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Toxicity to soil microorganisms

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Reference
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 %

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
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.

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.