Concrete of Rosa Damascena (Rosaceae) obtained from fresh flowers by extraction with an apolar solvent

Biodegradation in water: screening tests

Link to relevant study record(s)

Reference

Endpoint:

biodegradation in water: ready biodegradability

Type of information:

experimental study

Adequacy of study:

key study

Study period:

2017-01-10 to 2017-04-06

Reliability:

1 (reliable without restriction)

Rationale for reliability incl. deficiencies:

guideline study

Justification for type of information:

Read-across from an analogue substance.
The analogue substance Turkish Rose Absolute and the registered substance Turkish Rose Concrete have the same botanical origin: Rosa Damascena (Rosaceae). They are both obtained from fresh rose flowers. Overall, they both have the same main constituents in similar concentrations, regarding their respective SIP. Based on these similarities, both substances are intended to show similar environmental fate. Thereby, results from the experimental OECD 301F study assessing the ready biodegradability of the analogue substance Turkish Rose Absolute can be extrapolated to the registered substance.

Qualifier:

according to guideline

Guideline:

OECD Guideline 301 F (Ready Biodegradability: Manometric Respirometry Test)

Deviations:

no

Principles of method if other than guideline:

Not applicable

GLP compliance:

yes (incl. QA statement)

Remarks:

14 October 2013

Specific details on test material used for the study:

None

Oxygen conditions:

aerobic

Inoculum or test system:

activated sludge, domestic, adapted

Remarks:

Pre-conditioning consisted in aerating sludge (in mineral medium) for 5-7 days before the test and at the test temperature

Details on inoculum:

- Source of inoculum/activated sludge: The inoculum was a fresh sample of activated sludge and was collected from the aeration tank of a sewage treatment plant receiving predominantly domestic sewage.
- Sample site: Water treatment plant "STEP de Lille", 33290 Blanquefort (France).
- Laboratory culture: A filtration through a fine sieve (about 1 mm) was performed in order to remove coarse particles. After removal of any coarse particles, the sludge was washed by decantation in a mineral medium until sludge was considered free from excess substrate or inhibitor.
- Inoculum preconditioning: Pre-conditioning consisted in aerating sludge (in mineral medium) for 5-7 days before the test and at the test temperature.

Duration of test (contact time):

60 d

Initial conc.:

100 mg/L

Based on:

test mat.

Parameter followed for biodegradation estimation:

O2 consumption

Details on study design:

TEST ITEM PREPARATION:
- the test item was poorly soluble in water and in order to improve the dissolution the test item was dissolved in silicone oil AR 20 up to final concentration of 1 % v/v. Around 25 mg of test item was stirred with 2.5 mL silicone oil AR 20 by magnetically stirring until completely dissolved. Then, this solution was directly supplemented or completed into 250 mL with mineral medium and sludge directly in each test vessels.
The test medium was the mineral medium, a weakly saline aqueous medium.
The test item was tested at 100 mg/L in mineral medium containing 1 % v/v of silicone oil AR 20.

TEST CONDITIONS
- Composition of medium: Mineral medium according to OECD 301F guideline
- Test temperature: The test was performed in darkness between 22.0 to 22.5 °C (constant temperature +/- 1°C).
- Mineral medium - pH: 7.6
- Inoculum pH: 6.6
- Dissolved oxygen: 8.9 mg/L
- Suspended solids concentration: 3.47 g/L
- Continuous darkness: Yes

TEST SYSTEM
- Culturing apparatus: WTW Oxitop
- Number of culture flasks/concentration: 3 flasks (test item, silicone oil 1% and inoculum)
- Test performed in closed vessels: Yes
- A measured volume of inoculated medium containing a known concentration of the test item (100 mg/L) as the nominal sole source of Carbon, was stirred in a closed vessel at a constant temperature up to 28 days. The experiment was prolonged up to 60 days.
- Details of trap for CO2: Microbial respiration consumes O2 and releases CO2 which were absorbed by soda lime pellets present in the headspace of flasks. This produced a decrease in pressure in the flask proportional to the amount of oxygen taken up by the microbial population during biodegradation, which was expressed as a percentage of ThOD (Theoretical Oxygen Demand).
- Allowance was made for the endogenous activity of the inoculum by running parallel blanks with inoculum but without the test item. Furthermore, in order to check the procedure, a reference item control (sodium benzoate + inoculum) and a toxicity control (sodium benzoate + inoculum + test item+ silicone oil AR 20) were run in parallel. Moreover, a control with silicone oil AR 20 1% was performed to check that silicon was non toxic to bacteria and non biodegradable.
The pH of the contents was measured at the start and the end of the experiment.

