Environmental Engineering Reference
In-Depth Information
Table 4.2 Possible harmful consequences of the application of pesticides.
Pesticides
Effects
Fungicides
Herbicides
Zoocides
Direct
Non-target microfungi
Non-target plants
Non-target insects
Occupational health effects Occupational health effects
Neurotoxic effects on animals
Occupational health effects
Indirect Mutagenicity
Soil contamination
Soil contamination
Reprotoxicity
Surface water contamination
Surface water contamination
Endocrine disruption
Groundwater contamination Groundwater contamination
Immune disruption
Mutagenicity
Mutagenicity
Reprotoxicity
Reprotoxicity
Endocrine disruption
Endocrine disruption
Immune disruption
Immune disruption
(Waters et al., 2000) listing the effects of approximately 700 substances in 30 chemical
classes on the basis of over 8,000 references from the open literature. The database
plots the profile of each compound, giving their adverse effects on different organisms
in phylogenetic order: non-mammalian tests: prokaryotes, lower eukaryotes, plants
and insects, as well as in vitro and in vivo mammalian tests. In a limited number of
cases not only mutagenicity, but also carcinogenic activity has been reported (e.g.,
dichlorvos, chlorothalonil) by IARC. Severe types of detrimental side effects include
reprotoxicity, endocrine disrupting (Keith, 1997; Anonymous, 2000) and immune-
system disrupting effects (Repetto & Baliga, 1996) of the pesticide-active ingredients
and their residues.
As for ecological consequences of pesticide usage, the majority of pesticide-active
ingredients have significant negative effects on ecosystem components such as para-
sitoids and predators (Darvas & Polgár, 1998). In addition, not only active ingredients,
but other pesticide constituents assumed to be biologically inert, such as detergents,
adjuvants, formulating agents, may exert adverse biological effects. Such was the
case of the polyethoxylated fatty acids applied as adjuvants in the formulation of the
world leading herbicide active ingredient glyphosate, showing strong synergy in their
endocrine disrupting and cytotoxic effect, in which toxicity of the adjuvant vastly
exceed that of the active ingredient (Székács & Darvas, 2012; Németh & Székács,
2012). To redress such anomalies, as of June 14, 2011, activity enhancers (adjuvants)
and safeners (antidotes) are also subject to the same regulations as pesticide-active
ingredients (Pesticide Law, 2009).
4 OUTPUT INTENSITY OF AGROCHEMICALS
Industrially developed countries tend to rely on industrialized agriculture. This results
in intensive utilization of arable lands and use of agrochemicals. Indeed, countries
with higher gross domestic product (GDP) rates and greater population density apply
 
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