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BY SREEREMYA.S
Once applied to cropland, a number of things may happen 
to a pesticide (see Figure 1 ). It may be taken up 
by plants and/or ingested by animals, insects, worms, or 
microorganisms in the soil; it may move downward 
in the soil and either adhere to soil particles or dissolve; it 
may volatilize and enter the atmosphere; it may 
be broken down into less toxic compounds by microbes 
and chemical reactions; it may be leached or 
moved out of the plant's root zone by rain or irrigation 
water filtering through the soil; or it may be carried 
away in runoff water on the soil surface or carried away 
while attached to eroding sediment.
There are three basic ways that properly 
applied pesticides may reach surface water 
and groundwater 
runoff, run-in, and leaching.
Runoff is the physical transport of pollutants 
over the soil surface by rainwater that does 
not soak into the 
soil. Pesticides move from fields while 
dissolved in runoff water or "adsorbed" 
(chemically attached) to 
eroded sediment.
Run-in is the physical transport of pollutants 
directly to groundwater. For example, this 
can occur in areas 
of Karstcarbonate (limestone) aquifers, which 
contain sinkholes and porous or fractured 
bedrock. Rain or 
irrigation water can carry pesticides through 
sinkholes or fractured bedrock directly into 
groundwater.
Leaching is the movement of pollutants 
through the soil by rain or irrigation water, as 
the water moves 
downward through the soil. Soil organic 
matter content, clay content, and 
permeability all affect the 
potential for pesticides to leach in soils.
In general, soils with moderateto-high 
organic matter and clay 
content, and moderate or slow permeability 
are less likely to leach pesticides into 
groundwater. Scientists 
believe that "macropores," which are 
principally root channels and worm holes, 
may contribute to the 
leaching of pesticides in fine-textured soils.
Pathways of pesticide loss
Pathways of pesticide loss
Pathways of pesticide loss
Pathways of pesticide loss
Pathways of pesticide loss
Pathways of pesticide loss
Pathways of pesticide loss

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Pathways of pesticide loss

  • 2. Once applied to cropland, a number of things may happen to a pesticide (see Figure 1 ). It may be taken up by plants and/or ingested by animals, insects, worms, or microorganisms in the soil; it may move downward in the soil and either adhere to soil particles or dissolve; it may volatilize and enter the atmosphere; it may be broken down into less toxic compounds by microbes and chemical reactions; it may be leached or moved out of the plant's root zone by rain or irrigation water filtering through the soil; or it may be carried away in runoff water on the soil surface or carried away while attached to eroding sediment.
  • 3. There are three basic ways that properly applied pesticides may reach surface water and groundwater runoff, run-in, and leaching.
  • 4. Runoff is the physical transport of pollutants over the soil surface by rainwater that does not soak into the soil. Pesticides move from fields while dissolved in runoff water or "adsorbed" (chemically attached) to eroded sediment.
  • 5. Run-in is the physical transport of pollutants directly to groundwater. For example, this can occur in areas of Karstcarbonate (limestone) aquifers, which contain sinkholes and porous or fractured bedrock. Rain or irrigation water can carry pesticides through sinkholes or fractured bedrock directly into groundwater.
  • 6.
  • 7. Leaching is the movement of pollutants through the soil by rain or irrigation water, as the water moves downward through the soil. Soil organic matter content, clay content, and permeability all affect the potential for pesticides to leach in soils.
  • 8. In general, soils with moderateto-high organic matter and clay content, and moderate or slow permeability are less likely to leach pesticides into groundwater. Scientists believe that "macropores," which are principally root channels and worm holes, may contribute to the leaching of pesticides in fine-textured soils.