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Seminararbeit, 2007, 36 Seiten
Autor: Anne Hegge
Fach: Afrikawissenschaften
Details
Institution/Hochschule: Universität Bayreuth
Tags: Integrated, Pest, Management, African, Agriculture, Diversität, Pflanzenfamilien, Afrika
Jahr: 2007
Seiten: 36
Note: 1,0
Sprache: Englisch
ISBN (E-Book): 978-3-640-08972-7
Dateigröße: 132 KB
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Universität Bayreuth
Fachbereich Biologie
Lehrstuhl für Tierökologie
Hausarbeit
Integrated Pest Management in African Agriculture
vorgelegt von:
Anne Hegge
Studentin der Geographischen Entwicklungsforschung Afrikas
Bachelor of Arts
Abgabetermin: 27.03.2007
Table of Contents
I. Integrated Pest Management in African Agriculture
1 Introduction 3
1.1 Theory and Tactics of Pest Management 3
2 Conventional insecticides 5
2.1 DDT and chlorinated hydrocarbons 6
2.2 Botanical insecticides 7
2.3 Pyrethrum vs. Pyrethroid 8
3 Biological control 10
3.1 Natural enemies 10
3.2 Biocontrol of cassava pests 13
4 Insect growth regulators 18
4.1 Juvenile hormone agonists 20
4.2 The practice of IGRs 22
5 Biotechnology 23
5.1 Bacillus thuringiensis 24
5.2 Management of maize pests in agribusiness 25
6 Conclusions and prospectus 28
II. Bibliography 31
2
1 Introduction
The history of mankind is a history of ambitions to get control over the environment.
With the beginnings of agriculture, people suffered from crop losses due to insect
pests that they henceforth tried to control.
Today global losses caused by pests are estimated to be US$ 300 billion annually,
an amount equal to 30-40% of potential food, fiber and feed production.1 Facing the
predictions of ongoing human population growth, there is a need to increase food
production. Since World War II the use of chemical pesticides for agricultural
intensification has led to dramatic yield increases in crops. But the control of insect
pests on a long-term has not been achieved, rather severe problems concerning pest
resurgence, undesirable environmental effects and human health problems have
been the consequences - especially in developing countries. With the evident need of
adapted pest control, the concept of integrated pest management yields hope to
become a sustainable method of pest control for the future.
1.1 Theory and Tactics of Pest Management
There are various approaches to control pests in agriculture. According PEDIGO
1996, there are four main strategies to deal with insect pests:
1. Doing-Nothing
2. Reduce number of pest insects
3. Reduce susceptibility of the host
4. Combinations of 2 and 3.
At first sight, the Doing-Nothing Strategy seems to be preposterous, as a pest is
harming the plant. But often, the host plant tolerates the insect pest with no
consequences on economic losses in crop production. Therefore, the Doing-Nothing
Strategy is always appropriate when pest densities are below the economic
threshold. When densities reach the economic threshold as well as in a preventive
manner, the Reduce-Number Strategy is applied. It is the most widely used strategy
in pest management and various tactics are utilized. Most of the tactics aim to
increase mortality of the pest by creating of intensifying hazards to insects. This may
be via natural enemies, insecticides, many resistant cultivars, ecological
modifications or insect growth regulators. The Reduce-Number Strategy can work on
1 cp.: Natural Resource Institute in: Thomas 1999, p. 5944
3
reducing the carrying capacity so that the general equilibrium position2 is lowered
and highest population peaks will not reach the economic threshold. When the
general equilibrium position is low compared to the economic threshold, dampening
population peaks is the tactic. The strategy to reduce crop susceptibility does not
modify the insect population at all. It minimizes crop losses by involving elements of
host plant resistance or manipulations of the crop environment (e.g. fertilizer).
Reducing the susceptibility to insect injury is considered to be one of the most
effective strategy, while the last strategy, the combination of Reduce-Number and
Reduce-crop-susceptibility has less vulnerability to failure. The diversification of
strategies prevents economic losses when one tactic fails. 3
The integration of several compatible tactics to a sustainable pest management
program is the goal of Integrated Pest Management (IPM). The application of a single
tactic often fails in the long term because of insect′s ability to adapt to it. When
several tactics are used in a combined program, the possibility to recover is lowered
and sustainability of the pest management system can be achieved. Due to the
application of different tactics, the use of pesticides decreases, so that integrated
pest management systems are also less harmful to the environment.
Definitions of Integrated Pest Management are various, ranging from a single
separation from the conventional use of chemicals:
"use of various methods to combat pests as opposed to utilizing a single
approach (chemicals)" [www.biotech.ca]
to a complex proposal:
"A systems approach that combines a wide array of crop production practices
with careful monitoring of pests and their natural enemies. IPM practices
include use of resistant varieties, timing of planting, cultivation, biological
controls, and judicious use of pesticides to control pests. These IPM practices
are used in greenhouses and on field crops. IPM systems anticipate and
prevent pests from reaching economically damaging levels"
[www.soils.ncsu.edu].
This paper aims to give a general overview of selected practices of IPM methods,
accentuated on African agriculture.
As the insecticide era began with the discovery of DDT in 1939, chapter 2 outlines
the importance and impact of conventional insecticides. To demonstrate that the term
2 the pest′s long term average density
3 cp.: Pedigo 1996, p. 286ff
4
insecticide does not always imply the devastating characteristics of DDT, .also
botanical insecticides as part of IPM systems will be presented.
Moving from the insecticide era to the emerge of pest management in the 1950s,
Chapter 3 deals with biological control as the axiom of integrated control.
The African staple crop cassava, one of its major pests and the control by natural
enemies will be portrayed as a typical case study of biological control.
The integration of control techniques expanded in later years to include other
techniques. Referring to this, chapter 4 deals with the capabilities of insect growth
regulators with emphasises on juvenile hormone agonists.
Chapter 5 moves to today′s daily headlines: the use of insect-resistant genetically
modified plants for cultivation and human food consumption.
A final conclusion summarizes the different tactics of Integrated Pest Management
and leads to a critical perspective on the approach of truly integrated pest
management.
2 Conventional insecticides
Derived from the Latin suffix ,,cida" [killer], the word insecticide literally means killer of
insects. The word pesticide is used in a more general context, meaning killer of any
pest. Besides insecticides, pesticides include acaricides (mite and tick killers),
herbicides, fungicides and nematicides. Conventional insecticides are mostly
chemicals used for the control, prevention, destruction, repellence or mitigation of
pests. Most conventional insecticides are nerve poisons killing insects very quickly
while nonconventional insecticides, such as microbial insecticides and insect growth
regulators, show slower actions and are not operating on the insect′s nervous
system.
Pesticides are some of the most important chemicals for the wellbeing of humans. As
they are maintaining human beings nutrition they have a great impact on our
existence. Pesticides in agriculture are sustining and irreplaceable for the current
quality and quantity of food and fibre production. After the development of modern
synthetics in the 1940s, pesticide use increased constantly till the early 1980s when it
reached an all-time high. For now, insecticides account for over one third of
pesticides used in agriculture of the USA, about 750 insecticidally active ingredients
are registered in the US Environmental Protection Agency (EPA).4
4 cp.: Oregon State University 2007, http://oregonstate.edu/~muirp/pesthist.htm
5
The great advantage of insecticides is their short-time effectiveness. Within hours,
the active compounds of insecticides are working in the insect′s body and a pest
population can be depleted within few days. In an economic sense, insecticides offer
an easy way to prevent yield losses. They are easy to apply, even for unskilled
persons and cost/crop ratio is around four to five dollars return for every dollar
invested.5
Nonetheless, insecticides have great impacts if they are used frequently. Main
disadvantages on the agro-system are insecticide resistance, pest resurgence and
pest replacement. Furthermore, insecticides are also harming non-target species like
honey bees, fish and wildlife in and around the agroecosystem. Additionally,
insecticides can also be toxic to humans, applying insecticides or consuming
products treated with insecticides. On that score, the use of insecticides cannot be
calculated just by the cost/benefit ratio in terms of the crop. 6
But compared to alternative uses in pest control, the benefits of insecticides still lead
to accept the risks. Anyhow, a maximal output with minimal risks has not been
achieved in most situations. Therefore alternative pest management technologies are
the topic of this paper.
