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PLNT4600 Issues in Agricultural Biotechnology
Mini Report 1, part 1 of 1

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January 29, 2007

Bt Toxin (Bacillus thuringiensis)

Presented by: Meghan K. Rose


Outline:

            What is the Bt Toxin and how is it used

            Types of Bt crops

            Toxicity level and mode of action

Effects on Non-target organisms

Invasion and persistence of Bt genes in the natural environment

Resistance


What is the Bt Toxin and how is it used?

  • The Bt toxin (Bt Cry) a crystalline protein produced when the microorganism Bacillus thuringiensis sporulates
  • Toxic to insects (different strains of the microorganism toxic to different insects)
  • Fermented cultures have been used as a commercial insecticide spray for the past 40 years
  • In 1999, 29 million acres of Bt corn, potato and cotton were grown globally, saving $92 million in pesticide application in the USA alone
  • A very important insecticide available for use by Certified Organic farmers

                                                                                                                                                                               http://textbookofbacteriology.net/Anthrax.html

Sporulating Bacillus thuringiensis cellwww.learner.org/.../archive/images/1022.html

Bt transgenic Crops

  • Corn (field and sweet)
  • Cotton
  • Soybean
  • Potato
  • Tobacco
  • Rapeseed
  • Rice
  • These crops express short sequences of the Bt gene from Bacillus thuringiensis and thus can make the protein themselves                                                                    http://www.tricity.wsu.edu/aenews/April00AENews/Apr00AENews.htm#anchor5338542

-Ubiquitin promoter

-CryA- coding region

-PolyA tail from nopaline synthase gene

-constructed by PCR

R. Sardana et al. 1996. Construction and rapid testing of synthetic and modified toxin gene sequences               -plants transformed by particle bombardment

CryIA (b&c) by expression in maize endosperm culture. Plant Cell Reports. Vol 15:9                                                                   

Toxicity levels and mode of action

TABLE 1

No Observable Effect Level for mortality following exposure of rats to purified Bt toxic protein (A)

Registered Transgene
 Registrant
 NOEL (mg/kg)
 Digestibility

Bt CryIA(b)

Monsanto

>4000

Rapidly degraded

Bt CryIA(b)

Novartis

>3280

Rapidly degraded

Bt CryIA(c)

Dekalb

>5000

Rapidly degraded

Bt Cry9C

AgrEvo

>3760

Stable

Bt spray

Several

>5050

Degraded

Table Salt

 

3750 (B)

 

Caffeine

 

25

 

Vitamin A

 

4.3 (C)

 

2,4-D

 

1

 

A A) All information from the EPA Biopesticide Safety Sheets (See endnote 16)
B) LD50 for oral exposure of rats
C) Level of exposure causing adverse effects

·        Many household substances are more toxic to rats at a much lower dose than the Bt toxic protein

·        Humans exposed orally to 1000 mg/day for 3-5 days of Bt have showed no ill effects.

TABLE 2

Concentration of protein (microgram per gram of wet plant tissue) in various corn tissues and estimated grams of protein per acre of corn.

Registered Transgene
Whole Plant
Leaf
Roots
Pollen
Grain
Grams of insecticidal protein per acre

Bt CryIA(b)

3.65-4.65

7.93-10.34

NA

0.09

0.18-0.39

16.4-20.9

Bt CryIA(b)

0.6

4.4

<0.008 (A)

7.1

<0.005 (A)

2.7

Bt CryIA(c) (B)

0.22

0.10 - 0.26

0.03

NA

0.01

1.5

Bt Cry9C (B)

4.7

9.5

5.6

0.1

4

21.3

Bt spray (C)

NA (D)

NA

NA

NA

NA

14

(A) Limit of detection for the Novartis transgene protein was roots, 0.008 µg protein per gram tissue and grain, 0.005 µg/g
(B) In the RED the data were expressed per unit of dry tissue weight; all values were adjusted to wet weight using a median wet weight transformation factor of 0.215 published for sweet corn. (See endnote 18)
(C) Assumed a maximum rate of spray application of 0.81 kg/acre with a formulation containing 1.7% delta-endotoxin. (See endnote 1)
                                                               (D) Data not available.

