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EC number: 203-965-8 | CAS number: 112-38-9
- 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 macroorganisms except arthropods
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to soil macroorganisms except arthropods: long-term
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Q4 2015
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 222 (Earthworm Reproduction Test (Eisenia fetida/Eisenia andrei))
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
Not applicable. - Analytical monitoring:
- no
- Details on sampling:
- Analytical analysis not required by OECD 222.
- Vehicle:
- no
- Details on preparation and application of test substrate:
- ARTIFICIAL SOIL COMPOSITION
- Sphagnum Peat: 10 % of dry matter of artificial soil. The peat was air dried before use.
- Kaolin Clay: 20 % of dry matter of artificial soil. Bolus alba (white clay), pharmaceutical quality:
- Quartz Sand: 70 % of dry matter of artificial soil. Fine quartz sand (round grains) was used.
- Calcium Carbonate CaCO3: Analytical grade, used for pH adjustment
Preparation of Artificial Soil: the dry constituents of the soil were mixed thoroughly in a well-ventilated area.
The pH of the final mixture was measured as 6.1. A small part of this mixture was used for the 24 hours acclimatisation of the animals used in this test. For this it was adjusted with demineralised water to a calculated water content of 50 % of the maximum water holding capacity calculated in relation to dry matter.
For the test the artificial soil described above was divided into 10 portions of an appropriate amount (4400 g for the blank control resp. 2200 g for each treatment dry weight). The required amount of test item was given to each portion using demineralised water which was used for adjustment of the artificial soil to a calculated water content of 50% of the maximum water holding capacity calculated in relation to dry matter. Afterwards, it was mixed and 640.5 g wet weight of each portion was introduced into a 1 L glass preserving jar. - Test organisms (species):
- Eisenia andrei
- Animal group:
- annelids
- Details on test organisms:
- TEST ORGANISM
- Common name: earthworm (Eisenia andrei)
- Source: Bred at LAUS GmBH facilities
- Age at test initiation (mean and range, SD): at least 2 months
- Weight at test initiation (mean and range, SD): mean weight was 345 mg (281 - 587 min - max)
ACCLIMATION
- Acclimation period: 24 hours
- Acclimation conditions (same as test or not): Yes
- Health during acclimation (any mortality observed): Not reported. - Study type:
- laboratory study
- Substrate type:
- artificial soil
- Limit test:
- no
- Total exposure duration:
- 56 d
- Post exposure observation period:
- None.
- Test temperature:
- 18.2 - 22°C
- pH:
- 5.9-6.0
- Moisture:
- 53 - 64% of Maximum Water Holding Capacity (MWHC = 60% of dry soil), (min-max)
- Details on test conditions:
- TEST SYSTEM
- Test container (material, size): 1 L glass jar
- Amount of soil or substrate: 650 g of soil wet weight per jar
- No. of organisms per container (treatment): 10
- No. of replicates per treatment group: 4
- No. of replicates per control: 8
OTHER TEST CONDITIONS
- Photoperiod: 16L:8D
- Light intensity: 500 lux
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Adult survival after 28 days
- Adult growth after 28 days
- Juvenile production after 56 days (28 days after adult removal)
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 3.2
- Test concentrations: 0.1 ; 0.32 ; 1 ; 3.2 ; 10 ; 32 ; 100 ; 320 ; 1000 - Nominal and measured concentrations:
- 0.1 / 0.32 / 1.0 / 3.2 / 10 / 32 / 100 / 320 / 1000 mg/kg (dry matter). Concentrations not measured (not required by OECD 222 guideline).
- Reference substance (positive control):
- yes
- Remarks:
- Benomyl
- Duration:
- 28 d
- Dose descriptor:
- NOEC
- Effect conc.:
- > 1 000 mg/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- mortality
- Remarks on result:
- other: No dead worm in any treatment
- Duration:
- 28 d
- Dose descriptor:
- NOEC
- Effect conc.:
- > 1 000 mg/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- growth
- Key result
- Duration:
- 56 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 3.2 mg/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- reproduction
- Details on results:
- - Mortality at end of exposure period: None in any treatement
- Total mass of adults at beginning of test:
- Changes in body weigth of live adults (% of initial weight) at end of exposure period: -8 - 4% growth across treatements (min - max)
- No. of offspring produced: 98 - 142 juveniles across treatments (min - max) - Results with reference substance (positive control):
- The 56d-EC50 of Benomyl (CAS-Nr. 17804-35-2) was tested in a current reference test. The value was determined as 1.9 mg/kg dry soil, lying within the required range of OECD Guideline 222 of 1 – 5 mg/kg.
- Reported statistics and error estimates:
- The estimation of the biological data was accomplished using the software ToxRat® Professional (version 3.2) using the analysis set by default by Toxrat producers. Data were checked for normal distribution of residues (Shapiro-Wilk) and variance homogeneity among treatments (Levene). Both tests passed for all endpoints. For mean comparison, Williams multiple sequential t-test procedure was used.
- Validity criteria fulfilled:
- yes
- Conclusions:
- Eisenia andrei adults were exposed to 9 graded concentrations of undecylenic acid for 28 days and cocoon/juveniles for another 28 day period. Adult survival and growth and number of juvenile produced per treatment were examined. No adult mortality occur. No significant diffence nor trend were observed for growth. Regarding juvenile production, a NOEC of 3.2 mg/kg soil dry wet was determined, although non-monotonic dose-response was observed.
- Executive summary:
The study was performed using 9 concentrations ranging from 0.1 to 1000 mg/kg dry soil (4 replicates) and a control (8 replicates), following OECD 222 guideline protocol. In each replicate, 10 adult animals were exposed to the test item for 28 days in an artificial soil (except control group). After 28 days, the living adult animals were counted and weighted, and 28 days later, the number of juveniles produced was determined.
Non-monotonic statistical significant inhibition of reproduction (juvenile production) were observed compared to the control. None of the adult animals were dead in any treatment or control after the first 28 days. Adult growth was not significantly different between treatments. A NOEC of 3.2 mg/kg soil dry weight was determined.
Reference
See attached files
Description of key information
One reliable study assessing the long-term toxicity of the test item to the earthworm Eisenia andrei (OECD 222) is available. The study was performed using 9 concentrations ranging from 0.1 to 1000 mg/kg dry soil. The highest concentrations showed statistical significant inhibition of reproduction (juvenile production) compared to the control. None of the adult animals were dead in any treatment or control after the first 28 days. Growth was not significantly different between treatments. A NOEC of 3.2 mg/kg soil dry weight was determined.
Key value for chemical safety assessment
- Long-term EC10, LC10 or NOEC for soil macroorganisms:
- 3.2 mg/kg soil dw
Additional information
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