Pesticides vary in their effects on bees. Contact pesticides are usually sprayed on plants and can kill bees when they crawl over sprayed surfaces of plants or other areas around it. Systemic pesticides, on the other hand, are usually incorporated into the soil or onto seeds and move up into the stem, leaves, nectar, and pollen of plants.
Of contact pesticides, dust and wettable powder pesticides tend to be more hazardous to bees than solutions or emulsifiable concentrates. When a bee comes in contact with pesticides while foraging, the bee may die immediately without returning to the hive. In this case, the queen bee, brood, and nurse bees are not contaminated and the colony survives. Alternatively, the bee may come into contact with an insecticide and transport it back to the colony in contaminated pollen or nectar or on its body, potentially causing widespread colony death.
Actual damage to bee populations is a function of toxicity and exposure of the compound, in combination with the mode of application. A systemic pesticide, which is incorporated into the soil or coated on seeds, may kill soil-dwelling insects, such as grubs or mole crickets as well as other insects, including bees, that are exposed to the leaves, fruits, pollen, and nectar of the treated plants.
Pesticides are linked to Colony Collapse Disorder and are now considered a main cause, and the toxic effects of Neonicotinoids on bees are confirmed. Currently, many studies are being conducted to further understand the toxic effects of pesticides on bees. Agencies such as the EPA and EFSA are making action plans to protect bee health in response to calls from scientists and the public to ban or limit the use of the pesticides with confirmed toxicity.
Video Pesticide toxicity to bees
Classification
Insecticide toxicity is generally measured using acute contact toxicity values LD50 - the exposure level that causes 50% of the population exposed to die. Toxicity thresholds are generally set at
- highly toxic (acute LD50 < 2?g/bee)
- moderately toxic (acute LD50 2 - 10.99?g/bee)
- slightly toxic (acute LD50 11 - 100?g/bee)
- nontoxic (acute LD50 > 100?g/bee) to adult bees.
Maps Pesticide toxicity to bees
Pesticide Toxicity
Acute toxicity
The acute toxicity of pesticides on bees, which could be by contact or ingestion, is usually quantified by LD50. Acute toxicity of pesticides causes a range of effects on bees, which can include agitation, vomiting, wing paralysis, arching of the abdomen similar to sting reflex, and uncoordinated movement. Some pesticides, including Neonicotinoids, are more toxic to bees and cause acute symptoms with lower doses compared to older classes of insecticides. Acute toxicity may depend on the mode of exposure, for instance, many pesticides cause toxic effects by contact while Neonicotinoids are more toxic when consumed orally. The acute toxicity, although more lethal, is less common than sub-lethal toxicity or cumulative effects.
Sub-lethal and chronic effects
Field exposure of bees to pesticides, especially with relation to neonicotinoids, is most commonly sub-lethal. Sub-lethal effects to honey bees are of major concern and include behavioral disruptions such as disorientation, reduced foraging, impaired memory and learning, and a shift in communication behaviors. Additional sub-lethal effects may include compromised immunity of bees and delayed development.
Neonicotinoids are especially likely to cause cumulative effects on bees due to their mechanism of function as this pesticide group works by binding to nicotinic acetylcholine receptors in the brains of the insects, and such receptors are particularly abundant in bees. Over-accumulation of acetylcholine results in paralysis and death.
Colony collapse disorder
Colony collapse disorder (CCD) is a syndrome that is characterized by the sudden loss of adult bees from the hive. Many possible explanations for CCD have been proposed, but no one primary cause has been found. The US Department of Agriculture (USDA) has indicated in a report to Congress that a combination of factors may be causing CCD, including pesticides, pathogens, and parasites, all of which have been found at high levels in affected bee hives.
The development of a bee from egg to adult takes about three weeks.The queens daily laying rate will decline if contaminated materials are brought back to the hive such as pesticides.31.6% of exposed honey bees will fail to return to their colony every day while the rest will bring back contaminated pollen which in turn will not only affect the worker bees but also the queen.As a consequence there will be an upset in colony dynamics.
Colony Collapse Disorder has more implication than the extinction of one bee species; the disappearance of honeybees can cause catastrophic health and financial impacts. Honeybee pollination has an estimated value of more than $14 billion annually to the United States agriculture. Honeybees are required for pollinating many crops, which range from nuts to vegetables and fruits, that are necessary for human and animal diet.
The EPA updated their guidance for assessing pesticide risks to honeybees in 2014. For the EPA, when certain pesticide use patterns or triggers are met, current test requirements include the honey bee acute contact toxicity test, the honey bee toxicity of residues on foliage test, and field testing for pollinators. EPA guidelines have not been developed for chronic or acute oral toxicity to adult or larval honey bees. On the other hand, the PMRA (Pest Management Regulatory Agency) requires both acute oral and contact honey bee adult toxicity studies when there is potential for exposure for insect pollinators. Primary measurement endpoint derived from the acute oral and acute contact toxicity studies is the median lethal dose for 50% of the organisms tested (i.e., LD50), and if any biological effects and abnormal responses appear, including sub-lethal effects, other than the mortality, it should be reported.
The EPA's testing requirements do not account for sub-lethal effects to bees or effects on brood or larvae. Their testing requirements are also not designed to determine effects in bees from exposure to systemic pesticides. With colony collapse disorder, whole hive tests in the field are needed in order to determine the effects of a pesticide on bee colonies. To date, there are very few scientifically valid whole hive studies that can be used to determine the effects of pesticides on bee colonies because the interpretation of such whole-colony effects studies is very complex and relies on comprehensive considerations of whether adverse effects are likely to occur at the colony level.
