Praxis Biology 5236 study materials
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Five Years of Bt Corn Without a Refuge

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Five Years of Bt Corn Without a Refuge

A farmer plants continuous Bt corn on 400 hectares, using a single hybrid expressing one Cry protein active against European corn borer. Roughly 95% of the surrounding block also grows Bt corn, and the farmer has planted no non-Bt refuge for five years. Scouting records show the percentage of stalks with borer tunneling falling from 18% in year 1 to 1% in year 3, then rising to 3% in year 4 and 6% in year 5; late-instar larvae were found inside Bt stalks in year 5. The farmer proposes switching to a different single-toxin Bt hybrid and dropping scouting to reduce costs. The seed label requires a structured refuge, and extension staff note that Cry1 resistance has been documented in some regions.

1. Use selection and dose concepts to explain why resistance appeared under this management, and why a refuge slows it down.

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Why resistance was predictable here

  • Resistance alleles exist at low frequency before any Bt is planted. Bt kills susceptible larvae, so the survivors are disproportionately resistant - selection with a very high mortality rate on susceptibles is strong selection.
  • With 95% of the block in Bt corn, nearly all moths emerging from the block developed on Bt plants. Resistant survivors mate with each other, so the allele's frequency compounds each generation. Continuous Bt on the same land removes the susceptible reservoir entirely.

Why a refuge matters - the high-dose/refuge logic

  • A structured refuge of non-Bt corn produces susceptible moths. These are numerous relative to resistant survivors, so most matings are resistant x susceptible.
  • If resistance is functionally recessive and the Bt dose is high enough to kill heterozygotes, those matings produce no resistant offspring on Bt plants. The allele stays rare and effectively unexpressed.
  • The strategy breaks when: the dose is not high enough to kill heterozygotes (late-instar survival on Bt stalks is exactly the warning sign), resistance is dominant or partially dominant, refuge compliance is low, or the landscape is almost entirely Bt so refuges are too small and too far apart.

Reading the trend: a rebound from 1% to 6% damage with larvae completing development on Bt tissue is consistent with evolving resistance, though it is not proof on its own.

2. Critique the farmer's proposed response and evaluate the strength of his evidence.

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Evaluating the evidence

  • The damage series is a real signal: a five-year rebound plus late instars surviving on Bt tissue is the strongest single piece in the record and warrants investigation.
  • But it is not a controlled comparison. There is no non-Bt check strip, and borer pressure varies with weather and moth flight each year, so a rise in damage could reflect a heavier infestation.
  • Damage scoring has not been described: was the same number of plants sampled the same way each year, at the same growth stage? Was the observer blind to hybrid?
  • Confirmation would need dose-response bioassays of field-collected larvae on Bt and non-Bt tissue, and ideally genotyping for known resistance alleles.

Evaluating the plan

  • Switching to a different single-toxin Bt hybrid carries cross-resistance risk: if the new protein shares the same receptor or mode of action (e.g., another Cry1), the same resistant insects will survive. Rotation within a toxin family is not resistance management.
  • A pyramided hybrid with two toxins that bind distinct receptors, plus a compliant refuge, is the standard resistance-management package, because an insect would need two independent resistance alleles simultaneously.
  • Dropping scouting removes the early-warning system precisely when it is most needed. Scouting is the cheapest part of the program and is what turns a suspicion into a documented, actionable finding.
  • The refuge is also a label requirement, not a preference; abandoning it carries legal and market-access consequences on top of the agronomic risk.

3. This is a decision with parties beyond the farm gate. Identify the stakeholders, the landscape-scale argument, and an appropriate monitoring and decision process.

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Stakeholders

  • The farmer (yield, cost, seed choice), neighboring growers in the same 95% Bt block (shared resistance pool), the seed company (stewardship obligations, liability, product lifespan), regulators enforcing the label, and the public interest in pest management and non-target effects.

Why it is not a private decision

  • Resistant moths do not respect property lines. A refuge planted by one grower benefits neighbors; a grower who skips it free-rides on others' compliance while accelerating resistance for everyone. This is a classic collective-action problem, which is why refuge requirements are written into labels and why extension programs coordinate at the block or township level rather than field by field.
  • Landscape composition matters: the same 20% refuge is far more effective when Bt fields are clustered with nearby non-Bt hosts than when the refuge is a distant strip.

A defensible process

  1. Document: structured, repeatable scouting (fixed plant counts, defined growth stages, blind assessment), geo-referenced so years are comparable.
  2. Confirm: bioassay field-collected larvae and, if possible, genotype for resistance alleles; report to extension.
  3. Act: return that block to a non-Bt crop for a season to reduce local selection, adopt a pyramided hybrid, and plant the required refuge with the susceptible-strain logic intact.
  4. Coordinate: block-level refuge planning with neighbors and the seed company; keep records for compliance.
  5. Communicate uncertainty honestly: the trend is suggestive, not conclusive, and the response should be scaled to the evidence while protecting the shared resource.