Abstract
Considering the relevance and importance of photochemical processes in the environmental fate and behavior of organic micropollutants, the present review describes the state-of-the-art knowledge regarding the photodegradation of antifouling biocides in the aquatic environment. It includes data on photodegradation rates, primary and end photoproducts, and the pathways and mechanisms for most of the organic booster biocides (i.e., irgarol 1051, Sea-Nine 211, dichlofluanid, diuron, chlorothalonil, TCMTB, zinc and copper pyrithione, maneb, zineb, ziram, thiram, and triphenylboron-pyridine) used in antifouling paints.
Light-induced degradation took place both with direct or indirect (photosensitized) mechanisms via first-order kinetics. Direct photolysis in most cases seemed to be a minor event compared to photosensitized processes that usually enhanced the degradation. The composition of the water matrix is a key factor for the photofate of biocides in various natural waters. Half-lives ranged from a few minutes (zinc/copper pyrithiones) to several days (diuron and irgarol 1051) depending on the irradiation conditions as well as the constitution of the irradiated media. In most cases identified photoproducts were less toxic and innocuous than the parent compounds, however, the formation of more toxic compounds at the first degradation steps or synergistic effects among the transformation products should be taken into consideration.
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Abbreviations
- 3,4-DCA:
-
3,4-Dichloroaniline
- APCI:
-
Atmospheric pressure chemical ionization
- BT:
-
Benzothiazole
- CDOM:
-
Colored dissolved organic matter
- CPDU:
-
1-(3,4-Dichlorophenyl)-3,1-dimethylurea
- CuPT:
-
Copper pyrithione
- DCPMU:
-
1-(3,4-Dichlorophenyl)-3-methylurea
- DCPU:
-
1-(3,4-Dichlorophenyl)urea
- DMDC:
-
Dimethyldithiocarbamates
- DMSA:
-
N,N-Dimethyl-N′-phenyl-sulfamide
- DOM:
-
Dissolved organic matter
- DTCs:
-
Dithiocarbamates
- EBDC:
-
Ethylene(bis)dithiocarbamates
- EBIS:
-
Ethylene(bis)isothiocyanate sulfide
- EI-MS:
-
Electron impact–mass spectra
- ETU:
-
Ethylenethiourea
- EU:
-
Ethyleneurea
- FA:
-
Fulvic acids
- GC:
-
Gas chromatography
- GS26575:
-
2-Methylthio-4-tert-butylamino-6-amino-s-triazine
- HA:
-
Humic acids
- IMO:
-
International Maritime Organization
- LC:
-
Liquid chromatography
- MBT:
-
2-Mercaptobenzothiazole
- MBTS:
-
(bis)benzothiazolyl disulfide
- MEPC:
-
Marine Environment Protection Committee
- MS:
-
Mass spectrometry
- MTBT:
-
2-(methylthio)benzothiazole
- NHS:
-
Natural humic substances
- NOS:
-
Natural occurring substances
- OBT:
-
2(3H)-Benzothiazolone
- OHBT:
-
2-hydroxybenzothiazole
- PSA:
-
Pyridine-2-sulfonic-acid
- SIM:
-
Selected ion monitoring
- SPE:
-
Solid phase extraction
- TBT:
-
Tri-butyl tin
- TCMS pyridine:
-
2,3,5,6-Tetrachloro-4-(methyl sulphonyl) pyridine
- TCMTB:
-
2-(thiocyanomethylthio)benzothiazole
- TPBP:
-
Triphenylboron-pyridine
- USEPA:
-
United States Environmental Protection Agency
- UV:
-
Ultraviolet
- ZnPT:
-
Zinc pyrithione
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Sakkas, V.A., Konstantinou, I.K., Albanis, T.A. Photochemical Fate of Organic Booster Biocides in the Aquatic Environment. In: Konstantinou, I.K. (eds) Antifouling Paint Biocides. The Handbook of Environmental Chemistry, vol 5O. Springer, Berlin, Heidelberg . https://doi.org/10.1007/698_5_054
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