Insect Biotypes
Insect Biotypes
1
Ramesh Arora and Surinder Sandhu
Abstract
The green plants and insects represent the two dominant groups of living organ-
isms on Earth. The green plants occupy the most capacious segment among all
biological organisms, whereas the insects are the most specious group. These
two ‘empires’ are interconnected as well as interdependent. Green plants are the
primary producers of food, and all animals being heterotrophs depend directly or
indirectly on plant-produced food. In turn, nearly three fourths of all angio-
sperms require the services of insect pollinators. The entomophilic flowering
plants and their insect pollinators thus represent the most evident and widely
applicable example of mutualism among living organisms. But a wide variety of
phytophagous insects also flourishes, diversifies and sustains on these plants.
Consequently, the plants have evolved a dizzying array of morphological and
biochemical (constitutive as well as induced) barriers for protection against
insects and other herbivores. Evolutionary interactions between plants and
insects may have contributed to the increased biodiversity and success of both
these groups. The study of these interrelationships, as outlined in this chapter, is
of great practical significance for the future agricultural production. The devel-
opment of pest-resistant cultivars of crop plants and progress in integrated pest
management both require an intricate understanding of insect-plant relationships.
R. Arora (*)
Department of Entomology & Zoology, Eternal University,
Baru Sahib, Himachal Pradesh 173101, India
e-mail: arorarame@gmail.com
S. Sandhu
Department of Plant Breeding and Genetics, Punjab Agricultural University,
Ludhiana, Punjab 141 004, India
e-mail: surindersandhu@pau.edu
Keywords
Coevolution • Pollinators • Insect pests • Flowering plants • Mutualism • Plant
defences
1.1 Introduction
The ‘plant kingdom’ and the ‘class Insecta’ represent the two dominant groups of
living organisms, in terms of the abundance of species as well as in the amount of
biomass. Green plants are the primary producers of food, and all animals being
heterotrophs depend directly or indirectly on plant-produced food (Schoonhoven
et al. 2005). In turn, a majority of the 300,000 plant species require the services of
insect pollinators for reproduction. Colourful, scented flowers and floral nectarines
were in all probability developed by plants for attracting insect pollinators. Flower
anatomy ensured that while feeding, the insects also picked up the pollen (Kearns
et al. 1998). Consequently, to prevent over-exploitation, the plants have also evolved
a dizzying array of structural and biochemical barriers for protection against insects
and other herbivores. While some of these barriers are synthesized by plants regard-
less of the presence of herbivores (constitutive defences), many others are produced
only in response to herbivory (induced defences). Only those insect species, which
are able to overcome these barriers in one or more plant species by avoidance,
detoxification, etc., can access that plant species as food. The insects which damage
the economically important plants have been termed as ‘insect pests’ by humans.
The important mutualistic and antagonistic interactions between plants and insects
are introduced hereunder.
The most evident and widely applicable example of mutualism is that between
insect-pollinated flowering plants and their insect pollinators. Nearly 80% of all
flowering plants are bisexual and bear flowers with stamen and pistils in the same
flower. This promotes self-fertilization and consequently inbreeding. The plants
avoid self-fertilization either by separating the sexes in time and space (differences
in the timing of maturation) or by self-incompatibility. Both mechanisms promote
cross-pollination, which is assisted by various agencies e.g. wind, water, and ani-
mals, etc. More than three fourths of all flowering plants are wholly or partially
1 Insect-Plant Interrelationships 3
insect-pollinated (Faegri and Pijl 1971). The economic value of insect pollinators is
enormous. Most of the important oilseeds, pulses, fruits, vegetables, nuts, spices
and ornamentals (Hill 1997; Atwal 2000) show improved yields with animal polli-
nation (Klein et al. 2007). It has been estimated that animal pollination has an eco-
nomic value of €153 billion annually, which is nearly one tenth of global agricultural
production (Galai et al. 2009).
Some of the widely accepted estimates of the number of angiosperms pollinated
by animals vary from 67% to 96% of all angiosperm species (Axelrod 1960; Nabhan
and Buchmann 1997). Ollerton et al. (2011) observed that these estimates are not
based on firm data. They compiled data on published and unpublished community
level surveys of plant-pollinator interactions and concluded that proportion of
animal-pollinated species was 78% in temperate-zone communities and 94% in
tropical communities, with a global mean of 87.5% of all flowering plants. The pol-
linators benefit from rewards in the form of nectar and pollen. Both are nutrient-rich
foods with nectar containing 50% sugars and pollen 15–60% proteins and other
essential elements (Proctor et al. 1996; Roulston et al. 2000). Together, they provide
nourishment for the bees, which are the most important among insect pollinators
(Schoonhoven et al. 2005).
The entomophilous flowering plants and the pollinating insects constitute an
example par excellence of mutualism. However, the degree of mutualism varies
among various plant-pollinator combinations (Schoonhoven et al. 2005). In some
cases, there is obligate mutualism, and a species of plant can only be pollinated by
a single species of pollinator, which depends on it for food. For instance, figs (Ficus
spp., Moraceae) are dependent upon fig wasps (Agaonidae, Chalcidoidea) for pol-
lination (Wiebes 1979). Every species of fig is pollinated by a specific wasp species,
e.g. the pollination in Ficus carica Linnaeus is carried out by the fig wasp,
Blastophaga psenes (Linnaeus) (Ramirez 1970). Another example of obligate
mutualism is observed between yucca moths (Prodoxidae) and yucca plants
(Agavaceae). The yucca moths are the sole pollinators for yucca flowers and deposit
their eggs in the locule of the ovary of flowers so that the young caterpillars can feed
on the developing seeds (Pellmyr and Krenn 2002).
