Lecture 8: Bacillus thuringiensis (Bt) toxin Flashcards

– why is it such a good insecticide for biotechnological applications?

1
Q

The requirement for biotechnological solutions for control of insect pests in agriculture

A

*Chemical solutions to pest problems are still viable in many instances, but major problems have accumulated where pests have become resistant to pesticides (viral, bacterial, fungal or insect)

*Previous use of pesticides with toxicity to higher animals and humans has resulted (rightly!) in a regulatory regime that requires rigorous safety testing of existing and new compounds

*Pace of introduction of new pesticide classes has declined drastically – largely due to commercial reasons

Insects are generalists they land on a plant and begin feeding – there is very little time for a response e.g. locust plague in Kenya cleared crop fields in weeks – these situations are rare but devestating

> Chemical pesticides in common use are divided into a series of classes based on chemical structure. Most of these compounds are toxic to higher animals.

Californian farms import 3million honey bees yearly to pollinate fruit and almonds due to a lack of natural pollinators as a result of pesticide use

Note many “natural” compounds are equally toxic!

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2
Q

One response to pests/disease:
‘natural’ pesticides

A

”Naturally” occurring compounds from plants and other sources are widely suggested as a replacement for “synthetic” pesticides

Problems
*Often very limited efficacy, and thus may not be usable in commercial agriculture
*Compounds can be more toxic than the synthetic pesticides they are meant to replace

Natural does not mean non-toxic!!

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3
Q

Another response to pests/disease: endogenous resistance

A

If “natural” endogenous resistance to insect pests is available in the crop then pesticide application can be minimised

Problems:

*Often, no suitable naturally occurring resistance genes are available in the crop.

*Insects may already contain genes which enable them to adapt to resistance

Not a fast enough response for chewing insects (locusts etc.)

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4
Q

Can we use biotechnology to produce endogenous resistance to insect pests that is not limited by the genetic resources available in a crop species?

A

Syngenta testing site at Bracknell is a chemical testing warehouse where weather conditions are controlled and plants are infected with pests then sprayed to test for kill effectiveness

^the chemicals are then tested to avoid harm to mammals
^ each chemical developed costs £80,000 to make market ready

*The availability of technology to introduce genes into the plant genome opens up the possibility of engineering plants to produce novel insecticidal compounds

*Introducing novel biosynthetic pathways to produce molecules similar to existing “synthetic” pesticides is technically difficult (although not impossible) – and accumulation of “synthetic” pesticides in plant tissues may be significantly deleterious to the plant.

*Exploiting insecticidal compounds that can be produced from a single introduced gene is technically much more straightforward

– but what are these compounds?

*Insecticidal proteins are the major types of pesticides produced in engineered plants. One type of protein, the toxin from the bacterium Bacillus thuringiensis, accounts for almost all the commercially deployed insect resistant engineered crops.

*Insecticidal nucleic acids (RNAs) are a recent introduction in commercial insect-resistant crops.

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5
Q

Toxins from Bacillus thuringiensis (Bt toxins): naturally occurring insecticidal proteins

A

*Bacillus thuringiensis (Bt) is a bacterium found in soil and in the general environment

*A common feature of this species is the formation of bacterial spores containing crystalline deposits

*The crystalline deposits are made up of one or more proteins, which are toxic to insects (and other invertebrates in some cases). These are called Cry (for Crystal) proteins

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6
Q

Variability in Bt toxins between strains

A

*There is a high level of variability in toxins and their accumulation between different naturally occurring isolates of Bacillus thuringiensis – or, put more simply, different Bt strains contain different toxins

*Bt strains which produce similar proteins with other biological activities are known; the bacterium is closely related to other soil Bacillus spp.

*Bt toxins show a high level of specificity in toxic action - I.e. a given toxin is generally only highly toxic to a limited range of target species. Toxicity is often described as a specificity towards insect orders (e.g. lepidoptera, coleoptera), but this is misleading in that significant levels of toxicity are only shown towards a restricted range of insects, often corresponding to subfamily level

see: Toxicity of different Bt toxins towards different phyla, orders, families and species
From Baranek et al. (2020) Nature Scientific Reports, 1976
^ 97.9% of characterised Bt toxins are effective against Arthropods, of which 67.3% are effective against Lepidoptera, but only 0.5% are effective against (for example) Plutella xylostella.
(^ Note: data are incomplete, and biased towards toxicity to crop pests)

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7
Q

Bacillus thuringiensis interaction with pest lifecycle

A

see figure:
Bacteria accumulate on the surfaces of plants, especially young plants, and insect feeding may increase their accumulation – however, evidence for insecticidal levels of Bt on plants in field situations is limited the spores germinate within the insect that consumes it and it grows on the dead insect ready to infect more insects

