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EC number: 232-417-0 | CAS number: 8017-16-1
- 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
Short-term toxicity to fish
Administrative data
Link to relevant study record(s)
Description of key information
All available studies show that mortality is caused by low pH values. When adjusted to environmentally relevant pH values, phosphoric acid as pyrophosphate salt do not cause acute adverse effects on fish.
Key value for chemical safety assessment
Additional information
In accordance with Annex XI, section 1.5 of Regulation (EC) No 1907/2006 (REACH) a read across approach may be used when substances have similarities based on the likelihood of common breakdown products via physical and biological processes, which result in structurally similar chemicals. As mentioned in the hydrolysis summary, polyphosphoric acid is hydrolysed to orthophosphate in environmental conditions. Thus a read across from orthophosphoric acid to pyrophosphoric acid is justified. In addition, studies performed with pyrophosphate salts can also be used. Pyrophosphate salts are ionic in nature and therefore dissociate readily into cations and anions in water. Cations as potassium and sodium are essential micronutrients that are ubiquitous in the environment. As such, their uptake is tightly regulated and is therefore not considered to pose a risk for ecotoxicity. In environmental conditions, the pyrophosphate anion is unstable and a number of different processes result to an ultimate breakdown product of orthophosphate.
The study from Ellgaard and Gilmore (1982) focuses on the pH effects caused by phosphoric acid. Different pH levels have been tested in bluegill sunfish. The pH induced by phosphoric acid which caused 50% mortality was between 3.0 and 3.25, while no mortality was observed at pH 3.5 or above after 96h exposure. At neutral pH 7.5 no fish died.
Similar results were obtained for Aphanius dispar (Alkahem, 1989) with a median lethal pH of 3.58. Another study showed that a 96h-LC50 of phosphoric acid of 75.1 mg/L was obtained in Oryzias latipes (Korean study, 2005) when the pH was not adjusted to relevant environmental values. No mortality was observed at 100 mg/L when the pH was adjusted.
The studies show that a pH caused by adding phosphoric acid roughly between pH 3 (or lower) and 4 is critical for fish.
A study showed that survival times increased with increasing pH, and that this increase was more rapid at pH values above 3.5 (Gueylard and Duval, 1922). It can thus be concluded that it is the low pH which is causing the toxic effects. Wallen et al. cited by Von Burg as well described a study in which fish (Gambusia affinis) were exposed to both phosphoric acid and turbidity (600 ppm of clay particles), and in which phosphoric acid precipitated turbidity to levels below 25 ppm. The median tolerance limit after 24, 48 and 96h exposure was 138 ppm (i.e. about 138 mg/L). Townsend and Cheyne (1944) showed that exposure of Oncorhynchus kisutch fingerlings to 20 ppm of phosphoric acid (i.e. pH 6.75) induced no mortality at relatively normal dissolved oxygen concentrations (4.95 -8.15 ppm). However, when the dissolved oxygen concentration was lowered to 1.50 ppm, phosphoric acid at 12.0 and 20.0 ppm induced 100% mortality, which is obviously caused by the combination of the low dissolved oxygen concentration and the presence of increased hydrogen ion concentrations.
As regulatory ecotoxicity tests need to be conducted at pH 6-9, it can be expected that phosphoric acid will not cause adverse effects to fish when in this pH range.
To confirm this observation, a fish toxicity test study performed on rainbow trout with a pyrophosphate salt (tripotassium trihydrogen diphosphate dihydrate) has been investigated and gave a 96h LC50 of greater than 100 mg/L (Priestly, 2010). Indeed, no toxic effect has been observed at the highest test concentration (i.e. 100 mg/L).
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