Abstract
Climate change, an emerging global worry to farming in many countries and it is the most discussed topic in many forums as it affects the many livelihoods including human beings. Many weather affecting the different forms of life including hexapods by impacting in hexapod fecundity, habit, habitat, behavior, endurance, mobility, generation’s asynchrony between plants and pests, altered inter-specific interaction, increased hexapod vectored diseases and reduce the effectiveness of natural enemies. The global warming is also threatening overall food production any country by way of shifting hosts, moving to higher elevation, minor pests becoming major pests and increased invasiveness due to trade of different agricultural commodities. Many of the insect-pests are affecting hosts plants including vegetables as most of the insect are polyphagous in nature, they easily shift from one crop to other crop irrespective of cereals, pulses, vegetables and fruit crops there by damaging host plant and in turn reducing the productivity. Before we deal with different management strategies there is wide concern to address the climate change effects on the hosts as well environment as whole.
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14.1 Introduction
A regular swelling in the average heat of the Earth’s troposphere and its oceans is termed as climate change and a transformation that is thought to be altering the Earth’s weather endlessly. The overall temperature of the world has been progressively escalating from 1900 along with arise of approximately 1 °C. The highest upsurge has been observed in America, but in India’s the raise in temperature was between 0.2 °C and 1 °C.Likewise, the rate at which globe is heating was increasing; in the last 50 years the temperature increase was twice as compared to the last 100 years. The average temperature from July to October season (Kharif) and November to March season (rabi), in India is expected to augment up to 1.7 °C and 3.2 ° C respectively along with anticipated increase of 10% in precipitation by year 2070 (Gupta 2011).
The dialogue of the fast few decades remains the climate change. Due to variations in climatic aspects viz., temperature, rainfall, relative humidity and other meteorological gears will have impact on the superiority and amount of crop produce. Climate change is intimidating worldwide food production through straight effects in agricultural productivity and insect-pest and disease associated losses of crop plants. Every notch increase in temperature might cause 10–25% crop losses from insect pests. Intergovernmental Panel on Climate Change (IPCC 2007), defined it as “Change in climate over time, either due to natural variability or as a result of human activity”. Over the last 50 years the maximum of global warming reported is due to the anthropological actions, as described by IPCC. The increase in the temperature of globe is the consequence of the greater greenhouse effect, triggered due to the higher concentrations of greenhouse gasses (GHG) viz. Chlorofluorocarbon (CFC), Methane (CH4), Carbon-dioxide (CO2) and Nitrous oxide (N2O) in the surrounding environment. Over last 10 decades, the carbon-dioxide concentration in the atmosphere has gone up radically from280 ppm to 370 ppm and by 2100 it is expected to be doubled. According to IPCC (2007), temperature of globe has amplified by 0.6 + 0.2 °C and is predicted to attain 1.1–5.4 °C over the end of century. IPCC explains if 2 °C temperatures increase over the subsequent 100 years, then undesirable global warming effects might start to spread to maximum areas of the globe and it might straightly disturb many of the earth’s living organisms. Global warming with increase in temperature and carbon dioxide along with climate variability of the environment may have numerous consequences in agricultural sector viz. change in precipitation pattern, extended period of drought and reduced crop production due to minor insects becoming major insect.
The climatic conditions which regulate much of the natural and agro-ecological systems during the season and species diversity in that particular area. In agro-ecological system, weather disturbs quality of crop and its harvest, as the insect pests and diseases were managed by natural enemies; the management practice that mainly ignored (De Bach 1964). The preceding valuation report from the IPCC forecasts, by the year 2100 an augmentation in 1.1 to 5.4 °C mean temperature (Meehl et al. 2007).
14.2 Vegetables in Climate Change Scenario
Vegetables are considered as defensive food as they source vital vitamins, nutrients and minerals to the human lives and are the greatest source for killing micronutrient insufficiencies. The universal production of vegetables has doubled over the last 25 years and the worth of international trade in vegetables now surpasses that of cereals. In Asia, produces are maximum in the eastern side where the weather is predominantly sub-temperate and temperate. India is the second major producer after China in the world in vegetables production with17.3 t/ha and 22.5 t/ha respectively. In the last20 years, the olericulture production in India has been amplified 2.5 times. Vegetables are more succulent (have 90% water) and are usually more delicate to weather extravagances (Solankey et al. 2019), so therefore higher temperature along with inadequate moisture in soil remain the chief reasons of reduced harvests because they significantly disturb many biochemical and physiological developments like decreased photo synthesis, enzymatic and metabolic transformation, hot air wound to the vegetable plant tissues, reduction in pollination and ultimately reduced fruit set.
The implications of the changes in climate seriously hit the vegetable production. Under the shifting climatic circumstances failure of crops, reduction in yields and quality along with higher incidence of insect pest and disease complications are natural and they tend to the vegetable farming a loss-making enterprise. Thus, eventually questions the accessibility of nutrient source in man’s food. The South Asian seasonal monsoon will be arriving lately or becoming uncertain and that temperature upsurges will be dominant during the winter period. The disappointment of the reduced rains fallouts in shortage of water, ensuing in lesser average harvest of the crop. It is very much predominant in the many droughts hit areas viz. Rajasthan, northern Karnataka, eastern and southern Maharashtra Andhra Pradesh and Orissa. In the states like Karnataka, Andhra Pradesh and Tamil Nadu a high temperature along with insufficient precipitation at the sowing time and severe shower at the time of crop harvesting cause high crop losses.
The proportion of increase in minimum temperature throughout the Rabi season is significantly larger than in rainy season. The maximum temperature presented growing yearly in rainy season crop and rabi crop time periods nonetheless substantial increase was detected from 2000 year onwards. Ahead and noteworthy undesirable precipitation movements were detected many states of India. In spite of having a straight consequence on rain fed vegetable production, climate change disturbs water storage and water availability for irrigation. As the accessibility of water is partial, drought will become the foremost stress issue to vegetable growing, more stressing farming systems. Climate change happens to be the utmost important reason of biodiversity damage over the next 100 years, which causes fluctuations in species phenology, distributions and ecological interactions in the environment. For instance, most vegetable crops like Cole crops, onion and root crops are fertilized by insects as changes in pollinating insect species viz. honey bees, syrphids distribution will affect the pollination there by reducing the yield. Forays of agricultural crops by weeds can be additional big problem. Post-harvest value of vegetables was disturbed by seasonal variations may be by heavy yield losses, affect safety of food storage throughout storage period, by instigating fluctuations in fungi populations which are producing aflatoxin. The recurrent extreme weather actions under climate change might harm infrastructure, with destructive effects on storage and dispersal of vegetables. Along with the physiological and biochemical changes, climate change may impact the insect pest and disease incidence, host-pathogen interactions, distribution and biology of insects, time of appearance in cropping season, movement to new locations and their hibernating capacity. Growth and expansion of plant diseases largely depends on environment prevailing about the host and pathogen and a modification in the constituents may impact host vulnerability and therefore host, parasitoid and parasite relationship. Overall, global climate change has the capacity to change plant composition, mechanism of resistance and to modify expansion of the pathogen. Many other significant factors manipulating diseases in vegetable plant are air contamination, predominantly UV-B radiation and ozone along with nutrient accessibility.
