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Technical Opinion no. 1597/2008 - Commercial Release of Genetically Modified Corn, GA21 Corn


Technical Opinion no. 1597/2008


Proceedings:  01200.00.000062/2006-21
Applicant:  Syngenta Seeds Ltda.
CNPJ:   49.156.326/0001-00
Address: Avenida Nações Unidas, 1801, 4º Andar, 04795-900 São Paulo, SP.
Matter: Commercial release of Genetically Modified Corn.
Previous extract: 421/2006, Published on 02.21.2006.
Meeting: 116th CTNBio Regular Meeting, held on  September 18, 2008.
Decision:  GRANTED.


CTNBio, following approval of an application for Technical  Opinion related to commercial release of genetically modified glyphosate tolerant corn (GA21 Corn, Event GA21), as well as all progenies originated from the  GA21  transformation event  and its derivatives of crossing of non transgenic corn lineages and populations with lineages carrying event GA21, was favorable to the GRANTING under the terms of  this technical opinion.
Syngenta Seeds Ltda. requested a CTNBio Technical Opinion for the free registration, use, essays, tests, sowing, transportation, storage, marketing, consumption, import, release and discarding  of  glyphosate tolerant corn (Zea mays, L.). Event GA21 was produced through microprojectile bombarding with a suspension of culture cells, using plasmid pDPG434, derived from vector pSK, which is  commonly used in molecular biology and is in  turn derived from pUC19. Elements for insertion in the gene are contained  within NotI restriction fragment, containing  the  expression cassette used  to generate event GA21. GA21  corn contains the rice actin 1 gene that acts as promoter; mepsps gene (modified corn epsps gene) that codifies the mEPSPS protein  and grants tolerance to glyphosate herbicide; nos gene, responsible for transcription termination; and OTP sequences, responsible for digesting the  mEPSPS protein to  chloroplast. The genic construct used to insert the mepsps gene in corn resulted from stable insertion of a functional copy of such gene, which granted  plants tolerance to the glyphosate  herbicide. The mEPSPS enzyme amino acid sequence expressed in GA21 corn is 99.3% identical to the conventional corn endogenous enzyme sequence , which is  expressed in a concentration significantly lower than mEPSPS protein of GA21 event. Quantifiable concentration of mEPSPS protein has  been detected in most part of tissues  of plants derived from GA21. No sequence introduced  in event GA21 or of its donors  is known to be  pathogenic  to humans or  animals. EPSPS proteins are ubiquitous in  nature and are naturally present in food  derived from plant and microbial sources, included  in the everyday diet of  humans and animals. Bromatology tests and procedures for quantification of  corn kernel different nutritional components have been conducted. The analyses suggest that the level  of measured  components  have not  changed beyond corn natural variation. No consistent pattern emerged suggesting that biologically significant changes in composition or nutritive value of the kernel or forage took place following the  transformation or expression  of  the  mepsps transgene. Analysis of  amino acids  inserted in mEPSPS enzyme reveals no  homology with  toxic proteins  for mammals  and toxic potential for humans is not expected. Absence of toxicity was also verified  in studies with animals using  high doses of purified protein. The mEPSPS  enzyme expressed in corn with the GA21 event has no typical  characteristics of known  allergens. There is no homology regions when the introduced sequence is  compared with sequences of known allergens. The data  submitted indicate an extremely low likelihood that the intact protein may be absorbed through the intestine mucosa during consumption and establish immunochemical affinity to  antibodies, including  IgE antibodies, primarily responsible for  allergic reactions. In addition, mEPSPS enzyme is promptly degraded by acid and enzymatic hydrolysis when exposed to fluids similar to gastric and intestinal fluids. According to data on nutritional and compositional equivalence of GA21 corn with its conventional isogenic version, no GA21 corn metabolite has potential to concentrate in the food chain, in addition to what may be expected from the widely cultivated conventional corn. In Brazil, there are no kindred species of corn distributed in nature. However, genic flow for local open pollination varieties is possible, however this flow is as risky as the one caused by commercial genotypes available in the market. Coexistence of cultivars is possible between conventional corn (improved or local varieties) and transgenic from the agronomic viewpoint. The likelihood of a transgenic plant changing into a weed, as well as  of originating a weed by  crossing  GA21 corn with  other  corn plants is negligible,  due to the biologic characteristics of the species and the  fact that  corn does not survive well without human intervention. Therefore, it is expected that GA21 corn has an environmental behavior similar to that of common  corn. The likelihood that a mepsps gene of a transgenic plant migrates to other organisms is practically inexistent.  The epsps gene is common to plants, fungi and microorganisms,  is abundant in nature, and is not a significant risk for soil  microbiota. Besides, there is evidence that plant genes have sometimes been transferred to  bacteria in natural conditions. Glyphosate is registered with the Ministry of Agriculture and Supply – MAPA, Ministry of Environment – MMA and a monograph on glyphosate  is approved by the National Sanitary Surveillance Agency – ANVISA.  The use of the glyphosate herbicide in GA21 crops shall  comply with applicable rules, such as  Law no. 7,802, of July 11, 1989 (Agricultural  Defensives Act). CTNBio reached a conclusion that cultivation and consumption of GA21 corn are not potential causes of significant degradation to the environment and do not risk human and animal health. For these reasons, there are not restrictions to  the use of this corn and derivatives, except in locations mentioned by Law no. 11,460, of March 21, 2007. Coexistence between cultivars of conventional corn (improved or local varieties)  and transgenic corn  is possible from the agronomic viewpoint and shall  comply with the provisions of CTNBio Ruling Resolution no. 4. The applicant shall conduct a post-commercial release monitoring plan under CTNBio Ruling Resolution no. 3 and shall have a term of thirty (30) days from the date of publication of this Technical Opinion to adequate its proposed  post-commercial release monitoring plan, according  to Annex 1  of CTNBio Ruling Resolution no. 5, of March  12, 2008. Under Article 14 of Law no. 11,105/2005, CTNBio holds that the request complies with applicable rules and legislation aimed at securing the biosafety of the environment, agriculture and human and animal health.