2.1 DDT and chlorinated hydrocarbons
DDT is one of the most popular or better unpopular insecticides. DDT
(dichlorodiphenyltrichloroethane) belongs to the group of chlorinated hydrocarbons,
which are containing chlorine, hydrogen, carbon and sometimes sulphur and oxygen.
Chlorinated hydrocarbons are the first widely used synthesized organic insecticides
but due to environmental and human safety, their use has been restricted in most
countries of the world. While insecticides of other groups are relatively unstable and
broken down by enzymes in animals, in the environment of microorganisms, heat or
ultraviolet light;7 DDT, DDE TDE, dieldrin, aldrin, HCH and its isomers show high
stability and fat solubility. This causes a phenomenon called biomagnification. Unable
to be metabolized active pesticide residues are stored in nonlethal doses in the body
fat of animals (e.g. cows) fed on plants treated with DDT. From there it gets to the
humans body when fat-containing products (e.g. milk) are consumed.8
5 cp.: Pedigo 1996, p.366
6 cp.: Gatehouse, Gatehouse 1998, p.212
7 cp.: Oregon State University 2007, http://oregonstate.edu/~muirp/pesthist.htm
8 cp.: Pedigo 1996, p. 381
6
Besides mammals, also invertebrates fed on plants or detritus (such as predators)
store DDT residues in their tissues. Facing the food chain in every ecosystem,
rodents, fish, reptiles, amphibians and other insectivores are ingesting and
concentrating the insecticide residues. Other top predators (e.g. hawks or owls) fed
on these primary predators are yet accumulating higher doses of insecticide
concentrations. Looking on the food chain from down to up, the total biomass is
decreasing while the concentration of nonmetabolized pesticide residues increases.
Thin eggshells and reproductive failures are the consequences, and lead to the
decline of predators like ospreys, falcons, eagles, seagulls, pelicans and others.9
2.2 Botanical insecticides
Botanical (= plant derived) insecticides are natural plant materials or products derived
from plant materials. They have been used for centuries in tribal or traditional cultures
before introducing to Europe and North America in the late 1800s. In the U.S., the
application of botanical insecticides reached its peak in the 1960s. Thenceforward, a
steady decrease took place. Today, they represent a very small part of insecticides
annually used in the world.10
Nevertheless a resurgence of botanical products seems to have a great potential
because new effective and environmentally safe products have been discovered
recently. Thereto novel synthetic insecticides can be developed from insecticidally
active plant products.11
The use of botanical insecticides declined with the discovery and increasing
development of synthetic insecticides in the 1940s and 1950s. The newer synthetic
organic insecticides were less expensive, longer lasting and more effective than the
botanicals, which are expensive to extract, to test for environmental and human
toxicity and generally impractical for commercial use. Botanical insecticides are no
safer than the synthetics.12
The word botanicals does also not imply that they are not toxic or "nonchemical",
botanical insecticides are toxic to pest and beneficial insects so that - if they are
applied repeatedly - they have the potential to disturb the natural biotic control of
pests by natural enemies. It would be adverse to consider plant-derived toxins as
9 cp.: Pedigo 1996, pp. 381-383
10 cp.: Weinzierl 1998, p. 101ff
11 cp.: Pedigo 1996, p. 385
12 cp.: Weinzierl 1998, p.102f
7
harmless, although their limited persistence in the environment helps to minimize
undesired effects.13
Nonetheless botanical insecticides remain important in pest control for the following
three main reasons:
1. "They sometimes provide the most effective control of insect pests that have
become resistant to other insecticides.
2. Most are short-lived in the environment, and they pose relatively low risks to
nontarget organisms, including the beneficial predators and parasites [...], the
higher level predators in food chains, and the human consumer of treated
crops.
3. They are naturally occurring or derived or manufactured with minimal
technology, so they are sometimes accepted by organic certification programs
or by certain consumer groups; they also may be more readily available than
synthetic insecticide in developing countries."14
Therefore, botanical insecticides, as well as insecticidal soaps and oils, may be
agents in biological control systems rather than conventional insecticides, although in
practice, they are mostly not.
Currently, botanical insecticides of to plants are used for insect pest control. The first
one is neem, extracted from the neem tree (
Azadirachta india
) and sold under the
name Ornazin, AZA-Direct and Azatin.15 Neem insecticides are acting as insect
growth regulators. Therefore, neem will be discussed in chapter 4.
The second one is pyrethrum, which is by far the most widely used botanical
insecticide.
2.3 Pyrethrum vs. Pyrethroid
Pyrethrum is an extract from flower petals of
Chrysanthenum
cinerariefolium
and the
related species
C
.
coccineum
which are grown commercially in Kenya, where the
flowers have highest concentrations of active compounds.16, Moreover pyrethrum
daisies grow in Ecuador, and were once cultivated in Eastern Europe, the Middle
East and Japan.17
13 cp.: Weinzierl 1998, p. 103
14 Weinzierl 1998, p.101f
15 cp.: Cranshaw 2003, p.44
16 cp.: Weinzierl 1998, p.104
17 cp.: Casida 1973, Matsumura 1985 in Weinzierl 1998, p.104
8
The active compounds of pyrethrum are called pyrethrins. These constituent esters
are pyrethrin I and II, cinerine I and II and jasmolin I and II. Pyrethrin I and II, which
are the pyrethrole ester of chrysanthemic (I) resp. pyrethric (II) acids, offer highest
concentrations in pyrethrum.18
Pyrethrins are contact poisons acting on the nervous systems. They are influencing
the nerve transmission where they are slowing or preventing the shutting the sodium
channels in nerve axons.19 Mammals react with whole body tremors, insects are
convulsing or hyperactive.20 A few minutes after application, the insect cannot fly or
move away. But a knockdown dose does not mean the killing of the insect
population. Insect pests can recover because the natural pyrethrin is swiftly detoxified
by enzyms. Therefore pyrethrins have been synthetically derived. The core chemical
structure of synthetic pyrethrin, which is known as pyrethroid resembles natural
pyrethrin. To improve features, such as persistence, synthetic pyrethrins have been
modified to yield a more stable molecule. Carabamates, organophosphates or
synergigsts may be added to delay the enzyme action and a lethal dose is assured.21
This makes pyrethroids more toxic to humans and nontarget animals than natural
pyrethrin.22 But compared to conventional insecticides, pyrethroids are more effective
and safe in application. That is why they are replacing many older insecticides and
are the fastest growing group of modern insecticides. Currently, pyrethroids are
categorized in four generations of development; the third and fourth-generation
pyrethroids are the most widely used. Fourth-generation pyrethroids are the most
potent. In comparison with third-generation pyrethroids, only one tenth of third-
generation application rates in needed to achieve the same results. Even third-
generation application rates are very low; while 1.1 to 2.3 kg of actual ingredient per
hectare is needed using organophosphates or carbamates, only 0.11 kg of actual
ingredient per hectare is needed to protect various crops using third-generation
pyrethroids.23
The advantages of synthetic pyrethrins are diverse. In contrast to natural pyrethrin,
pyrethroids are able to induce quick knockdown effects and less recovery of
poisoned insects. They are highly toxic to insects at very low rates and are broken
18 cp.: Weinzierl 1998, p.104
19 cp.: Bloomquist 1996 in Weinzierl 1998, p.104
20 cp.: Weinzierl 1998, p.104
21 cp.: Oregon State University 1994, p.1
22 cp.: Cranshaw 2003, p.42
23 cp.: Pedigo 1996, p.378
9
down by ultraviolet light after 4 to 7 days.24 The most factor important for the
integration of pyrethroids in pest management systems is the economic advantage:
pyrethrum is too expensive to use commercially and therefore mostly used as a
household chemical. Pyrethroids are commercially used in agriculture, especially to
maize, soybeans and cotton fields.
