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EC number: 266-096-3 | CAS number: 66063-05-6
- 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
- Remarks:
- Determination of effects on reproduction
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2001-06-21 to 2001-09-07
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- ISO 11268-2 (Effects of Pollutants on Earthworms. 2. Determination of Effects on Reproduction)
- Version / remarks:
- First edition 1998-07-01
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: BBA, Guidelines for the Testing of Plant Protection Products Within Registration, Part VI, 2 - 2
- Version / remarks:
- January 1994
- Deviations:
- yes
- Remarks:
- since treated potatoes had been tested in this study, larger test containers with the 30-fold amount of artificial soil had been used and the peat content in the soil was 5%.
- GLP compliance:
- yes
- Specific details on test material used for the study:
- The test material is in a red powder form.
- Analytical monitoring:
- no
- Details on preparation and application of test substrate:
- The test soil consists of 74% fine quartz sand (83% of the sand has a particle size of 0.05 - 0.2 mm), 5% dried, finely ground peat (sphagnum peat; pH 2 - 4), 20% kaolin (kaolinite content of about 36%, pH value ca 7, "Kaolin W", from Erbsloh / Geisenheim) and around 1% calcium carbonate (pure) to adjust the pH value to 6 ± 0.5 .
The artificial soil was first of all mixed dry from these components and the food in a plough-share mixer, and moistened with the volume of water required for the final artificial soil. Test containers were plastic containers of 56 cm length, 36 cm width and 22 cm height (inner size). The resulting artificial soil surface area was 0.2 m2. Each test container was filled with 15 kg dry weight soil (= 18.673 kg wet weight). The potatoes were placed in a depth of 5 cm below the surface. Two replicates were used per dosage. Each container was covered with a transparent plastic sheet to prevent evaporation and to allow lighting. They were labeled (study number, rate, series number). The artificial soil was acclimatized for 1 day under test conditions before earthworms were placed on the test soil. All test containers were transferred into a climatic chamber after application.
The moisture content of the peat and the test soil as well as the maximum water capacity of the test soil were determined by drying the soil at high temperatures up to constant weight. The pH was determined with an electrode (WTW pH- Meter 330) The dressing of the potatoes was conducted with an application rate of 25 mg a.s./100 kg potatoes. For the study potatoes with a weight of aproximatly 40 g (corresponding to 2000 kg potatoes/ha) were chosen and treated with 82.6 mg formulation. The potatoes had been randomly selected for the test containers.
One day prior to the start of the study, earthworms were removed from the breeding substrate and kept in the test soil (without test substance) under the test conditions for acclimatization. They were removed from this artificial soil and transferred to test boxes two hours before the dressed potatoes were added. Thirty earthworms were placed in each test container. Earthworms were individually weighed at the start of the study. They were put into the test containers in a randomized procedure. At the start of the study, they had a mean weight of 0.30 g. - Test organisms (species):
- Eisenia fetida
- Animal group:
- annelids
- Details on test organisms:
- TEST ORGANISM
- Common name: Earthworm (Eisenia fetida)
- Age at test initiation: To obtain earthworms for the study, adult earthworms of breeding boxes were transferred to freshly prepared culture substrate for reproduction. The earthworms were removed after 4 weeks. After further 10 months, adult earthworms which developed from cocoons, were selected for the study.
- Weight at test initiation: At the start of the study, they had a mean weight of 0.30 g.
ACCLIMATION
One day prior to the start of the study, earthworms were removed from the breeding substrate and kept in the test soil (without test substance) under the test conditions for acclimatization. - Study type:
- laboratory study
- Substrate type:
- artificial soil
- Limit test:
- no
- Total exposure duration:
- 28 d
- Remarks:
- After 28 days the number of surviving animals and their weight alteration was determined. They were then removed from the artificial soil. After further 28 days, the number of offsprings was determined.
- Test temperature:
- 20 ± 2°C
- pH:
- 6 ± 0.5 (Test start: 6.24 - 6.26; test termination: 6.25 - 6.33)
- Moisture:
- Test start: 19.38 - 19.88%; test termination: 20.9 - 23.8%
- Details on test conditions:
- TEST SYSTEM
- Test container (material, size): Test containers were plastic containers of 56 cm length, 36 cm width and 22 cm height (inner size).
- Amount of soil or substrate: Each test container was filled with 15 kg dry weight soil (= 18.673 kg wet weight).
- No. of organisms per container (treatment): 30 earthworms per container.
- No. of replicates per treatment group: 2 replicates
- No. of replicates per control: 2 replicates
SOURCE AND PROPERTIES OF SUBSTRATE (if soil)
- Composition (if artificial substrate): The test soil consists of 74% fine quartz sand (83% of the sand has a particle size of 0.05 - 0.2 mm), 5% dried, finely ground peat (sphagnum peat; pH 2 - 4), 20% kaolin (kaolinite content of about 36%, pH value ca 7, "Kaolin W", from Erbsloh / Geisenheim) and around 1% calcium carbonate (pure) to adjust the pH value to 6 ± 0.5.