 CTNBio TECHNICAL OPINION
I. GMO Identification
GMO name:    GA21  corn, Event GA21.
Applicant:   Syngenta  Seeds  Ltda.
Species:   Zea mays – Corn
Inserted characteristics:  Tolerance to glyphosate herbicide
Method of insertion:  Particle bombarding (biobalistics)
Prospective use:  Production of fodder and kernels for  human and animal consumption of  the GMO and its derivatives.  
II. General  Information
Zea mays L., corn, is a species of the Maydae tribe, included in subfamily Panicoidae, family Graminea (Poacea). Genera belonging to the Maydae tribe  include Zea and Tripsacum in the Western Hemisphere.  Corn is a separate species within the Zea subgenus, with a chromosome number 2n = 20,21,22,24(16).
Corn is a cereal essentially of American origin, the continent where its closest wild relatives, teosinte and Tripsacum(31), may be  found. One assumes that the specific region of corn birth is Mexico and that it originates from teosinte, Z. mays Mexicana (Schrader) Itis, over eight thousand years ago. Teosinte may be found in Mexico and some locations of Central America, where it may cross with cultivated corn in production fields. Cultivated corn may also cross with a most distant genus, the Tripsacum. This crossing seldom happens and results in a male-sterile progeny.
Maize is an annual plant, high and robust. It is one of the most efficient plants in converting solar energy into food and  is the raw-material of several products, being one of the most important food sources in the world. Over the past eight hundred years, cultivated corn gained several valuable agronomic characteristics, at the cost of losing the ability to survive in nature.
Out of all cultivated plants, corn is probably the one possessing the largest genetic variability.  Today, about three hundred races of corn are identified and, within each such race, there are thousands of cultivars. Corn is currently the cultivated species that reached the highest degree of domestication and it may only survive in nature when raised by man(6). Normally, the maintenance of this genetic variability has been achieved through individualized storage, in germplasm banks, under controlled humidity and temperature. There are several germplasm banks, in Brazil and all over the world. Embrapa, the Brazilian Agricultural Research Agency, has two germplasm banks, one at Embrapa Recursos Genéticos e Biotecnologia, Embrapa Genetic Resources and Biotechnology, in Brasília, Federal District, Brazil, and another  at Embrapa Milho e Sorgo, Embrapa Maize and Sorghum, in Sete Lagoas, Brazil. Corn is farmed in over 100 countries, with a total estimated production of 705 million tons per year.
Brazil is the world third largest corn producer, with  an output of about 35 million tons  in 2005, behind the United States of America (282 million tons) and China (139 million tons)(18). In Brazil, corn is planted basically in two different crops (summer and safrinha, or  small  crop) and cultivated in practically all the domestic territory, with 92% concentrated in the Southern Region (47% of production), Southeastern Region (21% of production) and Center Western Region (24% of production)(9).
Corn is one of the most efficient plants  in converting solar energy in food  and is used as raw material for several products. The increase  in corn consumption exceeded 100 million tons between 1993 and 2001, representing an average  yearly increase  of 11.1 million tons per  year. A large part of this increased production was due to genetic  improvement, leading to  ears containing about  1,000 seed-corns. Increased corn production and consumption all over the world is associated to its multiple uses, population growth,  changes in feeding habits, and growth in the number of farmed swine and  poultry.
Weeds are among the main corn culture problems in Brazil. There are some alternatives for controlling weed and treatment with herbicides is the most used method. Brazil is the world’s third largest consumer of pesticides. The country has currently over 140  pesticides  registered for corn and the use of agricultural  defensives is one of the important factors affecting farmers’ health in Brazil, where it is responsible for intoxication of one million individuals each year(2). In this environment,  the use of corn cultivars containing event GA21 would be one  extra alternative to turn.
Development of GA21 represents one option to control weeds that compete negatively  with corn production. GA21 was obtained by transforming a culture of corn lineage through microprojetile bombardment (biobalistics) and expressed as a corn 5-Enolpiruvylshikimate-3-Phosphate double mutated synthase protein (mEPSPS), which grants tolerance to glyphosate herbicide. GA21 corn is already commercial  released for cultivation in Argentina (1998), Canada (1998), Japan (1998) and USA (1997). It is used in human and animal  food in Australia (2000), Canada (1998), European Union (2005), Japan (1999), Korea (since 2002), China (2004), Argentine (2005), Mexico (2002), Philippines (2003), South Africa (2002), Taiwan (2003) and USA (1996) (1).
III. Description of the  GMO and Proteins  Expressed
Corn plants of event GA21 express the mutated double corn 5-Enolpyryvilshikimate-3-phosphate synthase protein (mEPSPS). The enzyme belongs to the shikimic acid metabolic pathway, involved in the biosynthesis of aromatic amino acids (phenylanine, tryptophan and tyrosine), present in plants, fungi and bacteria, yet absent in animals (Figure 1).