3 Biological control
"use nature as a partial ally, not as a total adversary"25
Perkins 1996
Biological control is the oldest form of managing insect pests. Already in fourth-
century China, ants were used by humans to suppress caterpillars and beetles in
citrus horticulture.26
A natural enemy, like the ant in ancient China, feeds on the host or prey to extend its
own population at the expense of the pest population. Natural enemies are living
organisms, which kill or weaken insects so that pest population number reduces. For
many species, natural enemies are the main regulating force for their low population
number. Other reasons can be unfavourable weather conditions or missing material
requisites like food or nesting sites. Since nearly all insect populations are effected by
natural enemies, the knowledge about natural enemies leads to the understanding of
pest densities and the prediction of pest outbreaks.
Biological control is defined as the pest management tactic in which the manipulation
of natural enemies leads to the reduction of a pest population. Different from natural
control, biological control, or bio-control, does not implement other agents than
natural enemies, like the use of weather or food.27
3.1 Natural enemies
In the theory of biological control, the pest population is seen as the perfectly density-
independent factor which is regulated by the imperfectly density-dependent factor,
the natural enemy. In a self-sustaining system, the pest population density is kept
24cp.: Pedigo 1996, p.378
25 Perkins in Pedigo 1996, p.
26 cp.: Orr, Suh 1998, p.4f
27 cp.: Pedigo 1996. p.301f
10
under the economic injury level, so that food supply and reproductive capability of the
natural enemy is ensured without eliminating the pest which would include the death
of the natural enemy as well. The changes in natural enemy numbers are called
numerical response. When natural enemies destroy more pests per individual, a
functional response has taken place.28
Natural enemies of insects are diverse and include first of all insects themselves, but
also vertebrates, nematodes, microorganisms and invertebrates other than insects.
They are divided into parasites, parasitoids, predators or pathogens. The following
description of these control agents is according to PEDIGO 1996.
Parasites
A parasite feeds from the host it lives in or on, weakening or killing it. Insects,
nematodes and to a lesser extent mites are parasites with the greatest impact on
insect pest populations. There are frequently many parasites in one specific part of
the host.
Parasitoids
A parasitoid is an insect that parasitizes other insects or arthropods at any host
stage. A parasitoid is only parasitic in its immature stage. The free living adult lays its
eggs inside the host or attaches them outside.
Parasitoids are the most effective agents in biological control because
- of their good survival,
- they only need one (or less) host for development,
- they survive on low host populations,
- their narrow host range leads to a good numerical response to host density.
Nevertheless occur problems with parasitoids in biological control because
- weather and other forces reduce the host searching capacity,
- only the female are searchers
- the best searchers often lay few eggs,
- synchronization is often a difficulty.
The synchronization of the parasitoid life-cycle with that of the host is often interfered
by adverse environmental conditions.
86 families in the orders Coleoptera, Diptera, Hymenoptera, Lepidoptera, Neuroptera
and Strepsiptera are known as parasitoids. Small parasitic wasps of the families
Ichoneumonidae, Braconidae and Chalcidoidae are the most important parasitoids.
28 cp.: Pedigo 1996. p.303ff
11
Besides these Hymenoptera, the Tachinidae of the order Diptera play a significant
role in biological control.
Besides beneficial parasitoids, there are some that are nonbeneficial. Parasites living
on parasitoids are a threat for the success of a biological control program. The
phenomenon of a secondary parasite living on the primary parasite is called
hyperparasitism.
Predators
Predators are free-living individuals that feed on their prey in their immature and adult
stages. Predators need more than one prey to reach maturity, often devouring the
whole prey. Insect and mites have been the most successful predators in biological
control, especially Coleoptera, Neuroptera, Hymenoptera, Diptera and Hemiptera.
They are monophagus and oligophagus predators. In a group, predators are
considered polyphagus as they tend to accept a wide range of prey. In terms of
biological control, polyphagus species have the advantage that they survive low pest
densities as they have the ability to move to alternate prey. This can be also a
disadvantage when the predator does not suppress the growing pest population. The
difficulty of control lies in the prediction of the density response from food availability
alone. Biological control with predators has the advantage that
- predators kill their prey very fast,
- often immatures and matures of both gender are searching for the prey,
- synchronisation of predator and prey life-cycle is no difficulty.
Although parasitoids have been used more often than predators for biological control,
it is impossible to predict the best natural enemy as it depends on the particular
agroecosystem, the pest and the environmental circumstances. Hence, the best
management tactics are those including predators and parasitoids as natural
enemies.
Pathogenic microorganisms
Pathogenic microorganisms are used as microbial insecticides that are often applied
in a similar way to chemical insecticides. Microorganisms with impact on insect pests
are bacteria, viruses, protozoan and fungi. Mostly bacteria, fewer viruses and fungi
are used for pest control as they kill insects very quick. The spore-forming bacteria
are the most important species, particularly the genus Bacillus. The disadvantage of
the most successful bacteria (
Bacillus popilliae
and
B. lentimorbus
) is that it is difficult
and expensive to propagate them in vitro.
12
Future advances in biotechnology should allow a modification of fastidious microbial
pathogens for easier reproduction. Also the propagation of host-insect tissue from
single cells is expected. The expansion of the killing spectrum and improved
environmental stability through biotechnology has already been applied on Bt by
Ecogen Inc. and Mycogen Corp. The use of Bt as part of genetic engineering will be
further discussed in chapter 5.
3.2 Biocontrol of cassava pests
The following case study aims to portray a typical African crop, one of its pests and
biological methods to control it.
The cassava host plant
Cassava (
Manihot
esculenta
) was introduced to Africa by the Portuguese who took it
from South America. It penetrated into the interior of the continent only in the 20th
century but quickly became popular as adaptation has never been a problem.
Cassava grows on poor soils and can endure prolonged drought and is easily
propagated by its offshoots. Compared to other food crop in Africa, it gives the
highest output on the lowest input. Cassava is the crop of the poor. It is the main
staple food for about 200 million Africans, particularly in the poor countries.29
For centuries cassava has been relatively free from insect pest in Africa. Endowed
with a high cyanide and latex content in stem, leave and tuber, it has high natural
plant defences and was little attacked by arthropods in Africa, whereas in South
America co-evolved some 200 insects feeding on cassava. The situation changed
dramatically when in the early 1970s two pests invaded simultaneously the African
continent. The cassava mealybug was inadvertently introduced into to Republic of
Congo and D.R. Congo (former Zaire) in 1973; the first outbreaks of cassava green
mite pest were in Uganda. Both pests had been introduced by illegally imported plant
material from South America and quickly spread across almost all the African
continent.30
In West Africa it spread at 300km -1 per year, natural barriers like the Rift Valley
decelerated the spread of
P. manihoti
in East Africa.31 Within 20 years, nearly the
entire cassava belt32 was infested by the cassava mealybug.
P. manihoti
became the
number one pest of cassava on the continent, severely affecting the livelihood of
29 cp.: Lundborg 1999 p.22
30 cp.:Neuenschwander 2003, p.45
31 cp.:Herren, Neuenschwander 1991, p.259
32 Main exceptions are Madagascar and the Indian Ocean Islands
13
poor people.33 The losses of the farmers are estimated to be in the range of US$ 2
billion per year, cassava prices of 1999 were five times higher than two years ago.34
The cassava mealybug
Since the practice of biological control requires a comprehensive study of the
organisms involved in the control program, this chapter gives a short overview of the
main characteristics and the ecology of cassava mealybug.
Mealybug is the common name for insects of the Pseudococcidae. This family of
unarmored scale insects is found in warm, moist climates. The Mealybug is soft-
bodied with no outer shell like other scale insect families (e.g. Diaspididae). They are
covered by a white waxy powder. Pseudococcidae have filamentous projections
around the perimeter.35
Being sexually dimorphic, female mealybugs are wingless; they exhibit reduced
morphology and nymphal characteristics while males have wings and change their
morphology during their lives. Like other Homoptera, mealybugs are hemimetabolous
insects, meaning that they do not undergo a complete metamorphosis. However,
male mealybugs pass a radical change during their life cycle, changing from
wingless, ovoid nymphs to flying adults.36
Mealybugs are considered as pests because of feeding from plant juices of
greenhouse plants, house plants and subtropical trees. The females are responsible
for the name
mealy
bug because of secreting a powdery wax layer to protect their
environment while sucking plant juices. As adults, the males do not feed at all; their
short-time adult stage is for fertilizing the female.37 The most destructive pests are
the cassava mealybug and the mango mealybug (
Rastrococcus invadens
).