14.3 Insect-Pests and Climate Change
Insects-pests which belong to arthropods are coldblooded which means they change the temperature of their bodies is roughly similar to the surrounding environment. So, the most important ecological factor affecting insect/hexapod development, behavior, dispersal, existence, and reproduction is undoubtedly the temperature. The carbon-dioxide emitted by anthropogenic activities is almost twice more important for temperature rise than other greenhouse gases altogether. Even though, augmented CO2 would not straightly affect hexapods, the temperature surges determined by the intensification in CO2 by human activities will affect the hexapods in their phenology, dispersal, nourishment and as a disease carrying vectors.
14.3.1 Crop Production Influenced by Climate Change in Three Ways
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Fluctuations in precipitation, temperature and carbon dioxide stages directly on the host plant growth and well-being.
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Indirect consequence on plant well-being via climatic persuaded fluctuations in plant and competitor circulation along with species richness.
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Consequence on host plant well-being indirectly via deviations in advanced food chain communications of predators, parasitoids and competitors on plants and/or competitor dispersal along with richness.
The above-mentioned fluctuations in global temperature have radical impact on the financial system of farm oriented, biodiversity prosperous country like Republic of India. The global temperature raises is projected to have remarkable implications on numerous species on the earth (Table 14.1). The sign of a reply to long-term ecological trends, directly or indirectly connected to current global warming are remarkably quick and many fold particularly in insect species. It comprises movement towards northern and altitudinal in topographical choice, increased sum of generations for insect species especially in multivoltine, improved cold persistence along with extended hibernations. The climate change estimated patterns will contain manifold collaborative undeviating properties on the functioning herbivores and plant species as well. The ecological factors manipulating crop phenology like blossom bud maturation, strength in blossoming, period of development, produce of the crop laterally with superiority, insect pests, diseases occurrence, physiological ailments that might deliver whichever destruction of conventional places or ensure additional places becoming possible for farming of these crops, in all these ways the climate change looked to have obstructed. The communications between host plant and herbivores are manipulated by climate change in so many ways. To cite a few, the expected ecological fluctuations in CO2concentrations, raincloud cover, temperature, nutrient and water accessibility will disturb host plant vulnerability to plant feeders (Johnson and Lincoln 1991). The herbivores dietary necessities, growth time and hibernation survival will directly be influenced by climate change (Solbreck 1991). Indirectly the herbivores will involve variations in foodstuff in addition to the above impacts. There will be occasional penalty at the stage of populations, niche, ecosystem and communities due to modification in nature and strength of various plant herbivore exchanges induced by climate change. The progress might constitute the capability of numerous cultivators of temperate nuts and fruits to fruitfully yield the similar quantity as in the history.
14.3.2 Directs Effects of Climate Change on Insect-Pests
14.3.2.1 Effect on Population Growth Rate
The temperature can put for the diverse effects due to the different developmental stages of hexapods. Species with soaring thermal acceptance will carry out superior during harsh and recurrent extreme temperature events than other species (Burgi and Mills 2010). In tropical and subtropical regions, the temperature increases inside certain favorable ranges speed up the growth rates, multiplication and existence of hexapods. Thereupon, hexapods might be competent in finishing a higher cycles per year and eventually resulting in additional yield losses (Bale and Hayward 2010). In recent times, it was clearly observed in case of pests like Aphids and plant hoppers. Pandi et al. (2018) projected that for every 2 °C rise in temperature, hexapods will enhance one to five extra cycles in development per planting season. In addition to sucking pests, elevated temperature benefits some lepidopterans in number of ways by escalating their flight, thus leading to increased mating accomplishment and egg laying and eventually larger brood expansion. Elevated CO2 and temperature will increase activities of enzymes (e.g. midgut proteases, carbohydrates, and mitochondrial enzymes) and metabolic rates which in turn may guide to increased number of generations of insect pests (Akbar et al. 2016). Shrestha (2019) reported that insect causing yield losses could increase for every additional degree of temperature increase it would rise by 10–25%additionally.
14.3.2.2 Effect on Migrating Behavior and Habitat Ranges
Hughes et al. (2003) reported that rise in temperature likely to vigor the insect species to change their dispersals by intensifying into the newer zones of climate and by vanishing from places that have developed inappropriate climatically. Increasing temperatures will allow hexapod pests to transfer from subtropical and tropical areas to colder or temperate areas at increased elevations laterally with modifications in farming places host plant. Parry and Carter 1989 predicted that for every 1 °C increase in temperature might spread dispersal of insects140 km upwards in elevation or 200 km north. This is clearly indicating that global warming will cause more crop yield losses in temperate countries due to the expansion of insect range. At the same time, it makes them as vulnerable places for introduction of new invasive pests having potential threats to their agro ecosystems. Insect pests which increase its main host range outside those of their major predators and parasitoids potentially escaping biological pest control and may cause outbreaks. In near future, it is unfortunate to note that because of short life cycle and increased fighting ability of sucking insects, viral diseases may become prevalent and cause severe crop losses to farmers (Sharma et al. 2005). Several modeling studies predicted the range expansion of forest as well as agricultural insect pests. Few examples are given below. Global warming consequential heights wise host series enlargement and augmented hibernating existence of Heliothis zea (maize earworms) and cob worm Helicoverpa armigera might result in hefty decrease in crop yield and present chief obstacle for insect pests’ management in corn (Diffenbaugh et al., 2008). Increase in temperature will let the unfriendly pink bollworm, Pectinophora gossypiella (Lepidoptera: Gelechiidae), to increase the appetite on cotton interested in previously unreceptive parts effected by substantial ices and harm percentage might rise through-out the existing areas (Gutierrez et al. 2006). The northward expansion of southern pine beetle, Dendroctonus frontalis, has stayed associated to upgraded circumstances for hibernating beetles may be in larval or adults’ stages (Williams and Liebhold 2002).
14.3.2.3 Effect on Overwintering or Resting Periods
Hexapods undertaking hibernation are probable to have the experience the important thermal variations in their environment (Bale and Hayward 2010). Faster biological activity at advanced temperatures reduces the time period required for hexapod diapause that may be by faster reduction of stockpiled nutrient possessions. In winter, the global warming might postponement in beginning and initial summer season may help in quicker end of overwintering in hexapods, which can at that point recommence their vigorous development. Lower winter mortality of hexapods owing to hot midwinter temperatures might be significant in raising hexapod inhabitants (Hahn and Denlinger 2007). A warm, dry winter will aid aphid survival and increase population in wheat. The pupae of Helocoverpa armigera could emerge up to 7 days earlier from winter diapause when temperatures increase (Ouyang et al. 2016).
14.3.2.4 Effect on Abundance and Biodiversity
The comparative richness of different hexapods species might alter quickly owing to changes in climate, and the insect species incapable of withstanding the traumas might be vanished in the coming times (Jump and Penuelas 2005). As temperature increases, the species present in mountains or high latitudes are likely to be affected more comparatively to lower altitude and they will be enforced to modify their innate places to further advanced altitudes. Nonetheless, still if they are clever to transfer, they will ultimately run out of livable ranges and may unavoidably get destroyed. In addition to temperature, significant variations in precipitation will have a main effect on the richness and of diversity of insects. Severe shower may decrease the occurrence of sucking insect pests like thrips, aphids, leaf hoppers and whiteflies. Aberrant weather events cause the outbreak of insect pests for example, red hairy caterpillar outbreak may be seen due to heavy and frequent rains and extended dry spells followed by heavy precipitation reasons the epidemic of cutworm’s pests (Sardana and Bhat 2016).
