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Diss Factsheets
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EC number: 439-840-1 | CAS number: 20846-91-7
- 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 soil microorganisms
Administrative data
Link to relevant study record(s)
Description of key information
In a study using several endpoints to measure toxicity to soil micro-organisms, EDDS at 1.0 g/kg dw soil for 3 days (considered the study NOEC) did not affect substrate-induced respiration (used as an indicator of potential biomass activity) or the activity of four enzymes (considered important for the breakdown of organic matter), although it did cause a significant inhibition of soil basal respiration (Epelde et al. 2008).
Key value for chemical safety assessment
- Long-term EC10 or NOEC for soil microorganisms:
- 1 000 mg/kg soil dw
Additional information
Ethylenediamine disuccinate (EDDS) was studied for its effects on soil micro-organisms (microbial biomass, activity and diversity and community structure), using soil samples from a natural grassland in Larrauri, Northern Spain. After the addition of 1.0 g EDDS/kg dw soil, basal respiration (as an indicator of overall microbial activity) was measured and compared to substrate-induced respiration (as a measure of potentially active biomass) after the addition of glucose. Metabolic quotient (qCO2) was then calculated as the ratio of these two measurements to determine the effect of the test substance on the soil ecosystem. The activity of dehydrogenase, acid phosphatase, beta-glucosidase, and arylsulphatase were analyzed as representatives of four different classes of enzymes important for the breakdown of organic matter. Potentially mineralizable nitrogen was also measured as an indicator of the biological soil activity. Finally, substrate profiles were assessed to determine the functional diversity of the soil microflora.
Basal respiration was reduced slightly (by about 10%), whilst substrate-induced respiration was unaffected by the addition of the test substance. The qCO2 was significantly reduced compared to the control value, indicating development of the ecosystem. There were no significant changes in enzyme activities or potentially mineralizable nitrogen when compared to the controls. Functional diversity was actually increased by the presence of EDDS. In conclusion, 1 g EDDS/kg dw soil had no significant detrimental effect on the soil microflora; this value is considered the study 3-d NOEC (Epelde et al. 2008).
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