The cassava mealybug (
Phenacoccus manihoti
; Homoptera, Pseudococcidae) is a
pathenogenic insect with three nymphal instars. It is subsisting from
Manihot spp.
,
where it colonizes the cassava tips, but also found on other plants infrequently.38
The cassava mealybug population size has its optimum in the dry season. Owing to
the washing effect of the rain and the renewed growth of the cassava tips, cassava
mealybug populations collapse during the rain season. When the plant substrate
becomes unacceptable, it also occurs that the population drops even before the rainy
33 cp.:Neuenschwander 2003, p.46
34 cp.:Lundborg 1999, p.22
35 cp.:IPM of Alaska: 2005 www.ipmofalaska.com/files/mealybugs.html
36 cp.:Jahn, Beardsley 1998, p.73
37 cp.:Jahn, Beardsley 1998, p.74f
38 cp.:Herren, Neuenschwander 1991, p.262
14
season starts. Dispersal over long distances is by animals and humans. Cassava
mealybugs move with crawlers that are picked up by air currents. Also human spread
P. manihoti
by transporting infested plants.39
Mealybugs are found in warm, moist climates40, the cassava mealybug has a low
thermal threshold of 14,7 °C and shows no development above 36 °C. The optimal
temperature is about 28 °C. All life table parameters differ from plant varieties, but
not by the leaf age. The net reproductive rate is about 500 eggs, on stressed plants,
all life table parameters are marginally better.41
Most mealybugs are stunting the roots of their host plant42.
P. manihoti
is attacking
the cassava tips to suck plant sap with its mouthparts43. The shoot tips get stunted,
leaf distortion, yellowing and total leaf loss are damage symptoms of stunted
plants44. Due to the stop of leaf production, carbohydrates cannot be accumulated in
the tuber ceases. The early mobilisation of sugars causes results in severe quality
decline of tubers. Beside the loss of tubers and leaves for alimentation, contorted
stems become useless as planting material.45
The progress of biological control
The outstanding biological control program of the International Institute of Tropical
Agriculture (IITA) to control cassava pest in African agriculture, exemplifies the
different steps towards the implementation of biological control.
With the financial aid from the International Fund for Agriculture Development, the
IITA, headed by Hans Rudolf Herren in 1980 and 1981, initiated the Africa-wide
Biological Control Project (ABCP). The IITA Biological Control Program developed a
control strategy that began with the systematic exploration of the origins of the pest.
The second step was the rearing of the most promising natural enemies and their
taxonomic and biological characteristics as well as ecological impacts. After that, the
release of the selected natural enemies in Africa was started. The study also included
an analysis of the socio-economic impact of the pest. 46
Polyphagus and oligophagos predators and parasitoids attack the cassava
mealybug, They found a new food source when the cassava mealybug appeared in
39 cp.: Herren, Neuenschwander 1991, p.262
40 cp.:Jahn, Beardsley 1998, p.74f
41 cp.: Herren, Neuenschwander 1991, p.263
42 cp.:Jahn, Beardsley 1998, p.74f
43 cp.:Herren, Neuenschwander 1991, p.262
44 cp.:IPM of Alaska 2005 www.ipmofalaska.com/files/mealybugs.html
45 cp.: Neuenschwander 2003, p.47
46 cp.: Herren, Neuenschwander 1991, p258
15
Africa. 20 species are common in Africa and were identified to have some impact.
Coccinellid are important predators. They occur when the cassava mealybug
infestation is high but suffer from high parasitism. Other predators are the host-
specific cecidomyiid
Didrodiplosis manihoti
and the lycaenid
Spalgis lemolea
, which
occur unsteady. A few indigenous Hymenopterus parasitoids of the genus
Anagyrus
were found as well. 47
After the detection that the
Phenacoccus manihoti
in an invasive species which has
its origin the Neotropics, several researches started in South America to explore
natural enemies of
P. manihoti
. The parasitoids that were found on what researchers
thought to be
P
.
manihoti
, did not reproduce on mealybugs in Congo and former
Zaire because of misidentification of the cassava mealybug, which was not
P.
manihoti.
After 30 years of research on cassava in the Neotropics,
P. manihoti
was
finally identified in Paraguay in 1981 by A. C. Bellotti, working for the Centro
International de Agricultura Tropicana (CIAT). Following explorations showed that the
cassava mealybug has its origins in the Paraguay River basin where
P. manihoti
populations there are low and unsteady.48
It was Dr. Maajid Yaseen, principal entomologist of the Commonwealth Institute of
Biologiacl Control (CIBC), who discovered the parasitoid, which was selected for the
use in the biological release program. The encyrted parasitoid
Epidinocarsis lopezi
is
a parasitoid wasp which lays its eggs inside mealybugs where the larva feeds on the
intestines, killing the bug.49 In addition to that "
star enemy
"50, the coccinellid
predators
Hyperapsis raynevali, H. notata
and
Diomus spp
were introduced as well,
but played a marginal role compared to the principal agent
E. lopezi
. Even many
other predators and parasitoids became less abundant after the distribution of the
exotic parasitoid.51 E. lopezi became the most important parasitoid, wherever it was
established.
Epidinocarsis lopezi
Desantis (Hymenoptera: Encyrtidae) has some special
characteristics that made it an effective biocontrol agent:
Due to the shorter generation time compared to the host, its population has the
capacity to grow larger than that of the mealybug. Besides host-feeding and the
ability for mutilation,
E. lopezi
prevents the successful reproduction of the mealybug
47 cp.: Herren, Neuenschwander 1991, p.263
48 cp.: Herren, Neuenschwander 1991, p.260f
49 cp.: Lundborg 1999 p.23
50 Lundborg 1999 p.23
51cp.: Smith, Bellotti 1996, p.6
16
if it is not killed directly. Because of its high specificity, searching and dispersal
capacity, it survives even in case of low host population densities. This way,
E. lopezi
fills an ecological niche without competition less specialized competitors. In addition,
E. lopezi shows density-dependent aggregation and reproduction on most host
population densities.52 These features are not given the other tested natural enemies
so that
E. lopezi
was selected for the cassava mealybug control in Africa and
successfully did.
By 1987, eight of the 18 species of natural enemies that were found in the distribution
area of cassava mealybugs, were sent to England where rearing and host specificity
tests were done by CABI Bioscience. After the multiplication by the IITA in Ibadan
(Nigeria) and later in Cotonou (Benin), the first natural enemies of
P. manihoti
were
exposed in Nigeria and later send to various other African countries. Within three
years, parasitoids has spread over 200 000km2 in southwestern Nigeria. Until end of
1985, over 50 releases in 12 African countries has been done, by 1990
E. lopezi
covered an area of more than 12.7million km2 consisting of 24 countries. The
parasitoid established in all ecological zones that were infested by the mealybug.
Currently, the mealybug no longer poses a threat to most cassava growing regions in
30 African countries. 53
The biological control over cassava pest has shown great success in ecological and
economical matters.
Cassava yield losses decrease gradually by 10% during the first year to 90% in the
fifth year. In an economic sense, a cassava yield worth $1.7 billion will be saved after
the eighth year.54 In the savannah a great reduction of stunted cassava tips from
88% to 3% has taken place, the cassava yield increased by 2500kg/hectre compared
to areas were
E. lopezi
had not been established yet.55 SCHAAB 1996 estimated the
costs and benefits of the whole program from 1974-2013 to $49 million and $9.4
billion so that, depending on the scenario, the cost/benefit ratio ranges between
1:170 and 1:431. NEUENSCHWANDER and HERREN 1991 estimated a cost/benefit
ratio of 1:149 which would still be enormous compared to alternative pest control
strategies mentioned in the previous chapters.
