Pesticide resistance describes the decreased susceptibility of a pest population to a pesticide that was previously effective at controlling the pest. Pest species evolve pesticide resistance via natural selection: the most resistant specimens survive and pass on their acquired heritable changes traits to their offspring.
Cases of resistance have been reported in all classes of pests (i.e. crop diseases, weeds, rodents, etc.), with 'crises' in insect control occurring early-on after the introduction of pesticide use in the 20th century. The Insecticide Resistance Action Committee (IRAC) definition of insecticide resistance is 'a heritable change in the sensitivity of a pest population that is reflected in the repeated failure of a product to achieve the expected level of control when used according to the label recommendation for that pest species'.
Pesticide resistance is increasing. Farmers in the US lost 7% of their crops to pests in the 1940s; over the 1980s and 1990s, the loss was 13%, even though more pesticides were being used. Over 500 species of pests have evolved a resistance to a pesticide. Other sources estimate the number to be around 1,000 species since 1945.
Although the evolution of pesticide resistance is usually discussed as a result of pesticide use, it is important to keep in mind that pest populations can also adapt to non-chemical methods of control. For example, the northern corn rootworm (Diabrotica barberi) became adapted to a corn-soybean crop rotation by spending the year when field is planted to soybeans in a diapause.
Pesticide resistance probably stems from multiple factors:
- many pest species produce large broods. This increases the probability of mutations and ensures the rapid expansion of resistant populations.
- pest species had been exposed to natural toxins long before agriculture began. For example, many plants produce phytotoxins to protect them from herbivores. As a result, coevolution of herbivores and their host plants required development of the physiological capability to detoxify or tolerate poisons.
- humans often rely almost exclusively on pesticides for pest control. This increases selection pressure towards resistance. Pesticides that fail to break down quickly contribute to selection for resistant strains even after they are no longer being applied.
- in response to resistance, managers may increase pesticide quantities/frequency, which exacerbates the problem. In addition, some pesticides are toxic toward species that feed on or compete with pests. This can allow the pest population to expand, requiring more pesticides. This is sometimes referred to as pesticide trap, or a pesticide treadmill, since farmers progressively pay more for less benefit.
- insect predators and parasites generally have smaller populations and are less likely to evolve resistance than are pesticides' primary targets, such as mosquitoes and those that feed on plants. Weakening them allows the pests to flourish. Alternatively, resistant predators can be bred in laboratories.
- pests with limited diets are more likely to evolve resistance, because they are exposed to higher pesticide concentrations and has less opportunity to breed with unexposed populations.
Resistance has evolved in multiple species: resistance to insecticides was first documented by A. L. Melander in 1914 when scale insects demonstrated resistance to an inorganic insecticide. Between 1914 and 1946, 11 additional cases were recorded. The development of organic insecticides, such as DDT, gave hope that insecticide resistance was a dead issue. However, by 1947 housefly resistance to DDT had evolved. With the introduction of every new insecticide class – cyclodienes, carbamates, formamidines, organophosphates, pyrethroids, even Bacillus thuringiensis – cases of resistance surfaced within two to 20 years.
- Studies in America have shown that fruit flies that infest orange groves were becoming resistant to malathion.
- In Hawaii, Japan and Tennessee, the diamondback moth evolved a resistance to Bacillus thuringiensis about three years after it began to be used heavily.
- In England, rats in certain areas have evolved resistance that allows them to consume up to five times as much rat poison as normal rats without dying.
- DDT is no longer effective in preventing malaria in some places.
- In the southern United States, Amaranthus palmeri, which interferes with cotton production, has evolved resistance to the herbicide glyphosate.
- The Colorado potato beetle has evolved resistance to 52 different compounds belonging to all major insecticide classes. Resistance levels vary across populations and between beetle life stages, but in some cases can be very high (up to 2,000-fold).
- The cabbage looper is an agricultural pest that is becoming increasingly problematic due to its increasing resistance to Bacillus thuringiensis, as demonstrated in Canadian greenhouses. Further research found a genetic component to Bt resistance.
Multiple and cross-resistance
- Multiple-resistance pests are resistant to more than one class of pesticide. This can happen when pesticides are used in sequence, with a new class replacing one to which pests display resistance with another.
- Cross-resistance, a related phenomenon, occurs when the genetic mutation that made the pest resistant to one pesticide also makes it resistant to others, often those with a similar mechanism of action.
Pests becomes resistant by evolving physiological changes that protect them from the chemical.
One protection mechanism is to increase the number of copies of a gene, allowing the organism to produce more of a protective enzyme that breaks the pesticide into less toxic chemicals. Such enzymes include esterases, glutathione transferases, and mixed microsomal oxidases.
Behavioral resistance has been described for some chemicals. For example, some Anopheles mosquitoes evolved a preference for resting outside that kept them away from pesticide sprayed on interior walls.
Resistance may involve rapid excretion of toxins, secretion of them within the body away from vulnerable tissues and decreased penetration through the body wall.
