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Diss Factsheets

Environmental fate & pathways

Biodegradation in water: screening tests

Administrative data

Endpoint:
biodegradation in water: ready biodegradability
Type of information:
experimental study
Adequacy of study:
key study
Study period:
2016
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
2016
Report date:
2016

Materials and methods

Test guidelineopen allclose all
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
GLP compliance:
yes (incl. QA statement)

Test material

Constituent 1
Chemical structure
Reference substance name:
1-(methylamino)anthraquinone
EC Number:
201-417-2
EC Name:
1-(methylamino)anthraquinone
Cas Number:
82-38-2
Molecular formula:
C15H11NO2
IUPAC Name:
1-(methylamino)anthraquinone
Test material form:
solid

Study design

Oxygen conditions:
aerobic
Inoculum or test system:
activated sludge, non-adapted
Details on inoculum:
Species/Origin: Aerobic activated sludge, micro organisms from a domestic waste water treatment plant was supplied by the sewage plant Rossdorf, Germany.
Conditioning: The aerobic activated sludge used for this study was washed by centrifugation and the supernatant liquid phase was decanted. The solid material was re-suspended in tap water and centrifuged again. This procedure was done three times. An aliquot of the final sludge suspension was weighed, dried and the ratio of wet sludge to its dry weight was determined. Based on this ratio, calculated aliquots of washed sludge suspension, corresponding to 3.5 g dry material per litre were mixed with test water and aerated overnight. This suspension was used for the experiment.
Duration of test (contact time):
28 d
Initial test substance concentration
Initial conc.:
100 mg/L
Based on:
test mat.
Parameter followed for biodegradation estimation
Parameter followed for biodegradation estimation:
O2 consumption
Details on study design:
The purpose of this study was to determine the ready biodegradability of the test item . The test item was exposed to aerobic activated sludge from the aeration tank of a domestic waste water treatment plant for 28 days. The biodegradation was followed by the oxygen uptake of the microorganisms during exposure. As a reference item sodium benzoate was tested simultaneously under the same conditions as the test item, and functioned as a procedure control.
This type of study is recognized by the international test guidelines and should provide a rational basis to assess the ready biodegradation properties of the test item when incubated with aerobic activated sludge.
Test Units
Type and Size: Manometric Test System with test flasks containing a volume of approximately 500 mL.
Apparatus: BSB/BOD-Sensor-System, Aqualytic Dortmund, Germany
Principle: The test flasks were incubated at 22°C * 1°C. The pressure decrease in the reaction vessels was measured over complete experimental phase of 28 days using the BSB/BOD-Sensor-System, Aqualytic Dortmund, Germany. The test flasks were closed gas-tight by a measuring head. Potassium hydroxide solution (45%) was used for trapping the produced carbon dioxide. The amount of O2 consumed by the activated sludge was calculated from the decrease of pressure in the reaction vessel.

Preparation of Test Flasks:The amounts of test item and reference item were directly weighed into the test flasks. No emulsifiers or solvents were used.

Incubation: The closed test flasks were incubated in a climatised room under continuous stirring. The consumption of oxygen was determined by measuring the change of pressure in the flasks. Evolved carbon dioxide was absorbed in an aqueous solution (45%) of potassium hydroxide.
Test Duration: 28 days
Measurement of Oxygen: The change of pressure in the test flasks was measured by means of a manometric method (BSB/BOD-Sensor-System, Aqualytic Dortmund, Germany) each day.
Temperature: Temperature was measured each working day in the climatised room.
pH-Value: pH-values were measured in control, procedure control and a separately prepared test flask with test item at test start (to prevent loss of test item in the test flasks) and in all flasks at the end of the test using a pH-electrode WTW pH 340i.