52 cp.: Herren, Neuenschwander 1991, p.266
53 cp.: Neuenschwander 2003, p.48
54 cp.: Lundborg 1999, p.23
55 cp.: Smith, Belloti 1996, p.6
17
The $49 million required for exploration, biological studies, mass rearing, release and
impact studies is a one-shot investment. Once the natural enemies are established, a
natural balance between them and the host will follow so that no continuous costs for
the farmers are emerging. The case study showed that the classical approach to
biological control can be a very successful method for the control of serious insect
pests in African agriculture. IITA′s Africa-wide Biological Control Project, under the
direction of Hans Rudolf Herren, who was awarded the World Food Price for in 1995,
not only saved one of Africa′s major staple crops and farmers billion of dollars, but
demonstrated a reliable method of controlling serious insect pests on an international
level. The success of the program gives a momentum necessary for future programs
to manage other pests like the maize stem borer or insects on cowpeas via biological
control. As several exotic pests have invaded and in future times probably will
continue invading the African continent, the use of exotic parasitoids and predators
will be necessary. The establishment of invasive species always requires a
comprehensive study of the plant to be saved, the pest and its natural enemies, the
agrosystem and ecosystem to inhibit the threat of imbalances or undesired long-term
consequences.
4 Insect growth regulators
Besides the proved success of managing pests by methods of biological control, a lot
of anticipation is placed in the use of insect growth regulators to control insect pests.
This chapter demonstrates the function and impact of insect growth regulators on
insect pests and gives an idea of their use in pest management systems.
Insect growth regulators are pesticides that mimic the action of hormones on the
growth of insects.56
The insect′s developmental physiology is regulated by hormones produced by
endocrine glands. Molting and metamorphosis are regulated and initiated by brain
hormones, ecdysone and juvenile hormones. Brain hormones are secreted by
neurosecretory cells in the location of the pars intercerebralis. After linkage to
environmental stimuli with other hormone systems, the brain hormones get in the
blood. This causes the stimulation of the prothoracic gland which secretes ecdysone.
The result is that the insect molts. The concentration of the juvenile hormones from
the corpora allata in the blood is the determining factor for the body form of the
56 cp.: Cranshaw 2003, p.44
18
insect. A larva at full growth with a complete metamorphosis has a reduced
concentration of juvenile hormones, in the next molt the pupal form emerges. The
decreasing concentration of juvenile hormones allows the active growth of imaginal
disks. These cells have the potential the express the adult character in the following
molt. In a gradual metamorphosis, juvenile hormones reduce gradually so that in the
absence of juvenile hormones the adult stage emerges. Juvenile hormones can also
have reproductive functions influencing ovary development and egg yolk production.
Furthermore, juvenile hormones can stimulate diapause, behaviour, communication,
caste differentiation and morphogenesis. 57
As described above, juvenile hormones play a prominence role in the insect life
cycle. Through the interaction of hormone agonists and antagonists, growth and
metamorphosis can be stimulated. Insect growth regulators offer great potential
because of disrupting life processes that are unique to the insects.
Besides these chemicals disrupting metamorphosis there have been also developed
chemicals hat are modifying insect′s behaviour. Both are working on systems that
vertebrates do not have. Hence they seem to be a safe alternative to conventional
insecticides, which have no selective activity.58 Already mentioned in chapter 2,
conventional insecticides affect the insect′s nervous system. Facing that insect′s
nervous systems function in the same way like other animal′s nervous systems do,
conventional insecticides got a broad poisoning power. The use of these chemicals is
hazardous as it can cause harm to nontarget organisms. Insect growth regulators are
often attacking only one specific group of insects.59 For example Lepidoptera show
minimal toxicity for beneficial predators and parasitoids.60
First generation insecticides are the stomach poisons, second-generation
insecticides are contact poisons. Due to environmental safety and advanced
development, insect growth regulators (IGRs) are described as third-generation
insecticides. They are applied with insecticide equipment on a specific area.
Different from conventional insecticides, timing is more important and a limiting
factor, considering that IGRs can only function on immature insects.61 Due to this
insect′s stage sensibility, it is difficult to achieve a rapid breakdown of the insect pest
population and pest presence or levels of injury must be tolerated longer than with
57 cp.: Pedigo 1996, p.456f
58 cp.: Pedigo 1996, p.455
59 cp.: Cranshaw 2003, p. 44
60 cp.: Beckage 1998, p.123
61 cp.: Pedigo 1996, p.455f
19
conventional insecticides. This disadvantage can be avoided by using compounds
that have a longer in-vivo half life, so that it remains in the body until the insect′s
sensibility to IGRs is high. Disrupting the metamorphosis, juvenile hormone
antagonists are used for long-term control, whereas ecdysone antagonists cause an
unsuccessful molt within 24h. The antifeeding effects of azadirachtin show up
immediately, leading to disruption of molting. 62
4.1 Juvenile hormone agonists
Juvenile hormone agonists are highly effective IGRs causing a wide range of
development disturbances. Impacts on susceptible insects are disturbance of
embrogenesis, larval development, metamorphosis and reproduction. Compounds of
juvenile hormone agonists are the terpenoids methoprene and hydroprene as well as
the nonterpenoids fenocxycarb and pryproxyfen. 63
Azadirachtin
Azadirachtin is a tetranortriterpenoid found in the seeds of the Indian neem tree
(
Azadirachta indica
). This plant is for long time known as source for pharmaceuticals
in Asia and Africa.64 Neem seed extracts contain besides oils several compounds
affecting insect development. The most important is azadirachtin. This biological
insecticide has a strong antifeedant and repellent activity and shows pleiotropic
effects on growth, development and reproduction on chewing and sucking
phytophagous insects and stored product pests. More than 200 species are
susceptible, including aphids, lepidopterans, hemipterans, cockroaches, beetles and
orthopterans. Azadirachtin is translocated into the tissues of infested plants, but can
also reach insects via the leaf surface or by direct contact. It also works in water,
affecting aquatic species like mosquitoes. The affected insects often die during a
molt, usually a week or longer after treatment.65
The slow effects and narrow range of susceptible insects are the main disadvantages
of neem insecticides. Azadirachtin has shown excellent selectivity, it has minimal
effects on nontarget arthropods and no adverse effects on fish and livestock have
been detected. There are no environmental effects because residues are broken
down in sunlight and rainfall.66 Although this fact makes it safe in use, neem′s field
62 cp.: Beckage 1998, p.124
63 cp.: Beckage 1998, p.127
64 cp.: Cranshaw 2003, p.44
65 cp.: Beckage 1998, p.129ff
66 cp.: Pedigo 1996, p.456
20
performance has failed in many pest control uses because of low persistence and
and limited effectiveness in the presence of rain or sunlight.67 Nevertheless, its use is
highly recommended because of the broad-spectrum control and very low toxicity. 68
Terpenoids
Methoprene and kinoprene
Methoprene is affective on Diptera, Siphonaptera, Coleoptera and some Lepidoptera
and Homoptera. 69 Sold under the name Altosid®, it is used against mosquitoes and
horn flies (
Haematobia irritans
) attacking cattle.70 It disrupts the embryogenesis and
egg hatch. Mosquitoes are killed as larvae and as pupae, preventing the rotation of
the male genitalia. In houseflies and other Diptera, methoprene adverts adult
emergence. Maggots of the horn flies that feed on cattle dung are killed by
methoprene that is administered to animal food.71 Administered on Lepidoptera, it
causes molting to supernumerary instars and formation of intermediates. Kabat® is
sold to suppress Coleoptera and Lepidoptera and in stored tobacco.72
In African cotton farms, as well as in other parts of the world, methoprene is widely
used because of enhancing silk production in silk worms (
Bombyx mori
). Methoprene
and also fenoxycarb applied during summer season are helping to get improved
cocoon yield. Prolonging the larval life of insects, these two juvenile hormones
analogues cause improved quantitative and qualitative parameters of cocoon and silk
like cocoon and shell weight, silk filament length, winding capacity or tenacity.73
Kinoprene is attacking Homoptera, such as whiteflies.74
Fenoxycarb and pyriproxyfen
Fenoxycycarb and pyriproxyfen are nonterpenoidal juvenile hormones that have
recently appeared on the market and have been very successful because of greater
stability in the environment, compared to the terpenoid juvenile hormone agonists.
