Environmental Engineering Reference
In-Depth Information
through the preparation of formulations, but fundamental profiles, especially for a
specific monodisperse surfactant, are not fully studied. Reduced volatilization of a
pesticide from the formulation can be explained by analogy of a very simple
organic chemical, but the actual mechanism for the pesticide is still obscure. In
contrast, from the point of view of avoiding groundwater contamination with a
pesticide, adsorption/desorption profiles in the presence of surfactants and adju-
vants have been examined extensively as well as pesticide mobility in the soil col-
umn. The basic mechanism in micelle-catalyzed hydrolysis is well known, and
theoretical approaches including the PPIE model have succeeded in explaining the
observed effects of surfactants, but its application to pesticides is also limited.
Photolysis, especially in an aqueous phase, is in the same situation. The dilution
effect in the real environment would show these effects on hydrolysis and photoly-
sis to be much less than expected from the laboratory basic studies, but more infor-
mation is necessary to examine the practical extent of the effects in an early stage
of applying a pesticide formulation to crops and soil. Many adjuvants, including
surfactants, are biodegradable in the soil environment, and thus their effects on the
biodegradation of a pesticide in soil and sediment may be limited, as demonstrated
by field trials. Not only from the theoretical but also the practical aspect, the foliar
uptake of pesticide in the presence of adjuvants has been investigated extensively
and some prediction on the ease of foliar uptake can be realized in relation to the
formulation technology. However, effect on root uptake of pesticides is to be further
investigated. In an aqueous environment more or less contaminated by various
chemicals such as detergents and their degradates, it is necessary to investigate the
effect of adjuvants on uptake, bioconcentration, and trophic transfer of pesticides
for better understanding of pesticide contamination of aquatic species in the aquatic
environment.
References
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the degree of micellar ionization by amphiphiles and the micelle-water distribution coefficient
as a function of the surfactant chain length in sodium alkyl sulfates. J Phys Chem
89:2377-2384.
Abu-Hamdiyyah A, Rahman IA (1987) Distribution coefficients of nonpolar additives and factors
determining the solubilization tendency as a function of surfactant chain length in aqueous
solution of sodium alkyl sulfates. J Phys Chem 91:1530-1535.
Abu-Zreig M, Rudra RP, Dickinson WT (2000) Influence of surfactants on leaching of atrazine
through soil columns. Toxicol Environ Chem 75:1-16.
Ahmad R, Kookana RS, Alston AM (2004) Surfactant-enhanced release of carbaryl and ethion
from two long-term contaminated soils. J Environ Sci Health 39B:565-576.
Al-Awadi N, Williams A (1990) Effective charge development in ester hydrolysis by cationic
micelles. J Org Chem 55:2001-2004.
Allen CCR, Boyd DR, Hempenstall F, Larkin MJ, Sharm ND (1999) Contrasting effects of a noni-
onic surfactant on the biotransformation of polycyclic aromatic hydrocarbons to cis -dihydro-
diols by soil bacteria. Appl Environ Microbiol 65:1335-1339.
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