Within the insect:
Toxin binds to brush border
membrane of microvilli of midgut
epithelial cells; insertion of toxin
into membrane forms an open pore
leading to collapse of ionic
gradients across cell membrane and
leakage of components

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8
Q

Bacillus thuringiensis toxins (Bt toxins)
genetic composition

A

*Genes encoding Bt toxins are carried on plasmids; this allows exchange between different strains, and allows the population in the field to carry a wide range of variants of the plasmid-encoded toxins

*Bacillus thuringiensis contains plasmids 4,000 – 150,000 bp in size; a single strain can carry multiple plasmids (up to 17). Genes encoding insecticidal Cry proteins are found on “megaplasmids” , which are >50,000 bp in size

*Megaplasmids main function is as a reservoir for genes encoding Cry proteins

*The “typical” Bt toxin is a large protein, up to 200,000 Da, which contains a conserved structure of approx. 600 amino acids arranged in 3 distinct domains

*Most Bt toxins belong to this three-domain toxin family, designated Cry proteins - however, other types of toxin have been identified in some strains - two-component toxins (also designated Cry) and single-domain cytolytic proteins (Cyt)

*Bt also produces other insecticidal proteins during the normal growing phase - these are termed vegetative insecticidal proteins (Vip)

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9
Q

The “typical” Bt toxin is synthesised as an inactive precursor.
Activation requires proteolysis in the insect gut

A

The “three domain” structure is found in the N-terminal active toxin part of the molecule (red in the diagram below); the remainder of the inactive protoxin precursor (green in the diagram below) does not have a clearly defined structure.

The term “three domain toxin” strictly only refers to the active toxin, but is often used more loosely to refer to the whole protoxin.

3 domains: pro-toxin (cleaved when infecting a host) , N terminal , C terminal

Sub-families of Bt toxins are designated by a unified nomenclamature scheme based on sequence similarity; subdivisions are based on degree of similarity. Specificity of toxicity generally correlates well with sequence similarity (I.e. all toxins in a family have similar specificities)

“Cry” and “Cyt” are used as designations for all proteins found in crystalline deposits; not all Cry proteins are three-domain toxins!

See figures in notes:

^ Left: Conserved sequences in a range of different Bt toxin families; conserved sequence “blocks” are colour-coded. “Short” toxins do not fit 3-domain structure model.
From Trends in Genetics, 17, 193-199 (2001)

^Right: Clustal “tree” of sequence similarities in Bt toxins.
From http://www.lifesci.sussex.ac.uk/home/Neil_Crickmore/Bt/tree.gif

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10
Q

The three domains in a ”typical” Bt toxin have distinct structures and play different roles in the mechanism of action.

A

All three domains are globular, and the overall protein is globular and soluble

3 domains: pro-toxin (cleaved when infecting a host) , N terminal , C terminal

activated form depicted in notes:
Domain 1: Pore forming
Domain 2: Carbohydrate binding
Domain 3: Protein-protein interaction

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11
Q

The mechanism of action of three-domain Bt toxins involves multiple steps

A

(see figures in notes) :

1) Protein dissolves, and the protoxin is activated by proteases in insect gut, involving removal of variable C-terminal region to generate the three-domain active toxin. This process may be involved in determining overall specificity between insect orders.

2) Binding of activated toxin to an abundant membrane-anchored protein in cells of the gut epithelium (typically aminopeptidase N or alkaline phosphatase) in a low-affinity interaction involving domains 2 and 3.

3) Binding of the toxin to an integral membrane protein (typically cadherin-like) in a high affinity interaction involving domain 2 - normally determines fine specificity between insect species.

4) Proteolytic cleavage of the N-terminal pro-region on the active toxin (domain 1), followed by oligomerisation. Removal of the pro-region on domain 1 is necessary for oligomerisation, and pore formation (step 6) to occur.

5) Binding of the oligomerised toxin to the abundant membrane anchored protein in a high-affinity interaction involving domain 2, allowing the oligomerised toxin to interact with the membrane of the gut epithelial cell.

6) The oligomerised toxin forms an open pore by insertion of domain 1 of Bt toxin into the membrane of the gut epithelial cell. Free passage of ions through the channel leads to cell lysis and death - not normally involved in determining specificity.

