42 <strong>Bt</strong> <strong>Brinjal</strong>: <strong>The</strong> <strong>GEAC</strong> <strong>environmental</strong> <strong>risk</strong> <strong>assessment</strong>BFSB are not severe, <strong>the</strong>n adoption <strong>of</strong> <strong>Bt</strong> brinjal is likely to be low, <strong>and</strong> <strong>the</strong>re is a much lower <strong>risk</strong> <strong>of</strong> resistance. <strong>The</strong> proposededucation program will be designed to inform farmers that saving <strong>Bt</strong> brinjal seed will result in faster resistance evolution, <strong>and</strong>consequently <strong>the</strong>y should purchase new seed each year. It is not clear that saving seed will speed up resistance, but it is clearthat <strong>the</strong> education program will help increase seed sales.<strong>The</strong>re are several approaches to resistance management in small-scale production systems in Vietnam that are discussed inFitt et al. (2008). <strong>The</strong>se approaches should be considered in <strong>the</strong> context <strong>of</strong> <strong>Bt</strong> brinjal in India. One possibility is <strong>the</strong> use <strong>of</strong>unstructured refuges, <strong>and</strong> ano<strong>the</strong>r approach is to develop community-wide tactics.Finding 20. Event EE-1 <strong>Bt</strong> brinjal is a low dose event, which will require extra effort to manage effectively.Dose reflects <strong>the</strong> level <strong>of</strong> expression <strong>of</strong> <strong>the</strong> <strong>Bt</strong> transgene in <strong>the</strong> <strong>Bt</strong> plant <strong>and</strong> is ei<strong>the</strong>r high or low (Box 11). <strong>The</strong> dose is not<strong>the</strong> same as <strong>the</strong> efficacy or kill-rate <strong>of</strong> <strong>the</strong> <strong>Bt</strong>plant, but it has an operational definition relatedto efficacy (Box 11). EC-II, <strong>the</strong> Dossier <strong>and</strong><strong>the</strong> Supplemental Materials make it clear that<strong>the</strong> present population <strong>of</strong> BFSB is susceptibleto <strong>Bt</strong> brinjal. Examination <strong>of</strong> <strong>the</strong> results from<strong>the</strong> small-scale field trials (Dossier, volume 6),indicates that efficacy <strong>of</strong> <strong>Bt</strong> brinjal varies from38% to 97% kill <strong>of</strong> <strong>the</strong> BFSB population, withan average <strong>of</strong> 73% kill <strong>and</strong> a st<strong>and</strong>ard deviation<strong>of</strong> 21%. This is far less than <strong>the</strong> concentrationneeded for a high dose event. Indeed, even<strong>the</strong> highest observed kill rate (97% kill) is lessthan a high dose event. Consequently, eventEE-1 is a low dose event. To be clear, <strong>the</strong> dataprovided in <strong>the</strong> Dossier (volume 6) contradict<strong>the</strong> statement in <strong>the</strong> Dossier (volume 7) that <strong>Bt</strong>brinjal kills all BFSB larvae.Finding 21. Without any management <strong>of</strong>resistance evolution, <strong>Bt</strong> brinjal is projectedto fail in 4-12 years. Effective use <strong>of</strong> 20%non-<strong>Bt</strong> refuges can extend this time by 25%or more.For <strong>the</strong> purpose <strong>of</strong> providing a roughanalysis <strong>of</strong> resistance <strong>risk</strong> <strong>and</strong> IRM, we simulate<strong>the</strong> evolutionary process to project possibleevolutionary futures. To do this, we make <strong>the</strong>following simplifying assumptions:a. BFSB is found feeding only on brinjal.As discussed above, BFSB may feed onwild <strong>and</strong> weedy relatives <strong>of</strong> brinjal, <strong>and</strong> ifit does <strong>and</strong> <strong>the</strong>y are spatially intermixedwith brinjal, <strong>the</strong>se could provide a naturalrefuge, <strong>and</strong> <strong>the</strong> time to failure would belonger than projected here. In addition,BOX 11High Dose <strong>and</strong> Low Dose<strong>The</strong> dose <strong>of</strong> <strong>the</strong> insecticidal toxin in a <strong>Bt</strong> crop is a major factordetermining <strong>the</strong> level <strong>of</strong> resistance <strong>risk</strong>. Dose depends on both <strong>the</strong>concentration <strong>of</strong> <strong>the</strong> toxin in <strong>the</strong> <strong>Bt</strong> plant <strong>and</strong> <strong>the</strong> genetic characteristics<strong>of</strong> <strong>the</strong> target pest. Dose is a measure <strong>of</strong> <strong>the</strong> relative mortality <strong>of</strong> <strong>the</strong>three possible genotypes associated with resistance evolution. <strong>The</strong>segenotypes are <strong>the</strong> RR homozygotes (with two resistance, R, alleles), <strong>the</strong> SShomozygotes (with two susceptibility, S, alleles), <strong>and</strong> <strong>the</strong> RS heterozygotes(with one <strong>of</strong> each kind <strong>of</strong> allele).A “high-dose” is defined as one that kills a high proportion (>95 %)<strong>of</strong> heterozygous resistance genotypes, so that <strong>the</strong> RS heterozygotes have asimilar mortality as <strong>the</strong> homozygous susceptible genotypes (Georghiou <strong>and</strong>Taylor 1977; Roush, 1997; Gould, 1998). In this case, resistance is saidto be recessive, <strong>and</strong> resistance evolution can be slow <strong>and</strong> can be delayedsubstantially.A “low-dose” is anything that is not a high-dose. If <strong>the</strong> mortality<strong>of</strong> <strong>the</strong> RS heterozygote is similar to <strong>the</strong> RR homozygote, resistance issaid to be dominant, <strong>and</strong> resistance evolution can be extremely fast. If<strong>the</strong> mortality <strong>of</strong> <strong>the</strong> RS heterozygote is between <strong>the</strong> SS homozygote <strong>and</strong><strong>the</strong> RR homozygote, resistance is said to be inermediate, <strong>and</strong> resistanceevolution can be fast.A provisional operational definition <strong>of</strong> “high-dose” is: a <strong>Bt</strong> plant thatexpresses Cry toxin at a concentration that is 25 times <strong>the</strong> concentrationto kill 99% <strong>of</strong> <strong>the</strong> target pest (Gould <strong>and</strong> Tabashnik, 1998). Analternative is at least 99.99 % mortality <strong>of</strong> homozygote susceptiblesrelative to a non-<strong>Bt</strong> control (ILSI, 1999). Caprio et al. (2000) found thatdominance <strong>and</strong> SS survival were correlated, such that higher SS survivalwas associated with higher dominance (low-dose). <strong>The</strong>y showed that aconcentration <strong>of</strong> Cry toxin that is 50 times <strong>the</strong> concentration to kill 99%<strong>of</strong> <strong>the</strong> target pest is high enough that all known resistance alleles would befunctionally recessive (= high-dose).By any <strong>of</strong> <strong>the</strong>se criteria, EE-1 <strong>Bt</strong> brinjal is a low dose event.
Environmental Risk Assessment 43non-<strong>Bt</strong> brinjal refuges will cause a greater delay in resistance than projected here.b. BFSB is <strong>the</strong> only species at <strong>risk</strong> <strong>of</strong> resistance evolution on <strong>Bt</strong> brinjal. If <strong>the</strong>re are o<strong>the</strong>r species at <strong>risk</strong>, <strong>the</strong>y should beanalysed as well to determine if <strong>the</strong>y could be a more serious resistance <strong>risk</strong>.c. BFSB has evolved resistance to insecticides in India. <strong>The</strong> scientific documentation <strong>of</strong> this is thin, although it is widelystated. If BFSB has evolved resistance to insecticides <strong>the</strong>n we can conclude that it has a population structure that wouldallow evolution to <strong>Bt</strong> brinjal as well.d. BFSB larvae can move from plant to plant, <strong>and</strong> fruit to fruit. This would imply that seed mixtures may speed up <strong>the</strong> rate<strong>of</strong> resistance evolution, <strong>and</strong> this IRM tactic might best be avoided.e. BFSB adults can move a few hundred meters <strong>and</strong> males <strong>and</strong> females are similarly dispersive. No published papers onadult movement could be