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Diss Factsheets
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EC number: 947-917-0 | 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
Toxicity to microorganisms
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to microorganisms, other
- Remarks:
- Biodegradation in water: screening test, toxicity control is used to derive effect concentration
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- other: OECD Guideline 301 D (Ready Biodegradability: Closed Bottle Test)
- GLP compliance:
- yes (incl. QA statement)
- Vehicle:
- no
- Test organisms (species):
- activated sludge of a predominantly domestic sewage
- Details on inoculum:
- - Source of inoculum/activated sludge (e.g. location, sampling depth, contamination history, procedure): secondary effluent are withdrawn on November 29th, 2017 from the sewage treatment plant
Ruhrverband Kläranlage, Sunthelle 6, 57392 Schmallenberg, Germany, which is mainly fed with municipal wastewater
The samples were kept aerobic during transport to the laboratory. The samples were allowed to settle for 1 hour and filtered through a coarse filter paper. The inoculum was kept aerobic until required.
The concentration used in the test was 1 mL/L. - Test type:
- static
- Water media type:
- freshwater
- Total exposure duration:
- 28 d
- Test temperature:
- 20°C
- pH:
- 7.4 ± 0.2
- Nominal and measured concentrations:
- 5 mg/L
- Details on test conditions:
- TEST SYSTEM
- Culturing apparatus: 300 mL test vessels
- Number of culture flasks/concentration: 16
- Method used to create aerobic conditions: strongly aerated for 20 minutes and allowed to stand for 20 h at test temperature
- Measuring equipment: O2 electrode
SAMPLING
- Sampling frequency: test start and at day 2, 5, 7, 9, 14, 21, and 28
CONTROL AND BLANK SYSTEM
- Inoculum blank: The blank control consisted of inoculated mineral medium only, 16 vessels
- Abiotic sterile control: no
- Toxicity control: A toxicity control containing test item at 5 mg per litre and reference item at 2 mg per litre mineral test medium was applied, 8 vessels
- Procedural control: 16 vessels containing reference item (5 mg/L) and inoculum - Reference substance (positive control):
- no
- Duration:
- 14 d
- Dose descriptor:
- IC10
- Effect conc.:
- 5 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- inhibition of total respiration
- Details on results:
- The biodegradation of the test item after 28 days of incubation in the static test was found to be 0 % in the assays with 2 mg/L and 5 mg/L. Thus, no biodegradation within a 10-day-window could be obtained.
The biodegradation of the item mixture in the toxicity control was found to be 28 % after 14 days of incubation. Thus, the demanded threshold value of 25 % is exceeded and the test item can be identified as non-toxic in a ready biodegradability test. - Conclusions:
- The threshold value of 25 % is exceeded and the test item can be identified as non-toxic in a ready biodegradability test.
- Executive summary:
The biodegradation of Reaction product of lauryl-PDA/lauryl-DETA with chloroacetic acid was investigated over a 28-day period in a Closed Bottle Test according to OECD guideline 301 D and EU method C.4-E. The test medium was inoculated with microorganisms from a digester of a sewage treatment plant mainly fed with municipal wastewater.
The test solutions were incubated in closed flasks at 20 °C ± 1 °C for 28 days. The rate of degradation was monitored by measuring the decrease of oxygen in the medium over a 28-d period. The amount of oxygen taken up by the microbial population during biodegradation of the test item at a concentration of 2 mg/L (ThOD = 1.44 mg/L) and 5 mg/L (ThOD = 3.60 mg/L), respectively, corrected for uptake by the blank inoculum run in parallel, was expressed as a percentage of the ThOD (theoretical oxygen demand). In order to check the procedure, sodium benzoate was used as a degradable reference item at a concentration of 2 mg/L, along with a toxicity control at 5 mg/Ltest itemand 2 mg/L sodium benzoate.
The biodegradation of Reaction product of lauryl-PDA/lauryl-DETA with chloroacetic acid in the static test was found to be 0 % for a concentration of 2 mg test item per liter and 5 mg test item per liter after 28 days.Thus, no biodegradation within a 10-day-window could be obtained.
The degradation of the reference substance sodium benzoate had reached 72 % within the first 14 days.
The difference of extremes of replicate values of the removal of the test item at the end of the test is less than 20%. Therefore, the test can be considered as valid.
No inhibitory effects of the test item were observed (more than 25 % degradation occurred within 14 days) in the toxicity control.
Therefore, Reaction product of lauryl-PDA/lauryl-DETA with chloroacetic acid must be considered as not readily biodegradable under the chosen test conditions.
Reference
Description of key information
14 d IC10 >/= 5 mg/L (OECD TG 301D, RL1, GLP)
Key value for chemical safety assessment
- EC10 or NOEC for microorganisms:
- 5 mg/L
Additional information
The biodegradation of Reaction product of lauryl-PDA/lauryl-DETA with chloroacetic acid was investigated over a 28-day period in a Closed Bottle Test according to OECD guideline 301 D and EU method C.4-E. The test medium was inoculated with microorganisms from a digester of a sewage treatment plant mainly fed with municipal wastewater.
The test solutions were incubated in closed flasks at 20 °C ± 1 °C for 28 days. The rate of degradation was monitored by measuring the decrease of oxygen in the medium over a 28-d period. The amount of oxygen taken up by the microbial population during biodegradation of the test item at a concentration of 2 mg/L (ThOD = 1.44 mg/L) and 5 mg/L (ThOD = 3.60 mg/L), respectively, corrected for uptake by the blank inoculum run in parallel, was expressed as a percentage of the ThOD (theoretical oxygen demand). In order to check the procedure, sodium benzoate was used as a degradable reference item at a concentration of 2 mg/L, along with a toxicity control at 5 mg/Ltest itemand 2 mg/L sodium benzoate.
The biodegradation of Reaction product of lauryl-PDA/lauryl-DETA with chloroacetic acid in the static test was found to be 0 % for a concentration of 2 mg test item per liter and 5 mg test item per liter after 28 days.Thus, no biodegradation within a 10-day-window could be obtained.
The degradation of the reference substance sodium benzoate had reached 72 % within the first 14 days.
The difference of extremes of replicate values of the removal of the test item at the end of the test is less than 20%. Therefore, the test can be considered as valid.
No inhibitory effects of the test item were observed (more than 25 % degradation occurred within 14 days) in the toxicity control.
Therefore, Reaction product of lauryl-PDA/lauryl-DETA with chloroacetic acid must be considered as not readily biodegradable under the chosen test conditions.
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