key information
In a 14-days toxicity study, the cultures ofAnkistrodesmus falcatuswere exposed to Disodium arsenate (Na2HAsO4.7H2O) at nominal concentrations of 0, 0.01, 0.10, 1.0, 10, 25, 50, 75 and 100 mg/L (based on As(V)) under static conditions in accordance with the Algal Assay Procedure Bottle Test (US EPA 1971) and APHA (1975) test methods. The parameter followed is growth based on Chlorophyll a measurement compared to control. The 14d-EC50 is determined to 0.256 mg/L based on nominal concentrations of As(V). The corresponding NOEC was 0.01 mg/L. Even if the test method used is obsolete, the study design and the results are well documented. This toxicity study is classified as reliable with restrictions for algae toxicity study.
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 0.159 mg/L
- EC10 or NOEC for freshwater algae:
- 0.01 mg/L
Additional information
A large data set is available on the toxicity of Arsenic acid to algae and aquatic plants.
Long term toxicity data
In the study of Vocke, 1980, several algae species were tested and resulted in 14d EC 50 of 0.048 mg/L to 30.7 mg/L. In the study of Conwell, 1978, the resulting 24 days NOEC was 60 µg/L. This indicates that there is a large variability of sensibility between the species. The lowest result was a NOEC of 0.01 mg/L observed in a 14 d toxicity study onAnkistrodesmus falcatus.
Moreover, there are several references available on algae toxicity data that are either not detailed enough or that do not result in NOEC or EC50 type results.
In a 14-days toxicity study, the cultures ofAnkistrodesmus falcatuswere exposed to Disodium arsenate (Na2HAsO4.7H2O) at nominal concentrations of 0, 0.01, 0.10, 1.0, 10, 25, 50, 75 and 100 mg/L (based on As(V)) under static conditions in accordance with the Algal Assay Procedure Bottle Test (US EPA 1971) and APHA (1975) test methods. The parameter followed is growth based on Chlorophyll a measurement compared to control. The 14d-EC50 is determined to 0.256 mg/L based on nominal concentrations of As(V). The corresponding NOEC was 0.01 mg/L. Even if the test method used is obsolete, the study design and the results are well documented. This toxicity study is classified as reliable with restrictions for algae toxicity study.
In a 14-days toxicity study, the cultures ofScenedesmus obliquuswere exposed to Disodium arsenate (Na2HAsO4.7H2O) at nominal concentrations of 0, 0.01, 0.10, 1.0, 10, 25, 50, 75 and 100 mg/L (based on As(V)) under static conditions in accordance with the Algal Assay Procedure Bottle Test (US EPA 1971) and APHA (1975) test methods. The parameter followed is growth based on Chlorophyll a measurement compared to control. The 14d-EC50 is determined to 0.048 mg/L based on nominal concentrations of As(V). Even if the test method used is obsolete, the study design and the results are well documented. This toxicity study is classified as reliable with restrictions for algae toxicity study.
In a 14-days toxicity study, the cultures ofSelenastrum capricornatumwere exposed to Disodium arsenate (Na2HAsO4.7H2O) at nominal concentrations of 0, 0.01, 0.10, 1.0, 10, 25, 50, 75 and 100 mg/L (based on As(V)) under static conditions in accordance with the Algal Assay Procedure Bottle Test (US EPA 1971) and APHA (1975) test methods. The 14d-EC50 value is based on growth based on Chlorophyll a measurement. The 14d-EC50 is determined to 30.761 mg/L based on nominal concentrations of As(V). Even if the test method used is obsolete, the study design and the results are well documented. This toxicity study is classified as reliable with restrictions for algae toxicity study.
Another validated reference is the study of Conwell,a 24-days toxicity study, the cultures ofAsterionellawere exposed to arsenate at nominal concentrations of8, 60 and 160 µg/L (as As)under flow through conditions. The 24d-EC50 value is based on growth and oligo elements use. The 14d-EC50 is determined to 30.761 mg/L based on nominal concentrations of As(V).Even if the test method used is obsolete, the study design and the results are well documented. This toxicity study is classified as reliable with restrictions for algae toxicity study.
Acute toxicity data
From the document “Proposed EQS for Water Framework Directive Annex VIII substances: arsenic (total dissolved)”, the most severe reference for acute toxicity on algae is the study of Chen, 1994, is a EC50 of 0.159 mg/L of As as arsenicpentoxidetoScenedesmus obliquus.The study was conducted in semi-static conditions, the concentrations used were: 0, 50, 100, 200, 300μg l-1. The study lasted 96h hours. There are few details missing for methodology, but since the study is based on semi-static regime it is considered as valid.
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