Then Christoph, Bauer-Panskus Andreas
Testbiotech, Institute for Independent Impact Assessment in Biotechnology, Frohschammerstr. 14, 80807 Munich, Germany.
Environ Sci Eur. 2017;29(1):1. doi: 10.1186/s12302-016-0099-0. Epub 2017 Jan 11.
MON89788 was the first genetically engineered soybean worldwide to express a Bt toxin. Under the brand name Monsanto subsequently engineered a stacked trait soybean using MON89788 and MON87701-this stacked soybean expresses an insecticidal toxin and is, in addition, tolerant to glyphosate. After undergoing risk assessment by the European Food Safety Authority (EFSA), the stacked event was authorised for import into the EU in June 2012, including for use in food and feed. This review discusses the health risks associated with Bt toxins present in these genetically engineered plants and the residues left from spraying with the complementary herbicide.
We have compared the opinion published by EFSA [1] with findings from other publications in the scientific literature. It is evident that there are several issues that EFSA did not consider in detail and which will need further assessment: (1) There are potential combinatorial effects between plant components and other impact factors that might enhance toxicity. (2) It is known that Bt toxins have immunogenic properties; since soybeans naturally contain many allergens, these immunogenic properties raise specific questions. (3) Fully evaluated and reliable protocols for measuring the Bt concentration in the plants are needed, in addition to a comprehensive set of data on gene expression under varying environmental conditions. (4) Specific attention should be paid to the herbicide residues and their interaction with Bt toxins.
The case of the soybeans highlights several regulatory problems with Bt soybean plants in the EU. Moreover, many of the issues raised also concern other genetically engineered plants that express insecticidal proteins, or are engineered to be resistant to herbicides, or have those two types of traits combined in stacked events. It remains a matter of debate whether the standards currently applied by the risk assessor, EFSA, and the risk manager, the EU Commission, meet the standards for risk analysis defined in EU regulations such as 1829/2003 and Directive 2001/18. While this publication cannot provide a final conclusion, it allows the development of some robust hypotheses that should be investigated further before such plants can be considered to be safe for health and the environment. In general, the concept of comparative risk assessment needs some major revision. Priority should be given to developing more targeted approaches. As shown in the case of these approaches should include: (i) systematic investigation of interactions between the plant genome and environmental stressors as well as their impact on gene expression and plant composition; (ii) detailed investigations of the toxicity of Bt toxins; (iii) assessment of combinatorial effects taking into account long-term effects and the residues from spraying with complementary herbicides; (iv) investigation into the impact on the immune and hormonal systems and (v) investigation of the impact on the intestinal microbiome after consumption. Further and in general, stacked events displaying a high degree of complexity due to possible interactions should not undergo a lower level of risk assessment than the parental plants.
MON89788是全球首个表达Bt毒素的转基因大豆。孟山都公司随后以该品牌研发出一种叠加性状大豆,它结合了MON89788和MON87701——这种叠加大豆既表达一种杀虫毒素,又对草甘膦具有耐受性。在经过欧洲食品安全局(EFSA)的风险评估后,该叠加事件于2012年6月被批准进口至欧盟,包括用于食品和饲料。本综述讨论了这些转基因植物中存在的Bt毒素以及喷洒配套除草剂后残留物质所带来的健康风险。
我们将欧洲食品安全局发表的意见[1]与科学文献中其他出版物的研究结果进行了比较。显然,欧洲食品安全局未详细考虑的几个问题需要进一步评估:(1)植物成分与其他影响因素之间可能存在组合效应,这可能会增强毒性。(2)已知Bt毒素具有免疫原性;由于大豆天然含有多种过敏原,这些免疫原性引发了一些具体问题。(3)除了关于不同环境条件下基因表达的全面数据集外,还需要用于测量植物中Bt浓度的经过充分评估且可靠的方案。(4)应特别关注除草剂残留及其与Bt毒素的相互作用。
大豆的案例凸显了欧盟对Bt大豆植物监管方面的几个问题。此外,所提出的许多问题也涉及其他表达杀虫蛋白、对除草剂具有抗性或在叠加事件中兼具这两种性状组合的转基因植物。风险评估机构欧洲食品安全局以及风险管理者欧盟委员会目前应用的标准是否符合欧盟法规(如1829/2003和指令2001/18)中定义的风险分析标准,仍是一个有争议的问题。虽然本出版物无法给出最终结论,但它有助于提出一些有力的假设,在认为此类植物对健康和环境安全之前,应进一步对这些假设进行研究。总体而言,比较风险评估的概念需要进行一些重大修订。应优先开发更具针对性的方法。如这些大豆案例所示,这些方法应包括:(i)系统研究植物基因组与环境应激源之间的相互作用及其对基因表达和植物组成的影响;(ii)详细研究Bt毒素的毒性;(iii)考虑长期影响和喷洒配套除草剂后的残留物质,评估组合效应;(iv)调查对免疫和激素系统的影响;(v)调查食用后对肠道微生物群的影响。此外,一般来说,由于可能的相互作用而表现出高度复杂性的叠加事件,其风险评估不应低于亲本植物。