Fenoxycarb causes sterility, death of insect eggs, permanent larvae, and formation of
nonviable intermediates. It interferes with metamorphosis and affects caste
differentiation. The non-neurotoxic carbamate shows activity on a wide range of
67 cp.: Weinzierl 1998, p.112
68 cp.: Cranshaw, p.44
69 cp.: Beckage 1998, p.127
70 cp.: Pedigo 1996, p. 460
71 cp.: Beckage 1998, p.128
72 cp.: Pedigo 1996, p. 460
73 Mamatha et al 2006, www.academicjournals.org
74 cp.: Beckage 1998, p.128
21
insects, including Heteroptera, Lepidoptera, Hymenoptera, Coleoptera, Diptera,
Dictyoptera, Isoptera, and Homoptera.
Besides inducing permanent larvae in the silkworm (B. mori), it successfully inhibits
the development of the parasitoids Phanerotoma ocularis and Pseudoperichaeta
nigrolineata.
Other IGRs, such as methoprene also have impact on the emergence and
methamorphosis of parasitoids, but the effects seem less detrimental compared to
the effects of conventional neurotoxis pesticides.75
Another potent juvenile hormone agonist is pyriproxyfen. It is active on a wide range
of arthropods including ants, fleas, mole crickets, mosquitoes, flies, whiteflies, scales,
cockroaches, ticks as well as Lepidoptera. Like methoprene, it hinders the emerge of
horn flies, face flies and house flies from dung of cattle or other animals fed with
pyriproxyfen. Pyriproxyfen can also be applied directly on the horn fly.
Like the other juvenile hormone agonists discussed above, pyriproxyfen has multiple
impacts on a single species. Applied on the desert locus (
Schistocerca gregaria
), it
disrupts embryogenesis and metamorphic molt and leads to morphological
deformities.76
4.2 The practice of IGRs
The mentioned examples have shown that IGR have a wide range of application
against insect pests. For the effective implementation of IGR such as juvenile
hormones, which are thought to be the most appropriate for the control of insect
pests, STAAL 1975 has set certain requirements. The conditions, under which the
pest management should be applied, must include at least one of the following:
1. "Larvae of the pest species do not cause damage; only the adults are
perceived as harmful or nuisance.
2. Individual insects or low numbers are not harmful; only large populations that
expand through several short population cycles are significant (greenhaouse
Homoptera, stored product pests, and mushroom pests).
3. Environments where applied have a high degree of protection against
breakdown factors, particulary sunlight (most applications).
4. Environments are enclosed and thus protected against massive reinfestations
(stored products, greenhouses).
75 cp.: Beckage 1998, p.128
76 cp.: Beckage 1998, p.129
22
5. Sedentary insect targets (low mobility) are not likely to resurge quickly
because of reinfestation (scale insects, mealybugs).
6. Special instances exist in which the safety of the compound and the lack of
other control methods are the prevalent considerations (pharaoh ant
[Monomorium pharaonis])."77
This conditions required show that juvenile hormone agonists are most appropriate
where the infestation is from insects pests with short life cycles and enclosures
protect residues. In addition, there should be no need for immediate control and a
low number of infections can be tolerated.
Facing the selective activity among insects, often specific to one family or one group
of insects (for example caterpillars), the use of IGRs is compatible with the activity of
natural enemies of insect and mite pests.78
It can be concluded that IGRs are an acceptable modern pest management
technique, offering a compromise in selectivity between the less desirable extremes
of narrow specificity and broad-spectrum activity. The selective requirements are
satisfied so that a widely integrated use of IGRs and especially juvenile hormone
agonists in IPM tactics can be expected in the future.
5 Biotechnology
Biotechnology is the latest strategy to manage insect pests. The use of biotechnology
in various areas affecting human beings life is currently on of the most discussed
topics. To set an example for the use of biotechnology, this chapter provides vital
information about biotechnology and its achievements with
Bacillus thuringiensis
.
The Convention of Biological Diversity defined in 1992 the term biotechnology as
"any technological application that uses biological systems, living organisms, or
derivatives thereof to make or modify products or processes for specific use"
.79 In the
media, the term biotechnology is represented in many different ways and meanings.
Biotechnology is a technology that implies:
"1. genetic engineering for producing vaccines and improving plants and animals,
2. monoclonal antibodies for diagnosis of cell proteins,
3. new cell and tissue techniques for rapid propagation of living cells."80
77 cp.: Staal 1975, Pedigo 1998, p. 460f
78cp.: Cranshaw 2003, p.44
79 cp.: World Foundation for Environment and Development 2004 http://www.wfed.org/resources/glossary/
80 Pedigo 1996, p.441
23
In agriculture, biotechnology gives hope to solve many insect pest problems by the
development of new plant cultivars resistant to insect pests. Even though the
revolution in plant breeding and wide-scale mechanism of agriculture have brought
high yielding crop varieties and have protected the developed world from food
shortage, still famines and chronic shortages of calories supply are present in the
developing world.
As demonstrated before, the indiscriminate use of pesticides is a not sustainable
agriculture practice in the long term. Many insects have become resistant to
pesticides and have become even a greater problem than it was before the pesticide
was introduced. Therefore, a number of less harmful pesticides and methods of
biological control have been developed. Still, they do not give such high levels of
return on a short term level. As demonstrated in the example of managing the
mealybug pest on cassava, it took several years to achieve a reduction of pest
infestations.
For these reasons, genetic engineering for insect resistance of crops has been
enthusiastically adopted by government authorities and the agricultural industry.81 It
is asserted that new transgenic crops will reduce pesticide use and increase
productivity "
a promise that developing countries desperately want to believe
".82
Biotechnology allows the extension of the gene pool available to a specific species.
Genetic engineering of natural enemies of insects and mites by using recombinant
DNA technology currently includes viruses, protozoa, predators and parasitoids and
insect pathogens, such as bacteria.83 At present, resistant plants are developed by
inserting the gene responsible for producing delta endotoxin into the plant genome.
This gene comes from the insect pathogen
Bacillus
thuringiensis
.84
5.1 Bacillus thuringiensis
Bacillus
thuringiensis
(Bt) is a soil dwelling bacterium that also occurs on some plant
surfaces and in caterpillars of some moths and butterflies. Upon sporulation, Bt forms
a crystalline protoxin protein (cry toxin). The cry toxin is encoded by the cry gene
carried on a plasmid within the bacterium. Cry toxins have specific activities against
species of Lepidoptera, Diptera and Coleoptera. When these insects ingest the
spores, the protoxin is cleaved and active Bt toxin molecules are generated. After
81 cp.: Gatehouse, Gatehouse 1998, p.213
82 Kuyek 2002, p.1
83 cp.: Harrison, Bonning 1998, p.244
84 cp.: Pedigo 1996, p.443
24
binding to a specific glycoprotein receptor on the epithelial cells, the toxin inserts
itself into the gut cell membrane. There, the bound toxin causes ion channels in the
cell membrane of the gut epithelial cells. The free passage of ions leads to an
imbalance of ion concentration. The result is the death and lysis of the cells lining the
gut, leading rapidly to the insect′s death. The carcass serves as a substrate for the
growth of Bt. After sporulation, fresh spores get into the soil so that the cycle is
completed.
Thus, Bt serves as an important reservoir of Cry toxins and cry genes for production
of biological insecticides and insect-resistant genetically modified crops.
The use of Bt preparations (mostly sprays) as an conventional insecticide is very
limited. The proteins quickly break down in ultraviolet light and the spray is washed
from the plant surfaces in wet weather. But the high toxicity of Bt toxin protein,
together with the easy task of isolating the encoding gene made Bt evident for the
development of transgenic plants.85
Currently, there are many discussions about the use of the genetically modified
maize, which "
will benefit African farmers through increased yields and disease
resistant crops
"86, says biotechnology stakeholder AfricaBio. Therefore, the following
case study demonstrates the current discussions concerning the use of bt maize to
control insect pests in Africa.