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12
Q

Evidence for the 2-receptor/oligomerisation model

A

*Insects carrying mutations which make them insensitive to specific Bt toxins can be found

*Some insects resistant to specific Bt toxins have mutations in Aminopeptidase N or alkaline phosphatase genes (loss of function)

*Transfer of aminopeptidase N genes between insect species can transfer sensitivity to specific Bt toxins (gain of function) – specific example in transfer of lepidopteran aminopeptidase N to Drosophila (fly)

*Some insects resistant to specific Bt toxins have mutations in cadherin genes – this technique has been used to map the binding sites for Bt toxins on cadherin proteins

*Bt toxins that have been modified by removal of the N-terminal pro-region show enhanced toxicity, and do not require binding to cadherin to be toxic, due to oligomerisation occurring spontaneously

*Bt toxins can be shown to bind to aminopeptidase N, cadherin and other membrane proteins in vitro

Data are consistent with binding to both the membrane anchored receptor (aminopeptidase N or alkaline phosphatase) and the integral membrane receptor (cadherin) being necessary for toxicity

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13
Q

Binary toxins from Bacillus thuringiensis contain a protein which interacts with membranes, and a pore-forming protein

A

Both components of the binary toxin are necessary for insecticidal effects. The mechanism of action appears to involve binding to the surface of gut cells by Cry35, and formation of pores by Cry34, but details remain to be fully elucidated.

The diagram right (from Palma et al. Toxins 2014, 6(12), 3296-3325) shows the presence of motifs found in carbohydrate-binding proteins in Cry35; Cry34 has a structure resembling the bacterial pore-forming toxin aerolysin.

Cry binary toxins, such as Cry34/35 show toxicity towards coleopteran insects (beetles) – they have proved useful for control of pests such as corn rootworm

Proposed model for the action of Cry toxin. Cry toxin binds to BT-R and stimulates G protein and AC, which promotes production of intracellular cAMP. In turn, PKA activation destabilizes the cytoskeleton and ion channels, leading to cell death.

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14
Q

Bt toxins can be used as a “conventional” exogenously-applied insecticide

A

Easy to bottle in crystalline form and spray apply – but it is indiscriminate and large quantities needed – better to engineer into plant

*Preparations of Bt spores (produced by growing the bacterium in vitro) have been in use since the 1920s as a conventional, exogenously applied (spray) insecticide

*Approved as an “organic” insecticide (“natural” product)

*See http://www.ext.colostate.edu/pubs/insect/05556.html

Exogenous application not very effective due to:
*Run-off; most compound lost from plant surfaces
*Wash-off; rain removes compound from plant surfaces
*Inactivation; compound susceptible to degradation in the environment, inactivated by uv in sunlight
*Poor targeting to pest species; spraying distributes compound over both crop and surroundings
*Comparatively high dose required for toxicity (compared to organophosphate or pyrethroid insecticides)
*Not widely used as a commercial insecticide prior to increase in “organic” agriculture
- Fairly expensive to produce

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15
Q

Why is Bt toxin a good candidate for engineering endogenous resistance to insect pests in plants?

A

*Bt toxin is a protein insecticide and is thus suitable for expression in transgenic plants

–The insecticide is a direct gene product, thus only a single gene needs to be transferred to confer insecticidal properties

*Plants contain no potential targets for Bt toxin; bacterium is part of the normal plant microbiome

*Endogenous synthesis of this protein in crops would overcome many of the problems associated with its use as a conventional exogenously applied treatment

–Avoids run-off and potential exposure of non-target organisms

–Avoids inactivation

*The compound has a history of use as a conventional insecticide, and has been proven to have minimal deleterious effects on non-target organisms, and to be safe to humans

+ Pesticide run-off has become increasingly unacceptable due to pollution of watercourse

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16
Q

Expressing 3 domain toxins in transgenic plants

A

See figures in notes

The Bt toxin gene is a bacterial gene and will not function if it is transferred to a plant cell. In order to make this gene suitable for expression in plant cells, extensive changes to its structure must be carried out.

The Bt toxin gene is modified for expression in plant cells by replacement of the promoter, truncation and modification of the coding sequence, and replacement of the terminator.

Initial attempts to express Bt toxins in transgenic plants showed that
extensive modification of the bacterial gene was necessary to achieve
protein levels sufficient to cause insect mortality
^ modern promotors are able to create much higher levels of protein than original forms

Recent testing has proven transgenic Bt toxin expressing plants to be effective in pest management:
yellow corn stem borer stunted growth observed and eventually death results
(see figures in notes)

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17
Q

Transgenic plants expressing Bt toxins are a highly successful product - main commercial uses

A

Cotton expressing Cry1 toxins for resistance to lepidopteran pests - widely employed throughout the world

Corn (maize) expressing Cry1 toxins for resistance to lepidopteran pests - widely used in US, some use in Europe

Corn (maize) expressing Cry3 or Cry34/35 binary toxin for resistance to corn rootworm (coleopteran pest) - widely used in US

Rice expressing Cry1 toxins for resistance to lepidopteran pests - used on a significant scale in China

18
Q

Major Bt expressing crops

A

Cotton: cry1Ac, cry1F, and vip3A(a). Resistance to lepidopteran pests including, cotton bollworm, pink bollworm, tobacco budworm.

