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EC number: 254-400-7 | CAS number: 39290-78-3
- 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
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
- Study period:
- 25 February 2010
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: The study has been performed according to OECD and/or EC guidelines and according to GLP principles.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 209 (Activated Sludge, Respiration Inhibition Test
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.11 (Biodegradation: Activated Sludge Respiration Inhibition Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- ISO 8192 (Water quality - Test for inhibition of oxygen consumption by activated sludge for carbonaceous and ammonium oxidation)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on test solutions:
- The batch of 202028/A tested was a clear colourless liquid and was treated as 100% pure.
A stock solution of 0.5 g/l was prepared by adding 125.4 mg test substance to 250 ml of Milli-RO water (tap water purified by reverse osmosis; Millipore Corp., Bedford, Mass., USA). Thorough mixing (15 minutes) was used to accelerate dissolution and to ensure homogeneity. Volumes of the clear colourless stock solution, without flocks, corresponding to the test concentration were then added to the test media. A concentration of 100 mg/l was tested in duplicate. Optimal contact between the test substance and test medium was ensured applying continuous aeration and stirring during the 3-hour exposure period. - Test organisms (species):
- activated sludge of a predominantly domestic sewage
- Details on inoculum:
- The sludge was coarsely sieved, washed and diluted with ISO-medium. A small amount of the sludge was weighed and dried overnight at ca. 105°C to determine the amount of suspended solids (4.0 g/l of sludge, as used for the test). The pH was 7.8 on the day of testing. The batch of sludge was used one day after collection; therefore 50 ml of synthetic sewage feed was added per litre of activated sludge at the end of the collection day. The sludge was kept aerated at test temperature until use.
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 3 h
- Post exposure observation period:
- Oxygen consumption was measured and recorded for approximately 10 minutes after the 3 hours exposure period.
- Test temperature:
- between 18.5 and 19.1°C
- pH:
- between 7.8 and 8.0
- Dissolved oxygen:
- Oxygen consumption:
Control series:66-68 mg O2/l/h
Test substance series: 63-66 mg O2/l/h
The oxygen concentration at the start of measurements was at least 7.2 mg O2/l - Nominal and measured concentrations:
- Nominal concentration: 100 mg/l
- Details on test conditions:
- TEST SYSTEM
- Type (delete if not applicable): open
- Material, size, headspace, fill volume: All glass, approximately 300 ml oxygen bottles (measuring) and
1 litre test bottles(exposure)
- Aeration:During exposure with clean, oil-free air
- No. of vessels per concentration (replicates):2
- No. of vessels per control (replicates):2/ series
- Biomass loading rate:1.6 g/l suspended solids in final test mixture
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Tap-water purified by reverse osmosis (Milli-RO water)
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : The respiration rate from each vessel, in mg O2/l/hr, was calculated from the linear part of the respiration curve, which was generally between 2.5 and 6.5 mg O2/l.
TEST CONCENTRATIONS
- Test concentrations: limit study at 100 mg/l - Reference substance (positive control):
- yes
- Remarks:
- (3,5-dichlorophenol)
- Duration:
- 3 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 100 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.:
- > 4.4 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- element
- Remarks:
- Al
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Duration:
- 3 h
- Dose descriptor:
- EC10
- Effect conc.:
- > 100 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:
- EC10
- Effect conc.:
- > 4.4 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- element
- Remarks:
- Al
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Details on results:
- No significant inhibition of respiration rate of the sludge was recorded at 100 mg 202028/A per litre. The duplicate measurement confirmed the result of the first measurement. Therefore, no further testing was needed. Hence, the EC50 of 202028/A exceeded 100 mg/l (based on nominal concentrations).
- Results with reference substance (positive control):
- Results with reference substance valid: Yes
The inhibitory effect of 3,5-dichlorophenol on aerobic waste water (activated sludge) bacteria increased with increased with increasing concentration , ranging from a 29 % inhibition at 5.0 mg/l to 84 % at 30 mg/l. Relevant effects levels: The EC50 of 3,5-dichlorophenol was: 9.0 mg/l - Validity criteria fulfilled:
- yes
- Conclusions:
- Under the conditions of this present test, 202028/A was not toxic to waste water (activated sludge) bacteria at 100 mg/l. The 3-hour EC50 of 202028/A exceeded 100 mg/l (based on nominal concentrations).
Based on aluminum element the EC50 and EC10 are greater than 4.4 mg/l (total Al) - Executive summary:
Under the conditions of this present test, 202028/A was not toxic to waste water (activated sludge) bacteria at 100 mg/L. The 3-hour EC50 of 202028/A exceeded 100 mg/L (based on nominal concentrations). Based on aluminum element the EC50 and EC10 are greater than 4.4 mg/l (total Al).
- Endpoint:
- toxicity to microorganisms
- Type of information:
- experimental study
- Adequacy of study:
- other information
- Reliability:
- 3 (not reliable)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- The test results are based on test material. As it is not known what the exact purity is and how much aluminum is present. No analytical monitoring is performed, therefore it is not known how much dissolved aluminum was present in the test concentrations. Results can not be converted to aluminum element or dissolved aluminum and can not be compared with other results. It can therefore not be used in the hazard assessment for aluminum.
