MON 810 Environmental Risk Assessment Case Study
Disclaimer
Monsanto Company has generously consented to the use of the information provided in various of their regulatory submissions for event MON 810 as a training tool. It must be noted, however, that in order to enhance the utility of the case study as a training tool, liberties were taken with the information provided in the original applications. Certain information has been reduced to summaries and the data as presented in the case study are only a subset of that which was actually submitted. The case study in no way constitutes a complete application nor is it to be considered a complete safety assessment. To that end, the use of this information in the form of a training tool does not constitute an endorsement of the information or product nor should it be considered as a reflection of any of the original submissions.
Preface
This teaching module has been developed as a tool for providing regulators with practical training in the safety assessment of transgenic plants. The concepts of risk assessment as discussed in this text do not reflect any one country's regulatory approach, but rather have been modelled after international consensus documents such as those produced by the Organization for Economic Cooperation and Development (OECD), the World Health Organization (WHO) and the Food and Agriculture Organization (FAO) of the United Nations.
In order to provide some indication of the type of data usually presented in support of a safety evaluation, a case study using genetically engineered maize (
Zea mays) event MON 810 and its progeny has been developed. The content of the study includes excerpts from applications submitted to regulatory authorities in the European Union, the United Kingdom (UK), Japan, and the United States (US).

Maize line MON 810 (trade name YieldGard®) was developed through a specific genetic modification to be resistant to attack by European corn borer (ECB;
Ostrinia nubilalis), a major insect pest of maize in agriculture. The novel variety produces a truncated version of the insecticidal protein, Cry1Ab, derived from
Bacillus thuringiensis. Delta-endotoxins, such as the Cry1Ab protein expressed in MON 810, act by selectively binding to specific sites localized on the brush border midgut epithelium of susceptible insect species. Following binding, cation-specific pores are formed that disrupt midgut ion flow and thereby cause paralysis and death. Cry1Ab is insecticidal only to lepidopteran insects, and its specificity of action is directly attributable to the presence of specific binding sites in the target insects. There are no binding sites for delta-endotoxins of
B. thuringiensis on the surface of mammalian intestinal cells, therefore, livestock animals and humans are not susceptible to these proteins.
Event MON 810 received its first regulatory approval in the US in 1995 (US Department of Agriculture), and has since been approved for environmental release and use in livestock feed and/or human food from a number of countries including Argentina, Canada, Japan, South Africa, and the European Union (Table 1).
A Note on Quality Standards for Documentation
The evaluation of an application for environmental release is comparable to the peer review of a manuscript for publication in a scientific journal. Accordingly, the quality of the text and data presented must be commensurate with this.
Experimental procedures should be described in sufficient detail (or referenced accordingly) so that the methodology can be repeated. Spelling and usage should be standard and laboratory jargon avoided. It is recommended that international standards for nomenclature be adopted, such as those described in the International Union of Biochemistry and Molecular Biology’s Biochemical Nomenclature and Related Documents (1992) 2nd Ed. Portland Press, Inc., Chapel Hill, NC which contains the International Union of Biochemistry rules of nomenclature for amino acids, peptides, nucleic acids, polynucleotides, vitamins, coenzymes, quinones, folic acid and related compounds, corrinoids, lipids, enzymes, proteins, cyclitols, steroids, carbohydrates, carotenoids, peptide hormones, and human immunoglobulins. Correct chemical names should be given and strains of organisms should be specified. Trade names should be identified. Système International (SI) units and symbols should be used whenever possible.
Illustrations, tables and figures must be clear and legible. Original drawings, high-quality photographs or laser prints are acceptable; poor-quality reproductions that often result from photocopying prints are not. In particular, reproductions of gels or blots must be of sufficient quality to clearly show the described results.
GTS 40-3-2 Food Safety Assessment Case Study
Disclaimer
Monsanto Inc. has generously consented to the use of the information provided in various of their regulatory submissions for event GTS 40-3-2 as a training tool. It must be noted, however, that in order to enhance the utility of the case study as a training tool, liberties were taken with the information provided in the original applications. Certain information has been reduced to summaries and the data as presented in the case study are only a subset of that actually submitted. The case study in no way constitutes a complete application nor is it to be considered a complete safety assessment. To that end, the use of this information in the form of a training tool does not constitute an endorsement of the information or product nor should it be considered a reflection of any of the original submissions.