Maize: cry1Ab. cry9C, cry1F cry1Ac, cry1Ab European corn borer (Ostrinia nubilalis)

cry3Bb1, cry3A resistance to corn root worm (Coleoptera, Diabrotica spp.)

Stacked: cry34Ab1 and cry35Ab1, resistance to corn root worm (Coleoptera, Diabrotica spp.)

And a series of minor crops, including:

Eggplant (brinjal): cry1Ac. Shoot borer.

Potato: cry3A. Resistance to Colorado potato beetle (Leptinotarsa decemlineata, Say). Not continued for commercial agriculture

http://www.agbios.com/dbase.php

19
Q

Deploying insect-resistant transgenic crops expressing Bt toxins in the field

Problem: Insect resistant Bt crops in agriculture

A

*Bt-expressing transgenic plants have become a major success in modern commercial agriculture

*This success has been dependent on control over deployment, particularly on resistance management in target pests

*Unfortunately, Bt crops have not been as much of a success as they could have been in benefitting smaller farmers and growers

*Commercial self-interest, and regulatory and “environmental” concerns, have reinforced each
other in preventing this technology from getting into the hands of those who might benefit most from it

Terminator gene can be introduced to Bt seeds resulting in dependency on bioengineering companies

This could wipe out the ‘pest’ problem – in other words decimating insect populations globally

20
Q

An overall success: insect resistant cotton

A

Host Organism / Variety Gossypium hirsutum L. (Cotton) Bollgard®, Bollgard II

Trait Resistance to lepidopteran pests including, but not limited to, cotton bollworm, pink bollworm, tobacco budworm.

Expresses Cry1Ac (Bollgard); Cry1Ac + Cry2Ab2 (Bollgard II)

Trait Introduction Method Agrobacterium tumefaciens-mediated plant transformation.

Proposed Use Production of cotton for fibre, cottonseed and cottonseed meal for livestock feed, and cottonseed oil for human consumption.

Company Information Monsanto Company

21
Q

How Bollgard cotton functions

A

Pink Bollworm (Pectinophora gossypiella)
- is a pest susceptible to Bt Cry1Ac which is controlled by Bollgard cotton

Female moths lay their eggs in the cotton bolls, and larvae emerge to feed on the cotton seed, chewing through the cotton lint and damaging the boll.

The ‘Cotton boll’ is the harvested part of the cotton plant and includes the cotton itself (white fibres; lint) which encase the cotton seed. Cotton seed contains high levels of protein and oil and is used as animal feed.

22
Q

Economic Benefits to the Farmer: Bt Technology

A

see photo examples for cotton in notes

e.g. Cotton field showing mixed planting where Bt cotton has set more bolls. The conventional cotton has suffered insect damage to developing bolls, and has failed to set as much harvestable product, compensating by producing extra vegetative growth.

e.g. Cotton bolls. Upper panels show insect damage (left) to developing boll on conventional cotton, resulting in aborted development; transgenic cotton (right) is undamaged and develops normally.

Lower panels show damaged (left) and undamaged bolls (transgenic and conventional plants respectively); insect damage has reduced cotton fibre production significantly even where bolls do develop.

23
Q

But then pink Bollworm developed resistance to Bollgard cotton

A

The initial transgenic Bt cotton varieties broke down in the field in India

NEW DELHI—Monsanto has revealed that a common insect pest has developed resistance to its flagship genetically modified (GM) product in India. The agricultural biotechnology leader says it “detected unusual survival” of pink bollworms that fed on cotton containing the Cry1Ac gene from the bacterium Bacillus thuringiensis (Bt), which codes for a protein that’s toxic to many insect pests. In a statement to Science, Monsanto claims that the finding from western India “is the first case of field-relevant resistance to Cry1Ac products, anywhere in the world.”

Science 327, 1439 (2010)

“Breaking” the resistance of Bollgard cotton to pink bollworm emerged

^ how and why the problem was solved by the introduction of Bollgard II cotton is covered later

24
Q

Transgenic crops can have major environmental benefits: Pesticide usage on corn – a case study

A

European Corn Borer
&Corn Rootworm
^ Both of these species are difficult to control with conventional insecticides; corn borer tunnels inside stems, whereas corn rootworm is in the soil.

Other major pests include corn earworm and armyworm (lepidopteran), grasshoppers (orthopteran) and wireworms (coleopteran)

Insect pests also carry viruses, fungi (mycotoxins) and bacteria therefore reducing their impact on crops has multiple benefits – reducing toxin load and disease

Reduced insecticide use
- Data shows that increasing adoption of Bt corn in USA correlated with
decreased insecticide usage

see figure: http://www.vox.com/cards/genetically-modified-foods/are-gmo-
crops-good-or-bad-for-the-environment

Bt corn shows vigour and yields comparable to conventional varieties
- No evidence for yield penalty associated with transgene expression

Bt corn offers full-season protection against corn borer, while retaining high yields and vigour of non-transgenic varieties. Yield increases averaging 80% compared to non-treated conventional corn are routinely observed.