Mutation in only a single gene can lead to the evolution of a resistant organism. In other cases, multiple genes are involved. Resistant genes are usually autosomal. This means that they are located on autosomes (as opposed to allosomes, also known as sex chromosomes). As a result, resistance is inherited similarly in males and females. Also, resistance is usually inherited as an incompletely dominant trait. When a resistant individual mates with a susceptible individual, their progeny generally has a level of resistance intermediate between the parents.
Adaptation to pesticides comes with an evolutionary cost, usually decreasing relative fitness of organisms in the absence of pesticides. Resistant individuals often have reduced reproductive output, life expectancy, mobility, etc. Non-resistant individuals grow in frequency in the absence of pesticides, offering one way to combat resistance.
Blowfly maggots produce an enzyme that confers resistance to organochloride insecticides. Scientists have researched ways to use this enzyme to break down pesticides in the environment, which would detoxify them and prevent harmful environmental effects. A similar enzyme produced by soil bacteria that also breaks down organochlorides works faster and remains stable in a variety of conditions.
Integrated pest management (IPM) approach provides a balanced approach to minimizing resistance.
Resistance can be managed by reducing use of a pesticide. This allows non-resistant organisms to out-compete resistant strains. They can later be killed by returning to use of the pesticide.
When pesticides are the sole or predominant method of pest control, resistance is commonly managed through pesticide rotation. This involves switching among pesticide classes with different modes of action to delay or mitigate pest resistance. The U.S. Environmental Protection Agency (EPA) designates different classes of fungicides, herbicides and insecticides. Manufacturers may recommend no more than a specified number of consecutive applications of a pesticide class be made before moving to a different pesticide class.
Two or more pesticides with different modes of action can be tankmixed on the farm to improve results and delay or mitigate existing pest resistance.
Before glyphosate, most herbicides would kill a limited number of weed species, forcing farmers to continually rotate their crops and herbicides to prevent resistance. Glyphosate disrupts the ability of most plants to construct new proteins. Glyphosate-tolerant transgenic crops are not affected.
A weed family that includes waterhemp (Amaranthus rudis) has developed glyphosate-resistant strains. A 2008 to 2009 survey of 144 populations of waterhemp in 41 Missouri counties revealed glyphosate resistance in 69%. Weed surveys from some 500 sites throughout Iowa in 2011 and 2012 revealed glyphosate resistance in approximately 64% of waterhemp samples.
In response to the rise in glyphosate resistance, farmers turned to other herbicides—applying several in a single season. In the United States, most midwestern and southern farmers continue to use glyphosate because it still controls most weed species, applying other herbicides, known as residuals, to deal with resistance.
The use of multiple herbicides appears to have slowed the spread of glyphosate resistance. From 2005 through 2010 researchers discovered 13 different weed species that had developed resistance to glyphosate. From 2010-2014 only two more were discovered.
A 2013 Missouri survey showed that multiply-resistant weeds had spread. 43% of the sampled weed populations were resistant to two different herbicides, 6% to three and 0.5% to four. In Iowa a survey revealed dual resistance in 89% of waterhemp populations, 25% resistant to three and 10% resistant to five.
Resistance increases pesticide costs. For southern cotton, herbicide costs climbed from between $50 and $75 per hectare a few years ago to about $370 per hectare in 2014. In the South, resistance contributed to the shift that reduced cotton planting by 70% in Arkansas and 60% in Tennessee. For soybeans in Illinois, costs rose from about $25 to $160 per hectare.
During 2009 and 2010, some Iowa fields showed severe injury to corn producing Bt toxin Cry3Bb1 by western corn rootworm. During 2011, mCry3A corn also displayed insect damage, including cross-resistance between these toxins. Resistance persisted and spread in Iowa. Bt corn that targets western corn rootworm does not produce a high dose of Bt toxin, and displays less resistance than that seen in a high-dose Bt crop.
Products such as Capture LFR (containing the pyrethroid bifenthrin) and SmartChoice (containing a pyrethroid and an organophosphate) have been increasingly used to complement Bt crops that farmers find alone to be unable to prevent insect-driven injury. Multiple studies have found the practice to be either ineffective or to accelerate the development of resistant strains.
- Antibiotic resistance
- Male accessory gland
- Persistent organic pollutant
- Stockholm Convention on Persistent Organic Pollutants
- Vavilovian mimicry
- PBS (2001), Pesticide resistance. Retrieved on September 15, 2007.
- "Resistance Definition". Insecticide Resistance Action Committee. 2007. Retrieved December 2014. Check date values in:
- grapes.msu.edu. How pesticide resistance develops Archived 2007-08-17 at the Wayback Machine. Excerpt from: Larry Gut, Annemiek Schilder, Rufus Isaacs and Patricia McManus. Fruit Crop Ecology and Management, Chapter 2: "Managing the Community of Pests and Beneficials." Retrieved on September 15, 2007.