14.4 Indirect Effects of Climate Change on Insects through Host Plants
14.4.1 Effect on Host Plant and Insect Pest Synchrony
Normally, the natural timing of the insect lifecycle synchronizes with the lifecycle of the plants on which they feed. However, climate change has caused mostly negative consequences from the increasing asynchrony in ecological systems, due to variation in the phenological responses of insects and their host plants (Vissers and Holleman 2001). Many insect species feeding on specific plants will face pressure to adapt as the plants on which they feed undergo changes in their growth cycle. Consequently, predictable response in hexapods could comprise an advance in period for adult and larval emergence and upsurge in span of flying time (Menéndez 2007). Asynchrony in phenology of winter moth (Operophtera brumata, Lepidoptera: Geometridae) with its wood host Oak tree where moth eggs gamble with their own lives by hatching early (Van Asch and Visser 2007). It was observed the egg masses laid in 23 of 30 by the bay checker spot butterfly Euphydrya seditha (Lepidoptera: Nymphalidae) were emerged later the plants (Plantago and Castilleja) had gone through ageing, thereby none of the larvae from these batches attained the third instar stage (Singer and Parmesan 2010).
14.4.2 Effect of Increased CO2 on Host Plants
Lamarche et al., 1984 believed that increased atmospheric CO2 associated with global warming could stimulate plant growth because of increased photosynthesis rate of most of C3 plants, thus increasing the amount of food available which scientist originally believed that swelling carbon dioxide concentration might be an answer for global nourishment. Regrettably, these hopeful forecasts have not established precise. One motive for this is that hexapods also plague higher when florae are raised in higher levels of CO2 owing to poor nutritious superiority of host plant. According to the “Nutrition compensation hypothesis,” raised CO2concentrations can disturb indirectly the growth fitness of plants by altering the nutritive value of host plants. It had negative effects on insects by diluting the nitrogen in leaf tissues by 15–25% and increases the C: N ratio due to buildup of non-structural sugars (Lincoln et al. 1993). Insects especially chewing insects such as moths and butterflies may revealed to reply this proportion by accelerating eating in order to achieve the metabolic requirements for nitrogen to derive more amino acids called “compensatory feeding”. However, xylem and phloem eating hexapods such as the hemipterans may be least exaggerated by raised CO2 levels (Petzoldt and Seamann 2010). After investigating the effects of elevated CO2 on many lepidopteran pests, several studies revealed that it lengthy larval and pupal period and reduced pupation rate and pupal mass. It also resulted in increased relative consumption rate, decreased efficiency of conversion of ingested as well as digested food and low relative growth rate. It has been designated that raised CO2, increased 22% abbreviated tannins, 19% phenols, and 27% flavonoids whereas terpenoids nitrogen based secondary metabolites decreased by 13% and 16%, respectively (Robinson et al. 2012). Under elevated CO2 (> 550 ppm) augmented digestibility, and reduced effectiveness of alteration of swallowed diet into body matter have been documented in four consecutive cycles of caster semilooper, Archaea janata (L.) under raised CO2 (Srinivasa Rao et al. 2013). Higher activity of digestive and mitochondrial enzymes thereby increased rate of consumption of Helicoverpa armigera was observed by Akbar et al. (2016). Chen et al. (2004) reported that increase in population of Sitobion avenae (wheat aphid): Prasannakumar et al. (2012) on Nilaparvata lugens (Brown Plant Hopper) while Sudderth et al. (2005) on Macrosiphum euphorbiae (Potato aphid) due to higher CO2 levels.
14.4.3 Increased Temperature and Insect-Pests
Many effects of augmented temperature on hexapod routine have to do with the straight effects on insects due to temperature. As hexapods are exothermal, in warmer circumstances the insects incline to be more energetic. It is projected that for every 2° C temperature upsurge hexapod will have one to five added life sets in every season. The dietary quality host plants in will be increased due to higher photosynthetic activity as increase in temperature raises. It has been revealed that, to improve the plant feeding by hexapods indirectly by altering the development probability of host plants, which turn lead to the epidemic of insect pests in that area (Visser and Both 2005).
In few insects like thrips the gender percentages may be altered by temperature possibly affecting parthenogenic speed. Hexapods which devote significant time of their life cycle on the earth may be additionally exaggerated by temperature variations than individuals that are just above soil just for the reason that soil offers a protecting intermediate that determine or incline to shield temperature variations more than the air. Lesser winter death of hexapods due to warmer winter temperatures might be significant in swelling insect inhabitants. With higher latitude and altitude, the hexapods species variation per area leans towards to decline, indicating that increasing temperatures could consequence in higher hexapod species feeding a greater number of hosts plants in temperate weathers. In addition to above the production of plant secondary metabolites and some other plant distrustful characters will be affected and may become vulnerable to insect attack. Further, some other studies have revealed the contrary effects of raised temperature on plants, together with altered developing time period and enlargement in the usage of plant possessions for other plant feeders. Zhang et al. (2018) observed the noteworthy reduction in the larval period, pupal period of Spodoptera litura nourished on soybean raised in elevated temperature in divergence to ambient temperature. Primary start of invasion by Helicoverpa armigera in pulses and cotton in North areas of India may be due to reduced host defenses as a result of temperature stress (Sharma et al. 2005).
14.4.4 Precipitation Pattern and Insect-Pests
Under the changing climatic conditions early and appropriate sowing become more ambiguous. For example, with temperature and rainfall variations can influence hexapod pest parasitoids, predators and diseases ensuing in a multifaceted effect. Spores of fungus affecting hexapods are influenced by high relative humidity and their occurrence would be augmented by changes climate which increase time of high relative humidity and decreased by those individuals that lead to drier situations. Most of the smaller sized insects are delicate to rainfall and are get murdered or detached from host plants under heavy precipitation, and the deliberation is significant during selecting proper management practices for onion thrips.
14.4.5 Combined Effect of Elevated CO2 and Temperature on Insect-Pests
Overall, the herbivores cultivated in raised carbon dioxide are lesser nourishing to hexapod herbivores, as they might affect their behavior and performance. Physical appearance of host-plant deviates characteristically make foliage material plagued by hexapods which less healthy. As a result of this the hexapods have a more problematic time altering the nutrition they eat into biomass. To alleviate the diet which is of less nutritive, hexapod herbivores frequently eat higher quantity. Zvereva and Kozlov (2006) assessed that the level of nitrogen concentration in plants is decreased both under higher CO2 and higher temperature conditions.
In plants the ratio of carbon and nitrogen was increased under raised temperature and CO2 conducts, nonetheless the organic carbon related minor composites did not display an important reply to intensifications in any of the temperature and CO2. It was also reported that plant feeder act in relations to existence, growth of rate, pupal weight and egg laying were undesirably exaggerated by higher CO2 unaided, but then again definitely exaggerated by raised temperature; when studied concurrently, as two features had none of the evidences on the hexapod act (Cornelissen 2011). Antixenotic properties possessed by plants may also protect automatically, may be possessing hard leaf surfaces or by possessing leaf hair, scales, trichomes like structures on it.
The increased carbon dioxide led to better success of natural enemies praying upon the their pray as it is more visible. As the hexapods have more life cycle stages and typically take more time to develop, so that they are more visible in time to the attack of natural enemies. Higher leaf damage and frass production due to increased consumption rates are also the signals to natural enemies. However, recent studies observed detectable variation in insect population due to the interactive effect of elevated CO2 and temperature. Pandi et al. (2018) observed that elevated CO2 and temperature had showed encouraging effect on brown plant hopper reproduction, increasing its inhabitants (55.2 ± 5.7hoppers/hill) in contrast to normal carbon dioxide and temperature (25.5 ± 2.1 hoppers/hill). In a China based study, Zhang et al. (2018) observed the decrease in relative growth rate (RGR), Efficiency conversion of ingested food (ECI), Efficiency conversion of assimilated diet and increase of the actual daily when S. litura fed on a soybean cultivar.