Another interesting example is based on the great naturalist Charles Darwin’s
prediction. In 1862, while doing research on orchids, Darwin found that the astound-
ing Christmas orchid, Angraecum sesquipedale Thouars, had nearly a foot-long
green nectary. As this group of orchids was moth pollinated, Darwin predicted that
there must be a gigantic moth species with extended proboscis capable of feeding
on the long nectary. More than four decades later, Rothshild and Jordan in 1903
described the Morgan’s sphinx moth, Xanthopan morganii Walker with an extended
proboscis length of >12 in., as the only known pollinator of A. sesquipedale, which
is endemic to Madagascar (Kritsky 2001). However, such reciprocal evolution in
plant-pollinator relationships is not widespread. Burkle and Alarcon (2011)
observed that most plant-pollinator relationships have a fairly broad range with a
high degree of annual turnover of pollinator species, and the relative importance
4 R. Arora and S. Sandhu
of a pollinator species may vary in different years for pollination of the same
plant species.
Insect pollination has undoubtedly contributed to the evolutionary success of
angiosperms. The fossil records show that pollination originated around 250 Myr
ago (Labandeira 2013). The early angiosperms were probably pollenized both by
the wind and animals. In view of the advantages conferred by entomophily, its
importance increased over evolutionary time (Cox 1991; Crepet et al. 1991).
Entomophilic angiosperms display a diversity of flower size, shape, colour and fra-
grance which may have been determined by the requirements of the pollinators. The
pollen in flowers of such plants may have a sculptured structure and/or is covered
with sticky substances which help it to easily adhere to the insect body. The hairs on
the insect legs and other body parts also aid in pollen transfer. The bumble bee pol-
linated flowers in foxglove, Digitalis purpurea Linnaeus are bell shaped, while the
butterfly pollinated flowers of Calopheria spp. have tubular corolla, which is an
adaptation to the long probocis (Schoonhoven et al. 2005). In addition, the latter
contain higher levels of amino acids than flowers fed on by flies (Baker and Baker
1986). In order to attract pollinators, some plant species produce sterile ‘reward
anthers’ which are brightly coloured (Nepi et al. 2003). Flowers of the orchid Mirror
of Venus, Ophrys speculum Link, imitate the virgin female wasps of their pollinator,
Dasyscolia ciliata (Fabricius), by releasing the female sex pheromone to entice the
male wasps. The attracted male wasps try to mate with the flowers and in doing so
act as pollination vectors (Ayasse et al. 2003).
Hymenopterans, especially the Apoidea, are the most important group involved
in flower pollination at present, but other groups have been equally important in the
past. Basal angiosperms are even now primarily pollenized by the beetles and flies
(Thien et al. 2000). Bees are closely adapted to a floral diet (Atwal 2000) and are
able to assimilate pollen grains despite the presence of an almost impermeable cuti-
cle (Velthius 1992). Individual honeybees often exhibit flower constancy by prefer-
ably visiting flowers of a single species. It improves pollinator efficiency and also
helps in reproductive isolation of plant species. The insects’ ability to remember
combinations of flower odours and colours plays a central role in flower constancy.
Honeybees have been reported to have the capacity to distinguish at least 700 differ-
ent floral aromas (Schoonhoven et al. 2005).
Insects are the most diverse and a tremendously successful group of organisms on
Earth. The members of a number of insect orders infest plants and obtain food from
them. Species in some of the insect orders are almost exclusively (Lepidoptera,
Orthoptera, Phasmida) or predominantly (Hemiptera, Thysanoptera) herbivorous.
But Coleoptera, Hymenoptera and Diptera are only partly herbivorous and also
include numerous carnivorous species (Schoonhoven et al. 2005). Every vascular
1 Insect-Plant Interrelationships 5
plant species usually harbours several insect species. There are insect species feed-
ing on all parts of the plant including the roots, stem, bark, shoots, leaves, flowers
and fruits. While solid feeders chew plant tissues externally (defoliators) or inter-
nally (borers), others suck the sap (aphids, jassids), reduce plant vigour and even act
as vectors of plant pathogens, e.g. whitefly.
Most insects usually exhibit a high degree of specialization in their choice of
food plants. The monophagous insects feed on only a single or a few closely related
species of plants, while oligophagous ones feed on a number of plant species, all of
which belong to the same family. In contrast, the polyphagous insects use a wide
range of plants from different plant families as food (Panda and Khush 1995). But
most insects exhibit some degree of specialization in their host plant choice.
Investigation on herbivorous insects has revealed that only around one tenth of these
insects have the ability to feed on plants of more than three plant families. The host
range of each insect species is constrained by several structural, biochemical and
ecological factors. As a generalization, it may be stated that, except for Orthoptera,
all other orders of herbivorous insects are largely composed of species specialized
to feed on particular plant species (Schoonhoven et al. 2005). According to Bruce
(2015), the herbivores have evolved over time to become specialized feeders, even
though some of polyphages continue to be important agricultural pests. Insects have
the ability to recognize and respond to host cues for feeding and oviposition.
Despite the antagonistic relationships between plants and phytophagous insects
presumed to operate in all cases, herbivory has been observed to increase plant
growth and fitness in some cases (Owen 1980; Vail 1994; Sadras and Felton 2010).
Yield decreases due to arthropod feeding are quite common, but there are examples
of increased yield recorded in insect-damaged as compared to undamaged plants
(Harris 1974). The compensatory responses to herbivore damage may in some cases
more than offset the damage caused. It basically depends on how plants respond to
attack by insects or other herbivores.