Conclusion: Yield increase and reduced need for toxic chemical spray

25
Using transgenic crops to improve food quality: reducing fungal growth and decreasing Fusarium mycotoxin load
*Fusarium mycotoxins decrease grain quality and can potentially be the source of toxicity to animals or humans – other fungal toxins are much more harmful *Productivity is reduced, and yield decreased by fungal pathogens using insect damage to attack plants – preventing insect attack using Bt corn improves quality by decreasing fungal opportunities Better product, higher yield, lower toxin load, less damage to surrounding areas *A further potential “knock-on” advantage of Bt corn in relation to fungal pathogens is that less anti-fungal treatment is required *Pesticide usage again decreased *Fungicide usage is another target of environmental organisations – many of the chemicals used are significantly toxic
26
Benefits of Transgenic Insect-Resistant Crops
*Promotes greater sustainability of natural resources by reducing use of energy and chemicals ( more target use of pesticides and reduction in use of fossil fuels) *Reduction in land/water contamination through reduced pesticide usage *Preserving natural habitats for biodiversity (more efficient use of land) *Reduced impact on non-target organisms, including beneficials – to be considered *Enhancing safety of food crops by reducing mycotoxin contamination *Increased yield
27
GM crops, and specifically Bt-insect resistant crops, have been subject to a series of problems and objections, which can be divided into several categories:
1. Objections based on ethical or belief-based grounds (“Man should not play God”, “Plants should not belong to agribusiness”, etc.). These are of varying degrees of validity, but need a wider discussion than is possible in a science lecture agrotech companies could end up controlling yields worldwide? 2. Objections based on potential safety issues. Some of these objections, such as the consistent claim that Bt crops are not safe for human consumption, lack a scientific basis. Others, such as the claim that Bt crops could pose a threat to the environment, have been able to advance testable hypotheses which have justified scientific investigation. But safety of insect CONSUMERS? No food See: Engist, D., Guzman, L.M., Larsen, A. et al. The impact of genetically modified crops on bird diversity. Nat Sustain 7, 1149–1159 (2024). https://doi.org/10.1038/s41893-024-01390-y 3. Problems which have resulted from insects becoming resistant to these toxins, by similar mechanisms which have resulted in resistance to conventional insecticides. This is a real problem which has generated science-based solutions. 4. Problems based on over-restrictive regulatory and rights regimes, based on the one hand on dubious assumptions of potential hazards of Bt-crops (“the precautionary principle”), and on the other hand aggressive commercial tactics designed to maximise exclusivity of, and profits from, the technology. 5. Problems due to limitations in Bt toxins themselves – lack of toxicity towards some types of pests, high degree of specificity of a given toxin prevents the broad-coverage protection observed for synthetic pesticides. NOTE: Organophosphates and heavy chemicals are used in Organic farming
28
Are Bt crops safe when fed to animals/humans?
No evidence for any adverse effects on mammals (From Koch et al., 2015, Front. Plant Sci. https://doi.org/10.3389/fpls.2015.00283 No evidence of adverse effect in human consumption
29
The increased deployment of Bt corn has resulted in a decrease in the use of organophosphate insecticides in the USA
check for reliable source?
30
Specific problems in Bt-expressing insect resistant plants
Potential toxic effects on non-target species of insects and other arthropods –The high level of specificity of individual Bt toxins makes this less likely, although not impossible Specificity of toxic activity too narrow - affects target pest only –Allows emergence of insect species with similar feeding habits as secondary pests Insufficient toxicity of available Bt toxins towards target pest(s) –Can result in level of expression necessary to achieve high levels of control being difficult to achieve reliably and routinely in transgenic plants under varying (and non-optimal) growing conditions Development of resistance in targeted pests to toxins –Potential to become a serious problem based on observations from field use of Bt sprays, and laboratory studies No Bt toxins with activity against homopteran pests have been identified –May be a result of proteolytic activation mechanism of Bt toxins; homopteran plant pests generally have very low levels of digestive proteinases due to reliance on free amino acids in saps –No solution as of 2020, although some interesting possibilities raised
31
Field studies have generally failed to show any negative non-target effects of Bt crops
” The first-ever field level study of the effects of insect-resistant genetically modified Bt eggplants on non-target arthropod species, carried out in the Philippines . . . . The data, collected over three growing seasons in the Philippines' main eggplant-growing region of Pangasinan, shows no significant differences between the number of insects and other arthropod individuals and species between the genetically modified Bt and non-Bt control eggplants.” (Navasero et al., 2016 PLOS One https://doi.org/10.1371/journal.pone.0165190)
32
Non-target effects; Bt corn and monarch butterfly larvae – a case with some scientific basis