·        Not all tissues in the plant produce the same level of the protein

http://www.tricity.wsu.edu/aenews/April00AENews/Apr00AENews.htm#anchor5338542

 

·        Bacillus thuringiensis

o        var. tenebrionis - Colorado potato beetle, elm leaf beetle larvae

o        var. kurstaki - caterpillars

o        var. israelensis - mosquito, black fly, fungus gnat larvae

o        var. aizawai - wax moth larvae, various caterpillars, especially the diamondback moth caterpillar

 

 

 

 

 

 

 

 

 

 

 

http://www.nysaes.cornell.edu/ent/biocontrol/pathogens/bacteria.html

 

Effects on non-target organisms

  • Doesn’t persist in the digestive tract of mammals
  • Has shown some cases of eye and skin irritation in experiments with rabbits
  • Ladybugs and pollinator bees (beneficial insects) are unharmed as well as spiders, lacewings, hover flies, beetles, and earthworms. All these insects are more harmfully affected with the use of chemical pesticides.
  • MONARCHS
    • We’ve all heard this argument against Bt corn, here’s what I found

Cornell University Study (Nature May 20 1999)    www.news.cornell.edu/releases/May99/Butterflies.bpf.html

·        Milkweed leaves dusted with Bt transformed corn pollen and fed to monarch butterfly larvae caused an increase in mortality rate and a decrease in growth rate. Compared to larvae fed leaves with non transformed pollen - no effect.

·        Does the amount of pollen on this leaf accurately represent how much pollen would land on milkweed growing along the edges of fields and in ditches?

Lincoln Brower and Myron Zalucki Study (Feb. 2005)

·        Monarch Butterfly numbers are declining. Why?

o       Winter storm mortality was high in 03-04 season

o       Poor weather during 04 breeding season

o       Habitat deterioration in over wintering sites in Mexico

o       Summer breeding habitats and nectar sources in US being eliminated by herbicides

o       WHERE’S Bt?????????????? Didn’t make the list

·        Other findings

o        Not all strains Bt corn are equally toxic to the larvae and adult monarchs

o       The only milkweed with enough pollen to cause damage is adjacent to a corn field (a few meters). However, the EPA says there is not enough pollen in the surrounding 1 meter to be lethally toxic.

o       Pollen is only shed for a short period in the season

·        Solutions??

o       Can we eliminate expression of the gene in the pollen?

o       Can we keep the edges of corn fields free of Milkweed?

o       Can we eliminate the varieties of Bt Corn that are the most toxic?

 

Invasion and persistence of Bt genes in the natural environment

Results from the EPA, USA (September 2003 NATURE BIOTECHNOLOGY)

http://www.epa.gov/pesticides/biopesticides/pips/are_bt_crops_safe.pdf

 

·        gene flow from corn, cotton and potatoes to weedy species do not have “a reasonable possibility of occurring”

o       inability to pollinate wild relatives (differences in genomes and life cycles)

o       Cotton has the possibility of transferring genes through pollen to wild relatives in Hawaii, Puerto Rico, US Virgin Islands and Florida. Sale and production of Bt cotton in these areas is restricted.

·        horizontal gene transfer from Bt crops to soil microorganisms is “extremely rare” and only occurs under artificial circumstances favoring transfer, not field conditions.

Resistance

  • Bt sprays and crops are very important in agricultural practices in North America. Resistance to this type of pest management may appropriate the use of highly toxic chemicals to control insect populations which would be detrimental to the environment.
  • A major concern for organic farmers as Bt sprays is one a few pest management tools at their disposal
  • Currently the EPA has outlined the following measures to delay the onset of resistance in an IRM (insect resistance management) program. Similar standards exist in Canada (see Canadian Food Inspection Agency website)
    • Planting refuge crops for every Bt crop seeded

Refuge area

 

This set up increases the probability of a mating between a Bt resistant insect and a non-resistant insect leading to non-resistant offspring.

 

 

 

http://www.bt.ucsd.edu/crop_refuge.html

o       Monitoring target insect changes in susceptibility

o       Grower education

o       Remedial action plans by companies in the event resistance does occur

  • Failure of a producer to comply with these regulations may result in the ineligibility to purchase Bt crops
  • Currently in the field, only the diamondback moth larvae are known to be resistant to Bt toxin

 

In Conclusion

There are still some unknowns about how the Bt gene may affect wild relatives and whether there are more negatively affected non-target organisms. Overall, through my internet research I found that the risks associated with Bt crops do not out weigh the benefits of this environmentally friendly pest management system. Proper management of Bt crops (through IRM programs) is crucial for preserving their effectiveness.


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PLNT4600 Issues in Agricultural Biotechnology