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Environmental fate & pathways

Biodegradation in water: screening tests

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Endpoint:
biodegradation in water: ready biodegradability
Type of information:
experimental study
Adequacy of study:
key study
Study period:
From June 08, 2000 to July 06, 2000
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study
Qualifier:
according to guideline
Guideline:
OECD Guideline 301 F (Ready Biodegradability: Manometric Respirometry Test)
Deviations:
no
Qualifier:
according to guideline
Guideline:
EU Method C.4-D (Determination of the "Ready" Biodegradability - Manometric Respirometry Test)
Deviations:
no
Qualifier:
according to guideline
Guideline:
other: ISO 9408:1991
Deviations:
no
GLP compliance:
yes
Oxygen conditions:
aerobic
Inoculum or test system:
activated sludge, non-adapted
Details on inoculum:
Municipal activated sludge from the waste water treatment plant of Mannheim/Baden-Wurttemberg (Germany), stored in laboratory wastewater treatment plant which was fed with municipal sewage. The sludge was washed and aerated for 24 hours and then added to the test vessels to obtain a sludge concentration of 30 mg/L dry substance.
Test concentration in medium 1, 2 and 3: 100 mg/L
Volume of reaction mixture: 0.25 L
ThOD concentration in medium: 46.2 mg O2/L
ThOD per mg of test substance: 0.462 mg O2/mg test substance
Duration of test (contact time):
28 d
Initial conc.:
100 mg/L
Based on:
test mat.
Initial conc.:
46.2 mg/L
Based on:
ThOD
Parameter followed for biodegradation estimation:
DOC removal
Details on study design:
The monometric respiratory test is a static method for testing the ultimate aerobic biodegradability of a test substance in water. Mixtures of the test substance, a defined inorganic medium and an inoculum, which is not pre-adopted activated sludge of a municipal or laboratory waste water treatment plant, are incubated and aerated in a respirometer (Sapromat) at 22 ±1 °C up to 28 days. The oxygen used for the biodegradation of the test substance (biochemical oxygen demand, BOD) in continuously produced and measured by the test apparatus. Primary biodegradation is also calculated from supplemental specific chemical analysis made at the beginning and the end of incubation, and in addition ultimate biodegradation by DOC analysis. Any intermediates are identified, if possible.
Reference substance:
aniline
Key result
Parameter:
% degradation (DOC removal)
Value:
> 0 - < 10
Sampling time:
28 d
Key result
Parameter:
other: BOD of ThOD
Value:
> 0 - < 10
Sampling time:
28 d
Details on results:
Degree of biodegradation (BOD of ThOD) after 28 days: 0 – 10 %
Degree of substance specific elimination by UV-VIS after 28 days: 0 – 10 %
Degree of DOC elimination after 28 days: 0 – 10 %
The test substance is in this test poorly biodegradable.
Results with reference substance:
ThOD concentration of reference substance: 2.393 mg O2/mg reference substance
Validity criteria fulfilled:
yes
Interpretation of results:
under test conditions no biodegradation observed
Conclusions:
Under the study conditions, the test substance is not considered to be readily biodegradable.
Executive summary:

A study was conducted to determine the ready biodegradability of the test substance according to OECD Guideline 301 F (manometric respirometry), EU Method C.4 and ISO Method 9408:1991, in compliance with GLP. The test substance, at 100 mg/L, was inoculated for 28 d in a pre-aerated microbial system collected from a municipal sewage plant. The sludge was washed and aerated for 24 h, then added to the test vessels to obtain a sludge concentration of 30 mg/L dry substance. Three assays were conducted. Under the study conditions, the test substance did not biodegrade during the test period. Measured BOD values (except for assay 3) corresponded well with the values found with DOC and specific chemical analysis. Assay 3 was not validated due to technical deficiencies (leaky) (Beimborn, 2000).