“ . . a correspondence to Nature suggested that pollen from Bt corn could be hazardous to the larvae of the monarch butterfly, Danaus plexippus (L.) (Losey et al., 1999, Nature 399, 214). In that study, young monarch larvae were given no choice but to feed on milkweed (Asclepias curassavica L.) leaves dusted with pollen from a Bt corn hybrid. They ate less, grew more slowly, and had a significantly higher mortality rate than larvae feeding on leaves dusted with nontransgenic pollen.” This study was seized on by pressure groups as evidence for the harm caused by GM crops (see below). Worse, there is direct evidence that Bt toxins do affect monarch butterfly larvae. The effect is dependent on the presence of the toxin in pollen: “The only transgenic corn pollen that consistently affected monarch larvae, even at low levels, was from event 176 hybrids, which use a pollen-specific promoter for expression of the cry1Ab gene. There was no evidence that pollen from Cry1Ab events Bt11 and Mon810 affected larvae at pollen densities less than 1000 pollen grains/cm2.” (Hellmich et al., 2001, PNAS 98, 11925-11930) However, field studies have shown no significant effects of Bt corn on survival of monarch butterfly larvae feeding on nearby milkweed plants – and the larvae can only receive indirect exposure to Bt toxin, as they do not feed on corn. Spraying the corn with Bt toxin (as an “approved” organic insecticide) would, in fact, be more hazardous to monarch butterfly larvae; as would be conventional pesticides. It is now generally admitted (even by most pressure groups) that this was a “false alarm” and that Bt-corn does not have a direct deleterious effect on Monarch butterflies. The study was biased – plants were dusted all over with pollen – grain crops are self fertilised – they don't release pollen therefore the impact is avoided... but what about open pollinated crops such as tomatoes?
33
Development of resistance to Bt toxins (in transgenic plants) in insect pests is a real problem
*The development of resistance to insecticides in pests started to become a serious problem in the 1970s, when it became apparent that pests were developing resistance quicker than new pesticides could be brought to market *Insect pests have a variety of mechanisms for developing resistance to pesticides; these include –Degradation of the pesticide using hydrolysis (esterases), oxidation (cytochrome P450 oxidases) and/or conjugation (glutathione S-transferases); usually via up-regulation of gene expression –Mutation of the target of the pesticide to prevent binding/toxicity (e.g. mutation of voltage-gated sodium channel gene para to prevent pyrethroid binding); mutant allele of target gene –Some insects carrying mutations in genes which confer pesticide resistance are found in low frequencies in natural populations, and can be selected for; more rarely, mutations appear in populations under selection *The development of Bt-expressing insect-resistant crops was a response to pests of potato (Colorado potato beetle) and cotton (corn earworm; Heliothis virescens) developing resistance to major insecticide types Bt was first put into use due to the reducing effectiveness of pesticide chemicals due to tolerance development (^With thanks to: www.maf.govt.nz/mafnet/rural-nz/research-and-development/biotechnology/using-bt-toxins-in-new-zealand ) As is the case for other pesticides, resistance to Bt toxins is observed in crop pests *Resistance to Bt toxins in common pests could be produced within 4-10 generations of selection on field-collected populations in the laboratory *Stable lines of insect pests which are resistant to Bt toxins can be generated *Resistance is usually specific to a particular Bt toxin, and is based on mutation of receptors for the toxin in gut epithelial cells *Broad-range resistance, based on alterations to proteolytic activation of Bt toxins, has also been observed resistance to transgenic Bt toxin develops within 4 (to 10) generations and soon become as effective in killing plants – continuous feeding on Bt has this result – how can this be managed?
34
Insecticide resistance and resistance management
*Resistance to Bt toxins has also been observed in the field where extensive spraying of Bt toxin preparations has been carried out *The most compelling evidence that Bt toxin resistance can evolve comes from field populations of the diamondback moth (Plutella xylostella). This moth is a major pest of vegetables around the world and receives frequent exposure to pesticides. *Diamondback moth resistance to Bt toxin spray can evolve in the field in less than two years with sufficient selection pressure. The lack of field resistance to date in insects other than diamondback moth has been attributed to the relatively small amount of Bt toxin currently applied in comparison to other pesticides.
35
Resistance to Bt toxins is present in field pest populations – but frequency is low
Those with resistance appear to have lower overall fitness resulting in it being bred out in the field *Field populations of many crop pests contain individuals which are resistant to Bt toxins as a result of carrying allelic variations of specific genes –The frequency of occurrence of the "resistance" alleles is generally low and fairly constant –Like resistance to conventional pesticides, it is likely that resistance to Bt toxins carries a fitness penalty which prevents these alleles becoming more frequent in the absence of selection pressure see figure in notes : Mechanisms of resistance to Cry toxin ^ resistance requires reduced effectiveness of important functions within the resistant insect
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Insecticide resistance & resistance management