Reference substance
Reference substance:
benzoic acid, sodium salt

Results and discussion

% Degradation
Parameter:
% degradation (O2 consumption)
Value:
0
Sampling time:
28 d
Details on results:
The test item contains nitrogen;therefore the evaluation of biodegradation has to be
based ThODNH4 and ThODNO3. The criterion for ready biodegradability under the conditions of a manometric
respirometry test is the 10-day window, describing the period between reaching at least 10% degradation
and 60% degradation. This period should not exceed 10 days.

The mean biodegradation of Solvaperm-Rot PFS at test end after 28 days was 0% (ThODNH4, ThODNO3).

Conclusion:
The degradation rate of test item did not
reach 60% within the 10-day window or after 28 days. Therefore, Solvaperm-Rot PFS is considered to be not
readily biodegradable.


Biodegradation in the Toxicity Control

Percentage Biodegradation: In the toxicity control containing both, the test item and the reference item sodium benzoate, 35% (ThODNH4) biodegradation was noted within 14 days and 36% (ThODNH4) biodegradation after 28 days of incubation (33% and 34% based on ThODNO3). According to the test guidelines, the test item can be assumed to be not inhibitory to the aerobic activated sludge microorganisms because degradation was >25% within 14 days.
Conclusion: According to the test guidelines the test item can be assumed to be not inhibitory to the aerobic activated sludge microorganisms because degradation was >25% within 14 days.

BOD5 / COD results

Results with reference substance:
Biodegradation of Reference Item Sodium Benzoate
Percentage Biodegradation: The reference item sodium benzoate was sufficiently degraded to 76% after 14 days and to 81% after
28 days of incubation.
Conclusion: The percentage biodegradation of the reference item confirms the suitability of the used aerobic activated sludge inoculum.

Any other information on results incl. tables

Table2. Cumulative Biochemical Oxygen Demand (mg O2/L) in Test Flasks during the Test Period of 28 Days

  test item control Na-Benzoate abiotic C. Tox. Stand
day BSB [mg/L] FLASK
  1 2 3 4 5 6 7
1 0 0 0 0 55 0 60
2 0 5 5 5 75 0 75
3 5 5 5 5 110 0 110
4 5 5 10 5 125 0 125
5 5 5 10 10 135 0 135
6 10 10 15 15 140 0 140
7 10 10 15 15 140 0 145
8 10 10 15 15 145 0 145
9 15 10 15 15 145 0 150
10 15 10 20 15 145 0 150
11 15 15 20 20 150 0 150
12 20 15 20 20 150 0 155
13 20 15 20 20 150 0 155
14 20 15 20 20 150 0 155
15 20 20 20 20 155 0 155
16 25 20 25 20 155 0 155
17 25 20 25 25 155 0 160
18 25 20 25 25 155 0 160
19 25 20 25 25 160 0 160
20 25 20 25 25 160 0 165
21 25 20 25 25 160 0 165
22 25 20 25 25 160 0 165
23 25 20 25 25 165 0 165
24 25 20 25 25 165 0 165
25 25 20 25 25 165 0 165
26 25 20 25 25 165 0 165
27 25 20 25 25 165 0 165
28 25 20 25 25 165 0 165

            Flasks 1 and 2: Test item

            Flasks 3 and 4: inoculum control

Flask 5:reference(procedure control)

            Flask 6: abiotic control

            Flask 7: toxicity control

Table3. Percentage Biodegradation of the Test Itemand of the Toxicity Control based on
ThODNO3
and of Sodium Benzoatebased on ThODNH4

Time

Percentage Biodegradation1

(Days)

Test item1

Sodium Benzoate2

Toxicity
control1, 2

 

Flask 1 [%]

Flask 2 [%]

Flask 5 [%]

Flask 7 [%]