- Maximum water holding capacity (in % dry weigth): 55.03 – 58.32%
OTHER TEST CONDITIONS
- Photoperiod: 16:8 hours light-dark cycle.
- Light intensity: 400 - 800 lux - Nominal and measured concentrations:
- Nominal concentrations of 2000, 4000 and 10000 kg potatoes/ha.
- Reference substance (positive control):
- yes
- Remarks:
- Derosal (active ingredient: 36 % Carbendazim)
- Duration:
- 28 d
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 10 000 other: kg dressed potato/ha
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Key result
- Duration:
- 56 d
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 10 000 other: kg dressed potato/ha
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- reproduction
- Key result
- Duration:
- 56 d
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 3.3 other: mg a.s./kg soil ww
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- reproduction
- Remarks on result:
- other: The endpoint for a.s. was given in the DAR 2009.
- Details on results:
- The results of the pH determinations of the artificial soil and its moisture content are summarized in Table 1. Tables 2 and 3 summarize the amount of food added and portion ingested by earthworms during the study.
The mortalities (%) and weight changes (%) of the adult worms after 28 days are summarized in Table 4. The individual values of the study are given in Table 5. Table 6 lists the weight of individual earthworms at the start of the study. Abnormalities, e.g. changes in behavior, were not observed. The number of juvenile earthworms at the end of the study after 56 days are summarized in Table 7. In this table, the total numbers of juvenile earthworms per test container are shown which had been calculated according to the individual results of the evaluated soil samples given in table 8 (6 samples per test container, corresponding to 6 x 0.5 kg dry weight soil, which is 20% of the total soil of a test container).
The mortality rate in the control was below 10% which can be regarded as the limit for natural mortality according to test guidelines. Reproduction was greater than 3 juveniles per adult indicating acceptable reproductive output. Soil moisture and pH were maintained in acceptable ranges through the test. These data along with results from the positive control study indicate that this is a valid test.
Significant mortality or a significant body weight reduction of adult earthworms was not observed at any rate. Also, the number of offspring was not significantly reduced at any rate.
See "Attachments" in "Overall remarks, attachments" for the tables. - Results with reference substance (positive control):
- Under the same conditions, a study was carried out with the reference substance Derosal (active ingredient: 36% Carbendazim. The following dosages had been tested by application on the soil surface at the start of the study: 0.10, 0.25 and 0.50 kg/ha. Mortality of adult earthworms as compared to control organisms was not observed at any dosage. The body weight reduction was significant at 0.25 and 0.5 kg/ha. Only the highest dosage of 0.5 kg/ha reduced the numbers of juvenile earthworms by 46%. The no-observed-effect-level (NOEL) was 0.10 kg/ha (= 0.036 kg a.s./ha) and the lowest-observed-effect-level (LOEL), 0.25 kg/ha (= 0.090 kg a. s./ha).
- Validity criteria fulfilled:
- yes
- Conclusions:
- Mortality or a significant body weight reduction of adult earthworms was not observed in earthworms exposed in an artificial soil to treated potatoes up to 10000 kg potatoes/ha. Also, the number of offspring was not reduced at any rate.
- Executive summary:
This study was conducted in order to determine the influence of Pencycuron DS 12.5 on the reproduction of adult earthworms (Eisenia fetida) in an artificial soil with 5% peat content. The test was conducted at the following nominal concentrations of the test substance: 0 (control), 2000, 4000 and 10000 kg potatoes/ha. After 28 days the number of surviving animals and their weight alteration was determined. They were then removed from the artificial soil. After further 28 days, the number of offsprings was determined. No mortality was observed in the control or any of the treatments. Also, significant body weight reduction of adult earthworms was not observed at any rate. Furthermore, the number of offspring was not reduced at any rate. The NOEC was 10000 kg dressed potatoes/ha; the potatoes were dressed with 25 g a. s./100 kg potatoes.
Reference
Description of key information
A chronic earthworm study was conducted to determine the effect of Pencycuron on reproduction of the earthworm Eisenia fetida in a laboratory test. Reproduction was determined after 56 day, resulting in the NOEC of 3.3 mg/kg soil dw.
Test species | Result | Assessment | Reference |
Eisenia fetida | 14-d LC50 >10000 mg a.s./kg soil dw based on mortality | Supporting study | Heimbach (1999) |
Eisenia fetida | 56-d NOEC ≥3.3 mg a.s./kg soil dw based on reproduction | Key study | Meisner (2001) |
Eisenia fetida | 56-d NOEC = 100 mg a.s./kg soil dw based on reproduction | Supporting study | Heimbach (1999) |
Key value for chemical safety assessment
- Short-term EC50 or LC50 for soil macroorganisms:
- 10 000 mg/kg soil dw
- Long-term EC10, LC10 or NOEC for soil macroorganisms:
- 3.3 mg/kg soil dw
Additional information
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