CONTROL AND BLANK SYSTEM
- Inoculum blank: Yes; 3 flasks (inoculum only)
- Inoculum silicone control: 3 flasks (inoculum silicone oil AR 20 1% v/v
- Reference item: 2 flasks (Sodium benzoate and inoculum)
- Toxicity control: Yes; 2 flasks (test item, silicone oil AR 20 1% v/v, sodium benzoate and inoculum)

Reference substance:

benzoic acid, sodium salt

Preliminary study:

An elementary analysis of the test item (non GLP data) has been performed and gave the following results:
- % carbon = 79.11 and 79.11 for the measurement 1 and the measurement 2 respectively
- % hydrogen = 10.18 and 10.21 for the measurement 1 and the measurement 2 respectively
- % nitrogen = Absence for the measurement 1 and 2
- % oxygen = 10.47 and 10.59 for the measurement 1 and the measurement 2 respectively

Parameter:

% degradation (O2 consumption)

Value:

67.91

St. dev.:

0.99

Sampling time:

28 d

Parameter:

% degradation (O2 consumption)

Value:

75.04

St. dev.:

3.07

Sampling time:

60 d

Details on results:

Biodegradation of the test item:
The test item “ROSE TURKISH ABSOLUTE” contains no nitrogen according to the elementary analysis, the evaluation of biodegradation has to be based in the following expressed as ThODNH4.
The degradation for the 10-day window beginning was reached on day 2, but at the end of the 10-day window (reaching at least 60%), on day 12, the mean degradation was 48.93% following the ThODNH4, therefore the 10-day window failed.
The degradation rate of the test item “ROSE TURKISH ABSOLUTE” reached 67.91%, following the ThODNH4, after 28 days of incubation.
After 60 days, the degradation rate of the test item “ROSE TURKISH ABSOLUTE” reached 75.04%, following the ThODNH4.

Biodegradation of the Toxicity Control:
A biodegradation of 51.06% and 53.60% after 14 days of incubation was noted in the Toxicity control (containing both of the test item and the reference item) based on ThODNH4.
At the end on the test, 60 days of incubation, the results were respectively 68.49% and 72.16%.
Therefore, the test item was not inhibitory at the tested concentration on the aerobic activated sludge micro-organism because degradation was superior to 25% within 14 days (validity criterion)

Results with reference substance:

The reference item “Sodium benzoate” was degraded up to 79.68% and 81.08%( mean value: 80.38%) after 14 days (and 77.05 and 83.04% in the two replicates after 60 days of incubation at the end of the test). Therefore, it confirms the suitability of the used aerobic sludge inoculum.

Table 5.2.1/2: Percentage (%) Biodegradation during 60 days for Toxicity Control and Test item (“PYCNOGENOL”) with ThOD_NH4=1.524 mgO₂/mg Test item

