转基因植物环境监测进展

近20年来,转基因植物的商业化应用规模越来越大,而转基因生物安全问题依然是转基因植物产业进一步发展的最主要制约因素。转基因植物在商业化应用之前虽然预先进行了风险评估,但是,包括环境监测在内的风险管理措施是确保转基因植物安全应用的必要手段。在转基因作物大规模应用近20年之后,其在靶标生物抗性、对生物多样性的影响、基因漂移、在生态系统中的长期存留等方面产生的环境风险已经渐渐显现出来,表明风险评估无法为转基因植物应用提供足够的安全保障,还必须通过开展系统而长期的环境监测,明确转基因植物在生产应用后的实际环境影响。联合国环境规划署和欧盟等已经制定了转基因植物环境监测的法规和技术指南,一些国家实施了系统的转基因植物环境监测。对转基因植物所产生的环境风险以及环境监测应包括的内容进行了综述。     

转基因植物环境安全评价策略

构建完善的转基因植物环境安全评价技术体系是保障转基因生物产业健康发展的重要组成部分。本文综述了转基因植物环境安全评价技术发展历程与趋势,归纳了转基因植物环境安全评价的思路与内容。转基因植物环境安全评价应分为潜在风险分析、风险假设验证、风险特征描述等3个步骤,并采用逐层评价模式;安全评价应贯穿转基因植物新品种研发与产业化全程,包括应用前预测、研发中筛选、推广前评价、推广后监测。此外,基于科学性和个案分析原则,本文对复合性状、非生物胁迫抗性等新型转基因植物环境安全评价策略进行了探讨。     

Community response to transgenic plant release: using mathematical theory to predict effects of transgenic plants

Predicting the potential effects of introductions of plants on the structure of plant communities has been elusive. I suggest that mathematical models of resource competition might be useful for identifying categories of plants that either are unlikely to alter community structure or that have the potential for altering community structure. Assuming that the transgenic plant will escape and establish viable populations in nontarget habitats, this theory suggests that species that have a high minimum resource requirement are unlikely to alter community structure. The theory is elaborated to evaluate the potential effects on community structure of transgenic plants with resistance to primary consumers. Results indicate that the greatest reduction in the minimum resource requirement caused by resistance will occur when consumers are consuming enough plant biomass that the plant can no longer grow. If resistance to such a consumer were incorporated into a plant, it could lower the minimum resource requirement sufficiently that a transgenic plant would be able to alter community structure substantially. Examples of introductions of exotic plants, plant pathogens, and insect herbivores are given to support the conceptual basis of the theory. Not all transgenic plants with resistance, however, have the potential to alter community structure. Resistance to primary consumers that strongly reduce the biomass producing ability of a plant will probably be able to alter community structure, whereas resistance that reduces most other types of yield loss is less likely to alter community structure. The theory should be elaborated to incorporate more-realistic assumptions, such as those regarding reproduction, dormancy, and dispersal of the transgenic plants, and provide more detailed characterization of the potential hazard of transgenic plants to plant communities.     

First-generation transgenic plants and statistics

The statistical analyses of populations of first-generation transgenic plants are commonly based on mean and variance and generally require a test of normality. Since in many cases the assumptions of normality are not met, analyses can result in erroneous conclusions. Transformation of data to normality, the use of other distributions, or distribution-free statistical tests should then be used to obtain valid conclusions from these populations.     

Assessing the risks of insect resistant transgenic plants on entomophagous arthropods Bt-maize expressing Cry1Ab as a case study

One of the primary concerns related to theadoption of insect resistant transgenic plantsin the environment is the detrimental effectthat these may pose on non-target organisms,including entomophagous arthropods (parasitoidsfand predators) which have an important functionin regulating pests. Despite the fact thatregulatory bodies require information regardingthe potential risk of releasing transgenicplants in the environment, to date, no specificprotocols have been designed for assessing therisks of insect resistant transgenic crops onentomophagous arthropods. Here a framework forrisk assessment is proposed to evaluate theeffects of insect resistant plants onentomophagous arthropods. Using maizeexpressing the Bacillus thuringiensisgene which codes for the Cry1Ab toxin, weillustrate the procedure necessary forassessing the risks. As a first step, it isrequired to determine which entomophagousarthropods play a major role in regulatingmaize pests, and which may be at risk. Becausethe risk which transgenic plants pose toentomophagous arthropods depends on both, theirexposure, and their sensitivity to theinsecticidal protein, it is essential todetermine, as a second step, if and at whatlevel organisms are exposed to the transgenecompound. Exposure will be associated with thefeeding behaviour of phytophagous andentomophagous arthropods together with thetissue and cell specific temporal and spatialexpression of the insecticidal protein. Forthose organisms which could potentially beexposed to the insecticidal protein,sensitivity tests, as a third step, should beperformed to assess toxicity. The testingprocedure and the type of tests which should beadopted to quantify the effects of insectresistant plants on natural enemies aresubsequently illustrated. Taking the greenlacewing Chrysoperla carnea as anexample, we propose a procedure on how toperform tests and give evidence that Bt-maizeposes no risk to this predator.     

