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EC number: 266-442-3 | CAS number: 66669-53-2
- 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
In cases where no data are available for the substance, tetrasodium hydrogen 2-phosphonatobutane-1,2,4-tricarboxylate ("PBTCNa4"), results of the parent acid, 2-phosphonobutane-1,2,4-tricarboxylic acid ("PBTC"), are taken into account and a read-across approach is proposed with PBTC. In aqueous media, PBTCNa4 and PBTC dissociate into the corresponding anion (2-phosphonatobutane-tricarboxylate ion) and the sodium ion and hydrogen ion (proton), respectively. Fate, behavior and the ecotoxicological properties of PBTC and its tetrasodium salt are thought to be an effect of the phosphonato-carboxylate ion rather than of the sodium ion or the hydrogen ion (proton), which are normal constituents in environmental systems and have no relevant ecotoxic properties in low concentrations. Therefore a read-across between PBTCNa4 and PBTC is justified.
(1) Stability
Hydrolysis
With regard to its chemical structure PBTCNa4 does not contain hydrolysable functional groups and is therefore not expected to hydrolyses under environmental conditions.
In line with this, no indication for a hydrolysis after 5 days at 50 °C can be found and no half-life times and hydrolysis rates were determined for PBTCNa4 (Holzaht-Grimme, 2021).
Phototransformation in water
As there is no data on photodegradation available for PBTCNa4, results of the parent acid PBTC are taken into account for this endpoint. The results of modelling based on the irradiation of PBTC in buffer pH 9 and in presence of FeCl3 indicated that the mean photolysis half-life should range from 2-3 days in summer to 15-65 days in winter. The results of modelling based on the irradiation of PBTC in pure water and stored in brown glass prior to irradiation indicated that the mean photolysis half-lives should range from 0.2-0.3 days in summer to 1-10 days in winter.
(2) Biodegradation
Biodegradation in water
Follwing the EU Method C.4-B (Determination of the "Ready" Biodegradability - Modified OECD Screening Test) a degradation rate of 4 % within 28 days was determined for PBTCNa4, indicating that PBTCNa4 is "Not Readily Biodegradable". Inherent biodegradability of PBTCNa4 was assessed according to the OECD TG 203 B, showing 17% degradation after 28 days. Based on this result PBTCNa4 is considered to be not inherently biodegradable. Anaerobic biodegradation was determined with a method equivalent or similar to EPA OTS 796.3140 (Anaerobic Biodegradability of Organic Chemicals). As no degradation was observed within 56 days PBTCNa4 is regarded as not biodegradable under anaerobic conditions.
Biodegradation in water and sediment
Results of the parent acid, PBTC are taken into account for this endpoint, as no data are available for PBTCNa4. Opposed to OECD guideline 308, not a water-sediment system but the inocula gained from river water and river sediment were separately tested for their ability to degrade PBTC. The study has shown that biodegradation of PBTC in river water and river sediment under environmental conditions primarily depends on the presence of an alternative carbon source and could be optimized certain strains that can easily be enriched and isolated from these both compartments.
Biodegradation in soil
For PBTCNa4 no data on biodegradation in soil are available and results of the parent acid, PBTC are taken into account for this endpoint. The degradability of [3,4-14C]PBTC was investigated in three agricultural soils following the OECD guideline 304A. It was shown that PBTC is moderately degradable and is thoroughly metabolised to CO2 in soil. However, with a worst-case DT50 of 142 d the substance must be classified as persistant (P).
(3) Bioaccumulation
The QSAR determination of the logarithmic octanol-water partition coefficient for tetrasodium hydrogen 2-phosphonatobutane-1,2,4-tricarboxylate using the model KOWWIN included in the Estimation Program Interface (EPI) Suite v4.10 revealed a value of -5.45 of the dissociated form of the substance (Ranz, 2012).
Therefore, based on the physical-chemical properties for PBTCNa4 and its parent acid, PBTC, the substance is considered not likely to bioaccumulate.
(4) Transport and distribution
Adsorption / desorption
The QSAR determination of the carbon partition coefficient for PBTCNa4 using the model KOCWIN included in the Estimation Program Interface (EPI) Suite v4.10 revealed values of 0.001756 L/kg (logKow method) and 25.38 L/kg (MCI method). Both predicted values indicate no adsorption/desorption potential for PBTCNa4.
Henry's Law constant
The Henry's Law Constant (HLC) for PBTCNa4 was predicted using the QSAR calculation of the Estimation Program Interface (EPI) Suite v4.10. Based on the Bond contribution methodology the HLC was estimated to be 1.21E-21 Pa*m³/mol indicating that PBTCNa4 is essentially non-volatile from water.
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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