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EC number: 200-268-0 | CAS number: 56-35-9
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
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- Additional physico-chemical information
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- Endpoint summary
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- Environmental data
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- 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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- Biological effects monitoring
- Biotransformation and kinetics
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- Toxicological Summary
- Toxicokinetics, metabolism and distribution
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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:
- supporting study
- Study period:
- January-February 1968
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- documentation insufficient for assessment
- Qualifier:
- according to guideline
- Guideline:
- other: DIN 52 176
- Deviations:
- yes
- Remarks:
- (Impregnation of pine block test media diverged from the standard)
- Principles of method if other than guideline:
- Impregnation of pine sapwood block involved evacuating air from the blocks in the dry state followed by introduction of the preservative solutions under vacuum
- GLP compliance:
- not specified
- Analytical monitoring:
- not specified
- Vehicle:
- yes
- Details on preparation and application of test substrate:
- Solvent used was chloroform complying with DAB 6 (German Pharmacopoeia 6th edition).
- Test organisms (inoculum):
- soil
- Total exposure duration:
- 12 wk
- Moisture:
- Not reported
- Nominal and measured concentrations:
- For tests without leaching: 0.001, 0.0025, 0.0063, 0.016, 0.04, 0.1 %
For tests with leaching: 0.0025, 0.0063, 0.016, 0.04, 0.25 % - Validity criteria fulfilled:
- not specified
- Conclusions:
- Toxic limits for basidiomycetes exposed to tri-n-butyltin oxide without leaching ranged from 0.04% to 0.1% for Coniphora cerebella; 0.0025% to 0.0063% for Poria vaporaria; and 0.0063% to 0.016% for Lentinus lepideus. Toxic limits for basidiomycetes exposed to tri-n-butyltin oxide with leaching ranged from 0.1% to 0.25% for Coniphora cerebella; 0.0025% to 0.0063% for Poria vaporaria; and 0.0063% to 0.016% for Lentinus lepideus.
Toxic limits for soft rot fungi exposed to tri-n-butyltin oxide without leaching was greater than 0.1% for Chaetomium globosus; 0.04% to 0.1% for Paecilomyces sp., and greater than 0.1% for the soil burial test. Toxic limits for soft rot fungi exposed to tri-n-butyltin oxide with leaching ranged from 0.1% to 0.25% for Chaetomium globosus; 0.1% to 0.25% for Paecilomyces sp., and much greater than 0.25% for the soil burial test. - Executive summary:
Toxic limits for basidiomycetes exposed to tri-n-butyltin oxide without leaching ranged from 0.04% to 0.1% for Coniphora cerebella; 0.0025% to 0.0063% for Poria vaporaria; and 0.0063% to 0.016% for Lentinus lepideus. Toxic limits for basidiomycetes exposed to tri-n-butyltin oxide with leaching ranged from 0.1% to 0.25% for Coniphora cerebella; 0.0025% to 0.0063% for Poria vaporaria; and 0.0063% to 0.016% for Lentinus lepideus.
Toxic limits for soft rot fungi exposed to tri-n-butyltin oxide without leaching was greater than 0.1% for Chaetomium globosus; 0.04% to 0.1% for Paecilomyces sp., and greater than 0.1% for the soil burial test. Toxic limits for soft rot fungi exposed to tri-n-butyltin oxide with leaching ranged from 0.1% to 0.25% for Chaetomium globosus; 0.1% to 0.25% for Paecilomyces sp., and much greater than 0.25% for the soil burial test.
Leaching appeared to decrease the toxicity of tri-n-butyltin oxide to various fungi. Poria vaporaria was the most sensitive species tested.
Reference
The toxic limits determined in the tests are collated in the tables given below. The preservative loading is expressed in terns of the mean values from the 4 tested replicates. A deciding factor for the determination of the toxic limits was a weight loss of <3% for those blocks in every test series which were most strongly attacked.
Toxic Limits for Basidiomycete | ||
Tri-n-butyltin oxide | ||
Test fungi | Concentration (%) | Preservartive loading (kg/m³) |
Without Leaching | ||
Coniophora cerebella | 0.04-0.10 | 0.344-0.704 |
Poria vaporaria | 0.0025-0.0063 | 0.022-0.058 |
Lentinus lepideus | 0.0063-0.0160 | 0.054-0.144 |
With Leaching | ||
Coniophora cerebella | 0.10-0.25 | 0.681-2.178 |
Poria vaporaria | 0.0025-0.0063 | 0.021-0.055 |
Lentinus lepideus | 0.0063-0.0160 | 0.056-0.140 |
Toxic Limits for Soft Rot Fungi | ||
Tri-n-butyltin oxide | ||
Test fungi | Concentration (%) | Preservartive loading (kg/m³) |
Without Leaching | ||
Chaetomium globosum | >0.10 | >0.485 |
Paecilomyces spp. | 0.04-0.10 | 0.269-0.572 |
Soil burial test | >0.10 | >0.577 |
With Leaching | ||
Chaetomium globosum | 0.10-0.25 | 0.643-1.562 |
Paecilomyces spp. | 0.10-0.25 | 0.438-1.695 |
Soil burial test | >0.25 | >1.662 |
Description of key information
Toxic limits for basidiomycetes exposed to tri-n-butyltin oxide without leaching ranged from 0.04% to 0.1% for Coniphora cerebella; 0.0025% to 0.0063% for Poria vaporaria; and 0.0063% to 0.016% for Lentinus lepideus. Toxic limits for basidiomycetes exposed to tri-n-butyltin oxide with leaching ranged from 0.1% to 0.25% for Coniphora cerebella; 0.0025% to 0.0063% for Poria vaporaria; and 0.0063% to 0.016% for Lentinus lepideus.
Toxic limits for soft rot fungi exposed to tri-n-butyltin oxide without leaching was greater than 0.1% for Chaetomium globosus; 0.04% to 0.1% for Paecilomyces sp., and greater than 0.1% for the soil burial test. Toxic limits for soft rot fungi exposed to tri-n-butyltin oxide with leaching ranged from 0.1% to 0.25% for Chaetomium globosus; 0.1% to 0.25% for Paecilomyces sp., and much greater than 0.25% for the soil burial test.
Leaching appeared to decrease the toxicity of tri-n-butyltin oxide to various fungi. Poria vaporaria was the most sensitive species tested.
Key value for chemical safety assessment
Additional information
The study Liese, W., & Liese, Willeitner, H., H. (1969) was provided for informative purposes only. The study was limited in its level of reporting and was not performed to a standardised guideline or in compliance with GLP. The study was assigned a reliability score of 4.
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