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EC number: 233-046-7 | CAS number: 10025-87-3
- 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
Key value for chemical safety assessment
Genetic toxicity in vitro
Description of key information
“In water, phosphoryl trichloride hydrolyzes to phosphoric acid and hydrochloric acid with t1/2 < 10 seconds (Riess, 2002): POCl3+ 3 H2O→H3PO4+ 3 HCl” (OECD SIDS for phosphoryl trichloride, 2004).
“Phosphoryl trichloride as well as the hydrolysis product hydrochloric acid are not mutagenic in bacteria. As phosphoryl trichloride decomposes to acid in aqueous media the resulting acidity of the hydrolysis products may cause unspecific effects of low pH in in-vitro tests. The change in pH may induce chromosomal aberrations and other DNA damage. Specific effects of phosphoryl trichloride are not expected due to the rapid hydrolysis” (OECD SIDS for phosphoryl trichloride, 2004).
Phosphate and chloride are normal constituents of the body (OECD SIDS for hydrogen chloride, 2002; EFSA, 2005).
Chloride:
"Chloride is a normal constituent of the blood and the excess is expected to be excreted into the urine (Ganong, 2001). The uptake of sodium chloride via food is about 3.5-9 gram per person per day (Battarbee and Meneely, 1978; FASEB, 1979). It means 2.1-5.5 g chloride is taken into the body via food. The daily intake through inhalation during an 8-hour work shift is estimated to be only 108 mg/day under the worst case at the working place. The body pool of this anion (Cl-) is large, and the uptake of chloride via exposure to hydrogen chloride/ hydrochloric acid is much less than the uptake of chloride via food, it is therefore unlikely that occupational aerosol exposures significantly alter the normal body load. The uptake of protons via exposure to hydrogen chloride/ hydrochloric acid is not expected to change the pH in the blood under normal handling and use conditions (non-irritating). The pH of the extracellular fluid is regulated within a narrow range to maintain homeostasis. Via urinary excretion and exhalation of carbon dioxide, the pH is maintained at the normal pH of 7.4 (Ganong, 2001)" (OECD SIDS for hydrogen chloride, 2002).
Phosphate:
"Phosphorus (as phosphate) is an essential dietary constituent, involved in numerous physiological processes, such as the cell’s energy cycle (high-energy pyrophosphate bonds in adenosine triphosphate [ATP]), regulation of the whole body acid-base balance, as component of the cell structure (as phospholipids) and of nucleotides and nucleic acids in DNA and RNA, in cell regulation and signaling by phosphorylation of catalytic proteins and as second messenger (cAMP). Another important function is in the mineralization of bones and teeth (as part of the hydroxyapatite). Reviews and safety evaluations for phosphorus are available from the Joint FAO/WHO Expert Committee on Food additives (JECFA, 1982), the Food and Nutrition Board of the Institute of Medicine (FNB, 1997), and the UK Expert Group on Vitamins and Minerals (EGVM, 2003). JECFA has used the nephrocalcinosis, induced by excessive phosphate intake in rats, as the critical effect to set a maximum tolerable daily intake (MTDI) of 70 mg/kg for phosphoric acid and phosphate salts. The FNB set an upper level for phosphorus of 4.0 g/day for adults, based upon a NOAEL which represents the extrapolation of the phosphorus intake to serum phosphorus concentration curve in adults up to the intake of phosphorus which would result in serum phosphorus levels of infants, which are considered to be safe for tissues with respect to metastatic mineralization. The UK Expert Group on Vitamins and Minerals used the gastrointestinal effects due to high supplemental phosphate intake, to establish a NOAEL of 750 mg/day for supplemental phosphorus" (EFSA, 2005).
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (negative)
Genetic toxicity in vivo
Description of key information
“In water, phosphoryl trichloride hydrolyzes to phosphoric acid and hydrochloric acid with t1/2 < 10 seconds (Riess, 2002): POCl3+ 3 H2O→H3PO4+ 3 HCl” (OECD SIDS for phosphoryl trichloride, 2004).
“In vivo, the hydrolysis products, phosphoric and hydrochloric acid, will be neutralized immediately in the physiologic medium at low concentrations. The resulting anions chloride and phosphate are essential components of every living tissue. They are not expected to produce mutagenic effects. The reduced pH levels could lead to chromosomal changes and DNA damage at the portal-of-entry of phosphoryl trichloride. However, it is unlikely that systemic changes in pH would occur after exposure to phosphoryl trichloride, which are sufficient in magnitude to induce this effect in distant tissues or organs. Due to the corrosive nature of phosphoryl trichloride the performance of studies in animals is not warranted” (OECD SIDS for phosphoryl trichloride, 2004).
Additional information
No evidence of mutagenicity was seen in an Ames test performed with phosphoryl trichloride in the presence or absence of an exogenous metabolic activation system (Brusick, 1977).
“Phosphoryl trichloride as well as the hydrolysis product hydrochloric acid are not mutagenic in bacteria. As phosphoryl trichloride decomposes to acid in aqueous media the resulting acidity of the hydrolysis products may cause unspecific effects of low pH in in-vitro tests. The change in pH may induce chromosomal aberrations and other DNA damage. Specific effects of phosphoryl trichloride are not expected due to the rapid hydrolysis. In vivo, the hydrolysis products, phosphoric and hydrochloric acid, will be neutralized immediately in the physiologic medium at low concentrations. The resulting anions chloride and phosphate are essential components of every living tissue. They are not expected to produce mutagenic effects. The reduced pH levels could lead to chromosomal changes and DNA damage at the portal-of-entry of phosphoryl trichloride. However, it is unlikely that systemic changes in pH would occur after exposure to phosphoryl trichloride, which are sufficient in magnitude to induce this effect in distant tissues or organs. Due to the corrosive nature of phosphoryl trichloride the performance of studies in animals is not warranted” (OECD SIDS for phosphoryl trichloride, 2004).
Endpoint Conclusion: No adverse effect observed (negative)
Justification for classification or non-classification
Phosphoryl trichloride is not classified for genotoxicity according to Annex VI of Regulation (EC) No 1272/2008. No classification for genotoxicity is proposed on the basis of a negative Ames test and the considerations for HCl and H3PO4.
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