Plants are immobile organisms and have to defend themselves against insects and
other herbivores. Most plants in natural ecosystems show little or no obvious dam-
age in spite of the presence of wide variety of phytophagous insects in large num-
bers. Complete defoliation by phytophagous insects is an exception rather than a
rule. It has been estimated that on an average, insects consume only around 10% of
all annually produced plant biomass (Barbosa and Schulz 1987). This is primarily
due to the fact that plants have evolved a diverse range of structural and biochemical
characteristics to protect themselves from herbivores. In contrast, insect pest’s dam-
age is usually higher in agroecosystem as many of these characteristics have been
lost while breeding plants more palatable to human taste and/or outyielding the
traditional plant genotypes. There is a need to study these plant defences to exploit
them optimally in commercial agriculture.
6 R. Arora and S. Sandhu
1.3.1.1.2 Trichomes
The epidermal surface in plant is usually covered with hair-like structures, which
are variable in shape, size, location and function (Werker 2000). The hairs present
on the aerial parts of a plant are commonly referred to as trichomes, while the term
pubescence refers to the collective trichome cover of a plant surface. The trichomes
range in size from a few microns to several centimetres, and the shape varies greatly
in different species. The trichomes are of two types: non-glandular and glandular
(Payne 1978). Non-glandular trichomes may act as physical barriers against the
movements of insects over the plant surface or prevent the herbivores’ mouth parts
from accessing the feeding tissues of the plant (Ram et al. 2004). Glandular tri-
chomes are specialized to secrete a variety of chemicals (Fahn 2000), which act as
important chemical barriers against pests and pathogens (Glas et al. 2012). Hooked
trichomes of black bean, Phaseolus vulgaris Linnaeus, were found to impale the
aphid, Aphis craccivora Koch (Johanson 1953), and the leafhopper, Empoasca
fabae (Harris), leading to wounding and death (Pillemer and Tingey 1978).
Interestingly, in some cases, trichome density has been observed to be induced in
response to insect feeding. Feeding by the cabbage-white butterfly, Pieris rapae
(Linnaeus), and the cabbage looper, Trichoplusia ni (Hubner), on young black mus-
tard, Brassica nigra (Linnaeus) W. D. J. Koch, plants resulted in increased trichome
density on newly expanded leaves (Traw and Dawson 2002). Some insect pests have
also been reported to have developed morphological or biochemical adaptations to
neutralize the effect of trichomes. Trichomes may also have indirect effects on plant
resistance by limiting the searching capacity of natural enemies of herbivores. The
parasitic wasp, Encarsia formosa Gahan, is considerably more efficient in finding
its host – whitefly nymphs – on glabrous cultivars than on hairy leaves (van Lenteren
et al. 1995).
1 Insect-Plant Interrelationships 7
1.3.1.2.1 Nutrients
The suitability of a plant as a host for one or more insect species is dependent on its
ability to supply holistic nutrients for development and multiplication of these
insects. From an insect’s perspective, the plants usually supply a mixture of nutri-
ents at suboptimal concentrations, which are combined with indigestible structural
compounds, such as cellulose and lignin, and a variety of allelochemicals
(Schoonhoven et al. 2005). The latter may exert a wide range of behavioural,
8 R. Arora and S. Sandhu
physiological and growth-inhibiting effects, some of which may even lead to insect
mortality.
Most insects have qualitatively similar nutritional requirements, consisting of
carbohydrates, amino acids, fatty acids, sterols and a number of micronutrients.
Host plants are often nutritionally suboptimal per se. The main groups of primary
plant metabolites – amino acids, carbohydrates and lipids involved in fundamental
plant physiological processes – serve as essential nutrients for herbivores. Therefore,
changes in primary plant metabolites and nutrients greatly affect the survival and
multiplication of phytophagous insects (Berenbaum 1995).
Nitrogen is especially important as insects are unable to exploit inorganic nitro-
gen, and organic nitrogen content of plants is suboptimal for the insects (Schoonhoven
et al. 2005). This may constitute a major barrier to successful exploitation of plants
by a majority of insect taxa (orders). Interestingly, the herbivorous taxa include
nearly half of the total arthropod fauna in less than one-third of insect orders, indi-
cating that once the nitrogen deficiency barrier is breached, these organisms are able
to access an abundant supply of food (Strong et al. 1984).
Cotton Cotton genotypes with inbuilt defence based on nutritional factors have
been evolved for insects such as the leafhopper, Amrasca biguttula (Ishida); white-
fly, Bemisia tabaci (Gennadius); stem weevil, Pempherulus affinis (Faust); and the
thrips complex (Uthamasamy 1996). The whitefly B. tabaci-resistant genotypes
showed higher contents of K, P and Mg and lower of N and Fe as compared to sus-
ceptible ones. But the other parameters like sugars, proteins, Ca and Cu did not
show significant relationship with whitefly buildup. In another study, it was reported
that total sugar content of cotton cultivars was positively correlated with whitefly
incidence during the vegetative phase but negatively correlated with it after flower-
ing of the crop (Rao et al. 1990). In the case of leafhopper, A. biguttula, highly
susceptible genotype Acala 4–42 had higher amount of reducing sugars (2.55%),
proteins (18.49%) and free amino acids (10.15 mg/g) as compared to highly resis-
tant BJR 741 containing 1.63% reducing sugar, 13.45% proteins and 6 mg/g free
amino acids (Singh and Agarwal 1988).
taining few eggs, while those caged on susceptible varieties had normal ovaries full
of eggs (Sogawa and Pathak 1970). The gall midge Orseolia oryzae (Wood-Mason)-
resistant varieties PTB 18, PTB 21 and Leuang 152 had higher content of free amino
acids and less sugar in their shoot apices than susceptible varieties Jaya and IR8. In
the case of stem borer, Scirpophaga incertulas (Walker), stems of both the resistant
(TKM6) and moderately resistant (Ratna) genotypes had less amino acids and sug-
ars than susceptible genotype (IR8) (Vidyachandra et al. 1981).