转抗虫基因植物生态安全性研究进展

转抗虫基因植物如Bt棉花等已在美国、中国和澳大利亚等国家大规模商业化种植 ,有关转抗虫基因植物潜在的生态风险已引起广泛的关注。该文综述了转抗虫基因植物研究应用现状与安全性研究进展。主要内容包括 :转抗虫基因植物的种类及其对靶标害虫的抗性 ,对非靶标害虫和天敌发生的影响 ,对农田生态系统生物多样性的影响 ,靶标昆虫的抗性治理及转抗虫基因植物的基因漂移等     

转基因植物中抗生素抗性基因的安全性评价

20世纪80年代以来,植物转基因技术取得突飞猛进的进展。转基因植物大量出现,带来了巨大的经济效益和社会效益。与此同时,转基因植物的释放可能带来的风险也越来越受到人们的重视,抗生素抗性基因是筛选转基因植物的常用基因,其安全性引起了人们的普遍关注,作者就转基因植物中抗生素抗性基因的安全性作一综述。     

Biological Activity of Cry1Ab Toxin Expressed by Bt Maize Following Ingestion by Herbivorous Arthropods and Exposure of the Predator Chrysoperla carnea

A major concern regarding the deployment of insect resistant transgenic plants is their potential impact on non-target organisms, in particular on beneficial arthropods such as predators. To assess the risks that transgenic plants pose to predators, various experimental testing systems can be used. When using tritrophic studies, it is important to verify the actual exposure of the predator, i.e., the presence of biologically active toxin in the herbivorous arthropod (prey). We therefore investigated the uptake of Cry1Ab toxin by larvae of the green lacewing (Chrysoperla carnea (Stephens); Neuroptera: Chrysopidae) after consuming two Bt maize-fed herbivores (Tetranychus urticae Koch; Acarina: Tetranychidae and Spodoptera littoralis (Boisduval); Lepidoptera: Noctuidae) by means of an immunological test (ELISA) and the activity of the Cry1Ab toxin following ingestion by the herbivores. Moreover, we compared the activity of Cry1Ab toxin produced by Bt maize to that of purified toxin obtained from transformed Escherichia coli, which is recommended to be used in toxicity studies. The activity of the toxin was assessed by performing feeding bioassays with larvae of the European corn borer (Ostrinia nubilalis (Hübner); Lepidoptera: Crambidae), the target pest of Cry1Ab expressing maize. ELISA confirmed the ingestion of Bt toxin by C. carnea larvae when fed with either of the two prey species and feeding bioassays using the target pest showed that the biological activity of the Cry1Ab toxin is maintained after ingestion by both herbivore species. These findings are discussed in the context of previous risk assessment studies with C. carnea. The purified Cry1Ab protein was more toxic to O. nubilalis compared to the plant-derived Cry1Ab toxin when applied at equal concentrations according to ELISA measurements. Possible reasons for these findings are discussed.     

转基因植物与近缘种之间基因流的研究进展

随着转基因植物的大面积种植,转基因植物的生态风险受到广泛关注,其中主要的风险是转基因植物与近缘物种之间的基因流及其影响。本文综述了目前商业化种植的转基因作物油菜、棉花、玉米和大豆,以及未商业化种植的水稻、小麦的基因流研究进展;分析了不同转基因作物与其近缘种之间发生基因流的频率和最远发生距离;介绍了降低基因流发生的方法。基因流频率受物种亲缘关系、花期重叠时间、风速风向等因素的影响,最远发生距离受气候条件、传粉媒介、地理条件等因素的影响。转基因作物与其近缘种之间的基因流频率与距花粉源的距离呈负相关关系(y=-0.59x-0.46,R²=0.25,P<0.01),亲缘关系近的基因流频率高。为了降低转基因植物与其近缘物种之间的基因流风险,建议采取“分区管理”的策略,并加强基因流发生之后的生态风险评价研究。     

