Pesticide drift refers to the unintentional diffusion of pesticides and the potential negative effects of pesticide application—including, but not limited to: off-target contamination due to spray drift as well as runoff from plants/soil. This can lead to damage in human health, environmental contamination, and property damage.
With placement (localised) spraying of broad spectrum pesticides, wind drift must be minimized, and considerable efforts have been made recently to quantify and control spray drift from hydraulic nozzles. Conversely, wind drift is also an efficient mechanism for moving droplets of an appropriate size range to their targets over a wide area with ultra-low volume (ULV) spraying.
Himel (1974) made a distinction between exo-drift (the transfer of spray out of the target area) and endo-drift, where the active ingredient (AI) in droplets falls into the target area, but does not reach the biological target. Endo-drift is volumetrically more significant and may therefore cause greater ecological contamination (e.g. where chemical pesticides pollute ground water).
Herbicide volatilisation refers to evaporation or sublimation of a volatile herbicide. The effect of gaseous chemical is lost at its intended place of application and may move downwind and affect other plants not intended to be affected causing crop damage. Herbicides vary in their susceptibility to volatilisation. Prompt incorporation of the herbicide into the soil may reduce or prevent volatilisation. Wind, temperature, and humidity also affect the rate of volatilisation with humidity reducing in. 2,4-D and dicamba are commonly used chemicals that are known to be subject to volatilisation but there are many others. Application of herbicides later in the season to protect herbicide-resistant genetically modified plants increases the risk of volatilisation as the temperature is higher and incorporation into the soil impractical.
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Although there has been much public concern and research into spray drift, several studies[which?] have concluded that point source pollution (e.g. pesticides entering bodies of water following spillage of concentrate or rinsate) can cause greatest environmental harm.
- Aerial application
- Agricultural runoff
- Environmental issues with agriculture
- Environmental protection
- Farmworker justice
- Nonpoint source pollution
- Pesticide application
- "Pesticide Spray and Dust Drift". Pesticides: Topical & Chemical Fact Sheets. Environmental Protection Agency. Retrieved 25 March 2011.
- "Community Guide to Recognizing and Reporting Pesticide Problems". Community Guide to Recognizing and Reporting Pesticide Problems. CA Dept. of Pesticide Regulation. Retrieved 25 March 2011.
- Hewitt, A.J., Spray drift: impact of requirements to protect the environment, Crop Protection 19 (2000) p 623-627
- Andrew Pollack (April 25, 2012). "Dow Corn, Resistant to a Weed Killer, Runs Into Opposition". The New York Times. Retrieved April 25, 2012.
- Fabian Menalled and William E. Dyer. "Getting the Most from Soil-Applied Herbicides". Montana State University. Retrieved April 25, 2012.
- Himel, C.M. (1974) Analytical methodology in ULV. In: Pesticide application by ULV methods British Crop Protection Council Monograph No. 11, 112-119.
- Matthews G.A. (2006) Pesticides: Health, Safety and the Environment Blackwell, Oxford
- EarthJustice - health impacts of pesticide drift in rural farming community
- Pesticide Action Network North America (PANNA)- "Advancing alternatives to pesticides worldwide"
- International Pesticide Application Research Centre (IPARC)