 
Figure 1 – Shikimic acid pathway
Event GA21 was produced through microprojectile bombardment of a suspension   of culture cells(23), using plasmid pDPG434, derived from vector pSK, which is commonly used in molecular biology and is derived from pUC19. Elements for the insertion of the gene of interest are within the restriction fragment NotI, containing the expression cassette used  for generating event  GA21:
(a) Actin 1: Region 5’ of rice (Oryza sativa)  actin 1 gene containing  the promoter, the first exon and intron(27);
(b) OTP: N-terminal sequences of chloroplast transit peptide (CTP)  based on CTP sequences of sunflower Helianthus annus)  and corn (Z. mays), present to drive  the mEPSPS protein to the chloroplast(24);
(c) mepsps: sequence coding the corn (Z. mays) mEPSPS modified protein, granting tolerance to glyphosate(25);
(d) nos: region 3’ not translated of T-DNA Agrobacterium tumefaciens nopaline synthase gene, which terminates transcription and guides mRNA polyadenylation(10).
The epsps genes are ubiquitous in nature. Mutant gene epsps (mepsps) results from two changes in corn epsps gene and were introduced to alter two specific  amino acids of the wild epsps protein. The mutations are in the location of the 102 (from threonine to isoleucine) and 106 (from proline to  serine) amino  acids. Transformed corn plants with gene mepsps synthesize  the mEPSPS protein that grants  tolerance to herbicide  products containing glyphosate.
The result of  the Chi-Square Test (X2>3.84 for all generations) accepts  the hypothesis that the glyphosate tolerance characteristics behaves in a Mendelian way and segregates  at rate of 1:1. The number of transgenic loci in the insertion of event GA21  was examined by Southern blot, using digestion with  EcoRV and hybridization with two probes  generated by  PCR that represent the  functional elements contained in the NotI transformation segment of  pDPG434. The analysis showed that  the whole of the GA21 insertion is in one single locus and is  contained in a hybridization band of 20.5 kb. Southern blot hybridization analysis data on three  generations of event GA21 showed that the insertion of the  event is inherited in a stable way in all generations of plants derived from the event.
The amino acid sequence of mEPSPS enzyme  expressed in  GA21 Corn is 99.3% identical to the sequence of the conventional corn endogenous enzyme. The EPSPS endogenous protein is expressed in a significantly lower concentration than the GA21 mEPSPS protein. Quantifiable concentrations of the mEPSPS protein were found in most tissues of plants derived from event GA21. In all growth phases of event GA21 hybrids, average concentrations of mEPSPS measured in leaves ranged from about 0.2 ƒÝg/g of fresh weight to 15 ƒÝg/g of fresh weight (<0.3 to 7.0 ƒÝg/g of  dry weight); in roots, average concentrations ranged  from about 2 ƒÝg/g to 15 ƒÝg/g of fresh weight (<14 to 44 ƒÝg/g of  dry weight); and in the whole plant, ranged from about 3 ƒÝg/g to 15 ƒÝg/g of fresh weight (8 to 68 ƒÝg/g of  dry weight). Average concentrations measured in kernels in  seed maturity  and senescence  ranged  from about 4  to 7 ƒÝg/g of fresh weight (5 to 10 ƒÝg/g of  dry weight). Concentration of the mEPSPS protein  overnight in the air exhibited  an average of about  16 ƒÝg/g  of fresh  weight on the two GA21 event hybrids. mEPSPS concentrations in  corn chips and corn oil samples were below detection limits.
IV. Aspects Related to Human and Animal Health
The arrangement proposed to estimate risk in whole food, either conventional or genetically modified,  is different from the one classically conducted for well chemically characterized products, with a defined  purity, with  no relevant nutritional value and to which humans are exposed in low doses, as food additives, drugs, cosmetics and  chemical substances of industrial use. Whole foods, however, are complex chemical mixtures, each of them subject to changes  along time in its  composition and nutritional value, which limits their use in toxicological essays with experimentation animals, as they are validated. The difficulty in  performing traditional toxicological tests with whole foods, including GMO, led to an alternative proposal for assessing its food  safety based on comparative  analysis  between  a  certain product and its  similar, with an acceptable record of safe  consumption. The idea behind this approach coincides with the concept of substantial equivalence, considered the  most practical way of treating safety in foods and food components produced by biotechnology. This approach, formulated by FAO/WHO during  the  1990s, was used by reference institutions, such as OECD(30), Codex Alimentarius(17), the North-American FDA(43), the European Food Safety Agency(12),  and the American Society of Toxicology(33).
In the substantial  equivalence approach, an GMO is compared  to its closest natural similar to identify intentional and non-intentional differences, taking into consideration: identity, source, transformation process, composition, effects of processing, characteristics of recombinant DNA (stability of insert; potential genic  transfer); toxic, allergenic and other potential effects of the  protein  expressed by the transfene; and  possible side effects of the new  gene expression (interruption of metabolic pathways,  interference with macro- and micronutrients). Validation of substantial equivalence is  an important phase, yet  it shall not be misinterpreted as assessment of food risk itself. In case  there are any likelihood or risk, be  it toxic or nutritional, the assessment shall proceed to attempt and establish its nature and severity, including the possible conduction of  in vivo toxicological tests. The requirement  of such tests for assessing the safety of the GMO or its derivatives shall be decided on a case-by-case basis. Especially in the case of new proteins, tests shall be performed  when:
(1) there  is  no detailed record of previous safe consumption of the GMO and its products, by humans or by animals raised for food;
(2) available information on its safety is perceived as insufficient;
(3) its biochemical and functional  characterization was deemed insufficient: molecular weight, amino acid sequence, homology with proteins that  cause adverse effects, subsidiary enzymes, stability during processing  and storage, resistance to digestion, products from breaking, among others;
(4) there  is a possible interference of the new  protein with metabolic and functional pathways or  relevant structures;
(5) there is the possibility that the transgenicity may trigger unexpected genetic changes in the  transgenic plant (silencing or  overexpression of endogenous genes);
(6) the substantial  equivalence analysis  indicates dissimilarity  with the original product with which the GMO was compared.
