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Environmental fate & pathways

Phototransformation in water

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Administrative data

Link to relevant study record(s)

Reference
Endpoint:
phototransformation in water
Type of information:
experimental study
Adequacy of study:
supporting study
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study
Study type:
direct photolysis
Qualifier:
according to guideline
Guideline:
EPA Guideline Subdivision N 161-2 (Photodegradation Studies in Water)
Deviations:
no
Qualifier:
according to guideline
Guideline:
other: BBA Guideline IV/6-1 (Aqueious Photolysis)
Deviations:
no
GLP compliance:
yes
Specific details on test material used for the study:
- Radiolabeled test substance name: 14C-XDE-795
- Label: Labeled in the 2 position of the quinoline ring
- Purity: 99+%
- Reference no. A925-161
Radiolabelling:
yes
Analytical method:
high-performance liquid chromatography
other: liquid scintillation counting
Light source:
Xenon lamp
Light spectrum: wavelength in nm:
298
Duration:
8 h
Temp.:
20 °C
Initial conc. measured:
10 mg/L
Reference substance:
yes
Remarks:
DCHQ
Dark controls:
yes
Key result
% Degr.:
27
St. dev.:
12
Sampling time:
45 min
Test condition:
298 ± 8 nm and 20°C [solvent:acetonitrile:water (80:20 v/v)]
Quantum yield (for direct photolysis):
0.012
Key result
DT50:
> 1.7 - < 22.8 h
Remarks on result:
other: The half-lives (medium values assuming normal climate conditions) were between 1.7 (June) and 22.8 h (December)
Transformation products:
yes
Remarks:
One main radio-labeled component was found which contained between 6 and 30% of the radioactivity (was not identified). A minor degradation product (1-11 % of the initial radioactivity) corresponding to 5,7-dichloro-4-hydroxyquinoline
Validity criteria fulfilled:
yes
Conclusions:
Analysis of irradiated 14C-test substance solutions indicated the presence of two main photoproducts. The major product, which accounted between 6 and 30% of the radioactivity after 8 hours irradiation, was not identified during this study. A second product, 5,7-dichloro-4-hydroxyquinoline, which accounted for 1-11% of the radioactivity after 8 hours was identified by chromatographic comparison with an analytical standard.
Executive summary:

The degree of photolytic degradation and the quantum yield of the test substance were determined by irradiation at 298 ± 8 nm at 20°C in accordance with BBA guideline IV/6-1 (aqueous photolysis). Due to the low solubility of the test substance in water, the irradiations were performed in a mixture of acetonitrile and purified, de-ionized water (80:20 v/v), after showing that the acetonitrile had no effect on light absorption. HPLC analysis showed that test substance was degraded under these conditions (between 15 and 44 % within 45 min depending on concentration and lamp intensity). The quantum yield of the photodegradation was determined to be 1.2E-2 (±19%; n = 4; independent from concentration and lamp intensity).

Additionally, 14C-test substance was irradiated under the same conditions. Samples were analyzed by radio-HPLC after irradiation times of 4 to 8 h (with different lamp intensities). Test substance accounted for 55-93% of the radioactivity and one main radio-labeled component was found which contained between 6 and 30% of the radioactivity. This degradate was not identified within this study. A minor degradation product (1-11 % of the initial radioactivity) corresponding to 5,7-dichloro-4-hydroxyquinoline was identified by chromatographic comparison with an analytical standard.

Environmental half-life periods were predicted using a computer program. The determined UV/Vis absorption coefficients and quantum yield were used as input and no dissipation processes other than photolysis were considered. The half-lives (medium values assuming normal climate conditions) were between 1.7 (June) and 22.8 h (December).

Description of key information

Half-life = 18 minutes at 40ºN summer sunlight. CFBPQ (2-chloro-10-fluoro[1]benzopyrano[2,3,4-de]quinoline) was identified as the primary photodegradate of the test substance.

CFBPQ is formed very quickly under natural conditions. Once formed there is a rapid degradation of CFBPQ to material which is polar and multicomponent in nature. When sediment is present the amount of radioactivity present in the aqueous layer is greatly reduced due to partitioning of CFBPQ to the sediment.

Key value for chemical safety assessment

Half-life in water:
18 min

Additional information