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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
Study period:
November 24 - December 10, 2011
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
guideline study without detailed documentation
Qualifier:
according to guideline
Guideline:
OECD Guideline 207 (Earthworm, Acute Toxicity Tests)
Version / remarks:
1984
GLP compliance:
yes
Specific details on test material used for the study:
SOURCE OF TEST MATERIAL
- Source and lot/batch No.of test material: 20031/11
- Expiration date of the lot/batch: July 31, 2012
- Purity: 99.5 %
- Appearance: dark grey powder
Analytical monitoring:
no
Details on sampling:
not applicable
Vehicle:
no
Details on preparation and application of test substrate:
- Method of application to filter paper (if used): /
- Method of mixing into soil (if used): blended in a laboratory mixer
- Method of application to soil surface (if used): /
- Controls: yes (blank control)
- Chemical name of vehicle (organic solvent, emulsifier or dispersant): /
- Concentration of vehicle in test medium (stock solution and final test solution): /
- Evaporation of vehicle before use: /
Test organisms (species):
Eisenia fetida
Animal group:
annelids
Details on test organisms:
TEST ORGANISM
- Common name: Earthworm
- Source: Chenggong Earthworm Raising Farm, Dongli District, Tianjing, China
- Age at test initiation: adult (more than two months old with clitellum)
- Weight at test initiation: 320 - 574 mg; treatment groups: 426.8 ± 74.5 mg; control groups: 417.3 ± 69.6 mg

ACCLIMATION: 24h prior to testing
Study type:
laboratory study
Substrate type:
artificial soil
Limit test:
yes
Total exposure duration:
14 d
Test temperature:
18.56 - 19.74 °C
pH:
6.49
Moisture:
35 %
(Moisture content was detennined by drying a small sample at 105°C and re-weighing. Distilled water were added to give an overall moisture content of about 35 percent of the dry weight, and the medium were thoroughly mixed.)
Details on test conditions:
TEST SYSTEM
- Test container (material, size): height 19cm, length: 12 cm, width: 9 cm
- Amount of soil or substrate: 750 g
- 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: not applicable

SOURCE AND PROPERTIES OF SUBSTRATE (if soil)
- Composition (if artificial substrate): Sphagnum peat moss 10%; Kaolin clay 20%; Quartz sand 68%; Calcium carbonate 2%
- Pretreatment of soil: /
- Storage (condition, duration): test medium was freshly prepared on test day 0
- Stability and homogeneity of test material in the medium: no data

OTHER TEST CONDITIONS
- Photoperiod: continous lighting
- Light intensity: 675.5 to 683.3 Lux

EFFECT PARAMETERS MEASURED (with observation intervals if applicable): behaviour, pathological symptoms, mortality

VEHICLE CONTROL PERFORMED: not applicable

TEST CONCENTRATIONS
- Spacing factor for test concentrations: not appplicable, Limit test
- Justification for using less concentrations than requested by guideline: /
- Range finding study: yes
- Test concentrations: 1000 mg/kg soil dry weight
- Results used to determine the conditions for the definitive study: not reported
Nominal and measured concentrations:
1000 mg/kg soil dry weight (nominal)
Reference substance (positive control):
no
Key result
Duration:
14 d
Dose descriptor:
LC0
Effect conc.:
1 000 mg/kg soil dw
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mortality
Duration:
14 d
Dose descriptor:
LC50
Effect conc.:
> 1 000 mg/kg soil dw
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mortality
Details on results:
- Mortality at end of exposure period: 0 % in control and treatment groups
- Changes in body weight of live adults (% of initial weight) at end of exposure period: treatment group: ca. -5.1 % ; control group: ca. -5.5 %
- Morphological abnormalities: none
- Behavioural abnormalities: none
- Other biological observations: none
Results with reference substance (positive control):
Not applicable
Reported statistics and error estimates:
Because the definitive test was a limit test, it was not necessary to calculate the LC50.
Validity criteria fulfilled:
yes
Remarks:
After the test, no death or symptoms in the control groups were noted (criterion is below 10%), the test is valid.
Conclusions:
As neither mortality nor clinical signs were observed after 14 d exposure of earthworms (Eisenia foetida) to ZrC in artificial soil, it can be concluded that ZrC is not toxic to earthworms.
Executive summary:

In a 14 day acute toxicity study, earthworms (Eisenia foetida) were exposed to nominal ZrC concentrations of 0 (control) and 1000 mg/kg dry weight of artificial soil.  The experiment was carried out in accordance with OECD Guideline 207.  The 14 day LC50was > 1000 mg/kg dw of soil. The 14 day LC0 and NOEC, the latter based on behaviour and clinical signs, were 1000 mg/kg dw of soil/substrate. Thus, ZrC is considered to be non-toxic to earthworms up to/above a concentration of 1000 mg/kg dw of soil.

This study is classified as acceptable and satisfies the guideline requirements for an acute toxicity study with earthworms according to OECD Guideline 207.

 

Results Synopsis

 

Test organism size/age: Eisenia foetida, adults

Test Type: acute toxicity

 

14 day LC0:        1000 mg/kg dw soil

14 day NOEC:    1000 mg/kg dw soil

14 day LC50:    > 1000 mg/kg dw soil

Endpoint(s) Effected:  mortaility, behaviour, clinical signs



Description of key information

In a 14 day acute toxicity study, earthworms (Eisenia foetida) were exposed to nominal ZrC concentrations of 0 (control) and 1000 mg/kg dry weight of artificial soil.  The experiment was carried out in accordance with OECD Guideline 207.  The 14 day LC50was > 1000 mg/kg dw of soil. The 14 day LC0 and NOEC, the latter based on behaviour and clinical signs, were 1000 mg/kg dw of soil/substrate. Thus, ZrC is considered to be non-toxic to earthworms up to/above a concentration of 1000 mg/kg dw of soil.

This study is classified as acceptable and satisfies the guideline requirements for an acute toxicity study with earthworms according to OECD Guideline 207.



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Additional information