A March 2012 study conducted in Europe, in which minuscule electronic localization devices were fixed on bees, has shown that, even with very low levels of pesticide in the bee's diet, a high proportion of bees (more than one third) suffers from orientation disorder and is unable to come back to the hive. The pesticide concentration was order of magnitudes smaller than the lethal dose used in the pesticide's current use. The pesticide under study, brand-named "Cruiser" in Europe (thiamethoxam, a neonicotinoid insecticide), although allowed in France by annually renewed exceptional authorization, could be banned in the coming years by the European Commission.
Based on a risks to bee health as identified by EFSA, in April 2013 the EU decided to restrict thiamethoxam, clothianidin, and imidacloprid. The UK voted against the ban saying it would harm food production. Agrochemical companies Syngenta and Bayer CropScience both began legal proceedings to object to the ban. It is their position that there is no science that implicates their pesticide products.
Bee kill rate per hive
The kill rate of bees in a single bee hive can be classified as:
- < 100 bees per day - normal die off rate
- 200-400 bees per day - low kill
- 500-900 bees per day - moderate kill
- > 1000 bees per day - high kill
Pesticides Formulations
Pesticides come in different formulations:
- Dusts (D)
- Wettable powders (WP)
- Soluble powders (SP)
- Emulsifiable concentrates (EC)
- Solutions (LS)
- Granulars (G)
Pesticides
Highly toxic and banned in the US
- Aldrin banned by US EPA in 1974
- Dieldrin banned by US EPA in 1974
- Heptachlor
- Lindane, BHC (banned in California). Lindane was also denied re-registration for agricultural use in the US by the EPA in 2006
EPA Proposal to Protect Bees from Acutely Toxic Pesticides in the US
The EPA is proposing to prohibit the application of certain pesticides and herbicides known toxic to bees during pollination periods when crops are in bloom. Growers routinely contract with honeybee keepers to bring in bees to pollinate their crops that require insect pollination. Bees are typically present during the period the crops are in bloom. Application of pesticides during this period can significantly affect the health of bees. These restrictions are expected to reduce the likelihood of high levels of pesticide exposure and mortality for bees providing pollination services. Moreover, the EPA believes these additional measures to protect bees providing pollination services will protect other pollinators as well.
The proposed restrictions would apply to all products that have liquid or dust formulations as applied, foliar use (applying pesticides directly to crop leaves) directions for use on crops, and active ingredients that have been determined via testing to have high toxicity for bees (less than 11 micrograms per bee). These restrictions would not replace already existing more restrictive, chemical-specific, and bee-protective provisions. Additionally, the proposed label restrictions would not apply to applications made in support of a government-declared public health response, such as use for wide area mosquito control. There would be no other exceptions to these proposed restrictions.
General Measures to Prevent Pesticides Bee Kills
Application of Pesticides at evening or night
Avoiding pesticide application directly to blooming flowers as much as possible can help limit the exposure of honeybees to toxic materials as honeybees are attracted to all types of blooming flowers. If blooming flowers must be sprayed with pesticides for any reason, they should be sprayed in the evening or night hours as bees are not in the field at that time. Usual foraging hours of honeybees are when the temperature is above 55-60 °F during the daytime, and by the evening, the bees return to the hives.
See also
- Bees and toxic chemicals
- Colony Collapse Disorder
- Neonicotinoids
- United States Environmental Protection Agency
- Pollination
- Endangered arthropod
- Pesticide misuse
- Pesticides
- Pollinator decline
- Fipronil
- Imidacloprid effects on bees
References
External links
- " Productivist Agriculture: Who wants to kill the bees?" by Henri Clément, President of the French Beekeepers' Association (UNAF)
- "Who wants to kill the bees ? (It's difficult to work it out)" by Jean-Luc Brunet, Assistant Manager of the Combined Bee Research and Environment Unit
- Honey Bees and Pesticides, 1978, Mid-Atlantic Apiculture Research and Extension Consortium
- http://ir.library.oregonstate.edu/xmlui/bitstream/handle/1957/20772/pnw591.pdf How to Reduce Bee Poisoning from Pesticides PNW 591, A Pacific Northwest Extension Publication, Washington, Oregon, Idaho, Copyright 2006, Oregon State University. Revision of the WSU 1999 version of the same publication.
- Mayer, D.F., Johansen, C.A. & Baird, C.R.; How to Reduce Bee Poisoning from Pesticides, PNW518, A Pacific Northwest Extension Publication, Washington, Oregon, Idaho, Copyright 1999 Washington State University. Includes an extensive list of toxic chemicals such as pesticides that affect bees.
- McBride, Dean k.; Protecting Honeybees From Pesticides, 1997 North Dakota State University
- Sanford, Malcolm T.; Protecting Honey Bees From Pesticides, University of Florida Institute of Food and Agricultural Sciences Extension, April 1993
- US EPA Pesticide Registration (PR) Notice 2001-5
- Bee Health: Background and Issues for Congress Congressional Research Service
- Bee Health: The Role of Pesticides Congressional Research Service
- The Xerces Society for Invertebrate Conservation
Source of the article : Wikipedia
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