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EC number: 477-690-9 | CAS number: 874819-71-3
- 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 soil macroorganisms except arthropods
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to soil macroorganisms except arthropods: short-term
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2005-02-23 - 2005-04-19
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 207 (Earthworm, Acute Toxicity Tests)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on preparation and application of test substrate:
- An exactly weighed amount of of the test item was mixed with finely ground quartz sand, immediately prior to application. This stock mixture was diluted with quartz sand in a way that 10 g of the mixture contained the amount test item required for one test vessel to adjust the selcted concentration. Treated substrate was thoroughly mixed using a laboratory mixer.
Preparation of the test Substrate
The preparation of the test Substrate based on a wet weight of artificial soil/vessel of 750.6 g. Based on a water content of 35 %, the soil dry weight per vessel was 556 g artificial soil.
1. 546 g soil dry weight (556 g artificial soil - 1 0 g quartz sand) was prepared for each replicate of each test item concentration. 2. 194.6 g water was added to each 546 g soil dry weight, resulting in 740.6 g wet weight (at 35 % dry weight nominal water content). The soil was made with dried ingredients and was therefore at nominal 0 % moisture before mixing the components. 3. 10 g test item quartz sand mixture containing the required amount of the test item were added to each prepared amount of artificial soil, resulting in test Substrate concentrations of 100 and 1000 mg P 101/04/kg d.w., with final nominal moisture content 35 % dry weight. 4. The final water content was then checked to be 35 %. - Test organisms (species):
- Eisenia fetida
- Animal group:
- annelids
- Details on test organisms:
- Test organism: earthworm Eisenia fetida BOUCHE
Origin of the test organism:
originally purchased from “W. Neudorff GmbH KG“, An der Mühle 3, D-31860 Emmerthal
Breeding wider laboratory conditions
Breeding medium: mixture of horse manure, straw, peat (1:1:1); all ingredients were free from pesticide treatments
Breeding conditions: breeding cages (50 cm x 40 cm x 30 cm) constant diffuse light temperature: approximately 20 °C moist soil pH: approximately 7
Age of animals used in the test: adult worms (approximately 4 months old with clitcllum)
Time for acclimatisation to test conditions: approximately 24 hours
Weight of animals used in the test: 310 - 449 mg/worm - Study type:
- laboratory study
- Substrate type:
- artificial soil
- Limit test:
- no
- Total exposure duration:
- 14 d
- Test temperature:
- 18-21 °C
- pH:
- 6
- Moisture:
- 34.0- 34.3 %
- Details on test conditions:
- Test vessel: clear glass Container with clear glass lid (volume: 1 litrc)
Number of animals/ vessel (- replicate): 10
Number of replicate s/ treatment group: 4
Number of animals/ treatment group: 40 The test vessels were placed at random in the test room.
Artificial soil
Composition of the artificial soil:
10 % Sphagnum peat 20 % kaolinite clay 0.5 % calcium carbonate 69.5 % industrial quartz sand (more than 50 % of the particles between 0.05 mm and 0.2 mm) deionised water
Laboratory mixer: K 45 SS (KitchenAid Inc.; St. Joseph Michigan, USA) mixing time: 2 x 1 minute for each replicate rotations per minute: 240
Amount/test vessel: approximately 750 g wet weight corresponding to 556 g dry weight of artificial soil with approximately 35 % water content - Nominal and measured concentrations:
- 100, 1000 mg test item/kg soil dry weight
- Reference substance (positive control):
- yes
- Remarks:
- 2-chloroacetamide
- Key result
- Duration:
- 14 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 100 ng/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Key result
- Duration:
- 14 d
- Dose descriptor:
- LC50
- Effect conc.:
- > 1 000 ng/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Results with reference substance (positive control):
- To verify the sensitivity of the test System, the reference item 2-chloroacetamide was routinely tested at concentrations of 14.1, 18.3, 23.8, 31.0 and 40.4 mg a.i./kg d.w. In the most recent test with the reference item, dated 29.07.2004, the 14-day LC50 was calculated as 29.98 mg a.i./kg d.w. with 95 % confidence limits ranging from 28.85 to 31.16 mg a.i./kg d.w.
- Validity criteria fulfilled:
- yes
- Remarks:
- The validity criterion for the control group was accomplished: adult mortality: < 10 % (being 0 % after 14 days)
- Conclusions:
- In a 14-day toxicity study with P 101/04 on earthworm (Eisenia fetidd) the LC5Q was determined to be greater than 1000 mg P 101/04/kg soil dry weight, i.e. the highest concentration tested.
The NOEC was determined to be 100 mg P 101/04/kg soil dry weight. - Executive summary:
Effects of P 101/04 on survival and growth of the earthworm Eisenia fetida were determined at test concentrations of 100 and 1000 mg P 101/04/kg d.w. of artificial soil after an exposure period of 14 days. Three treatment groups including one quartz sand treated control group with four replicates each were tested.
At the beginning of the test, the fresh weight of the earthworms was in a ränge of 310 - 449 mg/earthworm. The physico-chemical parameters measured at the start and at the end of the test met the guideline requirements.