Naturally, toxicity essays of the GMO with experimentation animals (repeated exposure, 28 or 90 days), implies appropriate strategies  to harmonize the offer of test-materials to animals (form of presentation, dose levels, etc.). When the transgenic product is a modified protein, it may be isolated from the  GMO  itself or synthesized  by microorganisms and offered to test-animals in  this  isolated form. In this latter case, the isolated protein shall keep biochemical and functional correspondence with the protein of  the transgenic product. In very special situations, the test may be conducted with  the whole food that, in this case shall be supplied in the same form and at least in the amount consumed by  humans.
Safety assessment of foods derived from genetically modified raw materials is based on risk analysis, a scientific methodology comprising the phases of assessment, risk management and risk communication. In the risk assessment phase, a quantitative and qualitative characterization is  pursued of potential adverse effects, guided by the substantial equivalence  standard, in order to identify any differences between the new food and its corresponding conventional food.
In order to assess safety of a  genetically modified alimentary raw material or its equivalence  to the conventional food, it is recommended that four mail elements are analyzed in some depth:
(1) parental variety, that is to  say, the plant that  originated the new genetically modified raw material;
(2) transformation process, including full  description of  the construct used and  resulting event;
(3)  product of  the  inserted gene and potential  toxicity and allergenicity; and
(4) composition of  the new variety resulting  from genetic  transformation.
The set of data of such analyses shall enable an identification and description of potential adverse effects associated to consumption of the new raw material, to be used as basis for the phases of risk management and communication.
Z. mays is a well characterized species, with a solid  record  of safety for human consumption. In the proceedings, information comprising origin,  domestication, taxonomy, reproduction and changes in its composition are  mentioned(45), reflecting the high degree of  knowledge about this species. Corn is used basically as a  component of food by peoples through the whole  world, and is one of  the  most important grains used in the production of animal food for  being  one of  the most concentrated  forms of  energy, containing more energy able  to  be metabolized – or digestive nutrients – than any other  grain. Corn plants and kernels are not considered toxic for  humans, domestic animals or wild species. The cereal is at the base of nutrition for large groups  of people in Latin America, Asia and Africa. In the United States and Japan,  corn is generally used as food for animals. Corn is palatable, readily digested by humans and  monogastric  and ruminant animals and has a safe record of use as a human and animal food.
GA21 corn was obtained by bombarding  the plant material  with  particles  covered  with the genetic material of interest. Since this is a physical process of transference of DNA molecules, without intermediation of any biological  agent and is  performed  in aseptic  conditions,  the likelihood that DNA molecules that are not in the genic construct present in the particles are transferred to the plant cells is practically negligible. No sequence induced in GA21 event or its donors are known as pathogenic for  humans. EPSPS proteins are ubiquitous in nature and are naturally present in  food derived from plant and microbial sources present  in the normal diet of humans and animals(5, 13, 20).
Chemical composition analysis of the variety obtained  by genetic modification, mainly at the levels of its nutrients  and any toxic components  that may be present, aims at securing that this new variety is as safe  and nutritive as its conventional equivalent. Therefore, the analysis verifies that  the intentional  effects of the modification did not affect negatively its security nor resulted in unintended  effects. Presence and levels of natural constituents in  human animal food were analyzed and compared with genetically unchanged contour lines and data from the literature(22). Bromatologic analyses and  quantification of different nutritional components of  corn kernels, such as  carbohydrates, proteins, humidity, fat, ashes, starch, fibers, minerals, vitamins, amino acids, fatty acids, secondary metabolites and anti-nutrients(35).  The analyses suggested that the measured levels of components have not changed more than the  natural  variation found in corn.  No consistent pattern emerged that suggested significant  biological  changes in composition  or  nutritional value of the kernel or forage took place as a result of the  transformation or expression of the mepsps transgene. The data corroborate the studies of Grant and his collaborators(19) who  concluded that the use of  corn for silage or kernel does  not change the nutritional value of  the food. Erickson  et al.(14) verified the lack of change in nutritional value in cattle feeding. Similarly, studies carried out with birds in specific GMO diets did not reveal changes(42).
As mentioned above, the mEPSPS enzyme amino acid sequence expressed in GA21 corn is  identical to the conventional corn endogenous sequence. Analysis of amino acids inserted in mEPSPS enzyme fails to display homology with proteins toxic for mammas and it is  not deemed to  have any potential toxic for humans. Absence of toxicity was also  verified in studies  with animals  using high doses of purified protein.
 Studies lasting 90 days in rodents did not indicate any change in the animals with doses up to 400mg/kg  of CP4 EPSPS derived from Eschericha Coli. The protein is degraded in less than 15 seconds in the presence of pepsin and in 10 minutes  in the presence of trypsin.  Susceptibility of the mEPSPS  protein to proteolytic degradation was assessed in simulated mammal gastric fluid containing pepsin. Protein mEPSPS  obtained from E. coli and  corn was rapidly degraded, and was not detected intact in a sample of reaction mixture in the  first  sampling interval (one minute). No immune-reactive  fragment  of mEPSPS could be detected after incubation for five minutes in mammal simulated gastric fluid(37). These data corroborate  the EFSA(11) understanding, maintaining that there are no toxicity or allergenicity changes foreseeable by bioinformatics in studies  of in vitro digestibility and in in vivo  experimental studies.