Even Karthik et al. (2021) suggested that Temperature and elevated CO2 has a strong effect on insect growth, survival and reproduction and enrolls a major role in controlling the development and growth of their host plants. In addition, the development of plant secondary chemicals as well as the structural characteristics used to protect against herbivores are influenced by temperature. Thus, for both insects and plants, temperature has potentially significant consequences (Fig. 14.1).
14.4.6 Effect on Host Plant Distribution
Global warming can also influence the geological spreading of plant species and their growth outlines. There will be variations in the richness and dispersal of its grown and non-grown plants would the insect pest dispersal. Many new insect pests may notice, while some insect pests may turn out to be invasive by reaching new areas due to extended range of their host plants. Wang et al. (2017) in their modeling study on international dispersal of Colorado potato beetle revealed the risk of invasion of the beetle from its native range. Climate change indirectly can also impact biotic dispersal of vector borne viruses and diseases triggered by parasite will increase. In some part of the globe, there will be bigger disease epidemics and some other part of the world may eyewitness reduced outbreak of diseases too based on the type of disease parasite or vector accessible at a given time and space (Nwaerema 2020).
14.5 The Impacts of Climate Change on Insect-Pests May Include
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Variation in diversity and richness of hexapod pests
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Variations in pests’ dispersal among different geographical regions
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Amplified hibernation in insects
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Swift population build up and number of cycles
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Fluctuations in synchronization of insect pests and their host plants
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Deviations in resistance of host plants
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Changes in hexapod biotypes
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Variations in tritrophic exchanges
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Influence on extinction of insect species
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Changes in action and comparative richness of natural enemies
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Amplified threat of invasive pest species introduction
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Effectiveness of crop protection skills may be reduced
14.6 Impact of Climate Change and Insect-Pests
14.6.1 Rising Temperature
Temperature is recognized as main abiotic factor straight affects herbivorous hexapod pests. Insects being poikilothermic, have temperature of their bodies is similar as that of the surrounding situation. So, the growth rates of the insect’s life cycle phases are sturdily reliant on temperature. Many hexapods will be affected to some extend for every notch variation in temperature and so, insect life histories will be affected manifold due to this. Fleming and Volney (1995), Fye and McAda (1972), and Cammell and Knight (1991) based on many experiments models and support the notion that the ecology of hexapod pests is probable to reply to amplified temperatures. Through each notch increase in worldwide temperature, the overall life history of hexapod pests will be lesser as compared to normal temperature. The faster the insect life cycle, the more developed might be the inhabitants of insects. In colder climate, many of hexapod stake their development time throughout the hot portions of the year thereby the insect species which has a definite climatic regime whose niche area is well-defined, might reply additionally to changes in climate while individuals in which the place is unfinished by other living or nonliving factors will be fewer expectable (Bale and Hayward 2010). In the earlier situation, the overall forecast is that if temperatures of the globe upsurge, the insect species in question might swing their terrestrial ranges nearer to the poles or to advanced raises and increase their inhabitant’s population (Harrington et al. 2001; Sutherst 2000; Bale and Hayward 2010; Samways 2005). How the raise in temperature affects the insect pests is depicted in Fig. 14.2 (Skendzic et al. 2021).
Due to climate change, there will be rise in global temperature which ultimately influence the hexapod pests in many ways as.
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terrestrial areas expansion.
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more hibernation and aestivation.
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fluctuations in inhabitants’ development rate.
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amplified sum of life cycles.
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delay of expansion time.
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fluctuations in insect and crop synchronization.
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deviations in inter and intra-specific communications.
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augmented dangers of incursions and.
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entry of different hosts.
14.6.1.1 Changes in Insect-Pests Diversity
Increased realization of the deterioration of biological systems over the last couple of decades has led to a better appreciation of the loss of genes, species and ecosystems. In the overall animal kingdom insects play a major and dynamic role in providing many amenities of the ecosystem (Kannan and James 2009; Kremen et al. 1993). Hexapods multiplicity in an environment designates the healthiness of an environment as they are actual decent pointers of changes in environment (Gregory et al. 2009), which show a significant part in dietary chains and food webs. Alfred (1998) reported that in India approximately 6.83% of global hexapod species are present. The changes in climate might disturb the comparative wealth of unlike hexapod species and the incapable species to familiarize the variations may be vanished over the period of time (Thomas et al. 2004). Anand and Pereira (2010) and Hampson (1908) reported that in India western ghats is the only habitation to many species of colorful moths and butterflies which are erratic, endemic in the world. At present numerous butterfly species are under an actual danger just because of exhaustion of the normal flora for numerous man-made happenings as reported by Costanza et al. (1987), Sachs (2008), and Sidhu and Mehta (2008).
There is an essential to rise functional multiplicity in agricultural ecosystems susceptible to changes in climate to recover structure flexibility, and reduce the number of fatalities owing to hexapods (Newton et al. 2011). Still, variations in planting designs as a consequence of global warming might radically disturb the equilibrium amongst hexapods and their biocontrol agents. Foremost impact of changes in climate on hexapod pests and natural enemies ‘effect in diminished richness of predators, parasitoids and decomposers and higher plant feeding, which might have undesirable significances for building and facilities of the whole ecosystems. Answers of hexapod pests and natural enemies hang on both rainfall and temperature and ecosystem inclusive antagonistic problems are probable to higher beneath projected climatic changes (Zvereva and Kozlov 2006). Significances of temperature rises of 1-2 °C might be equivalent in size to the presently seen climate change (Bokhorst et al. 2008). Intensification in rainfall will mainly disturb the insect species with meager distribution competences, which will bind their capability to enlarge their native range (Xannepuccia et al. 2009). Huge gauge of variations in precipitation due to changes in climate might have a main effect on the richness and multiplicity of both hexapod pests and natural enemies. In case of extreme drought due to climate change are expected to decline trophic variety and alter the arrangement of ecosystem (environment and organisms). Habitat disintegration consequences in the subdivision of habitats into lesser units ensuing in their amplified narrowness as well as loss of total habitat area. Such disintegration deviates the local weather at the split limits and limits effects comprise microclimate, light fluctuations, relative humidity and temperature individually these can have a noteworthy influence on the liveliness.