Legumes The importance of amino acid concentration in the pea plant on suscep-
tibility to aphid, Acyrthosiphon pisum (Harris), was revealed by Auclair (1963). He
observed that the concentrations of amino acids in the sap of susceptible genotypes
were significantly higher than those in the resistant genotypes. It has been reported
that high percentage of non-reducing sugars and low percentage of starch in the
seeds of chickpea genotype GL 645 might be responsible for the low incidence of
the pod borer H. armigera in the test cultivar as compared to the infestor (Chhabra
et al. 1990).
Low amino acid, protein and sugar contents and high phenol content induced
resistance in pigeon pea cultivars against pod borers. Sugar content was high both
in seeds (3.64–4.82%) and in the pod coat (3.66–4.92%) of susceptible cultivars
(ICPLI, ICPLS7 and UP AS20). In the resistant cultivars, the total sugar content
ranged between 2.86 (ICPLS3024) and 3.51% (HS9–2) in the seeds and 2.91
(ICPLS3024) and 3.44% (HS9–2) in the pod coat. The amino acid content was low
in the pod coat (1.40–1.52 mg/g) and seed (1.39–1.55 mg/g) of resistant pigeon pea
cultivars tested as compared to the susceptible cultivars (1.89–2.57 mg/g in pod
coat; 2.04–2.62 mg/g in seed). Highly significant positive correlation observed
between amino acid content and incidence of individual borer species supported the
possible role of amino acids in offering resistance to the pod borers (Sahoo and
Patnaik 2003).
1.3.1.2.3 Allelochemicals
The plant-produced allelochemicals are mainly secondary metabolites which do not
play major role in primary metabolic pathways of plants. While the primary meta-
bolic pathways are common in almost all flowering plants, these secondary sub-
stances vary widely in different plant species (Schoonhoven et al. 2005). It was
Fraenkel (1959) who first postulated that these substances act to deter insects and
other herbivores. It has been observed that the plant produce a dazzling variety of
secondary metabolites, and more than 200,000 of these have been identified (Dixon
and Strack 2003).
The allelochemicals have been functionally classified into two categories: allo-
mones which benefit the producing organism, i.e. the host plant, and kairomones –
which benefit the organism perceiving it, i.e. the phytophagous insect. The
involvement of allelochemicals in various types of insect-plant relationships can
determine the status of a plant either as a host (presence of kairomone) and non-host
(absence of kairomone) or as resistant (presence of allomone) and susceptible
(absence of allomone) (Panda and Khush 1995). Allomones are considered a major
10 R. Arora and S. Sandhu
factor responsible for plant defence against insects, and these have been exploited to
increase levels of resistance in several agricultural crops (Green and Hedin 1986).
The various groups of secondary plant metabolites implicated in plant defence
against insects (Table 1.1) are briefly discussed here (Rosenthal and Berenbaum
1991; Arora and Dhaliwal 2004; Schoonhoven et al. 2005; Iason et al. 2012).
Nonprotein Amino Acids The nonprotein or unusual amino acids are common in
a number of unrelated families of higher plants as well as in some lower plants. At
least 600 such amino acids have been elucidated from various plants especially
legumes. Nonprotein amino acids may afford protection against predators and
pathogens due to their structural analogy to the common nutritionally important
amino acids. The biological effects on insects are partly due to the fact that the ana-
logue molecule gets misincorporated into protein synthesis of the insect or through
inhibition of biosynthetic pathways (Rosenthal 1991; Huang et al. 2011; Yan et al.
2015). Among these, canavanine, azetidine-2-carboxylic acid, 2,4-diaminobutyric
acid, mimosine, 3-hydroxyproline, 5-hydroxynorvaline, β-cyanoalanine and pipe-
colic acid are significant in causing insect growth disruption (Parmar and Walia
2001, Yan et al. 2015).
Terpenoids Terpenoids are the largest and most diverse class of organic com-
pounds found in plants. They exhibit enormous chemical variety and complexity,
but all are formed by fusion of five-carbon isopentane units, and most of them are
lipophilic substances (Ruzicka 1953). Terpenoids achieve their greatest structural
1 Insect-Plant Interrelationships 11
and functional diversity in the plant kingdom. Nearly 30,000 terpenoids are known
in plants, and a majority of them serve as defences against herbivores and pathogens
or as attractants for pollinators and fruit-dispersing animals. The terpenoids are con-
stituted of two or more five-carbon units in their structures: monoterpenoids (2xC5),
sesquiterpenoids (3xC5) diterpenoids (4x C5), triterpenoids (6xC5), tetraterpenoids
(8xC5) and polyterpenoids [(C5) n where n>8] (Gershenzon and Croteau 1991).
Monoterpenoids have been demonstrated to work as toxins and as feeding/ovipo-
sition deterrents against a large number of insects. The best known insect toxin
among monoterperoids is the botanical insecticide pyrethrum, found in the flowers
and leaves of certain Chrysanthemum species. The active ingredient in pyrethrum is
a mixture of monoterpene esters collectively known as pyrethroids (Casida 1973).