Toxicity of mEPSPS protein (83%p.p. pure)  was assessed by forced oral intake in a single dose of  2,000mg/kg  of body weight to CD-1 mice of  both sexes. The dose was selected  for it represents the borderline dose for  this  type of study. After fifteen days, the animals were  sacrificed and  submitted to full necropsy. There was no evidence  of effects on food ingestion, body weight and weight gain, hematologic profile and histology of all organs that might be associated to exposure  to GA21 corn. Some alterations recorded  in serum biochemical tests were deemed inconsistent and not associated to exposure to transgenic corn(39).
In another study, ALpk:APf SD male and female rats received GA21 corn in concentrations  of 10% or 45% in their food. Selection of corn offer levels  was made assuming that the lowest concentration (10%) represents a level “at least equivalent to the human chronic dietary  intake of corn (3mg/kg/day”. The highest level (41.5%) was selected as “the highest attainable level without causing nutritional imbalance to animals.”(40). The control used was a corn negative for event GA21, supplied in the same concentrations. Experimental food  was offered for ninety days,  and at the end the animals were  sacrificed and submitted to full necropsy. There was no evidence of effects in weight and body gain, food  consumption, clinical condition and functional performance during the study, hematologic profile,  organ weight and histology, as well  as no records of changes to ophthalmoscopy and serum biochemistry of animals exposed  to  GA21  corn(40). In this context of  GA21 toxic effect absence in both studies, it is important to emphasize  that there was no record of homology in the amino acid sequence of corn 5-Enolpiruvylshikimate-3-Phosphate double mutated synthase  protein (mEPSPS) with any other proteins already identified as toxic(36). The result corroborates the European Food Safety Authority (EFSA) conclusions(13) that the results of the studies fail to  indicate occurrence of adverse  effects in GA21 corn consumption.
The mEPSPS enzyme expressed in event GA21 corn does not have  the typical  features of  known allergenic substances, since the behavior of allergenic proteins in the digestive tract is well described(4, 7, 21). There are no homology regions when the introduced sequence is compared with sequences of known allergens. Besides, many food allergens  are known for  being stable when submitted to heat. Data collected evidenced that incubation for thirty days at 65ºC or 95ºC deactivated the mEPSPS  specific enzymatic activity(38), indicating a extremely low likelihood that the whole  protein might be absorbed through the bowel mucosa during consumption and establish immunochemical affinity for antibodies, including IgE antibodies, primarily responsible for allergic reactions(34). In addition, available data in the  literature(44) indicate normal digestibility  for transgenic corn varieties released for human consumption. Indeed, the mEPSPS enzyme is rapidly degraded by acid and enzymatic hydrolysis when exposed to fluids  that are  similar to gastric or intestinal fluids.
For the foregoing, the likelihood of mEPSPS protein to interfere in metabolic or functional pathways or in relevant structures is negligible, in view of the plant morphology, its agronomic performance, biochemical composition, nutritive content and digestibility. Therefore, it is not foreseen that transgenic modification  could cause unexpected genetic changes in the plant (silencing or overexpression of endogenous genes) and, in case such changes do occur, they will not  imply adverse effects.
According to data on GA21 corn nutritional and compositional equivalence as regards its  isogenic  conventional, no GA21 corn metabolite has  potential to concentrate in the food chain, in addition of  that already expected  for the widely cultivated conventional corn. Studies on acute oral toxicity in mice conducted with mEPSPS protein indicated that the mEPSPS protein failed to have any acute toxic effect  on the animals at the highest tested dose. No mortality associated to the test substance took place during the study  and no  clinic signal attributable to  the test substance was observed(39).
Besides, GA21 corn was already released for human and animal consumption in the United States, Japan, Canada, Argentina, Mexico, South Africa, Australia, New Zealand, Philippines, Thailand  and China, and in some of  these countries  for over  ten years, displaying a safe history of consumption without adverse effects scientifically proven(1).
For the foregoing, one reaches a conclusion that there  are not indications that consumption of GA21 corn or products derived from this event pose any risk to life  and health  of animals or humans, being as safe as the conventional corns commercialized in Brazil, and that the likelihood that it may harm human and animal health is negligible.
V. Environmental aspects
Corn is a monoic plant: a single individual  contains male and female flowers located separately. Corn plants  are crossed fecundation plants and largely pollinated with the help of wind, insects, gravity and others. The introduction of genic elements described above failed to change the reproductive characteristics of the plant. Therefore, the same likelihood of crossed fecundation existing between hybrids and lineages of conventional corn – non-genetically modified – will occur between  event GA21 and other corn plants.