14.6.1.2 Extension of Geographical Areas
The topographical dispersal and richness of animal and plant kingdom in nature is identified by insect specific weather necessities vital for their development, existence and replication. Circulation in insects will rise if there is small increase in temperature. One projection state that for 1 °C increases in temperature might authorize swiftness of 200 km north or 40 m elevation in upward direction. Parts that are non-favorable at existing due to less temperature might convert favorable with increase in temperature. Minimum temperature compared to maximum temperature act as significant player in influential the worldwide spreading of hexapod species, henceforth any surge in temperature might upshot in a better capability to hibernate at higher elevations, eventually producing a change. Numerous hexapods have topographical arrays that are non-straightly restricted due to foliage, nonetheless in its place are delimited by temperature. Prior investigations have revealed that whenever there will increase in temperature, the hexapods are predictable to spread their topographical areas at higher elevations laterally with variations in farming areas of their host species (Hill and Dymock 1989; Sharma et al. 2005; Kuchlein and Ellis 1997). The heating in pleasant area may direct to reduction in comparative richness of temperature subtle hexapod inhabitants (Sharma et al. 2005, 2010; Petzoldt and Seamann 2010). Typically, the Glacial areas are unnatural since the hexapod outburst sowing to less temperature then regularly happening ices (Volney and Fleming 2000). In the upcoming period, predictable global heating (Carroll et al. 2004) and amplified famine occurrence (Logan et al. 2003) is anticipated to source additional recurrent hexapod occurrences in mild areas too. As the species prosperity of hexapods tends to surge with temperature, it is imaginary that with arise in temperature additional species will be increased than lost. Hibernating survival and timing of the instigation spring are significant at higher latitudes, leading to residents increase. Choice allowance in Helicoverpa armigera, a key insect instigating damage to vegetables and many other crops in India is projected with global heating (Sharma et al. 2005). Afterward, the continuing changes in hexapod circulation and array owing to altering weather might change local construction, multiplicity and working of ecosystems (IPCC 2007).
14.6.1.3 Changes in Insect Phenology
Along with the modification in planetary of insect species dispersals, changes in climate led to an environmental swing in period, by means of fluctuations in insect species phenology (timing of life history stages insects). Root et al. (2003) noted that was ace of the coolest influences of changing climatic conditions to screen and is utmost recognized in this esteem for an extensive variety of creatures. Many of the insect species might restrict their larval stages for shorter period and may emerge as adults earlier than required due to the increase in temperature. So, predictable replies in hexapods might comprise an early payment in the judgment of larval as well as adult appearance with an upsurge in the duration of the flying time (Menéndez 2007). Moths and butterflies are the finest illustrations of such seasonal changes. Roy and Sparks (2000) reported variations in lepidopteran phenology in United Kingdom, where in 26 of 35 insect have increased their primary presence. Harrington et al. (2007) described premature adult emergence and an initial influx of migrant species might similarly been described for aphid’s insect pests in the United Kingdom. The influences climate changes on four hexapod species like honey bee, butterfly, fly and beetle was examined in Mediterranean and specified that entire insect species showed variations in their initial arrival day for the preceding five decades, which was associated with upsurges in spring season temperature (Gordo and Sanz 2005).
The fluctuations in insect phenology might be deliberated over continuing researches by adjustable planting times for witnessing the arrival of insects on plants. Similarly, the effectiveness of influx of hexapods can also be documented by different lures like light, suction trap or pheromone trap. Examination of continuing information on seasonal variation would disclose variations in the judgments of insect pest arrival under the changing climate scenario (Pathak et al. 2012). Equally, enduring statistics from numerous insect pest recording systems in Europe and North America have given indication for species becoming active, drifting or reproducing quicker in the year due to rises in temperatures that lead directly to augmented development rates or earlier appearance from winter hibernation (Roy and Sparks 2000). Swelling temperatures have also acceptable a many insect of species to persist dynamic for a lengthier time throughout the year or to rise fecundity. The nodal agency ICAR through its All India Coordinated Rice Improvement Programme (AICRIP) have also extensive system of the collecting data from each center on insect light trap throughout the year. Investigation of past trap data compared with present facts can deliver significant evidence on the ill effects of changes in climate on paddy insect.
14.6.1.4 Increased Hibernating Existence
Being ectotherms, hexapods have restricted capability of self-regulation with outside changes in temperature. Bale and Hayward (2010) revealed that a variety of insect established ways such as interactive evasion over relocation and adaptations in physiology like overwintering to back life span under thermally traumatic situations. The diapause is a deferred evolving period happening, the display of which is administered by ecological issues like relative humidity, photoperiod and temperature. The hibernation as an adaptive characteristic, plays vigorous role in periodic instruction of hexapod life cycles because of which the hexapod stake healthier benefit to live countless deal of ecological hardships. According to Chapman (1998), there are two key types of diapause in hexapods. One is aestivation and another is hibernation to with stand high and low temperature respectively during the life cycle. The researchers (IPCC 2007; IMD 2010) have revealed that increase in temperature is happening highest at high latitudes particularly in winter season than in summer. Observing at the historical 10 decades weather outline of India, global heating was noticeable higher all through midwinter and it was the maximum temperature not the least temperature where noteworthy upsurge was detected (IMD 2010). Bale and Hayward (2010) thus observed the hexapods experiencing hibernation are expected to practice the utmost noteworthy variations in their thermal situation.
The diapause time of insects might be increased at higher temperature and due to high metabolism leads to quicker exhaustion of deposited food capitals (Hahn and Denlinger 2007). Increase in temperature in cold season might lead to postponement in beginning and initial summer might lead to quicker relieving from diapause in hexapods, which can then recommence their energetic development and expansion (Harrington et al. 2001).
14.6.1.5 Increase in Number of Generations
Yamamura and Kiritani (1998) observed that with a temperature rise 2 °C, hexapods may have the capacity to increase life cycles to the tune of one to five per year supplementary to the existing. Some insects advance additional quickly through ages of period with appropriate temperatures. Augmented temperatures will quicken the growth of these kinds of hexapods may be ensuing in additional cycles per year (Awmack et al. 1997).
Yamamura and Kiritani (1998); Petzoldt and Seamann (2010) observed that the universal problem of global warming is within convinced promising range might hasten the rates of expansion, multiplication and existence in insect pests of tropical and subtropical regions. Thus, hexapods will be skilled of implementation a greater cycle within same period of time. Increase in temperature might reduce the incidence of heavy cold measures, which may in turn enlarge the hibernating area for hexapods (Patterson et al. 1999).
14.6.1.6 Introduction of Invasive Alien Species
The changes in climate can as well encourage introduction and establishment of the exotic insect species. Danger of introduction invasive alien hexapod species, upsurge with worldwide climate change. Dukes and Mooney (1999), IPCC (2007) revealed that for the biological incursions many reasons may exists and they are many-sided fluctuations in abiotic, biotic machineries of the atmosphere and are named as chief influencers of insect species assault. World agricultural trade globalization and liberalization joined with the speedy transportation and communication means these days have considerably and reasonably increased the probabilities of exotic introductions. The CBD i.e., Convention on Biological Diversity, is of the view that introduction of new species is the utmost danger to damage of diversity of that biosphere (Mooney and Hobbs 2000) and levy huge prices to farming and marine ecologies by changing their local construction, variety and working (Timoney 2003; Sutherst 2000).
14.6.1.7 Outbreaks and Population Dynamics of Insect Pests
The population dynamics is the feature of population ecology dealing with aspects distressing changes in population concentrations. The seasonal effects of climate and enduring fluctuations in climatical circumstances resolve straightly paves way for alterations in spreading and expansion of hexapod pests. According to Bale and Hayward (2010) the fluctuations in neighboring temperature surely include modifications in voltinism, expansion speed and existence of hexapods and later turn upon size, compactness and hereditary alignment of inhabitants and also on the degree of plant manipulation.
According to IPCC (2007) it might lead in distressing environmental equilibrium since random deviations in the inhabitants of insects along with natural enemies like predators and parasitoids. Variations in climatic factors might lead to augmented occurrence and increase in strength of epidemics hexapod pests (Rao et al. 2009). Epidemic of sugarcane aphid Ceratovacuna lanigera in cane growing areas of Karnataka and Maharashtra during 2002–2003 lead to 30% crop decrease (Joshi and Viraktamath 2004; Srikanth 2007). These circumstances of augmented and recurrent nuisance to the plants have made additional giant hole in the bags of previously upset growers by enhancing the input charge of crop defense and plummeting the percentage of return.
