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The term pollinator decline refers to the reduction in abundance of insect and other animal pollinators in many ecosystems worldwide beginning at the end of the twentieth century, and continuing into the present day.
Pollinators participate in sexual reproduction of many plants, by ensuring cross-pollination, essential for some species, or a major factor in ensuring genetic diversity for others. Since plants are the primary food source for animals, the reduction of one of the primary pollination agents, or even their possible disappearance, has raised concern, and the conservation of pollinators has become part of biodiversity conservation efforts.
- 1 Consequences
- 2 Increasing public awareness
- 3 Possible explanations
- 4 The structure of plant-pollinator networks
- 5 Solutions
- 6 See also
- 7 References
- 8 Further reading
- 9 External links
60 to 80% of the world’s flowering plant species are animal pollinated, and 35% of crop production and 60% of crop plant species depend on animal pollinators. It is commonly said that about one third of human nutrition is due to bee pollination. This includes the majority of fruits, many vegetables (or their seed crop) and secondary effects from legumes such as alfalfa and clover fed to livestock.
In 2000, Drs. Roger Morse and Nicholas Calderone of Cornell University attempted to quantify the effects of just one pollinator, the Western honey bee, on only US food crops. Their calculations came up with a figure of US $14.6 billion in food crop value. In 2009, another study calculated the worldwide value of pollination to agriculture. They calculated the costs using the proportion of each of 100 crops that need pollinators that would not be produced in case insect pollinators disappeared completely. The economic value of insect pollination was then of €153 billion.
Increasing public awareness
There are international initiatives (e.g. the International Pollinator Initiative (IPI)) that highlight the need for public participation and awareness of pollinator, such as bees, conservation 
Studies have linked neonicotinoid pesticide exposure to bee health decline. These studies add to a growing body of scientific literature and strengthen the case for removing pesticides toxic to bees from the market. Pesticides interfere with honey bee brains, affecting their ability to navigate. Pesticides prevent bumble bees from collecting enough food to produce new queens.
Neonicitinoids are highly toxic to a range of insects, including honey bees and other pollinators. They are taken up by a plant’s vascular system and expressed through pollen, nectar and guttation droplets from which bees forage and drink. They are particularly dangerous because, in addition to being acutely toxic in high doses, they also result in serious sub-lethal effects when insects are exposed to chronic low doses, as they are through pollen and water droplets laced with the chemical as well as dust that is released into the air when coated seeds are planted. These effects cause significant problems for the health of individual honey bees as well as the overall health of honey bee colonies and they include disruptions in mobility, navigation, feeding behavior, foraging activity, memory and learning, and overall hive activity.
A French 2012 study of Apis mellifera (western honey bee or European honey bee) that focused on the neonicotinoid pesticide thiamethoxam, which is metabolized by bees into clothianidin, a pesticide cited in legal action, tested the hypothesis that a sub-lethal exposure to a neonicotinoid indirectly increases hive death rate through homing failure in foraging honey bees. When exposed to sub-lethal doses of thiamethoxam, at levels present in the environment, honey bees were less likely to return to the hive after foraging than control bees that were tracked with Radio-Frequency Identification (RFID) tagging technology, but not intentionally dosed with pesticides. Higher risks are observed when the homing task is more challenging. The survival rate is even lower when exposed bees are placed in foraging areas with which they are less familiar.
In their 2014 study of Bombus terrestris (buff-tailed bumblebee or large earth bumblebee), researchers tracked bees using RFID tagging technology, and found that a sub-lethal exposure to either imidacloprid (a neonicotinoid) and/or a pyrethroid (?-cyhalothrin) over a four-week period caused impairment of the bumble bee's ability to forage.
Imidacloprid effects on bees were examined by researchers exposing colonies of bumble bees to levels of imidacloprid that are realistic in the natural environment, then allowed them to develop under field conditions. Treated colonies had a significantly reduced growth rate and suffered an 85% reduction in production of new queens compared to unexposed control colonies. The study shows that bumble bees, which are wild pollinators, are suffering similar impacts of pesticide exposure to "managed" honey bees. Wild pollinators provide ecosystem services both in agriculture and to a wide range of wild plants that could not survive without insect pollination.
In March, 2012, commercial beekeepers and environmental organizations filed an emergency legal petition with the U.S. Environmental Protection Agency (EPA) to suspend use of clothianidin, urging the agency to adopt safeguards. The legal petition is supported by over one million citizen petition signatures, targets the pesticide for its harmful impacts on honey bees. The petition points to the fact that the EPA failed to follow its own regulations. EPA granted a conditional, or temporary, registration of clothianidin in 2003 without a field study establishing that the pesticide would have no "unreasonable adverse effects" on pollinators. The conditional registration was contingent upon the submission of an acceptable field study, but this requirement has not been met. EPA continues to allow the use of clothianidin nine years after acknowledging that it had an insufficient legal basis for initially allowing its use. Additionally, the product labels on pesticides containing clothianidin are inadequate to prevent excessive damage to non-target organisms, which is a violation of the requirements for using a pesticide and further warrants removing all such mislabeled pesticides from use.