Preface

In order to provide some insight into the type of data usually presented in support of a novel food evaluation, a case study of genetically engineered soybean (
Glycine max) event GTS 40-3-2 and its progeny has been developed. The content of the study includes excerpts from applications for food safety assessment submitted to regulatory authorities in Canada, the United Kingdom (UK), and the United States (U.S.).
Soybean is grown as a commercial crop in over 80 countries, with a combined harvest of 162 million metric tonnes. The major producers of soybeans in 2000 were the United States, Brazil, China, Argentina, India, Canada and Paraguay. Soybean is grown primarily for its seed, which has many uses in the food and industrial sectors, representing one of the major sources of edible vegetable oil and of proteins for livestock feed use.
A major food use of soybean in North America and Europe is as purified oil, used in margarines, shortenings, and cooking and salad oils. It is also a major ingredient in food products such as tofu, tempeh, soya sauce, simulated milk and meat products, and is a minor ingredient in many processed foods. Soybean meal is used as a supplement in feed rations for livestock.
Weeds are a major production problem in soybean cultivation. Typically, weeds are managed using a combination of cultural (e.g. seed bed preparation, using clean seed, variety selection, and planting date) and chemical controls. Depending on the production area and the prevalent weed species, herbicides may be applied before planting (
e.g. pendimethalin, trifluralin, metribuzin), after planting but before emergence (
e.g. pendimethalin, linuron, imazethapyr), and/or after emergence (
e.g. bentazon, acifluorfen, fomesafen). Commonly, several different herbicides are required to adequately control weeds in soybean fields.
The soybean line GTS 40-3-2 was developed to allow for the use of glyphosate, the active ingredient in the herbicide Roundup®, as a weed control option. This genetically engineered soybean line contains a form of the plant enzyme 5-enolpyruvylshikimate-3-phosphate synthase (EPSPS) that allows GTS 40-3-2 to survive the otherwise lethal application of glyphosate. The EPSPS gene put into GTS 40-3-2 was isolated from a strain of the common soil bacterium
Agrobacterium tumefaciens called CP4; the form of EPSPS enzyme produced by this gene is tolerant to glyphosate.
The EPSPS enzyme is part of an important biochemical pathway in plants called the shikimate pathway, which is involved in the production of aromatic amino acids and other aromatic compounds. When conventional plants are treated with glyphosate, the plants cannot produce the aromatic amino acids needed to grow and survive. EPSPS is present in all plants, bacteria, and fungi. It is not present in animals, which do not synthesize their own aromatic amino acids. As the aromatic amino acid biosynthetic pathway is not present in mammals, birds or aquatic life forms, glyphosate has little if any toxicity for these organisms. The EPSPS enzyme is naturally present in foods derived from plant and microbial sources.
GTS 40-3-2 was developed by introducing the CP4 EPSPS gene into a commercial soybean variety using particle-acceleration (biolistic) transformation. The glyphosate tolerance trait expressed in GTS 40-3-2 has since been transferred into more than one thousand commercial soybean varieties by traditional breeding techniques.
GTS 40-3-2 has been tested in field trials in the United States, Central and South America, Europe, and Canada since 1991. Data collected from over 150 field trials conducted over a three-year period prior to commercialization in the United States demonstrated that GTS 40-3-2 did not differ significantly from conventional soybeans in morphology, seed production (yield), agronomic characteristics (such as time to flowering and pod set, or vigor) and tendency to weediness. GTS 40-3-2 did not negatively affect beneficial or nontarget organisms, and was not expected to impact on threatened or endangered species.
Soybean does not have any weedy relatives with which it can crossbreed in the continental United States or Canada. Cultivated soybean can naturally cross with the wild annual species
G. soja, however
G. soja, which occurs naturally in China, Korea, Japan, Taiwan and the former USSR, is not naturalized in North America. Additionally, soybean plants are almost completely self-pollinated and reproductive characteristics such as pollen production and viability were unchanged by the genetic modification resulting in GTS 40-3-2. It was therefore concluded that the potential for transfer of the glyphosate tolerance trait from the transgenic line to soybean relatives through gene flow (outcrossing) was negligible in managed ecosystems, and that there was no potential for transfer to wild species in Canada and the continental United States.