*From the start, deployment of Bt-expressing transgenic crops was carried out with a view to minimise the possibility of pest resistance developing *Resistance management is a serious problem, and, in protecting transgenic crops against loss of utility, seed companies have required farmers to sign agreements stipulating how Bt crops were used in the field The strategy used to control resistance development is based on two principles: Exploiting population genetics to avoid selecting insects resistant to Bt toxins. Using combinations of toxins which target different receptors to minimise the possibility of resistance mutations being selected. *This strategy has proved largely successful; evidence for resistance to Bt toxins caused by Bt toxin-expressing crops in the field has proved difficult to find, although under suitable “forcing” conditions it can be demonstrated (see Tabashnik et al 2008, Nature Biotech 26, 199-202). Continue to be effective today since 1970's *Large-scale loss of utility of Bt toxin-expressing crops has yet to occur in commercial agriculture, although this clearly remains a possibility. (NZ source again)
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Resistance management - High dose/refuge approach
*In the pest control context, the word "refuge" is used to mean an area of habitat where susceptible pests can survive To maintain your Bt yields you must allocate 25% of your cropland to refuge areas to prevent the double recessive insects that are tolerant – your yield is...the same? see Kathage paper 24% yield increase and 25% land allocated to refugia There is some yield from the non BT area and it supports insect populations and species dependent on them – this could be more effective for maintaining biodiversity than organic practices and is likely to be more sustainable than current practices in Europe Yield increase is even lower in tomatoes 15-20% See: Kathage J, Qaim M. Economic impacts and impact dynamics of Bt (Bacillus thuringiensis) cotton in India. Proc Natl Acad Sci U S A. 2012 Jul 17;109(29):11652-6. doi: 10.1073/pnas.1203647109. Epub 2012 Jul 2. PMID: 22753493; PMCID: PMC3406847. On average, GM technology adoption has reduced chemical pesticide use by 37%, increased crop yields by 22% (but require 25% of land as refugia), and increased farmer profits by 68%. Yield gains and pesticide reductions are larger for insect-resistant crops than for herbicide-tolerant crops. Yield and profit gains are higher in developing countries than in developed countries. Klümper W, Qaim M. A meta-analysis of the impacts of genetically modified crops. PLoS One. 2014 Nov 3;9(11):e111629. doi: 10.1371/journal.pone.0111629. PMID: 25365303; PMCID: PMC4218791. So yields may not benefit considerably but this is more sustainable than current practices *The refuge must contain host plants that make it possible for the susceptible insects to breed without being killed. The host plants do not necessarily need to be of the same species as the crop that is being protected. This process utilises natural tolerance limitations to maintain effectiveness – you could argue it works with nature *Refuges are aimed at maintaining susceptible populations in numbers that will sufficiently dilute any resistance that arises in the target populations. The approach assumes that mating will be random between insects living in the refuges and those in the crop *The amount and size of refuges that are necessary will differ depending on the mobility and ecology of the insect, the type of crop and geographical area. *The success of the high dose strategy depends on resistance being a rare and recessive trait. Insects with resistance genes may have varying degrees of resistance depending on whether they carry one (RS in Figure on next slide) or two copies of the gene for resistance (RR). *Controlling the dose is important. The dose of toxin should be sufficient to kill all homozygous susceptible individuals (SS) and all heterozygotes with genes for both resistance and susceptibility (RS). It is generally not feasible to deliver a high enough dose of toxin to kill individuals homozygous for resistance (RR). If the dose is allowed to degrade, heterozygotes may survive and increase the frequency of the resistance gene. *Quality control on the transgenic crop to ensure a sufficient dose of toxin is delivered to kill all but RR insects is very important. Fields with Bt crops are required to provide refuge areas to help control resistance. The refuge area supply a source of wildtype (non-mutant) insects to mate with possible resistant insects to produce nonresistant insects. Bt crops are planted with alternating rows of regular non-Bt crops. The insects that have developed resistance to Bt have more chances of mating with an insect that has not developed resistance to Bt. By the laws of genetics, the progenies produced will be insects that are not resistant to Bt.
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EPA refugia requirements (USA)
In the US, the EPA requires Bt corn farmers implement refuge areas to these guidelines. 1. Growers may plant up to 80% of their corn acres with Bt corn. At least 20% must be planted with non-Bt corn (refuge area) 2. Refuge area must be within, adjacent to or near the Bt cornfields. it must be placed within 1/2 mile of the Bt field. 3. If refuge are strips within a file, the strips should be at least 4 rows.
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Gene stacking/ pyramiding
