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Ecotoxicological information

Toxicity to soil macroorganisms except arthropods

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Reference
Endpoint:
toxicity to soil macroorganisms except arthropods: short-term
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:
OECD Guideline 207 (Earthworm, Acute Toxicity Tests)
Version / remarks:
1984
GLP compliance:
yes (incl. QA statement)
Vehicle:
yes
Remarks:
Acetone
Details on preparation and application of test substrate:
The respective test item amount was weighed out for each test item concentration and dissolved in acetone (2.5 mL per replicate). The appropriate amount of spiking solution was mixed thoroughly with quartz sand (10 g per replicate). After complete evaporation of the solvent, the spiked quartz sand was added to the artificial soil.
Test organisms (species):
Eisenia fetida
Animal group:
annelids
Details on test organisms:
TEST ORGANISM
- Common name: earthworm
- Source: Breeding stock culture maintained at the test facility
- Age at test initiation (mean and range, SD): aged 2- 12 month, with clitellum
- Weight at test initiation (mean and range, SD): 0.30 - 0.64 g/worm

ACCLIMATION
- Acclimation period: 2 days
- Acclimation conditions: same as test
Study type:
laboratory study
Substrate type:
artificial soil
Limit test:
no
Total exposure duration:
2 wk
Test temperature:
18-22 °C
pH:
Day 0: 5.76 - 5.84
Day 14: 5.74 - 5.84
Moisture:
Day 0: 27.7 - 28.3 % of DW
Day 14: 26.2 - 27.3 % of DW
Details on test conditions:
TEST SYSTEM
- Test container (material, size): Glass vessels, volume 1.5 L
- Amount of soil or substrate: 555 g soil dw
- No. of organisms per container (treatment): 10
- No. of replicates per treatment group: 4
- No. of replicates per control: 4
- No. of replicates per vehicle control: 4

OTHER TEST CONDITIONS
- Photoperiod: 24 h
- Light intensity: 595 lx +- 108 lx

EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : Mortality, behaviour and pathological symtoms after 7 and 14 days

VEHICLE CONTROL PERFORMED: yes

TEST CONCENTRATIONS
- Spacing factor for test concentrations: 2
- Justification for using less concentrations than requested by guideline:
- Range finding study: yes
- Test concentrations: 1, 10, 100, 1000 mg/kg soil dw
- Results used to determine the conditions for the definitive study: 100% mortality in the 1000 mg/kg soil dw conc. and 0% Mortalöity in the 100 mg/kg soil dw conc.
Nominal and measured concentrations:
control, solvent control, 50, 100, 200, 400, 800 mg/kg soil dw
Reference substance (positive control):
yes
Remarks:
2-Chloroacetamide
Key result
Duration:
2 wk
Dose descriptor:
LC50
Effect conc.:
383 mg/kg soil dw
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mortality
Duration:
2 wk
Dose descriptor:
NOEC
Effect conc.:
200 mg/kg soil dw
95% CI:
383 - 432
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
other: Motality, behaviour, pathological symtoms, biomass
Details on results:
- Mortality at end of exposure period: No mortality was observed in the controls and the test item concentrations 50 to 200 mg/kg SDW after 14 days of exposure. However, at the test item concentrations 400 and 800 mg/kg SDW a
statistically significant mortality of 57.5 % and 100 % occurred, respectively.
- Changes in body weight of live adults (% of initial weight) at end of exposure period: s. table 2
- Behavioural abnormalities and pahological symtoms: No pathological symptoms or changes in earthworm behaviour was observed in the controls and the test item concentrations 50 to 200 mg/kg SDW after 14 days of exposure. At the test item concentration 400 mg/kg SDW some earthworms showed spontaneous segmentation and
separation after 7 and 14 days of exposure
Results with reference substance (positive control):
LC50 (2 wk) = 44.5 mg/kg soil dw
Reported statistics and error estimates:
- Mortality / Biomass: The arithmetic mean and NOEC were determined.- Dunnett’s Multiple Comparison Test

- LC50-values and confidence ranges for mortality: The LC50-value in terms of mortality was determined by Sigmoidal dose-response (variable slope).

Table 1: Earthworm Mortality in [%] after 7 and 14 Days of Exposure




































































































































 Mortality [%]Statistically
Test item concentrationDay 7Day 14significant vs.
[mg/kg SDW]1234MV1234MVPooled Control*
Control0000000000-
Solvent Control0000000000-
Pooled Control-0-0-
500000000000No
1000000000000No
2000000000000No
4004020706047.54040906057.5Yes
800100100100100100#Yes

 


Table 2: Mean Live Weight and Mean Loss of Body Weight




















































































 Mean live weight 
Test itemTest startTest endInhibitionStatistically 
 concentration  MV ± SDMV ± SD[%]significant vs. 
[mg/kg SDW][g/worm][g/worm]  Pooled Control
Control0.48 ± 0.050.41 ± 0.0415
Solvent control0.48 ± 0.040.42 ± 0.0513-
Pooled Control0.48 ± 0.040.42 ± 0.0514-
500.48 ± 0.060.42 ± 0.0513No
1000.48 ± 0.060.40 ± 0.0517No
2000.48 ± 0.050.40 ± 0.0517No
4000.48 ± 0.060.38 ± 0.0821Yes
8000.48 ± 0.05#
Validity criteria fulfilled:
yes
Conclusions:
The LC50 (2 wk) of the test item to earthworm (Eisenia fetida) was determined to be = 383 mg/kg soil dry weight.
Executive summary:

The acute effects of the test item on the earthworm Eisenia fetida were determined according to OECD Guideline 207 according to GLP. The study was conducted under static conditions for 14 days with the test item concentrations 50 – 100 – 200 – 400 – 800 mg/kg SDW mixed into artificial soil containing 10 % peat. Artificial soil without test item was used as control and artificial soil without test item but treated with the solvent was used as solvent control. 40 test organisms divided into four replicates, were tested per test item concentration, control and solvent control. No statistically significant differences concerning mortality and biomass after two weeks of exposure in soil were observed between the control and the solvent control.  After 14 days, the EC50 of the test item to earthworm (Eisenia fetida) was determined to be 383 mg/kg soil dry weight.

Description of key information

Based on results of an OECD 207 compliant study with the test item an EC50 of 383 mg/kg soil dw was determined as key value for the risk assessment.

Key value for chemical safety assessment

Short-term EC50 or LC50 for soil macroorganisms:
383 mg/kg soil dw

Additional information

The acute effects of the test item on the earthworm Eisenia fetida were determined according to OECD Guideline 207 according to GLP. The study was conducted under static conditions for 14 days with the test item concentrations 50 – 100 – 200 – 400 – 800 mg/kg SDW mixed into artificial soil containing 10 % peat. Artificial soil without test item was used as control and artificial soil without test item but treated with the solvent was used as solvent control. 40 test organisms divided into four replicates, were tested per test item concentration, control and solvent control. No statistically significant differences concerning mortality and biomass after two weeks of exposure in soil were observed between the control and the solvent control.  After 14 days, the EC50 of the test item to earthworm (Eisenia fetida) was determined to be 383 mg/kg soil dry weight.