Cotton and related malvaceous plants possess spherical pigment glands in leaves,
flowers and most other parts of the plants. In addition to anthocyanin pigments,
these pigment glands contain high concentrations of a variety of mono- and sesqui-
terpenoids especially gossypol. Gossypol is a phenolic, sesquiterpene dimer with
two aldehyde residues. Gossypol is toxic to a variety of herbivorous insects, causing
significant decrease in the survival, growth and development of a number of impor-
tant lepidopterous and coleopterous pests. The toxicity of gossypol to herbivores is
supposed to result from its binding to proteins in the gastrointestinal tract, causing
a reduction in the rate of protein digestion. The proteins in the gastrointestinal tract
may be the ingested dietary proteins or the digestive enzymes produced by the
insect (Meisner et al. 1977). The sesquiterpene lactone, beta-D-glucopyranosyl
ester (TA-G), a major secondary metabolite of the common dandelion, Taraxacum
officinale G. H. Weber ex Wiggers, protects the plant against its major native root
herbivore, the common European cockchafer, Melolontha melolontha Linnaeus, by
deterring larval feeding (Huber et al. 2016).
Triterpenoids (C30) with six-C5 isoprene units are the largest of terpenoid com-
pounds. The three major groups of triterpenes which have significant roles in plant-
herbivore interactions are the cucurbitacins, limonoids and saponins. Cucurbitacins
are a group of about 20 extremely bitter and toxic tetracyclic triterpenes, confined
mainly to plants in the Cucurbitaceae family. These compounds serve as toxicants
and feeding deterrents against a wide range of phytophagous insects (Tallamy et al.
1997). Some specialist insects feeding on cucurbits are, however, able to metabolize
or avoid these toxic compounds and even use cucurbitacins as host recognition cues
(Abe and Matsuda 2000).
The limonoids are a large group of highly oxygenated substances with a basic
skeleton of 26 carbon atoms. Limonoids are found in three closely related families,
the Rutaceae, Meliaceae and Cneoraceae. Limonoids are powerful feeding deter-
rents against insects. Over 100 triterpenoids have been isolated from the neem
(Azadirachta indica A. Juss.) seeds, and a number of these are active as insect feed-
ing deterrents and antifeedants. Most important of these is the azadirachtin, which
is effective at dosages as low as 50 parts per billion. More than 400 species of
insects have been reported to be susceptible to neem preparations at various concen-
trations. In addition to antifeedant effects, neem is reported to affect the survival,
12 R. Arora and S. Sandhu
Alkaloids The alkaloids are a heterogeneous class of natural products that occur in
all classes of living organisms but are most common in plants. Alkaloids generally
include basic substances that contain one or more nitrogen atoms, usually in combi-
nation as part of a cyclic system. Most of them are derivatives of common amino
acids, such as lysine, tyrosine, tryptophan, histidine and ornithine (Facchini 2001).
Alkaloids are found in some 20% of the species of flowering plants. Generally, each
alkaloid-bearing species displays its own unique, genetically defined alkaloid pat-
tern. Numerous alkaloids have been reported to be toxic or deterrent to insects.
Because of their nitrogenous nature, many alkaloids interfere with the key compo-
nents of acetylcholine transmission in the nervous system. Nicotine and nornicotine
derived from tobacco plant were popular as botanical insecticides before the advent
of synthetic organic insecticides (Dhaliwal and Arora 2001). Several groups of
structurally unrelated alkaloids such as pyrrolizidines, quinolizidines, indole alka-
loids, benzylisoquinolines, steroid alkaloids and methylxanthines are feeding deter-
rents to many insects and other herbivores at dietary concentrations over 0.1%
(Schoonhoven et al. 2005).
Insect Hormone Mimics and Antagonists The endocrine system is critical for the
development, growth, survival and multiplication of insects. Although many insect
hormones are known, two powerful hormones, the juvenile hormone (JH) and the
ecdysone or moulting hormone (MH), are recognized to play a major role in these
processes. The analogues of these hormones are called juvenoids and ecdysteroids,
respectively. It is presumed that plants may have developed juvenoids and ecdyster-
oids as subtle defences against insect pests. Plant species having high ecdysteroid
content (> 1000 ppm) are avoided by insects. Farnesol, sesamin, juvabione, s terculic
acid, bakuchiol and thujic acid are some of the important juvenoids isolated from
plants and are known to disrupt metamorphosis, moulting and reproduction in
insects (Bowers 1991).
Phenolics Phenolics are aromatic compounds with one or more hydroxyl groups
and are ubiquitous in plants (Harborne 1994). Examples of relatively simple pheno-
lics include hydroxybenzoic acids like vanillic acid, the hydroxycinnamic acids like
caffeic acid and the coumarins (Schoonhoven et al. 2005). Coumarins possess a
5,6-benz-2-pyrone skeleton and may be variously hydroxylated, alkylated, alkoxyl-
ated or acylated. Coumarins can deter feeding as well as interfere with development
of insects. The simple coumarin, bergamottin, is ovicidal to the Colorado potato
beetle, Leptinotarsa decemlineata (Say), while mammein is toxic to the mustard
beetles. Coumarins appear to act as kairomones for certain insects that are special-
ized for feeding on coumarin-containing plants (Berenbaum 1991b).
Among the phenolics, flavonoids are found in nearly all higher plants, and most
plants show their own distinctive flavonoid profile. The flavonoids share a basic C6-
C3-C6 structure, which is linked to a sugar moiety to form a water soluble glycoside.
Common examples of flavonoids isolated from plants are catechin, botanical insec-
ticide rotenone and phaseolin, all of which act as feeding deterrents against insects
(Schoonhoven et al. 2005).
Tannins are polyphenolic compounds commonly found in higher plants. The
phenolic hydroxyl groups of tannins bind to almost all soluble proteins, producing
insoluble copolymers. Proteins bound to tannins are indigestible and thus decrease
the nutritional value of plant tissues (Schoonhoven et al. 2005).