- Miller GT (2004), Sustaining the Earth, 6th edition. Thompson Learning, Inc. Pacific Grove, California. Chapter 9, Pages 211-216.
- Levine, E; Oloumi-Sadeghi, H; Fisher, JR (1992). "Discovery of multiyear diapause in Illinois and South Dakota Northern corn rootworm (Coleoptera: Cerambycidae) eggs and incidence of the prolonged diapause trait in Illinois". Journal of Economic Entomology. 85: 262–267. doi:10.1093/jee/85.1.262.
- Service, Robert F. (20 September 2013). "What Happens When Weed Killers Stop Killing?". Science. 341 (6152): 1329. doi:10.1126/science.341.6152.1329. PMID 24052282. Retrieved December 2014. Check date values in:
- Ferro, DN (1993). "Potential for resistance to Bacillus thuringiensis: Colorado potato beetle (Coleoptera: Chrysomelidae) – a model system". American Entomologist. 39: 38–44. doi:10.1093/ae/39.1.38.
- Bishop BA and EJ Grafius. 1996. Insecticide resistance in the Colorado potato beetle. In: P Jolivet and TH Hsiao. Chrysomelidae Biology, Volume 1. SBP Academic Publishing, Amsterdam.
- Daly H, Doyen JT, and Purcell AH III (1998), Introduction to insect biology and diversity, 2nd edition. Oxford University Press. New York, New York. Chapter 14, Pages 279-300.
- Marten, Gerry "Non-pesticide management" for escaping the pesticide trap in Andrah Padesh, India Archived 2007-09-28 at the Wayback Machine. ecotippingpoints.org. Retrieved on September 17, 2007.
- Doris Stanley (January 1996), Natural product outdoes malathion - alternative pest control strategy. Retrieved on September 15, 2007.
- Andrew Leonard, "Monsanto's bane: The evil pigweed", Salon.com, Aug. 27, 2008.
- Alyokhin, A.; Baker, M.; Mota-Sanchez, D.; Dively, G.; Grafius, E. (2008). "Colorado potato beetle resistance to insecticides". American Journal of Potato Research. 85: 395–413. doi:10.1007/s12230-008-9052-0.
- Janmaat, Alida F.; Myers, Judith (2003-11-07). "Rapid evolution and the cost of resistance to Bacillus thuringiensis in greenhouse populations of cabbage loopers, Trichoplusia ni". Proceedings of the Royal Society of London B: Biological Sciences. 270 (1530): 2263–2270. doi:10.1098/rspb.2003.2497. ISSN 0962-8452. PMC 1691497. PMID 14613613.
- Kain, Wendy C.; Zhao, Jian-Zhou; Janmaat, Alida F.; Myers, Judith; Shelton, Anthony M.; Wang, Ping (2004). "Inheritance of Resistance to Bacillus thuringiensis Cry1Ac Toxin in a Greenhouse-Derived Strain of Cabbage Looper (Lepidoptera: Noctuidae)". Journal of Economic Entomology. 97 (6): 2073–2078. doi:10.1603/0022-0493-97.6.2073.[permanent dead link]
- Berenbaum M (1994) Bugs in the System. Perseus Books, New York.
- Yu, S.J. 2008. The Toxicology and Biochemistry of Insecticides. CRC Press, Boca Raton.
- Stenersen, J. 2004. Chemical Pesticides: Mode of Action and Toxicology. CRC Press, Boca Raton.
- Marino M. (August 2007), Blowies inspire pesticide attack: Blowfly maggots and dog-wash play starring roles in the story of a remarkable environmental clean-up technology Archived 2008-02-18 at the Wayback Machine. Solve, Issue 12. CSIRO Enquiries. Retrieved on 2007-10-03.
- Chris Boerboom (March 2001), Glyphosate resistant weeds. Weed Science - University of Wisconsin. Retrieved on September 15, 2007
- Onstad, D.W. 2008. Insect Resistance Management. Elsevier: Amsterdam.
- Graeme Murphy (December 1, 2005), Resistance Management - Pesticide Rotation Archived 2007-10-13 at the Wayback Machine. Ontario Ministry of Agriculture, Food and Rural Affairs. Retrieved on September 15, 2007
- "Colorado Potato Beetle Damage and Life History". Archived from the original on 2011-06-06.
- Gassmann, Aaron J.; Petzold-Maxwell, Jennifer L.; Clifton, Eric H.; Dunbar, Mike W.; Hoffmann, Amanda M.; Ingber, David A.; Keweshan, Ryan S. (April 8, 2014). "Field-evolved resistance by western corn rootworm to multiple Bacillus thuringiensis toxins in transgenic maize" (PDF). PNAS. 111: 5141–5146. doi:10.1073/pnas.1317179111. PMC 3986160. PMID 24639498. Retrieved December 2014. Check date values in:
- Kaskey, Jack (June 11, 2014). "War on Cornfield Pest Sparks Clash Over Insecticide". Bloomberg News. Retrieved December 2014. Check date values in: