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EC number: 236-337-7 | CAS number: 13308-51-5
- 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 microorganisms
Administrative data
Link to relevant study record(s)
- Endpoint:
- activated sludge respiration inhibition testing
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 209 (Activated Sludge, Respiration Inhibition Test
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: The test item was added directly on a weight basis. The requisite mass to reach the desired concentrations was applied on pieces of Teflon, which were subsequently added to the dilution water. To achieve a maximum dilution of the test item, the assay was stirred for 24 h.
- Controls: 6 inoculum blank, 1 abiotic control - Test organisms (species):
- activated sludge of a predominantly domestic sewage
- Details on inoculum:
- Fresh samples of activated sludge are withdrawn from a sewage treatment plant (Ruhrverband Kläranlage, Schmallenberg, Germany) mainly fed with municipal wastewater.
- Pretreatment: On return to the laboratory the sludge was left alone to settle and the supernatant was decanted. The sludge was wahsed one time with isotonic solution. A small amount of the sludge was weighed and dried. From this result a stock solution of activated sludge in tap water was prepared with a mixed liquor suspended solids level of 3.8 g dry mass sludge/liter. The sludge stock solution was fed with synthetic sewage feed and was incubated aerated overnight at 20 ± 2°C in the dark. The amount of food applied was 50 mL/L. after this preincubation, the activated sludge was adjusted on a mixed liquor suspended solids level of 3.8 g dry mass sludge/litre.
- Initial biomass concentration: 1.5 g/L - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 3 h
- Test temperature:
- 20°C
- pH:
- at test end: 8.2 - 8.4
- Nominal and measured concentrations:
- Nominal test substance concentrations: 10, 100, 1000 mg/L
- Details on test conditions:
- TEST SYSTEM
- Test vessel: 1 L Erlenmeyer flasks
- Material, size, headspace, fill volume: glass, 500 mL total volume
- Aeration: aerated (air flow 0.5 - 1 L/min) during incubation
- No. of vessels per concentration (replicates): 1 for 10 and 100 mg/L; 3 for 1000 mg/L
- No. of vessels per control (replicates): 6
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Deionized water, free from inhibitory concentrations of toxic substances (e.g. Cu2+ ions) was used.
- Intervals of water quality measurement: At the end of the test, the pH of each vessel was recorded. Incubation temperature was measured at test start and at test end.
OTHER TEST CONDITIONS
- Adjustment of pH: Before start, the pH was checked and buffered to the pH of 7.5 ± 0.5 using NaOH (1N) solution.
EFFECT PARAMETERS MEASURED (with observation intervals if applicable): The microbial respiration rate (total oxygen uptake including heterotrophic and nitrifcation uptake) was measured after 3 h. - Reference substance (positive control):
- yes
- Remarks:
- 3,5-dichlorophenol
- Duration:
- 3 h
- Dose descriptor:
- other: EC20
- Effect conc.:
- >= 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Duration:
- 3 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Results with reference substance (positive control):
- - Results with reference substance valid? yes, result is in the accepted range of 2 to 25 mg/L
- Relevant effect levels: EC50 (3h) = 11 mg/L - Validity criteria fulfilled:
- yes
- Conclusions:
- There is no significant inhibition of bacterial respiration by Boron orthophosphate up to and including a concentration of 1000 mg/L. The EC50 is > 1000 mg/L.
Reference
There is no significant inhibition of bacterial respiration by Boron orthophosphate up to and including a concentration of 1000 mg/L.
Inhibition (%) of the respiration rate by the test item
Test item concentration [mg T/L] |
||
10 mg/L |
100 mg/L |
1000 mg/L |
0.7% |
-16.0% |
6.6% |
Description of key information
Key value for chemical safety assessment
Additional information
The influence of Boron orthophosphate (CAS 13308-51-5) on the respiration of activated sewage sludge was investigated in a static OECD 209 test under GLP conditions. Activated sewage sludge was exposed to an aqueous dispersion of the test item at nominal concentrations of 10, 100 and 1000 mg/L for a period of 3 hours. The effect of Boron orthophosphate on the respiration of activated sewage sludge gave a 3h- EC50 of greater than 1000 mg/L. The EC20 (3h) was determined to be ≥ 1000 mg/L (nominal). No significant inhibition of bacterial respiration by Boron orthophosphate up to and including a concentration of 1000 mg/L was observed.
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