Latex Latex is present in specialized cells called laticifers and consists of chemi-
cally undefined milky suspensions or emulsions of particles in an aqueous fluid
(Agrawal and Konno 2009). Laticifers have a defensive function. Small insects may
be physically trapped in latex or their mouthparts may get glued together, and chem-
ical constituents in latex including proteins and toxins affect insect development
(Dussourd 1995). Wounding of laticifers by insects results in leakage at wound site
(Mithofer and Boland 2012). In the milkweed, Hoodia gordonii (Masson) Sweet ex
Decne, both larval feeding and adult oviposition by T. ni was deterred when latex
was added to artificial diet or painted on the leaves of the host plant (Chow et al.
2005).
capsule width of rootworm larvae. Wiseman et al. (1992) reported a highly signifi-
cant negative relationship between weights of corn earworm, Helicoverpa zea
(Boddie), as well as the fall armyworm, Spodoptera frugiperda J. E. Smith, larvae
and maysin concentration in the silks of a large number of corn entries.
developed several adaptive mechanisms to avoid the toxicity of tannins. The poten-
tial mechanisms insects use to avoid toxicity of tannins include alkaline gut pH,
tannin absorption through peritrophic membrane, polymerization and excretion of
the polyphenols after concentration (War and Sharma 2014). The surfactants formed
as products of lipid digestion in the gut lumen prevent precipitation of proteins
(Martin et al. 1987). Oxygen levels in foregut also play an important role in toxicity
of tannins. At higher pH, oxygen levels are low and reduce autoxidation of tannins,
thereby lowering their toxicity. The antioxidative system of insects also plays an
important role in reducing the tannin toxicity. For example, ascorbate reduces the
oxidation of tannins and formation of reactive oxygen species (ROS) in insect gut
(Krishnan and Sehnal 2006). The grasshoppers possess a strong midgut antioxida-
tive defence, which enables them to withstand tannins. This antioxidative defence
mainly comprises of glutathione, α-tocopherol and ascorbate. The tolerance to tan-
nins, and its association with peritrophic membrane in S. gregaria, has been attrib-
uted to the ultrafiltration of tannins. In some species including Melanoplus
sanguinipes (Fabricius), tannic acid does not bind to the peritrophic membrane. In
addition, peritrophic membrane protects the insect epithelium against lesions and
damage by ROS by adsorbing highly reactive ferrous ions (Barbehenn 2003).
Table 1.2 Variations in responses of wheat and Hessian fly during compatible and incompatible
interactions
Compatible interaction Incompatible interaction
Larval growth completed in 10–12 days Larvae die within 5 days of attack
No larval growth
Gut shows signs of toxin exposure
Seedling apical shoot meristem death Seedling survival
Shorter plants, fewer heads, fewer seeds
Increased cell permeability at attack sites Localized cell death
Accumulation of reactive oxygen species
Creation of nutritive cells Adjacent living cells fortified
Cell wall breakdown Transient increase in permeability
Epicuticular waxes accumulate
Membrane permeability increases Toxin production increases
Stress-related proteins increase Class III peroxidases increases
C/N ratio shift favours N (52% change) Phenylpropanoid metabolism increases
Nutrient metabolism and transport
increases
Cell wall metabolism decreases Cell wall and lipid metabolism increases. Nutrient
metabolism and transport suppressed
Basal defence response suppressed Fatty acid degradation suppressed
Phenylpropanoid metabolism suppressed Phospholipid metabolism suppressed
Histones and structural proteins decrease Stress-related protein decrease
Modified from Stuart et al. (2012)
As many as 35 distinct resistance genes (H1-H3, h4, H5-H34 and Hdic) from
wheat and related plants have been characterized and incorporated in commercial
wheat cultivars (Chen et al. 2006; Stuart et al. 2012). The HF-wheat system is con-
sidered a model system for study of gene-for-gene (GNG) interaction between host
plants and insect pests (Hatchett and Gallun 1970; Subramanyam et al. 2015). In the
case of resistant cultivars carrying R genes, the plants respond to attack of HF larvae
by accumulation of reactive oxygen species (Liu et al. 2010) and production of
enzyme inhibitors (Wu et al. 2008), lectins (Williams et al. 2002; Subramanyam
et al. 2008) and secondary substances (Liu et al. 2007). On the other hand, the com-
patible interactions are characterized by increased nutrient availability at the site of
attack along with an accumulation of nitrogen-rich molecules (Liu et al. 2007;
Williams et al. 2011). It has been revealed that the HF is able to overcome resistance
through recessive mutations in corresponding avirulence (HFAvr) genes (Aggrawal
et al. 2014). The HFAvr genes code for proteins (called effectors) that are injected
with the saliva in to the plant tissue during feeding (Hogenhout et al. 2009). The
plants carrying R genes are able to recognize these secretions and stimulate the
defence pathways (Chisholm et al. 2006). In virulent HF biotypes, the Avr proteins
are modified to avoid either detection by the plant or a failure to trigger the defence
pathway (Chen et al. 2016).
1 Insect-Plant Interrelationships 25
As early as 1859, Darwin in his magnum opus On the Origin of Species wrote of
‘Coadaptations of organic beings to each other…’. Every living organism interacts
with others of the same as well as another kind. Coevolution refers to genetic change
in two interacting species. In other words, coevolution is reciprocal evolutionary
change in interacting species. The term was originally used by C.J. Mode in 1958
for the coevolution of obligate parasites and their hosts. Ehrlich and Raven (1964)
were the first to extend its relevance to insect-host plant coevolution based on their
study of Monarch butterfly-milkweed (host plant) interactions.