Time (Days)	Tox Control		Test item
	Flask 27	Flask 28	Flask 34	Flask 29	Flask 30	Average
0	0,00	0,00	0,00	0,00	0,00	0,00
1	10,32	11,14	0,00	2,20	2,20	1,47
2	18,67	19,89	12,19	14,39	14,39	13,66
3	22,65	23,83	17,73	19,39	19,94	19,02
4	27,15	27,83	22,36	23,46	24,01	23,28
5	30,69	31,53	26,62	27,72	27,72	27,36
6	33,41	34,25	31,24	31,24	31,24	31,24
7	36,68	36,96	35,09	35,64	35,64	35,46
8	40,08	39,80	39,36	39,36	39,76	39,49
9	43,48	42,92	42,14	42,93	42,93	42,67
10	46,04	46,32	44,53	45,31	45,71	45,18
11	47,62	49,60	46,73	47,52	47,91	47,38
12	48,64	50,61	48,15	48,93	49,72	48,93
13	50,20	52,45	49,53	50,71	51,11	50,45
14	51,06	53,60	50,74	51,92	52,31	51,66
15	51,78	54,60	51,74	53,31	54,10	53,05
16	52,77	55,59	52,73	54,31	54,70	53,91
17	53,07	56,46	53,94	55,12	55,51	54,86
18	54,07	57,17	54,94	56,11	56,90	55,98
19	54,22	57,89	56,32	57,50	57,90	57,24
20	55,24	58,34	56,17	58,53	58,53	57,74
21	55,25	59,20	57,75	58,54	59,72	58,67
22	56,10	60,33	59,34	60,52	60,91	60,26
23	56,95	62,03	60,91	61,70	62,49	61,70
24	56,96	62,88	62,11	62,89	64,07	63,02
25	57,53	63,74	62,90	64,08	65,26	64,08
26	58,39	66,28	64,49	65,67	66,46	65,54
27	58,55	67,85	65,11	66,68	66,68	66,16
28	59,52	70,81	66,86	68,04	68,83	67,91
29	60,11	72,52	67,68	70,04	69,25	68,99
30	60,96	73,66	68,48	70,05	70,05	69,52
31	61,68	73,52	69,47	71,83	71,04	70,78
32	62,54	73,26	70,68	72,25	72,25	71,73
33	63,39	73,82	71,46	74,22	73,43	73,04
34	64,39	73,69	66,56	74,43	74,43	71,80
35	64,97	73,43	62,26	75,24	75,24	70,91
36	65,95	73,84	60,87	75,82	75,82	70,83
37	65,96	73,30	59,33	76,63	76,24	70,73
38	67,24	72,60	59,93	76,45	76,45	70,94
39	67,39	73,04	62,50	76,65	76,65	71,94
40	68,11	72,34	64,28	77,65	76,47	72,80
41	68,26	72,21	66,06	77,47	77,07	73,54
42	69,10	72,77	66,46	78,25	77,47	74,06
43	69,41	71,66	67,27	77,89	77,10	74,09
44	69,69	72,51	67,66	78,28	77,89	74,61
45	69,84	71,81	68,27	78,10	77,70	74,69
46	69,84	71,81	68,66	78,49	77,70	74,95
47	69,71	72,25	69,26	77,91	77,91	75,03
48	69,58	71,55	69,47	77,73	77,73	74,98
49	69,71	71,68	70,05	77,91	77,91	75,29
50	69,44	71,42	70,47	77,55	77,94	75,32
51	69,58	72,40	70,65	77,73	78,12	75,50
52	69,58	72,96	70,65	78,12	78,91	75,89
53	69,31	72,70	70,68	77,36	77,76	75,27
54	69,31	72,13	70,68	77,76	77,76	75,40
55	69,17	72,56	71,27	77,17	77,17	75,20
56	69,17	72,56	71,27	77,56	77,17	75,33
57	68,63	72,29	70,90	77,19	76,80	74,96
58	68,63	72,29	71,29	77,19	76,80	75,10
59	68,49	71,60	71,11	77,01	76,62	74,91
60	68,49	72,16	71,50	77,01	76,62	75,04

Table 5.2.1/3: Validity criteria conformity

Criteria	Validity for OECD 301F	Validity for the test
Oxygen uptake of the inoculum control in 28 days and up to 60 days	< 60 mg/L	Day 28	Day 60
		Yes	Yes
		Silicon Control 21.1 & 26.8 mg/L	Silicon Control 33.8 to 39.5 mg/L
		Control 14.1 to 22.5 mg/L	Control 22.5 to 31.0 mg/L
Variation between the test item replicates at the end of the test	< 20%	Yes (1.5%)	Yes (4.1%)
Biodegradability of the reference item within 14 days	> 60%	Yes (79.68% to 81.08%)
Biodegradability of the toxicity control within 14 days	> 25%	Yes (51.06% to 53.60%)
pH of the inoculum control at 60 days	6 to 8.5	Yes (7.4 to 8.1)

All the validity criteria were successful.

Validity criteria fulfilled:

yes

Interpretation of results:

readily biodegradable

Conclusions:

The degradation rate of the test item “ROSE TURKISH ABSOLUTE” reached 67.91%, following the ThODNH4, after 28 days of incubation and 75.04%, on Day 60.
Due to the fact that the substance is identified as an UVCB or as a complex, multi-constituent substance with structurally similar constituents, the 10-day window condition may be waived and the pass level applied at 28 days according to section 4.1.2.9.5 of CLP COMMISSION REGULATION (EU) No 286/2011 of 10 March 2011.
The test item is therefore considered to be readily biodegradable.

