o-phenylenediamine

Biodegradation in water: screening tests

Administrative data

Endpoint:

biodegradation in water: ready biodegradability

Type of information:

read-across from supporting substance (structural analogue or surrogate)

Adequacy of study:

key study

Reliability:

2 (reliable with restrictions)

Rationale for reliability incl. deficiencies:

guideline study with acceptable restrictions

Remarks:

The hypothesis underpinning this analogue approach relies on the fact that OPD and PPD, which are both disubstituted aromatic amines, are positional isomers. Degradation is dependent on structural similarity, functional groups, transformation pathways as well as similar physicochemical properties such as Log Kow which drive bioavailability and thus the extent of biodegradation. OPD and PPD are likely to have comparable bioavailability profiles based on their LogKow values. In addition, their transformation pathways as simulated by Catalogic 5.10.7 (LMC 2009) are comparable. Given their close structural and chemical similarity, it is reasonable to read-across available biodegradation data from PPD to OPD.

Justification for type of information:

Additional documentation, provided within the IUCLID Assessment Reports (Section 13), supports the read-across approach.

Cross-reference

Reason / purpose for cross-reference:

read-across: supporting information

Reference

Endpoint:

biodegradation in water: ready biodegradability

Type of information:

read-across from supporting substance (structural analogue or surrogate)

Adequacy of study:

key study

Justification for type of information:

Additional documentation, provided within the IUCLID Assessment Reports (Section 13), supports the read-across approach.

Reason / purpose for cross-reference:

read-across source

Parameter:

other: % Biodegradation (BOD/ThOD)

Value:

30

Sampling time:

28 d

Remarks on result:

other: without silica gel

Parameter:

other: % Biodegradation (BOD/ThOD)

Value:

30

Sampling time:

84 d

Remarks on result:

other: without silica gel

Parameter:

other: % Biodegradation (BOD/ThOD)

Value:

28

Sampling time:

28 d

Remarks on result:

other: with silical gel

Parameter:

other: % Biodegradation (BOD/ThOD)

Value:

28

Sampling time:

84 d

Remarks on result:

other: with silical gel

Data source

Reference

Reference Type:

study report

Title:

Unnamed

Year:

1994

Report date:

1994

Materials and methods

Test guideline

Qualifier:

according to guideline

Guideline:

OECD Guideline 301 D (Ready Biodegradability: Closed Bottle Test)

Deviations:

yes

Remarks:

The test was prolonged because the pass level was not reached at day 28. Since the test substance may be toxic to microorganisms, it was also tested in the presence of silica gel to reduce the concentration in the water phase.

GLP compliance:

yes

Test material

Test material information

Constituent 1

Reference substance name:

p-phenylenediamine

EC Number:

203-404-7

EC Name:

p-phenylenediamine

Cas Number:

106-50-3

Molecular formula:

C6H8N2

IUPAC Name:

benzene-1,4-diamine

Details on test material:

- Purity: Not reported

Study design

Oxygen conditions:

aerobic

Inoculum or test system:

activated sludge, domestic (adaptation not specified)

Details on inoculum:

- Source of inoculum/activated sludge (e.g. location, sampling depth, contamination history, procedure): WWTP Nieuwgraaf in Duiven, The Netherlands. The WWTP Nieuwgraaf is an activated sludge plant treating predominantly domestic waste water. The activated sludge was preconditioned to reduce the endogenous respiration rates by aerating for 1 week.
- Concentration of sludge: 2 mL DW/L
- Preparation of inoculum for exposure: The dry weight (DW) of the inoculum was determined by filtrating 100 mL of the activated sludge over a preweighed filter. The filter was dried for 1.5 hours at 104ºC and weighed after cooling. DW was calculated by subtracting the weighed filters.

Preparation of Mineral Medium: 8.5 g of KH2PO4, 21.75 g of K2HPO4, 33.3 g of Na2HPO4 2H20, 22.5 mg MgSo4 7H20, 27.5 mg CaCl2, 0.25 mg FeCl3 6H20 were dissolved in 1 L of deionized water. Ammonium chloride was omitted to prevent nitrification. Due to this omission the pH of the medium decreased slightly. The test compound was added to the bottles using a stock solution of 1.0 g/L.

