首页> 外文会议>ACS Symposium Series 892; Pan-Pacific Conference on Pesticide Science; 20030601-04; Honolulu,HI(US) >Impact of Bacillus thuringiensis Corn Pollen on Monarch Butterfly Populations
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Impact of Bacillus thuringiensis Corn Pollen on Monarch Butterfly Populations

机译:苏云金芽孢杆菌玉米花粉对帝王蝶种群的影响

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Nearly four years ago, in 1999, a note submitted to the editor of Nature from scientists at Cornell University claimed that pollen from a Bt corn hybrid harmed larvae of the monarch butterfly (1). They had sprinkled an unspecified amount of pollen from a Bt11 corn hybrid on milkweed leaves that they fed to small larvae of monarchs. The ensuing international reaction from anti-biotechnology activists created the impression that this pollen and its underlying technology might cause significant damage to populations of non-target insects such as the monarch as well as detrimental effects to the environment. A number of scientists in Canada and the United States who had evaluated Bt corn for efficacy, economic viability and its impact on non-targets in the agricultural environment gathered to initiate a collaborative investigation into the impact of Bt corn pollen on monarchs. As a group, we felt that, due to the naive methodology and inconclusive results of the reported laboratory study and the unjustified statements from activist groups, further appropriate and scientifically sound investigations were warranted. We approached this process with the objective of obtaining information on toxicity and exposure of monarch larvae to Bt corn pollen and to develop a classical risk assessment using this information. We performed a series of replicated bioassays using both purified toxins and pollen samples from a number of corn hybrids created with different transformation events. In these, we measured the effect of increasing doses of Bt pollen on feeding behavior and weight gain of first-instar monarch larvae. We established a no-observable-effect level (NOEL) from these results and compared that dose with the density of pollen that we estimated to occur on milkweed leaves in and around corn fields to determine the likelihood of encounter with an effective dose. To validate our laboratory observations and estimates of impact, we performed a series of field experiments over two years in three different locations within the Corn Belt. Monarch larvae were either caged on milkweed plants or fed milkweed leaves from plants in and around corn fields that had previously received corn pollen during pollen shed. Larvae were allowed to feed on the milkweed for the period of their development and their weight gain and survival monitored. Treatments were carried out on milkweed plants placed in fields of Bt corn, in conventional corn fields and in areas removed from corn altogether. Concurrently, we examined populations of monarchs in several locations within the Corn Belt to determine the synchrony of larval development in relation to pollen shed activity in corn fields. In addition, we attempted to estimate for the entire Corn Belt the amount of milkweed found in com fields, other agricultural fields and in non-agricultural land to determine the proportion of monarch larvae that could receive significant amounts of pollen in their diets. Response of monarch larvae to Cry proteins produced from various events used to create commercial corn hybrids was variable. Bt corn pollen from commercial hybrids at levels exceeding 1000 pollen grains/cm~2 of leaf area did not cause measurable impact to monarch larvae in bioassay trials. Only one type of pollen produced any impact, from Event Bt176 corn, and hybrids using that event never exceeded 2% of the production area and no longer are registered for use in North America (2). In every field trial, no impact was measured to larvae exposed to pollen from any Bt corn hybrid, except those developed from Event 176 technology. Even in subsequent trials, no monarch larvae have shown a measurable reaction to Bt corn pollen at field densities.
机译:大约四年前,即1999年,康奈尔大学(Cornell University)科学家向《自然》(Nature)编辑提交的说明声称,Bt玉米杂交种的花粉损害了帝王蝶的幼虫(1)。他们从Bt11玉米杂种上撒了一定量的花粉,撒在乳草叶子上,喂给君主的小幼虫。反生物技术活动家随后进行的国际反应给人的印象是,这种花粉及其潜在技术可能对君主等非目标昆虫的种群造成重大损害,并对环境造成不利影响。加拿大和美国的许多科学家对Bt玉米的功效,经济可行性及其对农业环境中非目标的影响进行了评估,他们发起了一项合作研究,调查Bt玉米花粉对君主的影响。作为一个小组,我们认为,由于所报告的实验室研究的幼稚方法论和不确定的结果以及激进主义者团体的不合理陈述,因此有必要进行进一步适当和科学的调查。我们采用这一方法的目的是获得有关帝王幼虫对Bt玉米花粉的毒性和暴露信息,并利用该信息进行经典的风险评估。我们使用纯化的毒素和来自许多具有不同转化事件的玉米杂交种的花粉样品进行了一系列重复的生物测定。在这些研究中,我们测量了增加剂量的Bt花粉对第一龄帝王蝶幼虫的摄食行为和体重增加的影响。我们根据这些结果确定了不可观察的水平(NOEL),并将该剂量与我们估计在玉米田中和周围的马利筋叶上发生的花粉密度进行了比较,以确定遇到有效剂量的可能性。为了验证我们的实验室观察结果和影响评估,我们在玉米带内的三个不同位置进行了为期两年的一系列现场试验。帝王幼虫要么被关在乳草植物上,要么被饲喂以前在花粉棚中接受过玉米花粉的玉米田及其周围地区的植物饲喂的乳草叶。允许幼虫以乳草为生,并对其体重增加和存活进行监测。对放置在Bt玉米田,常规玉米田和完全从玉米中移除的马利筋植物进行了处理。同时,我们检查了玉米带内多个位置的君主种群,以确定幼虫发育与玉米田中花粉脱落活动的同步性。此外,我们尝试估算整个玉米带在玉米田,其他农田和非农业土地上发现的马利筋草数量,以确定可以在饮食中接受大量花粉的帝王幼虫的比例。帝王幼虫对Cry蛋白的反应是可变的,这些蛋白是由用于创建商业玉米杂交品种的各种事件产生的。在生物测定试验中,商业杂交种的Bt玉米花粉水平超过1000花粉粒/ cm〜2叶面积,对君主幼虫没有可测量的影响。仅事件Bt176玉米中的一种花粉产生了任何影响,使用该事件的杂交种从未超过生产面积的2%,并且不再在北美注册使用(2)。在每个田间试验中,除了使用Event 176技术开发的那些幼虫外,均未测量到任何Bt玉米杂交种暴露于花粉的幼虫的影响。即使在随后的试验中,也没有帝王幼虫在田间密度下对Bt玉米花粉表现出可测量的反应。

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