Detection and monitoring of insect resistance to transgenic Bt crops

Transgenic crops expressing Bacillus thuringiensis （Bt） endotoxins havebecome one of the most important tools for managing corn and cotton insect pests in the US and other countries. The widespread adoption of transgenic Bt crops could place a high degree of selection pressure on the target insect populations and accelerate development of resistance, raising concerns about the long-term durability of Bt plants as an effective pest management tool. Conservation of Bt susceptibility in insects has become one of the most active research areas in modern agriculture. One of the key factors for a successful Bt resistance management plan is to have a cost-effective monitoring system that can provide information on. （i） the initial Bt resistance allele frequencies at low levels in field insect populations; and （ii） early shifts in Bt resistance allele frequencies so that proactive measures for managing resistance can be deployed well before field control failures. Developing such a monitoring program has been difficult because： （i） resistance traits that occur at very low frequencies are hard to detect; （ii） many factors affect the sensitivity and accuracy of a Bt resistance monitoring program; and （iii） monitoring resistance is costly. Several novel methods for detecting Bt resistance alleles developed during the last decade have made a cost-effective monitoring system possible. Future studies should focus on how to improve and standardize the methodologies for insect sampling and Bt resistance detection.     

Quantitation of chloramphenicol acetyl transferase in transgenic tobacco plants by ELISA and correlation with gene copy number

A monoclonal antibody to chloramphenicol acetyl transferase (CAT) was used in an indirect competitive enzyme immunoassay (ELISA) for the quantitation of CAT in leaf extracts of eighteen transgenic tobacco plants containing the CAT gene fused to the cauliflower mosaic virus 35S promoter. The ELISA could be used to quantify CAT when present in extracts at 20 ng/ml. Enzymatic activity and electrophoretic mobility of CAT in these extracts was not different from CAT from Escherichia coli. Concentrations of CAT in these transgenic plants ranged from 79 to 732 ng CAT/mg protein. The average coefficient of variation among three replicate samples was 15%. All plants were sampled on two separate occasions. The CAT concentrations often varied between the two sampling dates. We determined the CAT gene copy number and the number of independently segregating loci in each plant by Southern blot analysis and progeny testing. We found no significant differences in CAT expression among all ten plants with a single CAT gene. We also found a significant correlation between CAT gene copy number and the level of CAT expressed in each plant, although plants with one gene copy sometimes had more CAT than plants with more than one gene copy. In this population, therefore, gene copy number contributed more to the variation in CAT expression than did position effects.     

Genetically modified organisms and risks of their introduction

The major goal of this review is to assess food risks of the introduction of genetically modified (GM) crops. The author analyzes the properties of the several classes of target proteins used in the transgenic constructions and discusses the problems that arise due to the pleiotropic action of transgenic proteins, the horizontal transfer of the transgenic constructions, primarily in bacteria, and their instability. Particular consideration is given to elevated risks of using the GM plant varieties for producing pharmaceutical preparations, due to the probability of uncontrolled cross-pollination between the GM plants and the plants grown for foodstuff production. The author emphasizes the requirement for assessing in detail all hypothetic risks in each particular case of cultivating GM varieties; as a control, such assessment must involve a comprehensive comparison with the conventional parental forms.Translated from Fiziologiya Rastenii, Vol. 52, No. 1, 2005, pp. 115–128.Original Russian Text Copyright © 2005 by Kulikov.     

Implications of transgenic, insecticidal plants for insect and plant biodiversity