14.6.1.8 Crop-Pest Exchanges
The capacity of a plant feeding hexapods to finish its growth hinge on the variation equally, the host plant and the ecological environments. The global change of climate has been initiated to apply both the effects from bottom to top and from top to bottom on the tri-tropic communications amongst host crops, hexapods and their predators and parasitoids by the way of convinced biological variations particularly connected to host-suitability and dietary standing (Coviella and Trumble 1999; Gutierrez et al. 2008). This has been observed in gypsy moth feeding on sugar maple and red maple which had condensed larval weight, augmented eating time and lengthy development (Williams et al. 2000). The big epidemics seen in development parts on the novel host’s plants might be clarified whichever by the more vulnerability of the host’s plants or by the helplessness of predators and parasitoids to find the larvae of moth on a rare host (Battisti et al. 2006). Cleland et al. (2007) reported that photoperiod and temperature have remained to disturb intensely the serious measures viz., shoot extension, blossoming and fruit setting in the life sequence of plants.
14.6.1.9 Augmented Occurrence of Hexapod Vectored Diseases of Plant
Changes in climate might give way to increased occurrence of hexapods transmitted many plant viruses through host range extension and quicker production of hexapod vectors (Sharma et al. 2005; Petzoldt and Seamann 2010). Robert et al. (2000) in his findings reported that amplified temperatures, mostly in the initial season found to increase the frequency in potato due to initial establishment of aphids which contains virus, as it is the chief potato viruses vector potato growing areas. Amplified concentrations of CO2, one of the more evaluated features of global warming is the consequence of swelling meditations of carbon dioxide on florae. Florae basically made up of carbon and raised carbon dioxide concentration permit them to produce additionally quickly as they might adapt carbon very fast.
14.7 Tactics to Alleviate the Bad Effects of Climate Change
Cultural practices in the field, predator and parasitoid, plant resistance mechanisms, insecticides of plant and animal origin and organic insecticides are now in existence which are extensively used for management of pest and disease. Though, most of the approaches of insect pest management are extremely delicate to the surrounding weather. So, keeping in mind the changes in climate there is need to plan the suitable pest’s management methods for effective control of pests and diseases.
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the plants existential struggle to hexapods is utmost the ecological approachable mechanism for the management. It is significant to categorize and advance in more varietal release which are steady in appearance of confrontation to the marked pests.
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Recently developed genetically modified plants have been governing around many of the stubborn insect pest infestations.
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Crop modification is best approaches of growing the action profusion of predators and parasitoids. It is the requirement of the hour to progress plant varieties that are welcoming to the predators and parasitoids.
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It is also need of the hour to study and formulate the synthetic organic insecticides based on the changing climatic factors which are most effective and least affecting the environment.
Lastly, there is a necessity to use the newer methodologies in pests’ management like IPM practices that look into deliberation the alteration in insect pest range, patterns of florae and efficiency of diverse mechanisms of insect supervision for justifiable plant manufacture.
14.8 Conclusion
Hexapod has a marvelous influence on vegetable plants. The modification in circumstances of climate is a acknowledge threatening many for fruit and vegetable crops. Predictable changes in climate may also consequence in increasing the number of pesticide application as there will be increase in number of insect cycles per season. Evolutionary variations may ambiguous our capability to distinguish species reply to global warming- consequently, insects retort contrarily to fluctuations in weather. As many communications mechanisms exists and it is very difficult to forecast the influence on insect pests due to changes in climate in the future. Existing stride of ecological modification stresses novel methods to hasten the acceptance of innovative IPM practices. Plant and insect pest controllers might have to develop ‘nimbler’ in demand to manage with the quickening vitality of changes in climate.
It is an essential of the hour for policy makers in administration, business and other strategy architects to recognize the broader problems in upholding actual IPM systems in the aspect of modification and acknowledgement assumed to the kind of data desirable. Improved appraisal of existing hereditary capitals to recognize auspicious agreements for such insect is a decision for justifying harm by such deviations in concentration of precise insect. There is a necessity to emphasis on calibration of insect control strategies for usage, in circumstance of altered climatical situations. Specified the magnitude of the encounters we are facing to alleviate the influences of changes in climate, the period is accurate to strengthen goal slanted towards exploration within many disciplines in the direction to deliver the immediately required and lucrative practical answers for maintainable hexapod control. The greatest economic approach for crop cultivators to track is to use of IPM practices to carefully observe hexapods and viral incidence.
References
Akbar SM, Pavani T, Nagaraja T, Sharma HC (2016) Influence of CO2 and temperature on metabolism and development of Helicoverpa armigera (Noctuidae: Lepidoptera). Environ Entomol 45:229–236
Alfred JRB (1998) Faunal diversity in India: an overview. In: Alfred JRB (ed) Faunal diversity in India. ENVIS Centre, zoological survey of India, Calcutta, pp 1–495
Anand T, Pereira GN (2010) Butterflies-the flying jewels of the Western Ghats. http://www.daijiworld.com/chan/exclusive_arch.asp?ex_id=1003. 2008, Accessed on 28 Dec 2010
Awmack CS, Woodcock CM, Harrington R (1997) Climate change may increase vulnerability of aphids to natural enemies. Ecol Entomol 22:366–368
Bale JS, Hayward SAL (2010) Insect overwintering in a changing climate. J Exp Biol 213:980–994
Battisti A, Stastny M, Buffo E, Larsson S (2006) A rapid altitudinal range expansion in the pine processionary moth produced by the 2003 climatic anomaly. Glob Chang Biol 12:662–671
Bokhorst S, Huiskes A, Convey P, van Bodegom PM, Aerts R (2008) Climate change effects on soil arthropod communities from the Falkland Islands and the maritime Antarctic. Soil Biol Biochem 40:1547–1556
Burgi LP, Mills NJ (2010) Cold tolerance of the overwintering larval instars of light brown apple moth Epiphyas postvittana. J Insect Physiol 56:1645–1650
Cammell ME, Knight JD (1991) Effects of climate change on the population dynamics of crop pests. Adv Ecol Res 22:117–162