Genic flow of corn may occur through  transfer of  pollen and dispersion of  seeds. Dispersion of seeds is easily controlled, since domestication of corn eliminated the ancestor mechanisms  of seed dispersion and pollen movement is the  only effective means for genes  escaping from corn plants. Corn is an annual and allogamous plant, predominantly pollinated by wind, and distances covered by pollen depend on the wind  pattern, humidity and temperature. Corn pollen  disperses  freely near the area cultivated  with this  grass, and may reach the stigmas of the same or  different genotypes and, under adequate conditions, starts its germination, originating the pollen tube that promotes fecundation of the ovule within an average period of 24 hours. Studies on corn pollen dispersion have been conducted, and some of them show that corn pollen may travel long distances. However, most of the pollen released is deposited near the culture, with a very low translocation rate to  outside the source culture: over 95% of the pollen reaches distances within 60m from its source(32). The predominant pollinating agent  in corn is the wind, and the distance that  viable pollen may cover  depends on  wind patterns, humidity and temperature. Luna et. al.(26) assessed the isolation distance and  control of pollen, and  showed  that crossed  pollination took place within a maximum distance  of 200 m and that no  crossed pollination occurred  in distances exceeding 300 m from the pollen sources, in conditions of  absence of detasseling. The results indicate that pollen viability is maintained for two hours and that crossed pollination was not observed  in distances exceeding 300m from the  pollen source.
Comparing concentrations at 1 m from the source culture with winds  ranging from low to moderate, one estimates that about 2% of pollen are  recorded at 60m, 1.1% at 200m and 0.75-0.5% at 500m from the source. Ten meters away from a field, the average number of  pollen grains by unit of area is ten times less that the figure recorded at 1m from the border. Therefore, if the established distances of separation developed for corn seed production are  observed, one expects that the transfer of pollen to  adjacent varieties is  minimized, being unlikely the presence of glyphosate tolerant genetic material.
In Brazil there are not kindred corn species in natural distribution. However, the genic flow  to local varieties of open pollination is possible, but poses the same risk as commercial  genotypes available in the market. In the specific  case of crossing between GA21 corn and local (creole) varieties there is no expected selective pressure from management by small farmers: the transgene shall not be incorporated  to  the genome of  creole varieties because, in practice, the  small farmer  does not use herbicides.
From the agronomic viewpoint, coexistence between conventional (improved or creole) corn and transgenic(8,28) cultivars is possible. Old communities  and modern farmers have been able to easily live together with different corn cultivars, while keeping their genetic identities across time.
The likelihood of a transgenic plant to change into a weed species,  as well as the likelihood of a GA21 corn crossing with other corn plants and originate a weed  is  negligible, in view of the biologic characteristics of the species and the fact that  corn does not survive  well without human intervention, a result of a selection made along the plant evolution.  Corn is the species reaching the highest degree of  domestication among cultivated plants and lost its natural surviving characteristics as, for instance, the elimination of shucking. Therefore, corn is a plant unable to survive in natural conditions, without technical  assistance. In this context, one expects the GA21 corn to display an environmental behavior similar to ordinary  corn being therefore negligible the likelihood of changing into  an invading plant or weed.
The likelihood of the transgenic  plant mepsps gene  to pass to other organisms as, for instance, soil microorganisms is practically null(29,41). The epsps gene is common to plants, fungi  and microorganisms, its occurrence is abundant in nature, and  does not result in  significant  risk to the soil microbiota.  In addition, there are is no evidence that plant genes have ever been transferred to  bacteria under natural conditions.
Glyphosate is an organic compound that does not affect the nervous system and is highly efficient in eliminating weeds, besides being held as little toxic (toxicological  class IV). It is a large spectrum, non selective, herbicide that kills plants by inhibiting the 5-Enol-pyruvylshikimate-3-phosphate (EPSPS) synthase enzyme, important in the biosynthesis of aromatic amino acids. Glyphosate is registered  with the  Brazilian Ministry of Agriculture and Supply (MAPA), Ministry of the Environment (MMA) and has a monograph approved by the National Sanitary Surveillance Agency (ANVISA)(3). Use of the glyphosate herbicide  in crops of GA21 corn shall observe  the applicable rules as, for instance, Law no. 7,802, of July 11, 1989 (Pesticide Act).
VI. Restrictions on the use of the GMO and its derivatives
As established by Article 11  of Law no. 11,460, of March 21, 2007 “research and cultivation of genetically modified organisms may not be conducted in indigenous lands and areas of  conservation units.”
Studies submitted by applicant demonstrated that there is no significant difference  between hybrids of corn derived from unmodified  lineages and GA21 corn  regarding agronomic characteristics, reproduction methods, dissemination and ability to survive. All evidence submitted in the proceedings and bibliographic references confirm the transgenic variety level  of risk  as equivalent to  non transgenic  ones regarding  soil microflora, as well as other  plants and human and animal health. Therefore, cultivation and consumption  of  GA21 corn are not potentially a source of  significant degradation to the environment or of  risks to human and animal health. For the above reasons, there is no restrictions to the use of such corn or its derivatives, except in places as mentioned by Law no. 11,460, of March 21, 2007.
Vertical genic flow for local varieties (the so called creole corn) of open pollination is possible and poses the same risk caused by commercial genotypes available in the market (80% of conventional corn cultivated in Brazil comes from commercial seeds that have been genetically improved). Coexistence  of  conventional corn cultivars (either  improved or creole) and transgenic corn cultivars is possible  from the agronomic viewpoint(8,28) and shall comply with the provisions of CTNBio Regulating Resolution no. 4.
After ten years of use in different countries, no  problem has been detected for human or animal health or the environment that may be attributable  to transgenic corns.  It shall be emphasized that the lack of negative effects  in cultivating transgenic corn plants is not a guaranty that such effects cannot occur. Zero risk and absolute safety do not exist in the biology world and, although there is a host  of trustworthy scientific information and a safe history of use of ten years that enable us to affirm that  GA21 corn is as safe as the conventional versions. Therefore, applicant shall conduct  post-commercial release monitoring according to CTNBio Regulating Resolution no. 3.
