Benzophenone-based UVAs (Fig. 2) are often employed as additives because of their characteristic structure and efficient UV protection of the substrates. (Santos et al. 2012; Dobashi et al. 2005) A synthesis of QAUVAs is shown in Scheme 1. Selective monoalkylation of 2,4-dihydroxy benzophenone (I) using alkylidene dibromides led to the formation of the corresponding alkoxy bromides (2, 4, 6, 8) which on quaternization using trimethylamine furnished the water-soluble quaternary ammonium salts (3, 5, 7, 9) (Scheme 1). Monoalkylation of (I) was achieved by refluxing a mixture of (I), an alkylidene dibromide and anhydrous potassium carbonate in dry acetone. The alkylation occurred at the 4th position in benzophenone was evident from the IR absorptions at 2961 cm−1 in 2, 3016 cm−1 in 3, 3077 cm−1 in 4, 2960 cm−1 in 5, 3050 cm−1 in 6, 2945 cm−1 in 7, 3049 cm−1 in 8, 3013 cm−1 in 9 for intramolecularly hydrogen-bonded –O-H group and characteristic absorption bands at 1628 cm−1 in 2, 1624 cm−1 in 3, 1630 cm−1 in 4 and 9, 1634 cm−1 in 5, 1629 cm−1 in 6 and 8, 1638 cm−1 in 7 for the carbonyl group respectively. This is also in agreement with the earlier observation that 2,4-dihydroxy benzophenone, when reacted with epichlorohydrin gives the corresponding glycidyl ether, 2-hydroxy-4(2,3-epoxypropoxy)-benzophenone.(Manyasek et al. 1976) The monoalkylated compounds (II) were then converted into (III) by quaternization with an excess of trimethylamine in refluxing dry ethanol. After completion of the reaction, the solvent was removed under reduced pressure from the reaction mixture and the solid thus obtained was recrystallized several times from the mixture of dry acetone and methanol. Structures of all the compounds (2, 4, 6, 8 and 3, 5, 7, 9) were deduced from their UV, FTIR, PMR, 13C NMR, and elemental analyses.
Disulfoton (O,O-diethyl S-(2-(ethylthio)ethyl) phosphorodithioate), (Fig. 5), an organophosphate insecticide is shown to be a systemic poison useful against insects having sucking mouthparts. It is effective against a variety of insects including flies, aphids, and leafhoppers amongst many others. It can be applied to a wide range of crops and vegetables. (Cook 2001) Approximately 1.7 million pounds of it are used annually in the US alone, on cotton (61%), wheat (16%), variety of vegetable crops, plantation-grown Christmas trees, and home gardens.(Gianessi and Puffer 1992)
It is formulated as a granular product that is incorporated in the soil, an emulsifiable liquid that can be applied as a foliar treatment and in irrigation water, and for seed treatment of cotton. It is a systemic insecticide and is absorbed rapidly into plant tissues, conferring toxicity to many or all plant parts.(Parmar 2007) Disulfoton is one of the most photosensitive pesticides among seventy-nine pesticides commonly used all over the world.(Padalkar et al. 2014) According to literature reports, about 40% of disulfoton photodegrades rapidly on the soil to corresponding sulfoxide (Fig. 5) thus causing enormous economic losses.(Katagi 2004; Hirahara et al. 2001; Burrows et al. 2002; Gohre and Miller 1986)
The formulated pesticide alone or in the presence of a photo-protectant was irradiated in an immersion-well type of photochemical reactor. Photostabilization study of disulfoton by water-soluble QAUVAs (3,5,7,9) was carried out under irradiation from on HPMV lamp for 12 h and an analysis of the percentage recovery of disulfoton in methanol was done using HPLC. 61.80% of disulfoton was recovered when irradiated in the absence of any QAUVA which is also in agreement with the report by Hirahara et al.(Hirahara et al. 2001) The recovery of the insecticide was much higher (22.27 ~ 25.64%) when the irradiation of the insecticide was carried out in the presence of QAUVAs (n=2, 4, 6, 12) which indicates effective photoprotection provided by the QAUVAs (Fig. 6). All the four QAUVAs were found to be efficient in providing photoprotection to the insecticide with the QAUVA having n=2 to be marginally better amongst others. (Fig. 6)