Carroll AL, Taylor SW, Regniere J, Safranyik DL (2004) Effects of climate change on range expansion by the mountain pine beetle in British Columbia. In: Shore TL, Brooks JE, Stone JE (eds) Mountain pine beetle symposium: challenges and solutions. Natural Resources Canada, Canadian Forest Service, Pacific Forestry Centre, Victoria, British Columbia, pp 223–232
Chapman RF (1998) The insects-structure and function, 4th edn. Cambridge university press, p 788
Chen FJ, Wu G, Ge F (2004) Impacts of elevated CO2 on the population abundance and reproductive activity of aphid, Sitobion avenae Fabricius feeding on spring wheat. J Appl Entomol 128:723–730
Cleland EE, Chuine I, Menzel A, Mooney HA, Schwartz MD (2007) Shifting plant phenology in response to global change. TREE 22:357–365
Cornelissen T (2011) Climate change and its effects on terrestrial insects and herbivory patterns. Neotrop Entomol 40:155–163
Costanza R, d’Arge R, de Groot R, Farber S, Grasso M, Hannon B, Limburg K, Naeem S, O’Neill RV, Paruelo J, Raskin RG, Sutton P, van den Belt M (1987) The value of the World’s ecosystem services and natural capital. Nature 387:253–260
Coviella CE, Trumble JT (1999) Effects of elevated atmospheric carbon dioxide on insect-plant interactions. Conserv Biol 13:700–712
De Bach P (1964) Biological control of insect pests and weeds, p 350. Reinhold Publishing Corporation, New York
Diffenbaugh NS, Giorgi F, Pal JS (2008) Climate change hotspots in the United States. Geophys Res Lett 35:L16709. https://doi.org/10.1029/2008GL035075
Dukes JS, Mooney HA (1999) Does global change increase the success of biological invaders? TREE 14:135–139
Fleming RA, Volney WJ (1995) Effects of climate change on insect defoliator population processes in Canada’s boreal forests: some plausible scenarios. Water Air Soil Pollution 82:445–454
Fye RE, McAda WC (1972) Laboratory studies on the development, longevity, and fecundity of six Lepidopterous pests of cotton in Arizona. USDA, Washington, DC
Gordo O, Sanz JJ (2005) Phenology and climate change: a long-term study in a Mediterranean locality. Oecologia 146:484–495
Gregory PJ, Johnson SN, Newton AC, Ingram JSI (2009) Integrating pests and pathogens into the climate change/food security debate. J Exp Bot 60:2827–2838
Gupta HS (2011) Climate change and Indian Agriculture: Impacts, mitigation and adaptation. In: Proceedings of Xth Agricultural Science Congress on Soil, Plant and Animal Health for Enhanced and Sustained Agricultural Productivity. ICAR-NBFGR, Lucknow, India, pp 73–81
Gutierrez AP, D’Oultremont T, Ellis CK, Ponti L (2006) Climatic limits of pink bollworm in Arizona and California: effects of climate warming. Acta Oecol 30:353–364
Gutierrez AP, Ponti L, d’Oultremont T, Ellis CK (2008) Climate change effects on poikilotherm tritrophic interactions. Clim Chang 87:S167–S192
Hahn DA, Denlinger DL (2007) Meeting the energetic demands of insect diapause: nutrient storage and utilization. J Insect Physiol 53:760–773
Hampson GF (1908) The moths of India- supplementary papers to the volume in the Fauna of British India. Ser.III, Pt.X. J Bombay Nat Hist Soc 18:257–271
Harrington R, Fleming R, Woiwod I (2001) Climate change impacts on insect management and conservation in temperate regions: can they be predicted? Agric For Entomol 3:233–240
Harrington R, Clark SJ, Weltham SJ, Virrier PJ, Denhol CH, Hullé M, Maurice D, Roun-sevell MD, Cocu N (2007) Environmental change and the phenology of European aphids. Global Change Biol 13:1556–1565
Hill MG, Dymock JJ (1989) Impact of climate change: agricultural/horticultural systems. DSIR Entomology Division Submission to the New Zealand Climate Change Program. Department of Scientific and Industrial Research, Auckland, New Zealand, p 16
Hughes CL, Hill JK, Dytham C (2003) Evolutionary trade-offs between reproduction and dispersal in populations in expanding range boundaries. Proceedings of the Royal Society of London. Series B: Biolog Sci 270(2):147–150
IMD (2010) Annual climate summary. India meteorological department. Pune. Government of India, Ministry of Earth Sciences, p 27
IPCC (2007) Impacts, adaptation and vulnerability: scientific-technical analyses -contribution of working group II to the fourth assessment report of the intergovernmental panel on climate change, p 976. Cambridge University Press, Cambridge, UK
Johnson RH, Lincoln DE (1991) Sagebrush carbon allocation and grasshopper nutrition: the influence of CO2 enrichment and soil mineral nutrition. Oecologia 84:103–110
Joshi S, Viraktamath CA (2004) The sugarcane woolly aphid, Ceratovacuna lanigera Zehntner (Hemiptera: Aphididae): its biology, pest status and control. Curr Sci 87:307–316
Jump AS, Penuelas J (2005) Running to stand still: adaptation and the response of plants to rapid climate change. Ecol Lett 8:1010–1020
Kannan R, James DA (2009) Effects of climate change on global diversity: a review of key literature. Tropical Ecol 50:31–39
Karthik S, Sai Reddy MS, Yashaswini G (2021) In: Stuart A (ed) Climate change and its potential impacts on insect-plant interactions. The Nature, Causes, Effects and Mitigation of Climate Change on the Environment. Global Warming and Climate Change, Harris, pp 01–23
Kremen C, Colwell RK, Erwin TL, Murphy DD, Noss RF, Sanjayan MA (1993) Terrestrial arthropod assemblages: their use in conservation planning. Conserv Biol 7:796–808
Kuchlein JH, Ellis WN (1997) Climate-induced changes in the micro lepidoptera fauna of the Netherlands and the implications for nature conservation. J Insect Conserv 1:73–80
Lamarche VC, Graybill DA, Fritts HC, Rose MR (1984) Increasing atmospheric carbon dioxide: tree ring evidence for growth enhancement in natural vegetation. Science 225(4666):1019–1021. https://doi.org/10.1126/science.225.4666.1019
Lincoln DE, Fajer ED, Johnson RH (1993) Plant-insect herbivore interactions in elevated CO2 environments. Trends Ecol Evolut 8(2):64–68
Logan JA, Regniere J, Powell JA (2003) Assessing the impacts of global warming on forest pest dynamics. Frontiers in Ecol Env 1:130–137
Meehl GA, Stocker TF, Collins WD, Friedlingstein P, Gaye AT, Gregory JM, Kitoh A, Knutti R, Murphy JM, Noda A, Raper SCB, Watterson IG, Weaver AJ, Zhao ZC (2007) Global climate projections. In: Solomon S, Qin D, Manning M, Chen Z, Marquis M, Averyt KB, Tignor M, Miller HL (eds) Climate change 2007: the physical science basis. Contribution of working group I to the fourth assessment report of the intergovernmental panel on climate change. Cambridge University Press, Cambridge, United Kingdom and New York, NY, USA, pp 747–845
Menéndez R (2007) How are insects responding to global warming? Tijdschrift voor Entomologie 150:355–365
Mooney HA, Hobbs RJ (2000) Invasive species in a changing world. Island Press, Washington, DC
Newton AC, Johnson SN, Gregory PJ (2011) Implications of climate change for diseases, crop yields and food security. Euphytica 179:3–18
Nwaerema P (2020) Impact of climate change on insects, pest, diseases and animal biodiversity. Inter J Environment Sci Nat Res 23(5):151–153
Ouyang F, Hui C, Men X, Zhang Y, Fan L, Shi P (2016) Early eclosion of overwintering cotton bollworm moths from warming temperatures accentuates yield loss in wheat. Agricult Ecosyst Environ 217:89–98
Pandi GG, Chander S, Singh MP, Pathak H (2018) Impact of elevated CO2 and temperature on brown planthopper population in Rice ecosystem. Nat Acad Sci India Section B Biolog Sci 88:57–64