Duration of test (contact time):

28 d

Initial test substance concentration

Initial conc.:

2 mg/L

Parameter followed for biodegradation estimation

Parameter followed for biodegradation estimation:

O2 consumption

Details on study design:

Use was made of 3 bottles containing only inoculum, and 3 bottles containing test substance and inoculum. The concentration of the test substance in the bottles was 2.0 mg/L. The inoculum was diluted to 2 mg DW/L in the closed bottles. Each of the prepared solutions was dispensed into the respective group of BOD bottles so that all bottles were completely filled without air bubbles. The bottles were immediately analyzed for dissolved oxygen using an oxygen electrode. Subsequently all bottles were closed and incubated at 21±1°C in the dark. The oxygen concentration in the bottles was measured in the bottles using a special funnel that fit exactly in the BOD bottle. Subsequently, the oxygen electrode was inserted in the BOD bottle to measure the oxygen concentration. The medium dissipated by the electrode was collected in the funnel. After withdrawal of the oxygen electrode, the medium collected flowed back into the BOD bottle, followed by removal of the funnel and closing of the BOD bottle. Dissolved oxygen concentrations were measured at day 7, 14, 21, 28, 42, 56, and 84.

One extension from the protocol of the closed Bottle test was introduced. Since the test substance may be toxic to microorganisms, the test substance was tested in the presence of silica gel to reduce the concentration in the water phase. During the test period, the test substance should be released slowly from the silica gel (1 g/bottle). Although no additional oxygen consumption was expected, controls with silica gel were carried out as well (10 bottles containing test substance, inoculum, and silica gel).

The pH of the media was 6.9 at the start of the test and was 6.5-6.9 at day 28. Temperatures ranged from 20-22°C. ThOD and BOD were calculated, and biodegradation was calculated as the ratio of BOD to ThOD.

Reference substance

Reference substance:

not required

Remarks:

Inhibition of the degradation of a well-degradable compound by the test substance was not determined because possible toxicity of the test substance to microorganisms degrading acetate is not relevant.

Results and discussion

% Degradation

% Degradation 1

Parameter:

other: % Biodegradation (BOD/ThOD)

Value:

30

Sampling time:

28 d

Remarks on result:

other: without silica gel

% Degradation 2

Parameter:

other: % Biodegradation (BOD/ThOD)

Value:

30

Sampling time:

84 d

Remarks on result:

other: without silica gel

% Degradation 3

Parameter:

other: % Biodegradation (BOD/ThOD)

Value:

28

Sampling time:

28 d

Remarks on result:

other: with silical gel

% Degradation 4

Parameter:

other: % Biodegradation (BOD/ThOD)

Value:

28

Sampling time:

84 d

Remarks on result:

other: with silica gel

Details on results:

See Table 1 for additional information on oxygen consumption and percent biodegradation.

Any other information on results incl. tables

Table 1: Oxygen consumption and percentage biodegradation
Time (days)	Oxygen consumption (mg/L)		Biodegradation (%)
	Without silica gel	With silica gel	Without silica gel	With silica gel
0	0.0	0.0	0	0
7	0.7	0.6	18	15
14	1.1	1.1	28	28
21	1.3	1.1	33	28
28	1.2	1.1	30	28
42	1.4	1.1	35	28
56	1.3	1.0	33	25
84	1.2	1.1	30	28

 

Applicant's summary and conclusion

Validity criteria fulfilled:

yes

Interpretation of results:

other: partially biodegradable

Conclusions:

The test substance is not readily biodegradable. The biodegradation percentage reached demonstrates that the test substance should be classified as partially biodegradable.

Executive summary:

The ready biodegradability of the test substance was determined in the Closed Bottle test performed according to slightly modified OECD guidelines. The test was prolonged because the pass level was not reached at day 28. The test substance caused no reduction in the endogenous respiration. Therefore, the test substance is considered to be non-inhibitory to the inoculum. The test substance was biodegraded approximately 30% at day 28 in the Closed Bottle test. In the prolonged Closed Bottle test, the biodegradation percentage did not increase. The test substance is therefore not readily biodegradable. The biodegradation percentage reached demonstrates that this test substance should be classified as partially biodegradable. The test substance was also tested in a Closed Bottle test in the presence of silica gel because it was suspected to be toxic. In this test, the biodegradation percentages found were comparable to the percentages found in the test without silica gel. This result confirms that this test substance is not toxic to activated sludge. The tests are valid as shown by an endogenous respiration of 1.5 mg/L. The most important criterion was met by oxygen concentrations >0.5 mg/L in all bottles during the test period.