Rapid transfer of parasites and diseases of pollinator species around the world
Increased international commerce has moved diseases of the honey bee such as American foulbrood and chalkbrood, and parasites such as varroa mites, acarina mites, and the small African hive beetle to new areas of the world, causing much loss of bees in the areas where they do not have much resistance to these pests. Imported fire ants have decimated ground nesting bees in wide areas of the southern US.
Loss of habitat and forage
Researchers at the University of Virginia have discovered that air pollution from automobiles and power plants has been inhibiting the ability of pollinators such as bees and butterflies to find the fragrances of flowers. Pollutants such as ozone, hydroxyl, and nitrate radicals bond quickly with volatile scent molecules of flowers, which consequently travel shorter distances intact. There results a vicious cycle in which pollinators travel increasingly longer distances to find flowers providing them nectar, and flowers receive inadequate pollination to reproduce and diversify. 
Changes in seasonal behaviour due to global warming
In 2014 the Intergovernmental Panel on Climate Change reported that bees, butterflies and other pollinators faced increased risk of extinction because of global warming due alterations in the seasonal behaviour of species. Climate change was causing bees to emerge at different times in the year when flowering plants were not available.
The structure of plant-pollinator networks
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Wild pollinators often visit a large number of plant species and plants are visited by a large number of pollinator species. All these relations together form a network of interactions between plants and pollinators. Surprising similarities were found in the structure of networks consisting out of the interactions between plants and pollinators. This structure was found to be similar in very different ecosystems on different continents, consisting of entirely different species.
The structure of plant-pollinator networks may have large consequences for the way in which pollinator communities respond to increasingly harsh conditions. Mathematical models, examining the consequences of this network structure for the stability of pollinator communities suggest that the specific way in which plant-pollinator networks are organized minimizes competition between pollinators and may even lead to strong indirect facilitation between pollinators when conditions are harsh. This makes that pollinator species together can survive under harsh conditions. But it also means that pollinator species collapse simultaneously when conditions pass a critical point. This simultaneous collapse occurs, because pollinator species depend on each other when surviving under difficult conditions.
Such a community-wide collapse, involving many pollinator species, can occur suddenly when increasingly harsh conditions pass a critical point and recovery from such a collapse might not be easy. The improvement in conditions needed for pollinators to recover, could be substantially larger than the improvement needed to return to conditions at which the pollinator community collapsed.
Conservation and restoration
Efforts are being made[when?][where?] to sustain pollinator diversity in agro and natural eco-systems by some environmental groups[who?]. Prairie restoration, establishment of wildlife preserves, and encouragement of diverse wildlife landscaping rather than mono culture lawns, are examples of ways to help pollinators.
In June 2014 the Obama administration published a fact sheet "The Economic Challenge Posed by Declining Pollinator Populations", which stated that "President’s 2015 Budget recommends approximately $50 million across multiple agencies within USDA to [...] strengthen pollinator habitat in core areas, double the number of acres in the Conservation Reserve Program that are dedicated to pollinator health [...]".
The Obama administration's 2015 Budget also recommended to "enhance research at USDA and through public-private grants, [...] and increase funding for surveys to determine the impacts on pollinator losses".
Smartbee is a European research project of 16 entities (universities, research institutions and companies) funded by the EU, headquartered in Berlin. Its goal is to elicit causes of resistance to CCD, develop breeding to increase CCD resistance and to counteract the replacement of many native European bees with only two specific races. 
CoLOSS (Prevention of honey bee COlony LOSSes) is an international, non-profit association headquartered in Bern, Switzerland to "improve the well-being of bees at a global level", composed of researchers, veterinarians, agriculture extension specialists, and students from 69 countries. Their 3 core projects are standardization of methods for studying the honey bee, colony loss monitoring and B-RAP (Bridging Research and Practice)
The decline of pollinators is compensated to some extent by beekeepers becoming migratory, following the bloom northward in the spring from southern wintering locations. Migration may be for traditional honey crops, but increasingly is for contract pollination to supply the needs for growers of crops that require it.
- Bees and toxic chemicals
- Endangered arthropod
- Imidacloprid effects on bee population
- Pesticide toxicity to bees
- Regent (insecticide)
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