VII. Consideration on the particulars of different regions of the Country (Information to supervisory agencies)
In Brazil, there are no kindred species of corn in natural distribution.
VIII. Conclusion
Considering that the corn (Zea mays) GA21 belongs to  a  well characterized  species with a solid background of safety for human consumption and that the mepsps  gene introduced in this  variety codifies a protein that is ubiquitous in nature, present in plants, fungi and microorganisms participating in the alimentary diet of humans and animals.
Considering that the genic construct used to insert the gene in corn resulted from the stable  insertion of  a functional copy of mepsps, which granted tolerance to the  glyphosate herbicide.
Considering that centesimal composition data failed to  identify significant differences between the genetically modified and conventional varieties, suggesting nutritional equivalence between them.
Considering, in addition, that:
1. Corn is the species that reached  the highest domestication level among cultivated plants, and is  unable to survive  in nature with no human intervention.
2. In Brazil, there are no wild species  with which corn may intercross, since  the closest wild corn species is teosinte, found only in Mexico and in some Central America locations, where it may cross  with corn cultivated in production fields.
3. The mEPSPS protein was detected in low  levels in tissues analyzed  and displayed great susceptibility to digestion in simulated gastric fluids, lacking acute toxicity in mammals and similarity with known allergens.
4. The genetic modification introduced in GA21 event did not result in important differences  of chemical composition regarding nutrients, which are  within the normal variation range found between conventional varieties.
5 The DNA molecule is a natural  food component and there is no evidence that this molecule may have adverse effect to humans when ingested in food in acceptable amounts (no direct toxic  effect).
6. There is no evidence that  intact plant genes may be transferred and functionally integrated to the genome of human or other mammals exposed  to this DNA or to food produced with such elements(15).
7. The applicant  answered all questions stipulated by CTNBio Regulatory Instruction no. 20 and that no topic  indicated that this corn may have adverse effect in human and animal food.
8. The likelihood of a transgenic plant to change into a  weed species, as well as the crossing  of GA21 corn with other corn plants originating a pest is negligible.
9. The mEPSPS protein is common  to plants, fungi and microorganisms and  the  exposure of living organisms and the environment to this protein is an event that occurs  abundantly in nature without resulting significant risk to soil microbiota.
10. The coexistence between cultivars of conventional corn (either  cultivated or creole) and transgenic corn cultivars is possible from the agronomic viewpoint, under the provisions of CTNBio Regulatory Resolution no. 4.
11. Annex III  of the Cartagena Protocol on Biosafety (Decree  no. 5,705, of February 16, 2006) provides that risks associated to modified living organisms or to products derived therefrom, to  wit, improved materials  originated from a modified living  organism containing new detectable combinations of replicable genetic material obtained by modern biotechnology shall  be considered in the  context of  the risks posed by  the unmodified receptors in kindred organisms in the probable receiving environment.
12. The worldwide use history of this transgenic variety points out to a host  of trustworthy scientific information indicating that the variety is  as safe to the environment and human and animal heath as the hybrid corn varieties that have been used.
13.  After ten years of use  in different countries, no problem was detected to human and animal health  or  the environment that may be  attributable to transgenic corns.
For the foregoing and considering the internationally accepted  criteria in the process of analyzing the risk of genetically modified raw materials, one  may reach a conclusion that GA21  corn is as safe as its conventional equivalent.
CTNBio considers  that the activity is not potentially a cause of significant degradation to the environment or aggravation to human and animal health. Use  restrictions of the relevant GMO and its derivatives are determined by the provisions of  Law no. 11,460, of March 21, 2007, CTNBio Regulating Resolution no. 03 and CTNBio Regulating Resolution no. 04.
CTNBio analysis took into consideration opinions issued by the Commission members; ad hoc consultants; documents forwarded by applicant to  the CTNBio Executive Secretariat; results of planned releases to the environment; lectures, texts and discussions of the public hearing held on 03.23.2007. Third party independent scientific studies and publications submitted by applicant were also taken into  consideration and consulted.
Under Annex  I of Regulating Resolution no. 05, of March 12, 2008, applicant shall have a term of thirty (30) days  from publication of this Technical Opinion to adapt its proposed post commercial release monitoring plan.
IX. Mentioned bibliography
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2. ALVES FILHO, J.P. 2001. Agrotóxicos e Agenda 21: Sinais e desafios da transição para uma agricultura sustentável. In: II SINTAG Anais. II Simpósio Internacional de Tecnologia de Aplicação de Agrotóxicos: Eficiência, Economia e Preservação da Saúde Humana e do Ambiente, Jundiaí, SP, 07.17.2001 to 07.20.2001
3. ANVISA. 2008. http://wsww.anvisa.gov.br/toxicologia/monografias/g01.pdf.
4. ASTWOOD, J.; LEACH, J.N.; FUCHS, R.L. 1996. Stability of food allergens to digestion in vitro. Nat. Biotech. 14: 1269-1273.
5. AUSTRALIA NEW ZEALAND FOOD AUTHORITY. 2001. Food derived  from glyphosate-tolerant line corn GA21: a safety assessment. Technical Report Series nº 7, 25pp.
6. BAHIA FILHO, A.F.C.; GARCIA, J.C. 2000. Análise e avaliação do mercado brasileiro de sementes de milho. In: UDRY, C.V.; DUARTE, W.F. (Org.) Uma história brasileira do milho: o valor  dos recursos genéticos. Brasília: Paralelo 15, 167-172.