Parry ML, Carter TR (1989) An assessment of the effects of climatic change on agriculture. Clim Chang 15(2):95–116
Pathak H, Aggarwal PK, Singh SD (2012) Climate change impact, adaptation and mitigation in griculture: methodology for assessment and application division of environmental sciences. Indian Agricultural Research Institute, New Delhi, pp 111–130
Patterson DT, Westbrook JK, Joyce RJV, Lingren PD, Rogasik J (1999) Weeds, insects and disease. Clim Chang 43:711–727
Petzoldt C, Seamann A (2010) Climate change effects on insects and pathogens. Climate change and agriculture: promoting practical and profitable responses 6–16; Accessed online at http://www.climateandfarming.org/pdfs/FactSheets/III.2Insects.Pathogens.pdf
Prasannakumar N, Chander S, Pal M (2012) Assessment of impact of climate change with reference to elevated CO2 on rice brown planthopper, Nilaparvata lugens (Stal.) and crop yield. Curr Sci 103:1201–1205
Rao GGSN, Rao AVMS, Rao VUM (2009) Trends in rainfall and temperature in rainfed India in previous century. In: Aggarwal PK (ed) Global climate change and Indian agriculture case studies from ICAR network project. ICAR Publication, New Delhi, pp 71–73
Robert Y, Woodford JAT, Ducray-Bourdin DG (2000) Some epidemiological approaches to the control of aphid-borne virus diseases in seed potato crops in northern Europe. Virus Res 71:33–47
Robinson EA, Ryan GD, Newman JA (2012) A meta-analytical review of the effects of elevated CO2 on plant–arthropod interactions highlights the importance of interacting environmental and biological variables. New Phytol 194:321–336
Root TL, Price JT, Hall KR, Schneider SH, Rosenzweig C, Pounds JA (2003) Fingerprints of global warming on wild animals and plants. Nature 421:57–60
Roy DB, Sparks TH (2000) Phenology of British butterflies and climate change. Global Change Biol 6:407–416
Sachs J (2008) Common wealth: economics for a crowded planet. Allen Lane, London
Samways M (2005) Insect diversity conservation. Cambridge University Press, Cambridge, p 342
Sardana HR, Bhat MN (2016) Pest scenario, plant protection approaches in the current context of changing climate. In: Chattopadhyay C, Prasad D (eds) Dynamics of crop protection and climate change. Studera press, New Delhi, pp 167–186
Sharma HC, Dhillon MK, Kibuka J, Mukuru SZ (2005) Plant defense responses to sorghum spotted stem borer, Chilo partellus under irrigated and drought conditions. Inter Sorghum Millets Newsletter 46:49–52
Sharma HC, Srivastava CP, Durairaj C, Gowda CLL (2010) Pest management in grain legumes and climate change. In climate change and Management of Cool Season Grain Legume Crops. In: Yadav SS, McNeil DL, Redden R, Patil SA (eds). Business Media, Springer Science, Dordrecht, The Netherlands, pp 115–140
Shrestha S (2019) Effects of climate change in agricultural insect pest. Acta Scientific Agricult 3:74–80
Sidhu AK, Mehta HS (2008) Role of butterflies in the natural ecosystem with special reference to high altitude (Pangi Valley, Himachal Pradesh). In: Proceedings of international conference on climate change, biodiversity and food security in the South Asian Region, 3–4 November, 2008. Punjab State Council for Science and Technology, Chandigarh and United Nations Educational, Scientific and Cultural Organization, New Delhi, p 36
Singer MC, Parmesan C (2010) Phenological asynchrony between herbivorous insects and their hosts: signal of climate change or pre-existing adaptive strategy? Philosoph Transact Royal Society B: Biolog Sci 365:3161–3176
Skendzic S, Zovko M, Živković IP, Lesic V, Lemic D (2021) The impact of climate change on agricultural insect pests. Insects 12(5):440
Solankey SS, Prakash S, Pawan S, Randhir K (2019) Vulnerability of vegetable crops to climate change. In: Singh P (ed) National Seminar on “recent advances in agriculture for sustainable rural development (RAASRD-2019)”. VKSCoA, Dumraon (BAU, Sabour), Bihar, pp 64–70
Solbreck C (1991) Unusual weather and insect population dynamics: Lygaeus Equestris during an extinction and recovery period. Oikos 60:343–350
Srikanth J (2007) World and Indian scenario of sugarcane woolly aphid. In: Mukunthan N, Srikanth J, Singaravelu B, Rajula Shanthy T, Thiagarajan R, Puthira Prathap D (eds) Woolly aphid management in sugarcane, vol 154. Extension Publication, Sugarcane Breeding Institute, Coimbatore, pp 1–12
Srinivasa Rao M, Srinivas K, Vanaja M, Manimanjari D, Rao CAR, Venkateswarlu B (2013) Response of multiple generations of semilooper, Achaea janata feeding on castor to elevated CO2. J Environ Biol 34:877–883
Sudderth EA, Stinson KA, Bazzaz FA (2005) Host-specific aphid population responses to elevated CO2 and increased N availability. Glob Chang Biol 11:1997–2008
Sutherst R (2000) Climate change and invasive species: a conceptual framework. In: Mooney HA, Hobbs RJ (eds) Invasive species in a changing world. Island Press, Washington, DC, pp 211–240
Thomas CD, Cameron A, Green RE (2004) Extinction risk from climate change. Nature 427:145–148
Timoney KP (2003) The changing disturbance regime of the boreal forest of the Canadian prairie provinces. Forest Chronicle 79:502–516
Van Asch M, Visser ME (2007) Phenology of forest caterpillars and their host trees: the importance of synchrony. Annu Rev Entomol 52:37–55
Visser ME, Both C (2005) Shifts in phenology due to global climate change: the need for a yardstick. Proceed Royal Society London Series B Biolog Sci 272:2561–2569
Vissers ME, Holleman LJM (2001) Warmer springs disrupt the synchrony of oak and winter moth phenology. Proceed Royal Society London Series B Biolog Sci 268:289–294
Volney WJA, Fleming RA (2000) Climate change and impacts of boreal forest insects. Agric Ecosyst Env 82:283–294
Wang C, Hawthorne D, Qin Y, Pan X, Li Z, Zhu S (2017) Impact of climate and host availability on future distribution of Colorado potato beetle. Sci Rep 7:4489
Williams DW, Liebhold AM (2002) Climate change and the outbreak ranges of two north American bark beetles. Agricult Entomol 4:87–99
Williams R, Norby RJ, Lioncln DE (2000) Effects of elevated CO2 and temperature grown red and sugar maple on gypsy moth performance. Global Change Biol 6:685–695
Xannepuccia AD, Ciccihino A, Escalante A, Navaro A, Isaach JP (2009) Differential responses of marsh arthropods to rainfall-induced habitat loss. Zool Stud 48:173–183
Yamamura K, Kiritani K (1998) A simple method to estimate the potential increase in the number of generations under global warming in temperate zones. Appl Entomol Zool 33:289–298
Zhang YF, Wan GJ, Liu B, Zhang XG, Xing GN, Chen FJ (2018) Elevated CO2 and temperature alter development and food utilization of Spodoptera litura fed on resistant soybean. J Appl Entomol 42:250–262
Zvereva EL, Kozlov MV (2006) Consequences of simultaneous elevation of carbon dioxide and temperature for plant-herbivore interactions: a meta-analysis. Glob Chang Biol 12:27–41
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Prashant, M., Waseem, M.A., Managanvi, K., Erayya, Rai, V.L. (2023). Emerging Insect-Pests of Vegetables Due to Changing Climate. In: Solankey, S.S., Kumari, M. (eds) Advances in Research on Vegetable Production Under a Changing Climate Vol. 2. Advances in Olericulture. Springer, Cham. https://doi.org/10.1007/978-3-031-20840-9_14
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