Copper, [29H,31H-phthalocyaninato(2-)-N29,N30,N31,N32]-, [[3-(cyclohexylamino)propyl]amino]sulfonyl derivs.

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:

From 2017-07-20 to 2017-08-18

Reliability:

1 (reliable without restriction)

Rationale for reliability incl. deficiencies:

guideline study

Data source

Reference

Reference Type:

study report

Title:

Unnamed

Year:

2017

Report date:

2017

Materials and methods

Test guideline

Qualifier:

according to guideline

Guideline:

OECD Guideline 301 B (Ready Biodegradability: CO2 Evolution Test)

Deviations:

no

GLP compliance:

yes (incl. QA statement)

Test material

Test material information

1

Reference substance name:

Copper, [29H,31H-phthalocyaninato(2-)-N29,N30,N31,N32]-, [[3-(cyclohexylamino)propyl]amino]sulfonyl derivs.

EC Number:

309-627-7

EC Name:

Copper, [29H,31H-phthalocyaninato(2-)-N29,N30,N31,N32]-, [[3-(cyclohexylamino)propyl]amino]sulfonyl derivs.

Cas Number:

100545-46-8

Molecular formula:

C32H16-τN8Cu.(SO3)m.(SO3H)p.(C9H19N2SO2)O.(C9H20N2SO2)n

IUPAC Name:

Copper, [29H,31H-phthalocyaninato(2-)-N29,N30,N31,N32]-, [[3-(cyclohexylamino)propyl]amino]sulfonyl derivs.

Test material form:

solid: particulate/powder

Specific details on test material used for the study:

STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: Room temperature, protected from light, in the tightly closed original container

Study design

Oxygen conditions:

aerobic

Inoculum or test system:

activated sludge, domestic, non-adapted

Details on inoculum:

- Source of inoculum/activated sludge (e.g. location, sampling depth, contamination history, procedure): Municipal sewage treatment plant, 31137 Hildesheim, Germany. Activated sludge from the sewage plant at Hildesheim is well suited as it receives predominantly municipal sewage and hardly any industrial chemical waste.

- Preparation of inoculum for exposure: The activated sludge was washed twice with chlorine free tap water. After the second washing the settled sludge was resuspended in mineral salts medium and was maintained in an aerobic condition by aeration for 2 hours. Thereafter the sludge was homogenized with a blender. After sedimentation the supernatant was decanted and maintained in an aerobic condition by aeration with CO2 free air until test start (6 days). 10 mL/L of this mixture were used to initiate inoculation.

- Initial cell/biomass concentration: 4.1 x 10^7 CFU/L in the test vessel.

Duration of test (contact time):

ca. 28 d

Initial test substance concentration

Initial conc.:

ca. 19 mg/L

Based on:

TOC

Remarks:

corresponding to a carbon content of 10.7 mg C/L

Parameter followed for biodegradation estimation

Parameter followed for biodegradation estimation:

CO2 evolution

Details on study design:

TEST CONDITIONS
- Composition of medium: Mineral salts medium according to OECD 301 B / CO2 Evolution Test. The necessary amounts of ultrapure water, mineral salts medium and inoculum were placed in each incubation vessel.
- Test temperature: 20.5-24 °C

- Aeration of dilution water: 30 - 100 mL/min
- Continuous darkness: yes, Low light conditions (brown glass bottles)


TEST SYSTEM
- Culturing apparatus: Test vessels, 5000 mL, brown glass
- Number of culture flasks/concentration:
* Functional control (Sodium benzoate) : 1 replicate
* Toxicity control: 1 replicate
* Inoculum control : 2 replicates
* Test item : 2 replicates

- Method used to create aerobic conditions: The vessels were aerated for 24 h with CO2 free air. After 24 h the CO2 adsorption vessels were connected to the air outlets of the incubation vessels via a series of 3 gas wash bottles, each containing 100 mL of a 0.0125 mol/L Ba(OH)2 solution.


CONTROL AND BLANK SYSTEM
- Inoculum blank: Test medium without test and/or reference item
- Toxicity control: Test item and reference item in test concentration
- Functional control: sodium benzoate (CAS 532.32-1), purity 99.6% at 20 mg/L.

Reference substance

Reference substance:

benzoic acid, sodium salt

Results and discussion

Test performance:

The study was performed according to OECD 301 B and GLP Guidelines. The validity criteria were fulfilled according to the guideline:
• The total CO2 evolution in the inoculum control at the end of the test was 20.4 mg/L (validity criterion: < 40 mg CO2 /L after 28 days).
• The degradation of the functional control reached the pass level of  60% within 8 days (degradation: 70% on day 8).
• The differences of extremes of replicate values of removal of the test item at the end of the test was less than 20% (11% difference on day 28).
• The degradation of the toxicity control reached the pass level of 25% within 6 days (degradation: 32% on day 6).

% Degradation

Key result

Parameter:

% degradation (CO2 evolution)

Value:

ca. 15

Sampling time:

28 d

Applicant's summary and conclusion

Validity criteria fulfilled:

yes

Interpretation of results:

not readily biodegradable

Conclusions:

Under the test conditions the test item is classified as not readily biodegradable within the 28 day period of the study.

Executive summary:

The ready biodegradability of the test item was determined with a non-adapted activated sludge over a test period of 28 days in the Modified Sturm Test. The study was conducted from 2017-07-20 to 2017-08-18, according to OECD 301 B at the test facility.The test item was tested at a concentration of 19 mg/L with 2 replicates corresponding to a carbon content (TOC) of 10.7 mg C/L in the test vessels.The test vessels were incubated at low light conditions and at a temperature of 22 ± 2 °C.

The biodegradation of the test item was followed by titrimetric analysis of the quantity of CO₂ produced by the respiration of bacteria. The degradation was stopped on day 28 by acidification of the test solutions. The last titration was made on day 29 after residual CO₂ had been purged from the test solutions over a period of 24 hours. The percentage CO₂ production was calculated in relation to the theoretical CO₂ production (ThCO₂) of the test item. The biodegradation was calculated for each titration time.

 

To check the activity of the test system sodium benzoate was used as functional control. The percentage degradation of the functional control reached the pass level of 60% within 8 days and a maximum biodegradation of 95% on day 28.

 

In the toxicity control containing both test and reference item a biodegradation of 46% was determined within 14 days and it came to 53% after 28 days. The biodegradation of the reference item was not inhibited by the test itemin the toxicity control.

 

The biodegradation of the test item is shown graphically inFigure 1in comparison to the readily degradable functional control and the toxicity control. The mean of replicates reached the 10% level (beginning of biodegradation) on day 18. Both test item replicates did not reach the 60% pass level within the 28-day-period of the study. The mean biodegradation on day 28 was 15%.

Under the test conditions the test item is classified as not readily biodegradable within the 28 day period of the study.