A plant is neither susceptible to all the phytophagous insects nor any insect spe-
cies is a pest on all the species of plants it encounters in nature. Further, less than
one third of all insect orders contain exclusively (Lepidoptera, Orthoptera,
Phasmida), predominantly (Hemiptera, Thysanoptera) or partially (Coleoptera,
Diptera, Hymenoptera) phytophagous species. But such species comprise nearly
half of all insect species. This is attributed to the fact that all plants have developed
a dazzling array of structural and biochemical defences (constitutive as well as
induced) against herbivores. Only those species which are able to breach these
defences in one or more plant species can access such plants for food (Arora 2012).
The insects thus keep on developing strategies for detoxifying or otherwise over-
coming these defensive mechanisms.
The extant phytophages and their host plants are the result of a coevolutionary
process that has been ongoing for nearly 400 Myr (Labandeira 2013). Insects have
acquired a sensitive system for perceiving their external environment, analysing the
sensory input and responding to it suitably (Martin et al. 2011). Successful host
finding and acceptance are primarily controlled by chemical cues. The insect
responses are dependent on a combination of host and environmental cues (Riffell
et al. 2009; Webster et al. 2010). Concomitantly, the plants have also evolved numer-
ous structural and chemical defences for protection against insects and other herbi-
vores. The insects in turn have evolved to avoid or overcome these defences. A
number of theories have been propounded to explain this evolutionary arms race
between these two interdependent groups of organisms.
This theory was elaborated by Ehrlich and Raven (1964) and later supported by
Berenbaum (1983). According to this theory, many plant taxa manufacture a proto-
typical phytochemical that is mildly noxious to phytophages and that may have an
autecological or physiological function in the plant. Some insect taxa feed upon
plants with only this and other, similarly mild, phytochemicals, thus reducing plant
fitness. Plant mutation and recombination cause novel, more noxious phytochemi-
cals to appear in the plants. The same chemical can appear independently in dis-
tantly related plant groups. Insect feeding is reduced because of toxic or repellent
26 R. Arora and S. Sandhu
properties of the novel phytochemical; thus plants with more and more potent
defences are preferred by the pressure of insect herbivory. In response, the insects
have evolved the capacity to avoid or neutralize the effective chemical and even
utilize the same compound as well as the plant producing it for their own benefit. An
insect can specialize in feeding upon plants with the novel compound. Here it would
be free to diversify due to a lack of competition from non-adopted herbivores. The
cycle may be repeated, resulting in more phytochemicals and further specialization
of insects.
Some supporting evidence for the theory is available from species-level studies
on taxa of selected insects and their host plants. Closely related Phyllobrotica spe-
cies feed monogamously on closely related Scutellaria species as revealed by the
cladograms of the two groups (Farrell and Mitter 1990). Evidence is also available
at the level of populations. An analysis of different populations of wild parsnip,
Pastinaca sativa Linnaeus, and its specialist herbivore pest the parsnip webworm,
Depressaria pastinacella Duponchel, revealed trait matching between
furanocoumarin- based chemical defences in the plants and cytochrome P450
monooxygenase- based insects’ detoxification profiles (Berenbaum and Zangerl
1998, Zangerl and Berenbaum 2003).
An interesting example of coevolution is that involving the brassicaceous plants
and the pierid butterflies. The glucosinolate-myrosinase system evolved by
Brassicales (Sect. 1.3.2.3) around 90 Myr represents a key step in anti-herbivore
defences by plants. But shortly thereafter, the Pierinae butterflies which utilized
Fabales as host plants came up with a detoxifying system in the form of nitrile-
specific protein (NSP) and started colonizing the Brassicales. This resulted in
increasing the species diversification rates in Pierinae as compared with that of their
sister clade Coliadinae, whose members did not colonize Brassicales, thus lending
strong support to the coevolutionary theory (Wheat et al. 2007; Edger et al. 2015).
The theory of sequential evolution (Jermy 1976, 1984) proposes that evolution of
herbivorous insects follows the evolution of plants, without however significantly
affecting plant evolution. According to this theory, reciprocal selective interactions
between plants and herbivorous insects have not been proved so far. Plants undeni-
ably cause evolutionary changes in phytophagous insects, whereas the latter exert
selective pressure on the plants only in rare cases and even in these only weakly. The
insects choose their host plants largely based on perception of chemical cues.
Therefore, any changes in chemical composition of host plants or their chemosen-
sory perception by insects may lead to emergence of new insect-host plant relation-
ships. However, contradictory paleontological evidence in the form of insect familial
diversification preceding the major diversification of angiosperms contradicts this
theory. As a consequence, speciation in herbivorous insects may be mediated by
plants, but speciation in plants has not been proved to occur as a consequence of
interaction with herbivorous insects.
1 Insect-Plant Interrelationships 27
The theory of diffuse coevolution proposes that, instead of the pairwise reciprocal
evolutionary interactions, coevolution must be considered in a community context
and not simply as a reciprocal two-species interaction. Every plant may be affected
by a diversity of herbivores, plant pathogens, competing conspecifics, plants of
other species including alternate host plants of insect pests and organisms at higher
tropic levels (Fox 1988). This theory is thus only an extension of the coevolutionary
theory.
This theory states that the coevolutionary process operates at the level of popula-
tions rather than at species level. Thompson (1994, 1999, 2005) propounded that
interspecific interactions commonly differ in outcome among populations. These
differences result from the combined effects of differences in the physical environ-
ment, the local genetic and demographic structure of populations and the commu-
nity context in which the interaction occurs. As a result of these differences in
outcomes, an interaction may coevolve some populations (coevolutionary hot spot),
affect the evolution of only one of the participants in other populations (coevolu-
tionary cold spot) and have no effect on evolution in yet another local population
(again coevolutionary cold spot). In addition, populations differ in the extent to
which they show extreme specialization to one or more species. Some populations
may specialize on and sometimes coevolve locally with only one other species,
other populations may specialize on and perhaps coevolve with different species
and yet others may coevolve simultaneously with multiple species. These inter-
populational differences in outcome and specialization create a geographic mosaic
in interactions. Gene flow among populations, random genetic drift, selection for
novel traits and extinction of some demes reshape the geographic mosaic of coevo-
lution as the adaptations and patterns of specialization developed locally spread to
other population or are lost. The result is a dynamic geographic pattern of coevolu-
tion between any two or more species.