5.2 Management of maize pests in agribusiness
As the focus of previous described pest management systems was given to the
practical application, this chapter wants to portray the maize pest with emphasis on
the decision-making forces behind pest management.
Maize
(Zea mays
L. spp.
mays
) is the second most important food crop in Africa.
95% of total maize production is done by small and medium scale farmers across the
whole continent in different ecological conditions.87 Besides a number of
environmental factors like droughts or soil fertility, various insect pests are main
constraints to farmers, who grow maize in resource-poor systems. About 20-40% of
the potential yield can be decimated by the larvae of certain moths: cereal
stemborers.88 The ICIPE (African Insect Science for Food and Health) even
85 cp.: Gatehouse, Gatehouse 1998, p.214f
86 Venter 2005 http://www.africabiotech.com/news2/article.php?uid=129
87 cp.: DeVries; Toenniessen in Kuyek 2002, p.12
88 cp.: Kuyek 2002, p.12
25
estimates to yield losses in chronically infested areas between 10-70%.89
Gramineous stemborer pests occur in nearly every maize cropping90 and are
therefore considered to be the most damaging insect pests91. The various species of
cereal stemborer pests in Africa are all indigenous, except
Chilo partellus
, which
invaded the continent from Asia. In 1930, it was first found in Malawi, from where it
spread over whole East and Southern Africa, at times displacing indigenous species.
Chilo partellus
quickly became the most injurious pest for maize and sorghum.92
But still, indigenous stemborers have an economical importance throughout the
continent as their occurance is depending on the elevation. In West Africa the
pyralids
Eldana
saccharina
and
Mussidia
nigrivenella
and the noctuids Sesamia
calamistis
and
S
.
botanephaga
occur most frequent. The noctuid
Busseola
fusca
is
the main pest in Cameroon and Central Africa, prevalent in all altitudes, while in East
and Southern Africa, it causes economic injuries in areas above 1000 meters above
sea level. The crambid
Chilo partellus
has economic importance in both lowlands and
mid-altitudes and is moving up to higher altitudes.93 At present, 50% of all maize
plantations in developing countries show insect pest infestations, alone in Kenya,
stemborers allayed the ultimate harvest of 15%.94
The introduction of genetically modified maize seems to be an easy solution to get
out of this regression. Crylab, a bt gene that have been introduced into maize and
commercially released in the U.S., is proven to be effective against African insect
pests. African farmers who used bt maize have seen increased yields with lower
inputs of pesticides. The decreased health risks together with increased yields and
incomes, must outweigh the risks of the new technology, affirms KANAMPIU 2002,
stressing the easy method of application as African farmers "
prefer their inputs being
in the form their most used to the seed and not insecticides
".95
Proponents of biotechnology are claiming that bt maize will relieve hunger around the
world. But does bt maize really meet the needs of the vast majority of African small
scale farmers? Who is interested in the introduction of bt maize in Africa?
Facing the global importance of maize production, it is not surprising that stemborer
pest control became a major interest for agribusiness. The industry focussed in
89 cp.: ICIPE 2006 http://stemborer.icipe.org/
90 cp.: Kuyek 2002, p.13
91 cp.: Youdeowi in Overholt et al 1996, p.1
92 cp.: Overholt at al 1996, p.1
93 cp.: ICIPE 2006 http://stemborer.icipe.org/
94 cp.:Kanampiu 2002, p.108
95 cp.:Kanampiu 2002, p.108
26
particular on the incorporation of bt-gene. All bt maize is sold by large seed Trans
National Corporations (TNCs) who also hold the patents on the relevant
technologies. In South Africa, where in 1999 over 50 000 hectars of bt maize were
planted; the market for transgenic seeds is controlled by the seed TNCs Monsanto,
Pioneer Hi-Bred and Pannar.96
Transnational pesticide corporations are pushing genetic engineering into agriculture
by investing in agricultural biotechnology. The buyout of seed companies and
financing Research and Development (R&D) secures the monopoly over the control
of genes and leads to privatisation of biodiversity. Private and public sector have
become allies of the industry that will spread their technologies throughout Africa.
Merchandising genes is an industrialist′s interest but does not meet the needs of
most African subsistence farmers.97
The bt maize sold by the TNCs has been incorporated in maize varieties for
commercial use and are therefore not suitable for small scale farmers with no market
access. Pioneer Hi-Bred runs a program for such subsistence farmers, but without a
specific breeding program designed for that area, where the bt hybrid maize was
introduces for "
philanthropic reasons
"98. Private and public sector did little research
into maize for small scale farmers. For the mid-altitudes of Kenya, where small
farmers grow 40% of Kenyans maize, no adapted variety has been developed by the
public sector. The Kenya Agricultural Research Institute (KARI) focussed on the high
potential lands, where cash crops are grown on big farms.
This case from Kenya is not a single one which demonstrates that governments are
not meeting the needs of small farmers.
Fact is that small farmers have already developed cultural control techniques to fight
pest infestations. Additionally direct applications such as neem or pyrethrum have
shown success in pest management. In the case of maize infestations with
stemborers in Kenya, biological control strategies have shown that the infestation
rate can be reduced by 53%. In 1991, ICIPE has released the natural enemy of
Chilo
partellus
on different sites in Kenya. The result was that not only the exotic stemborer
could be controlled by the parasitic wasp
Cortesia
flavipes
Cameron (Hymenoptera:
96 cp.: Mwangi, Ely 2001, www.biotech-monitor.nl/4803.htm
97 Cp: Kuyek 2002, p.14f
98 Kuyek, 2002, p.13
27
Braconidae), but also three other stemborer varieties were attacked by the exotic
parasitoid.99
Concluding that great achievements has already been done in the development of
genetically modified crops to control insect pests in the far future, genetically modified
crops will not solve the fundamental problems affecting African small farmers. If so,
the root causes of poverty, which lay in land distribution, market constraints and
affordable technologies and practices that work with on-farm resources, such as soil
and water management, biodiversity conservation strategies and mixed cropping
systems would be addressed.
6 Conclusions and prospectus
With the beginnings of agriculture people suffered from crop losses due to insect
pests and developed various tactics and techniques of pest management. After
World War II, the use of conventional insecticides such as DDT was thought to be the
solution to eliminate any insect pest. Indeed, pesticides are pre-eminent on their
short-time effectiveness, but on a long term the use of pesticides resulted in the
direct opposite. Not only insecticide resistance, pest resurgence and pest
replacement were the effects; as DDT and related pesticides do not easily break
down in the environment, they accumulated in the food chain and spread throughout
ecosystems with devastating effects. While conventional pesticides are therefore not
suitable for the integration in pest management systems, botanical insecticides
quickly break-down in the environment and show lower risks to nontarget organisms.
Especially in African developing countries botanical insecticides may be potential
control agents as they are naturally occurring and minimal technology is needed for
production. But as the comparison between natural pyrethrin and synthetic pyrethroid
has shown, the use of botanical insecticides in the practice is limited to the non
commercial use while pyrethroids have been established on commercial crop fields.
The third generation of insecticides are insect growth regulators. While most
pesticides are acting on any nervous system and are therefore toxic to nontarget
organisms, insect growth regulators provide environmental safety and high
specificity. Juvenile hormone agonists have been widely used to control different
pests such as the desert locus, or even enhanced silk production in Africa. Therefore,
99 cp.: Overholt at al 1996, p1ff
28
IGRs are highly recommended for Integrated Pest Management because of
compatibility with the activity of natural enemies.
The practice of biological control has currently proven to be a successful method to
manage pests on the long term. The cassava mealybug, which had become a
serious pest throughout the African cassava belt, is nowadays controlled by the
Africa-wide establishment of the parasitoid
Epidinocarsis lopezi
. Different from the
application of insecticides, biological control provides a reliable mechanism of pest
control by the same time offering an excellent cost/benefit ratio.
