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EC number: 911-811-2 | CAS number: -
- 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
Due to its high adsorption and low toxicity to aquatic organisms, HEBMP was assigned to soil hazard category 3 and a PNECscreen was conducted, based on the equilibrium partitioning method (PEC * 10 / PNECscreen). Testing for toxicity to terrestrial organisms has been commissioned with two taxonomic groups and representing two trophic levels (decomposers and consumers): earthworms (OECD 222) and soil microorganisms (OECD 216).
The results from the OECD 216 toxicity to soil microorganisms study indicate no effects of HEBMP-xNa to soil microorganisms, based on nitrate formation rate (NOEC ≥ 1000 mg active acid/kg soil dry weight). However, the OECD 222 toxicity to soil macroorganisms except arthropods study (conducted with HEBMP-H) is not available for the present update. Therefore, the current PNECsoil has not been updated and is derived by the equilibrium partitioning method. The PNECsoil and environmental exposure assessment will be updated with both terrestrial toxicity results once the OECD 222 study becomes available. Currently, the terrestrial RCRs based on the PNECsoil derived by the equilibrium partitioning method are < 1, therefore no further toxicity testing of soil organisms is currently considered to be necessary. The need for additional testing will be reviewed once the results from the OECD 222 study become available.
Additional information
- HEBMP is present as HEBMP-H or one of its ionised forms. The degree of ionisation depends upon the pH in vivo and not whether HEBMP-xNa salt, HEBMP-H (acid form), or another salt was used for dosing.
- Disassociated sodium cations. The amount of sodium present depends on which salt was dosed.
- It should also be noted that divalent and trivalent cations would preferentially replace the potassium ions. These would include calcium (Ca2+), magnesium (Mg2+) and iron (Fe3+).
The acid and sodium salts in the HEBMP category are freely soluble in water. The HEBMP anion can be considered fully dissociated from its sodium cation when in dilute solution. Under any given conditions, the degree of ionisation of the HEBMP species is determined by the pH of the solution. At a specific pH, the degree of ionisation is the same regardless of whether the starting material was HEBMP-H, HEBMP-xNa, or another salt of HEBMP.
Therefore, when a salt of HEBMP is introduced into test media or the environment, the following is present (separately):
The terrestrial environment is exposed to HEBMP predominantly via application of WWTP sludge, and as such this phenomenon also directly affects soil in the receiving environment.
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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