found. <strong>The</strong> level <strong>of</strong> dispersal that is assumed is low relative to o<strong>the</strong>r species <strong>of</strong> Crambidae thatare pests in o<strong>the</strong>r crops. Given <strong>the</strong> small size <strong>of</strong> brinjal fields, this assumption means that most adults will leave <strong>the</strong> fieldthat <strong>the</strong>y were born in (<strong>the</strong>ir natal field), but <strong>the</strong>y will have little trouble finding ano<strong>the</strong>r field (or returning to <strong>the</strong>ir natalfield). This leads us to assume that <strong>the</strong>proportion <strong>of</strong> adult males <strong>and</strong> females thatleave <strong>the</strong>ir natal field is 0.9 (r = 0.9). If r Figure 2. Time to failure <strong>of</strong> <strong>Bt</strong> brinjal for a. 50% adoption rate <strong>of</strong> <strong>Bt</strong> brinjal<strong>and</strong> b. 90% adoption rate. For each adoption rate, time to failure is shownwere lower, evolution would be delayed, but for heterozygosity (h) = 0.2 <strong>and</strong> 0.4, <strong>and</strong> for each <strong>of</strong> <strong>the</strong>se heterozygosityif r were too low, evolution will speed up. values, time to failure is shown for four refuge options, no refuge (or nocompliance to <strong>the</strong> refuge), 5%, 10% <strong>and</strong> 20% refuge (assuming 100%f. All <strong>Bt</strong> brinjal have <strong>the</strong> same level <strong>of</strong>compliance). Failure time is <strong>the</strong> time until <strong>the</strong> R allele frequency reaches 0.5.control <strong>of</strong> BFSB (including any non<strong>of</strong>ficialseed). Heterogeneity in expression 0.9, s = 1, F = 100, a = 6, b = 0.8, p 0Simulations are based on <strong>the</strong> model <strong>of</strong> Alstad <strong>and</strong> Andow (1996) with r == 0.0001, K = 0.27, L = 1, <strong>and</strong> 3generations <strong>of</strong> BFSB on <strong>Bt</strong> brinjal per year. O<strong>the</strong>r generations <strong>of</strong> BFSB are<strong>of</strong> Ccry1A could create hot spots where assumed to be on non-<strong>Bt</strong> plants during <strong>the</strong> rest <strong>of</strong> <strong>the</strong> year.evolution occurs very rapidly <strong>and</strong> spreadsto o<strong>the</strong>r areas. This would result in fasterresistance failures. Based on <strong>the</strong> survivalrates reported in <strong>the</strong> Dossier (volume 6), wecalculated <strong>the</strong> average survival on <strong>Bt</strong> brinjalto be 0.27, so K = 0.27.g. <strong>The</strong>re is no fitness cost <strong>of</strong> resistance inBFSB (L = 1). A fitness cost <strong>of</strong> resistanceis defined as when <strong>the</strong> resistance genehas a lower fitness than <strong>the</strong> susceptibilitygene in <strong>the</strong> absence <strong>of</strong> selection forresistance. Thus, <strong>the</strong> resistance allelewould be favoured on <strong>Bt</strong> brinjal, but <strong>the</strong>susceptibility allele would be favoured onany non-<strong>Bt</strong> host plant, such as <strong>the</strong> non-<strong>Bt</strong>refuge. Actually, a fitness cost is expected.Gassman et al. (2009) showed that nearly all<strong>Bt</strong> resistance genes had some level <strong>of</strong> fitnesscost, however, it is not possible to predict<strong>the</strong> fitness cost until resistance is discovered. Because <strong>the</strong> fitness cost varies from nil, which would have no influenceon resistance evolution, to large, which would greatly delay resistance if a refuge were used, we modelled no fitness cost.This is a worst-case assumption. If it turns out that BFSB resistance has a significant fitness cost, <strong>the</strong>n <strong>the</strong> time to controlfailures would take longer to reach. More significantly, however, <strong>the</strong> use <strong>of</strong> effective 20% refuges would extend <strong>the</strong> time toresistance by much more than 25%.h. BFSB has as many as 8 generations a year (Alam et al 2003), but only three <strong>of</strong> <strong>the</strong>m will be associated with <strong>Bt</strong> brinjal.