Another way to face insect pests is the development of insect-resistant plants by
using recombinant DNA technology. Bt maize may be able to fight serious maize
pests in African agriculture systems, like the stemborer
Chilo partellus
. But in a
political sense, genetically modified crops do not pose a sustainable method to
control insect pest as the use of genetically modified crops is causing unpredictable
risks for environmental and human wellbeing. From the viewpoint of African small
scale farmers, the use of genetically modified crops additionally creates new
dependencies on a socio-economic level in the way that the negative impacts
outweigh the suspected benefits. Therefore, genetically modified crops in African
agriculture are neither supporting the empowerment of farmers nor following the
concept of IPM to be user-orientated.
It has been figured out that various strategies have been developed and applied to
control insect pests; all of them seem to have specific advantages as well as
disadvantages. The paper has shown that in recent years, the focus of controlling
pests has been either on short-term or/and single technology interventions. The
biological control program to fight the cassava mealybug for instance, has replaced
the use of chemical by another single technology. Strategies of pest management
are still dominated by a single technology (e.g. biological insecticides, IGRs or
biological control) instead of implementing Integrated Pest Management systems in
its true sense which means the break away from the search for the "magic bullet".
Only a combination of different tactics and techniques can address the problems of
sustainable agriculture.
No matter which methodological or technical advances in improved food production
are identified to become part of IPM, effective implementation with social and
economical benefits for African farmers will only be assured by appropriate economic
and political support.
29
Truly integrated pest management is the only answer to fight food insecurity in its
roots which means the reduction of poverty. The eradication of extreme poverty and
hunger and an ensured environmental sustainability are point 1 and 7 of the
Millennium Development Goals. If the United Nations want them to be realized by
2015 they have to take in account that the implementation of IPM has to become a
major subject. So far, the realization of Integrated Pest Management remains one of
the most challenging goals to achieve a sustainable food production on a global
level.
30
II. Bibliography
Beckage, N. E.: Insect Growth Regulators. In: Rechcigl, J.E; Rechcigl, N.A: Biological
and Biotechnological Control of Insect Pests. Boca Raton (Florida) 1998
Cranshaw, W.: Classes of Pesticid Used in Landscape/Nursery Pest Management.
In: Tactics and Tools for IPM. Minnesota 2003
http://www.entomology.umn.edu/cues/Web/042ClassesOfPesticides.pdf (21.03.2007)
Gatehouse, J. A.; Gatehouse A. M. R.: Genetic Engineering of Plants for Insect
Resistance. In: Rechzigl, J.E.; Rechcigl, N.A.: Biological and Biotechnological Control
of Insect Pests. Boca Raton (Florida) 1998
Government of British Columbia, Ministry of Agriculture, Food and Fisheries
Pesticide Info: Pyrethrin. British Coumbia 2001
http://www.agf.gov.bc.ca/pesticides/infosheets/pyrethrin.pdf (16.03.2007)
Harrison, R.L.; Bonning, B.C.: Genetic engineering of Biocontrol Agents for Insects.
In: Rechcigl, J.E.; Rechcigl, N.A.: Biological and Biotechnological Control of Insect
Pests. Boca Raton (Florida) 1998
ICIPE (African Insect Science for Food and Health): African Stemborer Information
System. Nairobi 2006
http://stemborer.icipe.org (12.01.2007)
IPM of Alaska: Integrated Pest Management Bulletin. Wasilla 2005
www.ipmofalaska.com/files/mealybugs.html (16.03.2007)
Jahn, G. C.; Beardsley, J.W.: 1998. Presence/ absence sampling of mealybugs, ants,
and major predators in pineapple. In: Plant Protection in the Tropics 11(1). Oxford
1998
31
Kanampiu, F.; Ransom, J.; Gressel, J.; Jewell, D.; Friesen, D.; Grimanelli, D.;
Hoisington, D.: Appropriateness of Biotechnology to African Agriculture:
Striga
and
maize as paradigms. In: Plant Cell, Tissue and Organ Culture 69. Amsterdam 2002
Kuyek, D.: Genetically Modified Crops in African Agriculture Implications for Small
Farmers. 2002
www.grain.org/briefings/?id=12 (14.01.2007)
Lundborg, G.: Insect vs Insect. Biological Control of Crop Pests on the Fields of
Africa. International Development Research Centre Ottawa. Ottawa 1999
http://idrinfo.idrc.ca/archive/ReportsINTRA/pdfs/v13n3e/110878.pdf (16.03.2007)
Mamatha, M.D.; Cohly, H.P.P.; Raju, A. H. H.;Rajeswara Rao, M.: Studies on the
quantitative and qualitative characters of cocoons and silk from methoprene and
fenoxycarb treated
Bombyx mori
(L) larvae. In: African Journal of Biotechnology Vol.
5 (15) 2006
http://www.academicjournals.org/AJB/abstracts/abs2006/3Aug/Mamatha%20et%20al
.htm (10.03.2007)
Mwangi, P.N.; Ely A.: Assessing Risks and Benefits: Bt maize in Kenya. In:
Biotechnology and Development Monitor, No 48. Amsterdam 2007
www.biotech-monitor.nl/4803.htm (19.03.2007)
Neuenschwander, P.: Biological Control of Cassava and Mango Mealybugs in Africa.
In: Neuenschwander, P., Borgemeister, Ch., Langewald, J.: Biological Control in IPM
Systems in Africa. Wallingford, Cambridge 2003
Oregon State University: Pesticide Information Profiles: Pyrethrins and Pyrethroids
In: EXTOXNET Extension Toxicology Network. Oregon 1994
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Oregon State University: A History of Pesticide Use. 2007
http://oregonstate.edu/~muirp/pesthist.htm (16.03.2007)
32
Orr, D.B.; Suh, C. P.-C.: Parasitoids and Predators. In: Rechcigl, J.E.; Rechcigl, N.A.:
Biological and Biotechnological Control of Insect Pests. Boca Raton (Florida) 1998
Overholt, W.A.; Ngi-Song, A.J.; Omwega, C.O.; Kimani-Njogu, S.W.; Mbapila, J.;
Sallam, M.N.; Ofomata, V.: An Ecological Approach to Biological Control of
Gramineous Stemborers in Africa: The introduction and establishment of
Cotesia
flavipes
Cameron (Hymenoptera: Braconidae). In: University of Minnesota: Radcliff′s
IPM World Textbook. International Centre of Insect Physiology and Ecology. Nairobi
1996
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Pedigo, L. P.: Entomology and Pest Management. New Jersey 1996
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study on the cassava mealybug
Phenacoccus manihoti
mat.-Ferr. Marburg 1997
Smith, L.; Bellotti, A.C.: Successful Biocontrol Projects with Emphasis on the
Neotropics. Cornell Community Conference on Biological Control 11 13 April 1996.
Cali (Columbia) 1996
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Thomas, M.B.: Ecological approaches and the development of "truly integrated" pest
management. Proceedings of the National Academy of Science of the United States
of America. Volume 96,1999 . Colloquium Paper from Natl. Acad. Sci. colloquium
"Plants and Population: Is there time?" Irvine (California) 1998
Venter, B.: GM Maize to Help African Agriculture. Pretoria News from 11.04.2005.
Pretoria 2005
http://www.africabiotech.com/news2/article.php?uid=129 (18.03.2007)
Weinzierl, R. A.: Botanical Insecticides, Soaps, Oils. In: Rechzigl, J.E.; Rechcigl,
N.A.: Biological and Biotechnological Control of Insect Pests. Boca Raton (Florida)
1998
33
WFED (World Foundation for Environment and Development): Glossary of term of
the Convention on Biological Diversity. Washington 2004
http://www.wfed.org/resources/glossary/ (17.03.2007)
34
Ehrenwörtliche
Erklärung
Hiermit versichere ich, dass ich die vorliegende Arbeit selbstständig und ohne Benutzung
anderer als der angegebenen Hilfsmittel angefertigt habe. Alle Stellen, die wörtlich oder
sinngemäß aus veröffentlichten und nicht veröffentlichten Schriften entnommen sind, sind als
solche kenntlich gemacht. Die Arbeit hat in gleicher oder ähnlicher Form noch keiner
anderen Prüfungsbehörde vorgelegen.
Bayreuth, den
----------------------------------------------------------------------
Anne Hegge
35
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