Executive summary:

The aim of this study was to determine the effects of the test item “ROSE TURKISH ABSOLUTE”, according to the OECD 301F guideline, ready biodegradability within an experimental period of 28 days by respirometric method. According to the study monitor’s decision, the experiment was prolonged up to 60 days.

The amount of oxygen taken up by the microbial population during the biodegradation of the test item (corrected by blank inoculum, run in parallel) was determined from the change in pressure in apparatus and will be expressed as percentage of theorical Oxygen Demand (ThOD).

Results:

Treatment	Reference item (Sodium benzoate)		Test item (“ROSE TURKISH ABSOLUTE”)
% Biodegradation at Day 28	Mean                          (Standard deviation)		66.86	Mean                     (Standard deviation)
	84.97	82.78% (3.10)	68.04	67.91% (0.99)
	80.58		68.83
% Biodegradation at Day 60	83.04	80.05% (4.24)	71.50	75.04% (3.07)
	77.05		77.01
			76.62
pH at Day 60	7.9		7.6

The degradation rate of the test item “ROSE TURKISH ABSOLUTE” reached 67.91%, following the ThODNH4, after 28 days of incubation and 75.04%, on Day 60.

Due to the fact that the substance is identified as an UVCB or as a complex, multi-constituent substance with structurally similar constituents, the 10-day window condition may be waived and the pass level applied at 28 days according to section 4.1.2.9.5 of CLP COMMISSION REGULATION (EU) No 286/2011 of 10 March 2011.

The test item is therefore considered to be readily biodegradable.

Validity criteria conformity:

Criteria	Validity for OECD 301F	Validity for the test
Oxygen uptake of the inoculum control in 28 days and up to 60 days	< 60 mg/L	Day 28	Day 60
		Yes	Yes
		Silicon Control 21.1 & 26.8 mg/L	Silicon Control 33.8 to 39.5 mg/L
		Control 14.1 to 22.5 mg/L	Control 22.5 to 31.0 mg/L
Variation between the test item replicates at the end of the test	< 20%	Yes (1.5%)	Yes (4.1%)
Biodegradability of the reference item within 14 days	> 60%	Yes(79.68% to 81.08%)
Biodegradability of the toxicity control within 14 days	> 25%	Yes(51.06% to 53.60%)
pH of the inoculum control at 60 days	6 to 8.5	Yes(7.4 to 8.1)

All the validity criteria were successful.

Description of key information

Based on a read-across from an experimental GLP study performed on the analogue substance Turkish Rose Absolute according to the OECD 301F guideline, the registered substance Turkish Rose Concrete can be regarded as readily biodegradable.

 

Key value for chemical safety assessment

Biodegradation in water:

readily biodegradable

Additional information

A study on the registered substance was not available. Therefore, in order to assess the ready biodegradability of the registered substance, the results from an experimental GLP study performed on the analogue substance Turkish rose absolute have been used.

In this study, the test item Turkish rose absolute was investigated for its ready biodegradability in a manometric respirometry test over a period of 28 days,according to the OECD 301F guideline, further extended to 60 days. The amount of oxygen taken up by the microbial population during the biodegradation of the test item (corrected by blank inoculum, run in parallel) was determined from the change in pressure in apparatus and will be expressed as percentage of theorical Oxygen Demand (ThOD).

The degradation rate of the test item reached 67.91%, following the ThODNH4, after 28 days of incubation and 75.04%, at Day 60.

The 10-day window failed but due to the fact that the substance is identified as an UVCB, the 10-day window condition may be waived and the pass level applied at 28 days according to section 4.1.2.9.5 of CLP COMMISSION REGULATION (EU) No 286/2011 of 10 March 2011.

Therefore, the test item can be considered as readily biodegradable. In addition, it has been shown that the test item was not inhibitory to aerobic activated sludge micro-organisms because the degradation was >25% within 14 days in the toxicity control.

The validity criteria were successful and the study respected the requirements of the guideline. This study was therefore considered acceptable for that endpoint and the read-across justification is provided in the related iuclid record.