The food and livestock feed safety of GTS 40-3-2 soybean was established based on: the evaluation of the similarity of the structure and function of CP4 EPSPS protein to this same enzyme naturally present in foods and livestock feeds, the fact that CP4 EPSPS protein constitutes a small amount of the protein in GTS-40-3-2 soybeans so there is little dietary exposure, the lack of toxicity or allergenicity of EPSPS proteins from plants, bacteria and fungi, and by direct laboratory studies of the CP4 EPSPS protein. Comparative analyses of key nutrients, including proximates (
e.g. protein, fat, fibre, ash, and carbohydrates), as well as antinutrients between GTS 40-3-2 soybeans and conventional soybeans did not reveal any significant differences. Feeding studies with rats, broiler chickens, cows, and fish further supported the safety and nutritional quality of GTS 40-3-2 as human food and livestock feed.

Event GTS 40-3-2 received its first regulatory approval in the US in 1994 (US Department of Agriculture), and has since been approved for environmental release and use in livestock feed and/or human food by a number of countries, including Argentina, Australia, Canada, Japan, and others (Table 1). In 1996, glyphosate tolerant soybeans were planted on less than 5% of the US soybean acreage. In the 2000 growing season, 54% of the soybeans - approximately 40 million acres of the 75.4 million acres of soybeans grown in the United States - were glyphosate tolerant. In Argentina, where the adoption rate is estimated at 95%, glyphosate tolerant soybeans were grown on over 20 million acres in 2000. Globally, glyphosate tolerant soybeans made up 58% of all transgenic crops grown in 2000.
A Note on Quality Standards for Documentation
The evaluation of an application for environmental release is comparable to the peer review of a manuscript for publication in a scientific journal. Accordingly, the quality of the text and data presented must be commensurate with this.
Experimental procedures should be described in sufficient detail (or referenced accordingly) so that the methodology can be repeated. Spelling and usage should be standard and laboratory jargon avoided. It is recommended that international standards for nomenclature be adopted, such as those described in the International Union of Biochemistry and Molecular Biology’s Biochemical Nomenclature and Related Documents (1992) 2nd Ed. Portland Press, Inc., Chapel Hill, NC which contains the International Union of Biochemistry rules of nomenclature for amino acids, peptides, nucleic acids, polynucleotides, vitamins, coenzymes, quinones, folic acid and related compounds, corrinoids, lipids, enzymes, proteins, cyclitols, steroids, carbohydrates, carotenoids, peptide hormones, and human immunoglobulins. Correct chemical names should be given and strains of organisms should be specified. Trade names should be identified. Système International (SI) units and symbols should be used whenever possible.
Illustrations, tables and figures must be clear and legible. Original drawings, high-quality photographs or laser prints are acceptable; poor-quality reproductions that often result from photocopying prints are not. In particular, reproductions of gels or blots must be of sufficient quality to clearly show the described results.
Preface

In Canada and the United States (U.S.), the regulation of genetically modified (GM) crops, livestock feeds and human foods, shares many similarities: both countries have a coordinated approach whereby regulatory responsibility is shared by several agencies; risk assessments are based on sound science; and each regulated product is assessed on a case-by-case basis.
At the heart of the risk assessment process is the principle that GM foods or plants can be compared with traditional counterparts that have an established history of safe use, and that this comparison can be based on an examination of the same types of risk factors for both (
e.g., toxins, potential allergens, weediness, pest potential, etc). The objective is to determine if the novel plant or food presents any new or greater risks in comparison with its traditional counterpart, or whether it can be used interchangeably with its traditional counterpart without affecting the health or nutritional status of consumers, or the environment is which it is grown. The goal is not to establish an absolute level of safety, but rather the relative safety of the new product such that there is a reasonable certainty that no harm will result from intended uses under the anticipated conditions of production, processing and consumption. For example, a transgenic insect- and/or virus-resistant potato is first and foremost a potato, and the goal is to evaluate what, if any, additional risks to human health or impacts on the agro-ecosystem may result from the incorporation of these new traits. This comparative principle, whereby the plant or food being assessed is compared with one that has an accepted level of safety, is often expressed in the concept of "substantial equivalence".
The objective of this module is to provide basic information on the regulatory approaches taken by both Canada and the U.S., the roles and responsibilities of the different regulatory agencies, and access to specific regulatory guidelines and policy documents.
Decision Support Toolbox for Biosafety Implementation
This is Version 2.0 of the toolbox. Online version and updates available through ISNAR, at: www.isnar.cgiar.org/ibs/biosafety
This toolbox is designed to assist policy makers, biosafety managers and other stakeholders in understanding and applying a biosafety framework for capacity-building and regulatory decision making.
This toolbox has been developed by ISNAR and FAO, in consultation with UNEP/GEF, and is based on a conceptual framework published by ISNAR Biotechnology Service (IBS) and recommendations from a joint workshop on biosafety (May, 2002).