1

0

0

32

14

2

0

0

41

17

3

0

0

61

25

4

0

0

68

28

5

0

0

73

30

6

0

0

73

30

7

0

0

73

31

8

0

0

76

31

9

0

0

76

33

10

0

0

74

32

11

0

0

76

31

12

0

0

76

33

13

0

0

76

33

14

0

0

76

33

15

0

0

78

33

16

1

0

77

32

17

0

0

76

33

18

0

0

76

33

19

0

0

78

33

20

0

0

78

34

21

0

0

78

34

22

0

0

78

34

23

0

0

81

34

24

0

0

81

34

25

0

0

81

34

26

0

0

81

34

27

0

0

81

34

28

0

0

81

34

            1ThODNH3of Test item: 2.428 mg O2/mg test item
            2ThODNH4of sodium benzoate: 1.666 mg O2/mg reference item

Table4.pH-Values at the End of the Test

Flask No.

Treatment

pH-value

1

Test item

7.8

2

Test item

7.9

3

Inoculum control

7.9

4

Inoculum control

7.8

5

Reference item (procedure control)

7.9

 

 

 

 

 

 

Applicant's summary and conclusion

Validity criteria fulfilled:
yes
Interpretation of results:
not readily biodegradable
Conclusions:
Degradation of test item was 0% after 28 days.
Therefore, test item is considered to be not readily biodegradable.


Executive summary:

Title:

Test item: Ready Biodegradability in a Manometric Respirometry Test

 

 

Guidelines:

-     Commission Regulation 440/2008/EC, Method C.4-D of: Manometric Respirometry Test (EEC Publication No. L 142/496, May 2008)

-     OECD Guideline for Testing of Chemicals No. 301 F: "Ready Biodegradability: Manometric Respirometry Test", adopted

 

 

Material and Methods:

 

Test Item:

Sanodal-Rot B3LW

Test Species:

Aerobic activated sludge (microorganisms from a domestic waste­water treatment plant) was supplied by the sewage treatment plant of Rossdorf, Germany.

Test Design:

The test item Sanodal-Rot B3LW was investigated for its ready biodegradability in a manometric respirometry test over a period of 28 days. The biodegradation was followed by the oxygen uptake of the microorganisms during exposure. As a reference item sodium benzoate was tested simultaneously under the same conditions as the test item, and functioned as a procedure control.

Endpoints:

Degradation rate of test item calculated by the oxygen consumption of the aerobic activated sludge microorganisms after 28 days of incubation.

Test Item Loading Rate (initial concentration in medium C0):

103.3 mg/L corresponding to an oxygen demand of about 222.9 mg/L (ThODNH4) and 250.8 mg/L (ThODN03)

Reference Item:

Sodium Benzoate

Reference Item Loading Rate:

103.3 mg/L corresponding to an oxygen demand of about 172.1 mg/L (ThODNH4)

Test Conditions:

22°C ± 1°C, darkness

 

 

Results:

Biodegradation of Sanodal-Rot B3LW:

The test item contains nitrogen; therefore the evaluation of biodegradation has to be based ThODNH4and ThODNO3. The criterion for ready biodegradability under the conditions of a manometric respirometry test is the 10-day window, describing the period between reaching at least 10% degradation and 60% degradation. This period should not exceed 10 days.

The mean biodegradation at test end after 28 days was 0% (ThODNH4, ThODNO3).

Therefore,test item is considered to be not readily biodegradable based on ThODNH4/ ThODNO3.

 

 

 

Biodegradation of Sodium Benzoate:

The reference item sodium benzoate was sufficiently degraded to 76% after 14 days and to 81% after 28 days of incubation, thus confirming the suitability of the aerobic activated sludge inoculum used.

 

Biodegradation of the Toxicity Control:

In the toxicity control containing both, the test item and the reference item sodium benzoate, 35% (ThODNH4) biodegradation was noted within 14 days and 36% (ThODNH4) biodegradation after 28 days of incubation (33% and 34% based on ThODNO3). According to the test guidelines, the test item can be assumed to be not inhibitory to the aerobic activated sludge microorganisms because degradation was >25% within 14 days.

This study is classified acceptable and satisfies the guideline requirements for ready biodegradability studies.