Genetically modified plants are widely grown predominantly in North America and to a lesser extent in Australia, Argentina and China but their regions of production are expected to spread soon beyond these limited areas also reaching Europe where great controversy over the application of gene technology in agriculture persists. Currently, several cultivars of eight major crop plants are commercially available including canola, corn, cotton, potato, soybean, sugar beet, tobacco and tomato, but many more plants with new and combined multiple traits are close to registration. While currently agronomic traits (herbicide resistance, insect resistance) dominate, traits conferring “quality” traits (altered oil compositions, protein and starch contents) will begin to dominate within the next years. However, economically the most promising future lies in the development and marketing of crop plants expressing pharmaceutical or “nutraceuticals” (functional foods), and plants that express a number of different genes. From this it is clear that future agricultural and, ultimately, also natural ecosystems will be challenged by the large-scale introduction of entirely novel genes and gene products in new combinations at high frequencies all of which will have unknown impacts on their associated complex of non-target organisms, i.e. all organisms that are not targeted by the insecticidal protein. In times of severe global decline of biodiversity, pro-active precaution is necessary and careful consideration of the likely expected effects of transgenic plants on biodiversity of plants and insects is mandatory.In this paper possible implications of non-target effects for insect and plant biodiversity are discussed and a case example of such non-target effects is presented. In a multiple year research project, tritrophic and bitrophic effects of transgenic corn, expressing the gene from Bacillus thuringiensis (Bt-corn) that codes for the high expression of an insecticidal toxin (Cry1Ab), on the natural enemy species, Chrysoperla carnea (the green lacewing), was investigated. In these laboratory trials, we found prey-mediated effects of transgenic Bt-corn causing significantly higher mortality of C. carnea larvae. In further laboratory trials, we confirmed that the route of exposure (fed directly or via a herbivorous prey) and the origin of the Bt (from transgenic plants or incorporated into artificial diet) strongly influenced the degree of mortality. In choice feeding trials where C. carnea could choose between Spodoptera littoralis fed transgenic Bt-corn and S. littoralis fed non-transgenic corn, larger instars showed a significant preference for S. littoralis fed non-transgenic corn while this was not the case when the choice was between Bt- and isogenic corn fed aphids. Field implications of these findings could be multifold but will be difficult to assess because they interfere in very intricate ways with complex ecosystem processes that we still know only very little about. The future challenge in pest management will be to explore how transgenic plants can be incorporated as safe and effective components of IPM systems and what gene technology can contribute to the needs of a modern sustainable agriculture that avoids or reduces adverse impacts on biodiversity? For mainly economically motivated resistance management purposes, constitutive high expression of Bt-toxins in transgenic plants is promoted seeking to kill almost 100% of all susceptible (and if possible heterozygote resistant) target pest insects. However, for pest management this is usually not necessary. Control at or below an established economic injury level is sufficient for most pests and cropping systems. It is proposed that partially or moderately resistant plants expressing quantitative rather than single gene traits and affecting the target pest sub-lethally may provide a more meaningful contribution of agricultural biotechnology to modern sustainable agriculture. Some examples of such plants produced through conventional breeding are presented. Non-target effects may be less severe allowing for better incorporation of these plants into IPM or biological control programs using multiple control strategies, thereby, also reducing selection pressure for pest resistance development.     

Development and deployment of transgenic plants: Biosafety considerations

Summary Recombinant DNA technology has great potential to enhance and extend the advantages of conventional plant breeding, and increase the production and productivity of crops to meet the increasing demand for food and food products in the future. Judicious application of this technology provides opportunities for alleviating some of the major constraints to crop productivity under subsistence farming conditions in the developing countries. Considerable progress has been made in developing strategies for the production and deployment of transgenic crops. However, biosafety concerns have been raised regarding the deployment and release of genetically engineered plants. This debate has divided the farming and consumer communities over acceptability of genetically modified foods. There is a need for a thorough investigation regarding the fate of transgenic plants in the environment, and their interaction with wild relatives and non-target organisms. The production and release of transgenic plants should be based on experience and sound scientific reasoning. The regulatory requirements for deployment of transgenic crops should be streamlined and harmonized, in order to achieve sustainable food production, poverty reduction, and environmental protection in resource-poor countries in the semi-arid tropics.     

转基因植物的表型变异、分子检测与遗传分析

本讨论了转化方法、体细胞克隆和选育过程等影响转基因植物表型变异的因素,并对转基因植物不同群体的表型变异组成和效应进行了比较分析,提出了转基因植物分子检测和遗传分析的技术策略。多数情况下,分析转基因植物回交后代(BClF1)比分析T1代能获得更可靠和有价值的结论。     

Paraquat resistance of transgenic tobacco plants over-expressing the Ochrobactrum anthropi pqrA gene

Transgenic tobacco plants over-expressing the Ochrobactrum anthropi pqrA gene, which encodes a membrane transporter mediating resistance to paraquat, were generated. Transgenic plants displayed higher resistance against paraquat than wild-type plants, as estimated by plant viability, ion leakage and chlorophyll loss, but no resistance against other active oxygen generators, such as H2O2 and menadione. Moreover, lower levels of paraquat accumulated in transgenic plants, compared to wild-type plants, indicating that the PqrA protein detoxifies paraquat either via increased efflux or decreased uptake of the herbicide, but not by removing active oxygen species. The results collectively demonstrate that the bacterial paraquat resistance gene, pqrA, can be functionally expressed in plant cells, and utilized for the development of paraquat-resistant crop plants.     

转基因植物释放后在环境中成为杂草的风险性

随着转基因植物释放规模的增大,转基因植物对环境的影响,特别是转基因植物是否会成为不可控制的杂草等问题已引起人们的关注。本文对近年来在转基因植物相关野生种的近缘性;发生杂交的适合性;授粉模式;种子扩散模式等方面转基因扩散机制的研究进展以及减少转基因扩散的有关措施进行了综述。     

转基因植物的基因漂流风险

讨论了近10年有关转基因植物漂流方面的5个主要研究领域,转基因进入相关植物野生种或近缘种中的实证性研究,以花粉为煤体的基因漂流特性研究,基因漂流实验和风险评价方法研究,基因漂流风险安全性评价标准的争论和基因漂流的长期生态效应研究,提出了目前应进一步开展的研究课题。