- Qualifier:
- according to guideline
- Guideline:
- DIN 38412-8 (Pseudomonas Zellvermehrungshemmtest)
- GLP compliance:
- no
- Analytical monitoring:
- no
- Vehicle:
- no
- Test organisms (species):
- Pseudomonas putida
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 16 h
- Duration:
- 16 h
- Dose descriptor:
- EC10
- Effect conc.:
- 13 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth inhibition
- Duration:
- 16 h
- Dose descriptor:
- EC50
- Effect conc.:
- 70 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth inhibition
- Executive summary:
This 16 hour static test was performed on Pseudomonas putida to evaluate the toxicity of Polyaluminium hydroxychlorosulfate (Sachtoklar). It was conducted according to DIN 38412 -8 guideline, not under GLP conditions. The following results were obtained : 16h-EC10 = 13 mg/L and 16h-EC50 = 70 mg/L, both based on growth inhibition and nominal concentrations.
- Endpoint:
- activated sludge respiration inhibition testing
- Type of information:
- migrated information: read-across based on grouping of substances (category approach)
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Guideline study according to GLP
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 209 (Activated Sludge, Respiration Inhibition Test
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- no
- Vehicle:
- no
- Test organisms (species):
- activated sludge, domestic
- Details on inoculum:
- - Laboratory culture: yes, Municipal activated sludge taken from a laboratory wastewater treatment plant fed with municipal sewage.
- Preparation of inoculum for exposure: The inoculum was washed, brought to a concentration of 5 g/L dry substance and aerated during the night. 50 ml were added to a total volume of 250 ml to obtain a concentration of 1 g/L dry substance in the test. - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 180 min
- Test temperature:
- 20 ± 2 °C
- Dissolved oxygen:
- Oxygen concentration during aeration: > 2,5 mg/l
Oxygen concentration immediately before measurement: > 6,5 mg/l - Nominal and measured concentrations:
- 0, 62.5, 125, 250, 500, 1000 mg/l nominal
- Details on test conditions:
- TEST SYSTEM
- Test vessel: Erlenmeyer-vessel (nominal volume 250 ml)
- No. of vessels per concentration (replicates): 1
- No. of vessels per control (replicates): 3
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water:
Synthetic medium: 8 ml/vessel 100-fold concentrated OECD medium - Reference substance (positive control):
- yes
- Remarks:
- dichlorophenol
- Duration:
- 180 min
- Dose descriptor:
- EC10
- 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:
- 180 min
- Dose descriptor:
- EC10
- Effect conc.:
- > 200 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- element
- Remarks:
- Al
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Duration:
- 180 min
- 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
- Duration:
- 180 min
- Dose descriptor:
- EC50
- Effect conc.:
- > 200 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- element
- Remarks:
- Al
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Results with reference substance (positive control):
- satisfactory
- Validity criteria fulfilled:
- yes
- Executive summary:
This 3h static test was performed according to OECD 209, under GLP conditions, to evaluate the toxicity of aluminium trichloride on microorganisms of activated sludge.
The following results were obtained :
-EC10 (respiration rate) > 1000 mg/L (based on nominal concentrations) ; EC10 (respiration rate) > 200 mg/L (based on nominal concentrations of the aluminium element)
-EC50 (respiration rate) >1000 mg/L (based on nominal concentrations) ; EC50 (respiration rate) > 200 mg/L (based on nominal concentrations of the aluminium element).
Referenceopen allclose all
Description of key information
OECD guideline 209, EU method C.11, GLP, key study, validity 1 (Desmares-Koopman, 2010), polyaluminium chloride hydroxide sulfate:
3h-EC50 (respiration rate) > 100 mg/L (based on nominal concentrations)
3h-EC50 (respiration rate) > 4.4 mg/L (based on nominal concentrations of the aluminium element)
Key value for chemical safety assessment
- EC50 for microorganisms:
- 4.4 mg/L
Additional information
Two studies performed on the registered substance are available :
1) This 3h-static test was performed according to OECD guideline 209 and EU method C.11 and according to GLP, on activated sludge of predominantly domestic sewage to evaluate the toxicity of Polyaluminium chloride hydroxide sulphate. Under the conditions of this present test, Polyaluminium chloride hydroxide sulphate was not toxic to activated sludge bacteria at 100 mg/l. The 3-hour EC50 of Polyaluminium chloride hydroxide sulphate exceeded 100 mg/L (based on nominal concentrations). Based on aluminum element the EC50 and EC10 are greater than 4.4 mg/L (total Al).
2) This 16 hour static test was performed on Pseudomonas putida to evaluate the toxicity of Polyaluminium hydroxychlorosulfate (Sachtoklar). It was conducted according to DIN 38412 -8 guideline, not under GLP conditions. The following results were obtained : 16h-EC10 = 13 mg/L and 16h-EC50 = 70 mg/L, both based on growth inhibition and nominal concentrations.
A read across study performed on aluminium trichloride is available :
This 3h static test was performed according to OECD 209, under GLP conditions, to evaluate the toxicity of aluminium trichloride on microorganisms of activated sludge.
The following results were obtained :
-EC10 (respiration rate) > 1000 mg/L (based on nominal concentrations) ; EC10 (respiration rate) > 200 mg/L (based on nominal concentrations of the aluminium element)
-EC50 (respiration rate) >1000 mg/L (based on nominal concentrations) ; EC50 (respiration rate) > 200 mg/L (based on nominal concentrations of the aluminium element).
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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