Gene stacking, or pyramiding, refers to transgenic crops containing multiple genes which confer useful agronomic traits. This was recognised as a major goal of plant biotechnology to increase field durability of transgenic crops, and in engineering crops with multi-gene multi-mechanistic resistance (Hilder & Boulter, 1999). In relation to Bt-crops, three types of gene stacking are important: Stacking unrelated traits which confer separate agronomic properties – plants that are insect-resistant and herbicide-tolerant form the main commercial application Stacking different Bt toxin genes to give a wider range of pests that can be controlled – for example, corn expressing separate Bt toxins active against corn earworm (lepidopteran pest) and corn rootworm (coleopteran pest) Stacking different Bt toxin genes which target different receptors in the same pest to prevent resistance to the toxin developing – for example Bollgard II cotton (Cry1Ac+Cry2Ab) ^Engineered plants containing multiple introduced transgenes can be produced by a variety of methods; crossing lines containing single transgenes is feasible, if lengthy, but modern methods prefer introduction of multiple genes at a single transformation. Biolistic transformation methods have successfully introduced up to 12 genes simultaneously.
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Resistance management - “Gene stacking” approach
*As a complementary approach to managing emergence of resistance to Bt toxins in transgenic crops, the use of multiple toxins which target different receptors in the insect gut has been proposed *Simultaneous mutation of two different targets for toxin binding to prevent toxicity should occur at a very low frequency in insect populations *To verify this hypothesis, an extensive glasshouse trial was carried out in which transgenic broccoli plants expressing either Cry1Ac, or Cry1C, or both proteins, were exposed to a population of diamondback moth (Plutella xylostella) which carried Bt resistance genes at a relatively low frequency *Cry1Ac and Cry1C show negligible cross-resistance in Plutella – that is, selection for resistance to one toxin does not confer resistance to the other *After 24 pest generations, plants carrying two transgenes showed a significant delay in the selection of a resistant population of insects. *However, pests can acquire resistance to multiple toxins - for example, a strain of the lepidopteran cotton pest Heliothis virescens has been identified which has simultaneous resistance to Cry1Ac and Cry2Aa, with different genetic bases of resistance to each toxin *The multiple toxin approach is not a “cure all” solution.
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Increasing pest resistance in transgenic crops using the “gene stacking” approach
*Introduction of additional Bt cry genes into the crop can afford protection against a wider range of pests. *Commercial use of transgenic cotton containing two Bt genes began in 1999, three years after the release of the original single Bt variety. Cotton plants expressing both Cry1Ac and Cry2Ab proteins were more toxic to bollworms (Helicoverpa zea; target pest) and two species of armyworms (Spodoptera frugiperda and Spodoptera exigua; secondary pests) than cotton expressing Cry1Ac alone in laboratory trials and in greenhouse and field trials *Improvements in plant transformation methods have enabled the expression of multiple toxins in transgenic plant varieties - primarily via improved Agrobacterium-based transfer technology using plasmids containing multiple gene expression constructs, giving integration of several genes at a single locus *Example - recent announcement of transgenic maize variety containing six insect resistance genes, active against corn rootworm and lepidopteran pests (rootworm; Cry34Ab1 + Cry35Ab1, modified Cry3Bb1: lepidoptera; Cry1F, Cry1A.105, Cry2Ab2) as a “one stop” pest solution
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Conclusions
*Transgenic plants engineered with genes encoding Bt toxins are a well-developed technology with a proven track record of success in a range of commercial applications. *No evidence for deleterious effects on the environment, or for toxicity to higher animals, has been observed. *Development of resistance to Bt toxins in pest insects is a real problem and requires careful management to preserve the protection of the crop. Where management of resistance in pests breaks down, as has happened in India, crops fail due to insect damage. However, gene stacking methods to enhance resistance in crops, which result in production of multiple toxins, have proved able to restore and preserve crop protection. *Regulatory constraints have negatively impacted the continuing development of this technology, although many of the shortcomings of Bt toxins as insecticides could be tackled with further research. *Regulatory constraints have prevented Bt crops achieving their full potential for making a positive contribution to agriculture across the world – many countries that could have benefitted from the technology have been prevented from doing so by potential markets being unwilling to accept imports of GM food crops. How to regulate Bt crop usage to make sure that 25% of land is assigned to refugia ^ is there a risk because metastudy (below) suggests that 22% yield increase is the average Klümper W, Qaim M. A meta-analysis of the impacts of genetically modified crops. PLoS One. 2014 Nov 3;9(11):e111629. doi: 10.1371/journal.pone.0111629. PMID: 25365303; PMCID: PMC4218791. Would farmers settle for this? Privatised systems work in US and canada – but what about undeveloped countries with poor connections with supply?