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Environmental fate & pathways

Biodegradation in water: screening tests

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Reference
Endpoint:
biodegradation in water: ready biodegradability
Type of information:
experimental study
Adequacy of study:
key study
Study period:
12 Apr 1988 - 10 May 1988
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
guideline study with acceptable restrictions
Reason / purpose for cross-reference:
reference to same study
Qualifier:
according to guideline
Guideline:
ISO DIS 9408 (Ultimate Aerobic Biodegradability - Method by Determining the Oxygen Demand in a Closed Respirometer)
Deviations:
no
Principles of method if other than guideline:
Manometric respirometry of the BOD (biological oxygen demand)
GLP compliance:
yes
Oxygen conditions:
aerobic
Inoculum or test system:
activated sludge, domestic, non-adapted
Details on inoculum:
- Source of inoculum/activated sludge: domestic, laboratory sewage treatment plant
- Concentration of sludge: 750 mg/L
Duration of test (contact time):
28 d
Initial conc.:
91 mg/L
Based on:
test mat.
Parameter followed for biodegradation estimation:
O2 consumption
Details on study design:
TEST CONDITIONS
- pH: 6.5 - 7

TEST SYSTEM
- Number of culture flasks/concentration: 7

SAMPLING
- Sampling frequency: daily

CONTROL AND BLANK SYSTEM
- Inoculum blank: yes (2)
- Reference control: yes (1)
- Toxicity control: yes (1)
- Abiotic sterile control: yes (1)
Reference substance:
aniline
Parameter:
other: ThOD
Value:
68
Sampling time:
10 d
Remarks on result:
other: mean of 7 samples
Parameter:
other: ThOD
Value:
70.9
Sampling time:
28 d
Remarks on result:
other: mean of 7 samples
Parameter:
other: COD
Value:
100
Sampling time:
28 d
Remarks on result:
other: mean of 7 samples
Details on results:
Duration of lag-phase: 3 days
Duration of log-phase: 5 days
Results with reference substance:
ThOD of the reference substance (without nitrification): 2670 mg/g
ThOD of the reference substance (with nitrification): 3180 mg/g
% Degradation after 28 d: 73.2 % (of ThOD)

Duration of lag-phase: 3 days

Duration of log-phase: 5 days

IB1/2 = Inoculum blank

RC = Reference control

IH = Toxicity control

PC = Abiotic sterile control

1 -7 = Flasks with test substance and Inoculum

BOD (mg/L)

 time [d]  IB1  IB2  RC  IH  PC  1  2  3  4  5  6  7
 1  1 0 1  1  1  1  1  1  1  1  1
 2  1  1  4  1  1  1  1  1  1  1  1  1
 3  4  4  5  1  1  4  1  8  1  3  13  33
 4  6  6  8  189  1  181  111  96  91  137  158  139
 9  9  33  113  1  194  167  107  186  145  166  149
 6  10  10  149  114  1  201  177 124  215  171  191  171
 7  11  11  177  117  1  214  186 135   228  188  200  179
 8 11   11  194  117  1  228  193  139  235  186  207  186
 9  11  11  205  120  1  235  200  144  238  191  211

 189

 10  13  13  212  120  1  240  209  145  241  194  215

 192

 28  14  14  247  148  1  257  223  149  248  197  219  196

BOD (% of ThOD)

 time [d]  IB1  IB2  RC  IH  PC  1  2  3  4  5  6  7
 1   -4.1 0.3  -4.7 -4.7 -4.7 -4.7 -4.7 -4.7 -4.7
 2    -3.2  -1.1 0.3   -4.7   -4.7  -4.7   -4.7  -4.7   -4.7   -4.7
 3    -2.9  -1.5  0.3 -3.6   -4.7  -2.2   -4.7   -4.0  -0.4  6.7
 4      -1.9  36 0.3 59.6  34.6 29.2 27.5  43.9 51.4 44.6
     5.9 28.5 0.3 64.2 54.6 33.2  61.4 47.1 54.2 48.2
 6      42.4 -12.6 0.3 66.7 58.2 39.2 71.7 56.0 63.2 56.0
 7     51.2 -21.5 0.3 71.4 61.4 43.2 76.7 59.2 66.4 58.9
 8      56.6 -27.6 0.3 76.4 63.9 44.6 78.8 61.4 68.9 61.4
 9     60.0 -38.4 0.3 78.9 66.4 46.4 80.0 63.2 70.3

62.5

 10      62.2 -32.9 0.3 80.7 69.6 46.7 82.0 64.2 71.7

63.5

 28      73.2 -35.4 0.3 86.7 74.6 48.2 83.5 65.3 73.2 65.0

After 28 d (ThOD of the test substance: 3077 mg/g):

   IB1  IB2  RC  IH  PC  1  2  3  4  5  6  7
 BOD [mg/g]      2330 -1088  10.9  2670  2296  1483  2571  2011  2252  2000
 BOD*100/ThOD      73.2  -35.4  0.3  86.7  74.6  78.2  83.5  65.3  73.2  65.0

Specific analytic at the end of the test:

Theoretical test concentration at the beginning of the test: 91 mg/L

Measured test concentration at the end of the test: < 0.05 mg/L

Elimination: 100 %

Validity criteria fulfilled:
not specified
Interpretation of results:
readily biodegradable
Executive summary:

Styrene was tested for readily biodegradability. The biodegradation after 28 d was determined to be 100%.

Description of key information

Readily biodegradable (according to OECD criteria). According to BASF 1988 the degradation rate is 100% for COD after 28 d.

Key value for chemical safety assessment

Biodegradation in water:
readily biodegradable

Additional information

Ready biodegradation

Several tests are available which show that styrene is readily biodegradable. Ready biodegradability test ISO DIS 9408 (Directive 79/831/EEC Annex V, Part C – manometric respirometry test, equivalent to OECD 301F) was carried out by BASF AG (Ecological laboratory, unpublished data, test no. 388576, 1988). From an initial concentration of 91 mg/l in an activated sludge of domestic origin, 68% of ThOD was reached after ten days.

The closed bottle test was carried out with an initial concentration of 3,7 and 10 mg/l with bacteria from non-adapted domestic wastewater, first in freshwater and secondly in synthetic seawater (Price et al., 1974). Biodegradation was measured as BOD as a percentage of ThOD. The results were: degradation of 65% and 87% after five days and twenty days respectively in freshwater; and 8% and 80% after five days and twenty days respectively for the synthetic seawater. The closed bottle test is an approved EC test procedure, although this study pre-dates adoption by the EC. The guidelines suggest an initial concentration between 2 mg/l and 5 mg/l, and an inoculum derived from the secondary effluent of a treatment plant or lab-scale unit receiving predominantly domestic sewage. The test as performed matches the guidelines sufficiently to be considered as a valid test.

Another test result of ready biodegradability has been found, using the standard dilution BOD method (APHA Standard Methods No 219) with added alkyl thiourea to prevent nitrification. Magnetic stirring was used for sparingly soluble chemicals including styrene. From an adapted inoculum of predominantly domestic sewage, 80% degradation was observed after five days. From a non-adapted inoculum, 42% degradation occurred in the same period (Bridié et al., 1979).

Inherent biodegradation

The modified MITI test (II) (OECD Guideline 302C) was used to determine the inherent biodegradability of styrene (CITI, 1992). From an initial concentration of 30 mg/l in activated sludge, 100% had degraded after 14 days, leading to the conclusion that styrene is at least inherently biodegradable.