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Diss Factsheets

Environmental fate & pathways

Biodegradation in water: screening tests

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Administrative data

Endpoint:
biodegradation in water: ready biodegradability
Type of information:
read-across from supporting substance (structural analogue or surrogate)
Adequacy of study:
weight of evidence
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
study well documented, meets generally accepted scientific principles, acceptable for assessment
Remarks:
Study well documented, meets generally accepted scientific principles, acceptable for assessment.
Justification for type of information:
Read across
Cross-reference
Reason / purpose for cross-reference:
read-across source
Reference
Endpoint:
biodegradation in water: ready biodegradability
Type of information:
read-across from supporting substance (structural analogue or surrogate)
Adequacy of study:
weight of evidence
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
study well documented, meets generally accepted scientific principles, acceptable for assessment
Remarks:
Test item concentration not in accordance to guideline.
Justification for type of information:
Read across
Reason / purpose for cross-reference:
read-across source
Qualifier:
according to guideline
Guideline:
other: Continuous biological activated sludge treatment system
Principles of method if other than guideline:
Continuous biological activated sludge treatment system
GLP compliance:
not specified
Specific details on test material used for the study:
Name of test material (as cited in study report): Methyldiethanolamine (MDEA; CAS: 105-59-9)
Oxygen conditions:
aerobic
Inoculum or test system:
activated sludge (adaptation not specified)
Details on inoculum:
- Source of inoculum/activated sludge (e.g. location, sampling depth, contamination history, procedure): activated sludge from municipal wastewater treatment plant (TOC: 1920 mg/l, total solids (TS): 9.4 g/l)
Parameter:
% degradation (TOC removal)
Value:
> 91
Sampling time:
21 d
Details on results:
- start-up period: ca. 2 weeks;
degradation for TOC of influent > 95 % - 80 ml/d MDEA (40 %): rise of TOC in effluent, increase of
degradation after 2 weeks - 40 ml/d MDEA (40 %): recovery after reduction of MDEA load; 95 % TOC degradation - MDEA-solution easily eliminated after adaption of the sludge: up to 96 % TOC-removal

- The continuous flow experiment showed a very good biodegradability of the wastewater including for high concentrations of MDEA solution with a TOC removal of 96%.
Conclusions:
- very good biodegradability of the wastewater including for
high concentrations of MDEA-solution (TOC removal: 96 %)

- high biodegradation probably due to adaptation of
microorganisms

Data source

Reference
Reference Type:
publication
Title:
Biodegradation of triethanolamine.
Author:
West RJ and Gonsior SJ
Year:
1996
Bibliographic source:
Environ Toxicol Chem 15(4): 472-480.

Materials and methods

Test guideline
Qualifier:
according to guideline
Guideline:
other: CO2 evolution test
GLP compliance:
not specified

Test material

Constituent 1
Chemical structure
Reference substance name:
2,2',2''-nitrilotriethanol
EC Number:
203-049-8
EC Name:
2,2',2''-nitrilotriethanol
Cas Number:
102-71-6
Molecular formula:
C6H15NO3
IUPAC Name:
2,2',2''-nitrilotriethanol
Specific details on test material used for the study:
- Name of test material (as cited in study report): [14C]-triethanolamine
- Analytical purity: >= 98 %
- Specific activity (if radiolabelling): 17.61 mCi/mmol

Study design

Oxygen conditions:
aerobic
Inoculum or test system:
other: Mixed liquor activated sludge (secondary effluent)
Details on inoculum:
- Source of inoculum/activated sludge (e.g. location, sampling depth, contamination history, procedure): West Bay County WWTP, Bay City, Michigan, treating primarily municipal sewage up to 4 mio gallons per day
Duration of test (contact time):
6 d
Initial test substance concentration
Initial conc.:
> 600 - < 5 500 µg/L
Based on:
test mat.
Parameter followed for biodegradation estimation
Parameter followed for biodegradation estimation:
CO2 evolution
Details on study design:
TEST CONDITIONS
- Composition of medium: minimal salts basal medium according to Stainer et al. (1966; J Gen Microbiol 43: 159-271)
- Additional substrate: no
- Solubilising agent (type and concentration if used): no
- Test temperature: 25 °C
- pH:
- pH adjusted: yes/no
- CEC (meq/100 g):
- Aeration of dilution water:
- Suspended solids concentration:
- Continuous darkness: yes
- Other:

TEST SYSTEM
- Culturing apparatus: 500-mL polypropylene Erlenmeyer flasks, sealed with rubber stoppers and fitted with CO2 traps
- Number of culture flasks/concentration: 2
- Method used to create aerobic conditions:
- Method used to create anaerobic conditions:
- Measuring equipment:
- Test performed in closed vessels due to significant volatility of test substance:
- Test performed in open system:
- Details of trap for CO2 and volatile organics if used: glass tubular CO2 traps (4 mL 1N KOH)
- Other: test material amended with 14C-TEA to yield 0.7 µCi/mL

SAMPLING
- Sampling frequency:
- Sampling method:
- Sterility check if applicable:
- Sample storage before analysis:
- Other:

CONTROL AND BLANK SYSTEM
- Inoculum blank:
- Abiotic sterile control: yes, via addition of formaldehyde (final concentration: 2.8%)
- Toxicity control:
- Other: performed in duplicate

Results and discussion

% Degradationopen allclose all
Parameter:
% degradation (test mat. analysis)
Value:
ca. 100
Sampling time:
1 d
Remarks on result:
other: Primary biodegradation of 0.6 mg/l TEA in a test with 164 mg/l municipal activated sludge
Parameter:
% degradation (test mat. analysis)
Value:
ca. 100
Sampling time:
5 d
Remarks on result:
other: Primary biodegradation of 0.6 mg/l TEA in a test with 164 mg/l municipal activated sludge
Details on results:
The rate constants in all test batches for degradation and mineralization are >0.359. According to GHS legislation, the substance is rapidly biodegradable. Therefore it can be assumed that the substance is also readily biodegradable.

Any other information on results incl. tables

Biodegradation (activated sludge):

Activated sludge

(mg/L MLSS)

Test item

concentration (mg/L)

Biodegradation

rate constant (/d)

Biodegradation

half-life (d)

CO2/ThCO2

(%)

164

0.6

6.86

0.1

56+-10

164

5.7

1.36

0.51

54+-3

818

0.6

30

0.02

55+-1

818

5.7

6.7

0.01

52+-0

 

Mineralisation (activated sludge):

Activated sludge

(mg/L MLSS)

Test item

concentration (mg/L)

Mineralisation rate

constant (/d)

Mineralisation

half-life (d)

164

0.6

1.92

0.36

164

5.7

1.04

0.67

818

0.6

2.86

0.24

818

5.7

1.69

0.41

Applicant's summary and conclusion

Validity criteria fulfilled:
yes
Interpretation of results:
other: rapidly biodegradable according to GHS (readily biodegradability is therefore assumed)