The coevolutionary relationship between the obligate seed predator, the camellia
weevil, Camellia japonica Linnaeus, and its host plant, the Japanese camellia,
Camellia japonica Linnaeus, represents an interesting example of geographic
mosaic across the Japanese islands (Toju and Sota 2006, Toju et al. 2011). The
thickness of camellia pericarp through which the female weevils bored to lay eggs
into seeds correlated with the length of rostrum in females. Further, the pericarp was
significantly thicker on islands with weevils than on islands devoid of weevils, and
the trait was heritable.
28 R. Arora and S. Sandhu
and cyfluthrin became popular insecticides during the 1980s (Dhaliwal and Arora
2006). Similarly synthetic analogues of nicotine, another popular botanical insecti-
cide obtained from tobacco, called neonicotinoids are currently widely used against
a broad range of sucking insect and mite pests (Simon-Delso et al. 2015). Thus,
botanical insecticides have not only proved useful directly in pest control but have
also served as models for generation of new classes of synthetic insecticides. Since
plants contain tens of thousands of such chemicals, the scope of their utilization in
insect pest management is almost endless.
which biotype development has led to breakdown of resistance in the field (Aggrawal
et al. 2014; Subramanyam et al. 2015). The durability of insect resistance can be
increased by sequential release of cultivars, gene pyramiding/stacking and gene
rotation (Sandhu and Arora 2013). An improved understanding of insect-plant inter-
actions is crucial for efficient management of insect biotypes resulting in greater
stability of resistant genotypes.
The losses caused by weeds are estimated to be higher than those caused by insect
pests to agricultural crops and the global use of herbicides exceeds that of insecti-
cides in crop protection (Oerke 2006). In view of the widespread problems caused
by extensive use of herbicides, there is an urgent need to strengthen biological con-
trol of weeds. Exotic weeds may be successfully managed by introducing monopha-
gous or oligophagous insect species from the plants’ place of origin. Important
successful examples include management of shellmound prickly pear, Opuntia
stricta (Haworth) Haworth, in Australia through releases of the small Argentinian
moth, Cactoblastis cactorum Berg (Dodd 1940), and of giant salvinia, Salvinia
molesta D. S. Mitchell, in Papua New Guinea by releasing the weevil Cyrtobagous
salviniae Calder & Sands imported from Brazil (Room 1990). In Hawaii extensive
programmes on biological control of weeds through releases of herbivorous insects
as well as pathogens have been undertaken, resulting in complete control of 7 out of
21 target weed species and significant partial control of another 3 species (Gardner
et al. 1995; McFadyen 2003).
In some cases, the native insects have also been artificially multiplied and
released or otherwise manipulated for the control of native weeds. Native coccids,
Austrotachardia sp. and Tachardia sp., are used for the control of Cassinia sp.,
native woody shrubs in Australia (Holtkamp and Campbell 1995). Conservation/
augmentation of the stem-boring agromyzid, Phytomyza orobanchia Kaltenbach,
has been utilized for managing the parasitic weeds, Orobanche spp. in the southern
USSR (Kroschel and Klein 1999).
Insect pollinators are essential for successful pollination and reproduction by a vast
majority of terrestrial flowering plants. Even self-pollinating crop species may show
yield enhancement in vicinity of a good pollinator habitat. Coffee shrubs, for
instance, show significant yield increases in regions with stable native or introduced
bee populations (Roubik 2002). Most studies on plant-pollinator systems have
focused on a single plant species and usually one or a few closely associated visitor
taxa. But recent studies have revealed that pollinator complexes are relatively gen-
eralized, due to spatiotemporal variation in pollinator visits (Herrera 1996; Waser
1998; Burkle and Alarcon 2011). It is important to understand the bases of spatial
1 Insect-Plant Interrelationships 33
1.7 Conclusions
Insects and green plants, the two dominant life forms in the terrestrial ecosystem,
are bound together by intricate relationships. A majority of the angiosperms require
the services of pollinating insects for successful reproduction. The shape, size,
colour and scent of flowers all serve to attract pollinators, which mostly feed on
nectar and pollen produced by these plants. Further, nearly half of all insect species
are herbivorous and depend on plants for food, shelter (at least for a part of life
cycle) and oviposition sites. Consequently, the plants have evolved a staggering
variety of structural and biochemical barriers to protect themselves from insects and
other herbivores, as well as pathogens. The insects which are able to overcome these
barriers (through avoidance, detoxification, sequestration, etc.) can gain an abun-
dant supply of food with very little competition from other herbivores. Reciprocal
adaptation and counter-adaptation between plants and insects have, thus, been an
important mechanism driving a steady increase in biodiversity of both these groups
of organisms over the last more than 400 million years.
The study of these interrelationships between insects and flowering plants is of
great practical importance for future agricultural production. We are only just begin-
ning to understand the intricacies of these relationships. The new techniques of
molecular biology including genomics, proteomics and RNAi offer exciting oppor-
tunities for further exploration and precise understanding of insect-plant interac-
tions, which is essential for conserving ecosystem biodiversity and developing
insect-resistant crop plants, as well as for sustainable management of insect pests
and weeds.
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