Endpoint:
biodegradation in water: ready biodegradability
Type of information:
experimental study
Adequacy of study:
supporting study
Study period:
From August 17, 1993 to September 14, 1993
Reliability:
4 (not assignable)
Rationale for reliability incl. deficiencies:
documentation insufficient for assessment
Remarks:
Substance purity not specified
Qualifier:
equivalent or similar to guideline
Guideline:
OECD Guideline 301 E (Ready biodegradability: Modified OECD Screening Test)
Deviations:
no
Qualifier:
according to guideline
Guideline:
other: Official Journal of the European Communities No L383 A, July 31, 1992
Deviations:
no
Qualifier:
according to guideline
Guideline:
other: EEC Directive 92/69/EEC
Deviations:
no
GLP compliance:
yes
Oxygen conditions:
aerobic
Inoculum or test system:
activated sludge, domestic, non-adapted
Details on inoculum:
Effluent of a municipal waste water treatment plant.
Duration of test (contact time):
28 d
Parameter followed for biodegradation estimation:
DOC removal
Preliminary study:
TOC: 212 mg/g
DOC: 214 mg/g
Key result
Parameter:
other: DOC removal (mg/L)
Value:
< 20
Sampling time:
28 d
Results with reference substance:
Stock solution: 431 mg/L
DOC value stock solution: 258 mg/L
> 90

Data evaluation:

If DOC decrease due to abiotic processes like stripping or adsorption may be excluded, the test substance is biodegradable. The DOC concentration at the end of the test is compared with the initial concentration. The degradation is calculated as per cent value, stated in 10%-steps and interpreted as follows:

DOC-decrease >70 % in 10 days (ready biodegradable)

DOC-decrease >70 % biodegradable

DOC-decrease 20-70 % moderately or partially biodegradable

DOC decrease <20 % poory biodegradable

Validity criteria fulfilled:
yes
Interpretation of results:
under test conditions no biodegradation observed
Conclusions:
Under the study conditions, the test substance was not considered to be readily biodegradable.
Executive summary:

A study was conducted to evaluate the ready biodegradability of the test substance according to a modified OECD Guideline 301 E, EEC Directive 92/69/EEC and the Official Journal of the European Communities No L383 A, July 31, 1992, in compliance with GLP. The test substance at a concentration of 20 mg dissolved organic carbon (DOC)/L, a defined dilution water and, as inoculum, effluent of a laboratory waste water treatment plant fed with municipal sewage were mixed together and aerated up to 28 d at 20-25°C. Samples were taken at regular intervals to measure the DOC concentration according to DIN 38409 Part 3 (1983). Under the study conditions, the degree of biodegradation was lower than 20 mg DOC/L after 28 d. Under the study conditions, the test substance was therefore not considered to be readily biodegradable (Taeger, 1993).

Description of key information

Key value for chemical safety assessment

Biodegradation in water:
under test conditions no biodegradation observed

Additional information

A study was conducted to evaluate the ready biodegradability of the test substance according to a modified OECD Guideline 301 E, EEC Directive 92/69/EEC and the Official Journal of the European Communities No L383 A, July 31, 1992, in compliance with GLP. The test substance at a concentration of 20 mg dissolved organic carbon (DOC)/L, a defined dilution water and, as inoculum, effluent of a laboratory waste water treatment plant fed with municipal sewage were mixed together and aerated up to 28 d at 20-25°C. Samples were taken at regular intervals to measure the DOC concentration according to DIN 38409 Part 3 (1983). Under the study conditions, the degree of biodegradation was lower than 20 mg DOC/L after 28 d. Under the study conditions, the test substance was therefore not considered to be readily biodegradable (Taeger, 1993).

A study was conducted to determine the ready biodegradability of the test substance according to OECD Guideline 301 F (manometric respirometry), EU Method C.4 and ISO Method 9408:1991, in compliance with GLP. The test substance, at 100 mg/L, was inoculated for 28 d in a pre-aerated microbial system collected from a municipal sewage plant. The sludge was washed and aerated for 24 h, then added to the test vessels to obtain a sludge concentration of 30 mg/L dry substance. Three assays were conducted. Under the study conditions, the test substance did not biodegrade during the test period. Measured BOD values (except for assay 3) corresponded well with the values found with DOC and specific chemical analysis. Assay 3 was not validated due to technical deficiencies (leaky) (Beimborn, 2000).