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EC number: 429-900-5 | CAS number: 82356-51-2
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
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- Density
- Particle size distribution (Granulometry)
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- Oxidation reduction potential
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- Stability: thermal, sunlight, metals
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- 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
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- Nanomaterial pour density
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- Endpoint summary
- Stability
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- 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
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- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
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- Irritation / corrosion
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- Specific investigations
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- Additional toxicological data

Toxicity to soil microorganisms
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to soil microorganisms
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- From 2002-06-02 to 2002-08-14
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- Experiment conducted under GLP, and following OECD Guidelines. No deviations were observed.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 216 (Soil Microorganisms: Nitrogen Transformation Test)
- Deviations:
- no
- Principles of method if other than guideline:
- not applicable.
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Inspected on 28 February 2000. Signed on 26 April 2000
- Analytical monitoring:
- no
- Details on sampling:
- - Concentrations: 1000 mg/Kg
- Sampling method: Based on the results of the range-finding test, a limit test was conducted at a concentration of 1000 mg/Kg to confirm that at the maximum recommended concentration given in the test guidelines no effect on nitrogen transformation was observed.
- Sample storage conditions before analysis: none. - Vehicle:
- yes
- Details on preparation and application of test substrate:
- VEHICLE:
- Chemical name of vehicle (organic solvent, emulsifier or dispersant): acetone
- Concentration of vehicle in test medium (stock solution and final test solution): no data
- Evaporation of vehicle before use: no data - Test organisms (inoculum):
- soil
- Total exposure duration:
- 28 d
- Remarks:
- none
- Test temperature:
- 21 +/-1°C
- Moisture:
- 40%
- Details on test conditions:
- TEST SYSTEM
- Testing facility: glass beakers
- Test container (type, material, size): no data
- Amount of soil: 50 g
- No. of replicates per concentration: 6
- No. of replicates per control: 3
- No. of replicates per vehicle control: 3
SOIL INCUBATION
- Method: series of individual subsamples
SOURCE AND PROPERTIES OF SUBSTRATE (if soil)
- Geographical reference of sampling site (latitude, longitude): Heath farm, Leicester Lane, Warwickshire, UK
- History of site: The sampling site had not been treated with crop protection products for approximately 3 years and no organic fertiliser had been applied for approximately 5 years prior to sampling.
- Vegetation cover: no data
- Treatments with pesticides or fertilizers: no
- Accidental contamination: no data
- Other: none
- Depth of sampling: no data
- Initial microbial biomass as % of total organic C: 282 µg C/g equivalent to 2.0% of the total soil organic carbon content.
VEHICLE CONTROL PERFORMED: yes
RANGE-FINDING STUDY
- Test concentrations: 1.0, 10, 100, 1000 mg/kg
- Results used to determine the conditions for the definitive study: no effect observed. - Nominal and measured concentrations:
- 1000 mg/Kg
- Reference substance (positive control):
- no
- Key result
- Duration:
- 28 d
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 1 000 mg/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- nitrate formation rate
- Details on results:
- See table 6.3.4/1 in "Any other information on results incl. tables".
- Results with reference substance (positive control):
- Not applicable.
- Reported statistics and error estimates:
- no data
- Validity criteria fulfilled:
- yes
- Conclusions:
- The test material showed no significant effect on the nitrogen transformation activity of soil microorganisms at a test concentration of 1000 mg/Kg over a 28 -day period and therefore can be considered to have no long-term effect on nitrogen transformation in soil.
NOEC >= 1000 mg/Kg. - Executive summary:
A study was performed to assess the long-term effect of the test material after a single exposure, on nitrogen transformation activity of soil microorganisms. The method followed that described in the OECD guidelines 216, EPPO 1994, under GLP.
Following a preliminary range-finding test (conducted over a range of test concentrations of 1.0, 10, 100, and 1000 mg/Kg) soil microorganisms were exposed to the test material at a single concentration of 1000 mg/Kg for 28 days at a temperature of 21 +/-1°C with the addition of powdered Lucerne-green-grass meal to act as a respiratory substrate. The inhibition effect of the test material on nitrogen transformation was assessed by the determination of nitrate concentration on the soil samples and compared to data obtained from control and solvent control soil samples.
The test material showed no significant effect on the nitrogen transformation activity of soil microorganisms at a test concentration of 1000 mg/Kg over a 28 -day period and therefore can be considered to have no long-term effect on nitrogen transformation in soil.
NOEC >= 1000 mg/Kg.
Reference
Table 6.3.4/1: Nitrate concentrations on each sampling occasion.
Nominal concentration (mg/Kg) |
Nitrate concentration (mg NO3/Kg) |
|||
Day |
||||
0 |
6 |
28 |
||
Control |
R1 |
123.38 |
212.28 |
367.59 |
R2 |
121.20 |
201.76 |
362.87 |
|
R3 |
124.83 |
197.76 |
359.97 |
|
Solvent control |
R1 |
118.66 |
214.09 |
332.03 |
R2 |
133.90 |
216.63 |
331.66 |
|
R3 |
132.08 |
216.27 |
339.65 |
|
1000 |
R1 |
140.43 |
199.58 |
341.10 |
R2 |
141.52 |
201.76 |
344.36 |
|
R3 |
142.97 |
205.38 |
355.61 |
|
R4 |
143.70 |
203.21 |
344.73 |
|
R5 |
139.34 |
206.47 |
378.11 |
|
R6 |
140.43 |
204.66 |
379.92 |
Description of key information
OECD Guideline 216, EPPO 1994, GLP, key study, validity 1:
No significant effect on the nitrogen transformation activity of soil microorganisms at a test concentration of 1000 mg/Kg over a 28 -day period.
No long-term effect on nitrogen transformation in soil.
NOEC >= 1000 mg/Kg.
Key value for chemical safety assessment
- Long-term EC10 or NOEC for soil microorganisms:
- 1 000 mg/kg soil dw
Additional information
One key study is available to assess the long-term effect of the registered substance after a single exposure, on nitrogen transformation activity of soil microorganisms. The method followed that described in the OECD guidelines 216, EPPO 1994, under GLP.
Following a preliminary range-finding test (conducted over a range of test concentrations of 1.0, 10, 100, and 1000 mg/Kg) soil microorganisms were exposed to the test material at a single concentration of 1000 mg/Kg for 28 days at a temperature of 21 +/-1°C with the addition of powdered Lucerne-green-grass meal to act as a respiratory substrate. The inhibition effect of the test material on nitrogen transformation was assessed by the determination of nitrate concentration on the soil samples and compared to data obtained from control and solvent control soil samples.
The test material showed no significant effect on the nitrogen transformation activity of soil microorganisms at a test concentration of 1000 mg/Kg over a 28-day period and therefore can be considered to have no significant effect on long-term nitrogen transformation in soil up to the maximum concentration tested.
NOEC >= 1000 mg/Kg.
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