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2-Plants: First field system to test Bt resistance management plans developed (1)
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TITLE: Testing Bt refuge strategies in the field
SOURCE: Nature Biotechnology, Volume 18 Number 3
by Fred Gould
DATE: March 2000
-------------------- archive: http://www.gene.ch/ --------------------
Testing Bt refuge strategies in the field
Fred Gould (e-mail: fred_gould@ncsu.edu) is professorof entomology
North Carolina State University, Raleigh, NC, 27695.
In 1999, an estimated 24% of corn and 5% of cotton grown worldwide
contained a transgene for an insectical protein derived from the
bacterium Bacillus thuringiensis (Bt). The prevalence of these so-
called "Bt crops" has raised concerns about the possible widespread
emergence of Bt resistant pests, which could ruin the utility of Bt
crops. In 1996, the Environmental Protection Agency (EPA; Washington,
DC) and industry moved to circumvent this danger by requiring farmers
to plant a certain percentage of their cotton acreage in non Bt-
producing cultivars. This would provide pests a refuge where they
could feed on plants lacking toxins, thereby maintaining Bt
susceptible resistance alleles within the insect population. Since
that ruling, there have been calls for increases in Bt refuge sizes
by scientific panels by the EPA2, industry3, and the Union of
Concerned Scientists4 (Washington, DC), as well as two independent
groups led by extension entomologists working directly with corn and
cotton farmers5. However, critics have argued that before going
forward with such increases, field tests are needed to prove that
refuge strategies are effective. Now in this issue, Shelton et al.6
have moved us one step forward in addressing this concern, by
reporting the results of controlled field tests to evaluate the
impact of pest refuges on the evolution of insects' resistance to
transgenic insecticidal crops.
The premise for pest refuges is based on population genetic theory,
which predicts toxin-susceptible insects produced in pest refuges
will mate with toxin-resistant insects that survive on the transgenic
insecticidal crops, thereby diluting the alleles for resistance and
prolonging the pest population's susceptibility. The 1996 EPA-
approved plan required that cotton farmers plant 4% of their acreage
in non-Bt-producing cultivars, and not treat this acreage with any
insecticides that kill Bt-targeted pests, to ensure their survival in
the refuge. Farmers who did not want to risk the potential crop
damage in the 4% untreated refuge were offered the option of planting
at least 20% non-Bt cotton that could be sprayed. The logic here was
that conventional pesticides are expected to kill about 80% of the
pests, therefore the 20% and 4% refuges should preserve an equivalent
number of surviving Bt-susceptible insects.
As illustrated in Fig. 1, refuges are expected to be very effective
if the transgenic insecticidal crops produce a "highdose" at least 25-
fold the amount of toxin needed to kill susceptible insects. In fact,
the EPA science advisory committee concluded that "a refuge/high dose
approach must be employed within the current understanding of the
technology"2.
Unfortunately, the only way to directly test the refuge/high dose
theoryis to use it on a wide scale in some areas and not in others;
economic and ethical issues, however, make this impossible. Even
small scale field tests have faced major obstacles because they
generally involve the release of pest insects with resistance
alleles. Shelton et al. have circumvented this problem by developing
Bt-producing broccoli, and using it for field tests of the
diamondback moth in upstate NY where the moth cannot survive the
winter.
Shelton et al. planted broccoli in plots with various types of
refuges.They released insects with a known frequency of resistance
alleles and examined how the refuges impacted both resistance allele
frequency and pest population density. Unfortunately, Shelton et al.
needed to release insects with a high frequency of resistance alleles
(0.12 and 0.80) for practical reasons, even though they realized that
the refuge/high dose approach relies on initially low resistance
allele frequencies. This problem made it impossible for Shelton et
al. to test the refuge/high dose strategy as a whole, but they were
able to examine some aspects of the refuge component of the strategy.
One question addressed by Shelton et al. was how far away from the
Bt plants must the non Bt refuge plants be grown? One extreme is to
plant a mixture of seeds, with Bt and non Bt plants side by side. A
criticism of this approach is that larvae which begin feeding on non
Bt plants might move to, and feed on Bt plants, thereby diminishing
the number of larvae completely escaping the selective impacts of the
toxin. Shelton et al.'s field data indicate that this is a legitimate
concern for the diamondback moth. While this would not be a problem
for cotton pests, such as the pink bollworm, that don't generally
move between plants, it could affect other target insects such as the
tobacco budworm and European corn borer. Fortunately, the current and
proposed refuge recommendations for these pests do not endorse seed
mixtures.
Shelton et al. also tested whether insects would evolve resistance
more rapidly when a refuge was sprayed than when it was unsprayed. In
the 27 day period between the time that insect releases ended and the
field measurement of resistance allele frequency was begun, insects
from 20% sprayed refuge treatment and 20% unsprayed refuge treatment
showed no difference in changes in allele frequency. (The initial
frequency was 85%, and first field measure was 76%, based on the
assumption that only larvae homozygous for resistance survive). The
second field measurement indicated that the frequency of alleles in
the sprayed refuge had increased by about 2%, but in the unsprayed
refuge the frequency had decreased by about 12%. Between the second
and third measurement the frequencies in both 20% refuge treatments
had risen 0.5%. The heterogeneity in response to the two refuges over
time is unexplained, but the overall difference of 10% is certainly
in line with theoretical expectations.
Shelton et al. also found higher numbers of insects on Bt plants in
the sprayed refuge treatments which they attribute to lower Bt
susceptibility of these populations. Unfortunately, differences in
susceptibility do not really explain the differences in densities
because in period 1, when the mortality of larvae from the sprayed
and unsprayed treatments are equivalent, there are already
differences in the densities. The results from this experiment are
also hard to interpret because Shelton et al. do not report on the
efficacy of the spraying.
Although there are obvious limitations to these studies, they do
confirm, in the field, that the mixed seed approach could be
problematic and that an unsprayed refuge results in more rapid
adaptation than an equal size sprayed refuge. Although scientists may
not be surprised by these results, field studies like this one are
essential for developing public confidence in resistance management
techniques.
REFERENCES
James, C. Global Review of Commercialized Transgenic Crops. (ISAAA,
Ithaca, NY, 1999).
E.P.A. 1998. Scientific Advisory Panel, Subpanel on Bacillus
thuringiensis (Bt) plant-pesticides and resistance management,
February 9-10, 1998. Docket No. OPPTS-00231.
ILSI. An evaluation of insect resistance management in field corn: a
science-based framework for risk assessment and risk management.
(ILSI International Life Sciences Institute, November 23, 1999).
Rissler, J. and M. Mellon. Now or never: Serious new plans to save a
natural pest control. (Union of Concerned Scientists, CambridgeMA.,
1998).
E.P.A. and U.S.D.A. 1999. E.P.A. and USDA position paper on insect
resistance management in Bt crops. http://www.epa.gov/pesticides/
biopesticides/otherdocs/bt_position_paper_618.htm
Shelton et al., Nat. Biotechnol. 18, 339-342(2000).
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