The maximum burrowing time was 5 minutes in the control group and in the P 101/04 treated groups.
The test item caused no mortality at the concentrations of 100 and 1000 mg P 101/04 /kg d.w. of artificial soil (table 3). No mortality (0 %) occurred in the control group.
No abnormal behaviour or toxic Symptoms of the worms were observed in any treatment or control group during the test.
Earthworm mean fresh weights were reduced by 8.8 % in the control and 11.2 % and 19.0 % for the 100 and 1000 mg P 101/04/kg d.w. treatment groups, respectively (table 2). The weight reduction was statistically significant (p < 0.05) relative to the control at the test item concentration of 1000 mg P 101/04/kg d.w.
The LC50 could not be calculated but it can be concluded that the LC50 is greater than 1000 mg P 101/04/kg soil dry weight.
Based on the Statistical evaluation of these results, the no-observed-effect-concentration (NOEC) was determined to be 100 mg P 101/04/kg soil dry weight.
Reference
Treatment group |
mg P 101/04/kg d.w. |
||||
|
Control |
100 | |
1000 |
||
Replicate |
Initial fresh weight / worm [mg]। |
mean |
jer replicate) |
||
1 2 3 4 |
360.9 368.3 382.0 384.5 |
363.2 367.4 377.6 392.5 |
369.4 371.0 372.6 389.8 |
||
mean |
373.9 |
375.2 |
375.7 |
||
SD |
11.2 |
13.0 |
9.5 |
||
cv % |
3.0 |
3.5 |
2.5 |
||
|
Fresh weight / worm [mg] after 14 days (mean per replicate) |
||||
1 2 3 4 |
328.6 344.4 338.1 352.7 |
325.9 338.2 332.0 336.1 |
292.4 310.3 307.6 307.3 |
||
mean |
341.0 |
333.1 |
304.4 |
||
SD |
10.2 |
5.4 |
8.1 |
||
cv % |
3.0 |
1.6 |
2.7 |
||
|
Biomass change (change in fresh weight after 14 da weight) weight / worm [mg] (mean per re] |
ys relative to initial fresh □licate) |
|||
1 2 3 4 |
32.3 23.9 43.9 31.8 |
37.3 29.2 45.6 56.4 |
77.0 60.7 65.0 82.5 |
||
mean |
33.0 |
42.1 |
71.3* |
||
SD |
8.2 |
11.6 |
10.2 |
||
|
Biomass change (change |
in fresh weight after 14 days relativ weight) [%] mean per replicate |
e to initial fresh |
||
1 2 3 4 |
8.9 6.5 11.5 |
||||
384.5 |
363.2 367.4 377.6 392.5 |
369.4 371.0 372.6 389.8 |
|||
mean |
373.9 |
375.2 |
375.7 |
||
SD |
11.2 |
13.0 |
9.5 |
||
cv % |
3.0 |
3.5 |
2.5 |
||
|
Fresh weight / worm [mg] after 14 days (mean per replicate) |
||||
1 2 3 4 |
328.6 344.4 338.1 352.7 |
325.9 338.2 332.0 336.1 |
292.4 310.3 307.6 307.3 |
||
mean |
341.0 |
333.1 |
304.4 |
||
SD |
10.2 |
5.4 |
8.1 |
||
cv % |
3.0 |
1.6 |
2.7 |
||
|
Biomass change (change in fresh weight after 14 da weight) weight / worm [mg] (mean per re] |
ys relative to initial fresh □licate) |
|||
1 2 3 4 |
32.3 23.9 43.9 31.8 |
37.3 29.2 45.6 56.4 |
77.0 60.7 65.0 82.5 |
||
mean |
33.0 |
42.1 |
71.3* |
||
SD |
8.2 |
11.6 |
10.2 |
||
|
Biomass change (change |
in fresh weight after 14 days relativ weight) [%] mean per replicate |
e to initial fresh |
||
1 2 3 4 |
8.9 6.5 11.5 |
Treatment group |
mg P 101/04/kg d.w. |
||
|
Control |
100 |
1000 |
Replicate |
Number of surviving adult worms per replicate (14 davs after test initiation) |
||
1 |
10 |
10 |
10 |
2 |
10 |
10 |
10 |
3 |
10 |
10 |
10 |
4 |
10 |
10 |
10 |
mean |
10.0 |
10.0 |
10.0 |
SD |
0.0 |
0.0 |
0.0 |
cv % |
0.0 |
0.0 |
0.0 |
|
Mortality (%) |
||
mean |
0.0 |
0.0 |
0.0 |
Description of key information
In a 14-day toxicity study with P 101/04 on earthworm (Eisenia fetidd) the LC5Q was determined to be greater than 1000 mg P 101/04/kg soil dry weight, i.e. the highest concentration tested.
The NOEC was determined to be 100 mg P 101/04/kg soil dry weight.
Key value for chemical safety assessment
- Short-term EC50 or LC50 for soil macroorganisms:
- 1 000 mg/kg soil dw
Additional information
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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