7. BANNON, G.A.; COCKRELL, G.; CONNAUGHTOH, C.; WEST, C.M.; HELM, R.; STANLEY, J.S.; KING, N.; RABJOHN, P.; SAMPSON, H.A.; BURKS, A.W. 2001. Engineering, characterization and  in vitro efficiency of the major peanuts allergens for use  in immunotherapy. Int. Arch. Allergy Immonol. 1241-3) 70-72.
8. BROOKES, G.; BARFOOT, P.; MELÉ, E.; MESSEGUER, J.; BÉNÉTRIX, F.; BLOC, D.; FOUEILLASAR, S.; FABIÉ, A.; POEYDOMENGE, C. 2004. Genetically modified maize: pollen movement and crop coexistence. Dorchester, UK: PG Economics, 20 pp. (www.pgeconomics.co.uk/pdf/Maizepollennov2004final.pdf)
9. CONAB. Milho total  (1ª e 2ª safra) Brasil – Série histórica de area plantada: safra 1976-1977 a 2006-2007. http://www.conab.gov.br/conabweb/download/safra/MIlhoTotalSeriehist.xls
10. DEPICKER, A.; SATCHEL, S.; DHAESE, P.; ZAMBRISKY, P.; GOODMAN, H.M. 1982. Nopaline synthase: transcript mapping and DNA sequence. J. Mol. Appl. Gen. 1: 562-573.
11. EUROPEAN FOOD SAFETY AUTHORITY – EFSA. 2003. Opinion  on the Scientific Panel on Genetically Modified Organisms on a request from the Commission related to the Notification (Reference CE/ES/00/01) for the placing on the market of herbicide-tolerant genetically modified maize NK603, for import and processing, under Part C of Directive 2001/18/EC from Monsanto. The EFSA Journal 10: 1-13.
12. EUROPEAN FOOD SAFETY AUTHORITY – EFSA. 2003. Guidance document of the scientific panel on genetically modified organisms for risk assessment of genetically modified plants and derived food and feed. The EFSA Journal 99: 1-100.
13. EUROPEAN FOOD SAFETY AUTHORITY – EFSA. 2007a. Opinion of the Scientific Panel on Genetically Modified Organisms and applications (references EFSA-GMO-UK-2005-19 and EFSA-GMO-RX-GA21) for the placing on the market of glyphosate-tolerant genetically modified maize GA21, for food and feed uses, import ant processing and for renewal of the authorization of maize GA21 as existing product, both under Regulation (EC) no. 1829/2003 from Syngenta Seeds S.A.S. on behalf of Syngenta Crop Protection AG. The 1829/2003 from Syngenta Seeds S.A.S. on behalf of Syngenta Crop Protection AB. The EFSA Journal 541: 1-25.
14. ERICKSON, G.E.; ROBBINS, N.D.; SIMON, J.J.; BERGER, L.L.; KLOPFENSTEIN, T.J.; STANISIEWSKI, E.P.; HARTNELL, G.F. 2003. Effect  of feeding glyphosate-tolerant (Round-up events GA21 or nk603) corn compared with reference hybrids on feedlot steer performance and carcass characteristics. J. Anim. Sci. 81: 2600-2608.
15. FAO/WHO – Food and Agriculture Organization of the United Nations / World Health Organization. 2000. Safety Aspects of Genetically Modified Foods of Plant Origin. Report of a Joint FAO/WHO Expert Consultation on Foods Derived from Biotechnology, 29 May – 2 June 2000. World Health Organization, WHO Headquarters, Geneva, Switzerland. 35 pp. (http://www.who.int/foodsafety/publications/biotech/en/ecjune2000en.pdf)
16. FAO/WHO – Food and Agriculture Organization of the United Nations / World Health Organization. 2000a. Grassland Index. Zea mays L. (http://www.who.org/WAICENT/faoinfo/agricult/agp/agpc/doc/gbase/data/pf000342.htm)
17. FAO/WHO – Organización de las Naciones Unidas para la Agricultura y la Alimentación / Organización Mundial de la Salud. 2004. Codex Alimentarius: Alimentos obtenidos por medios biotecnológicos. Roma: FAO, 57 pp.
18. FAO/WHO – Food and Agriculture Organization of the United Nations / World Health Organization. 2007. FAOSTAT; http://faostat.fao.org/site/34/default.aspx.
19. GRANT, R.J.; FANNING, K.C.; KLEINSCHMIT, D.; STANISIEWSKI E.P.; HARTNELL, G.F. 2003. Influence of Glyphosate-Tolerant (event nk603) and Corn Rootworm Protected  (event MON863) Corn Silage and Grain on Feed Consumption and Milk Production in Holstein Cattle. J. Dairy Sci. 86: 1707-1715.
20. HEALTH CANADA. 1999. Glyphosate Tolerant Corn, GA21: novel food information  -- food biotechnology.
http://www.hc-sc.gc.ca/fn-an/gmf0-agm/appro/ofb-099-133-1-eng-php.
21. HILEMAN,R.D.; SILVANOVICH, A.; GOODMAN, R.E.; RICE, E.A.; HOLLESCHAK, G.; ASTWOOD, J.D.; HEFLE, S.L. 2002. Bioinformatic methods for allergenicity assessment using  a comprehensive allergen database. Int. Arch. Allergy Immonol., 128, 280-291.
22. INTERNATIONAL LIFE SCIENCE INSTITUTE – ILSI. 2004. Nutritional  and safety assessment of foods and feeds nutritionally improved through biotechnology. Compr. Rev. Food Sci. Saf.3:35-104.
23. KLEIN, T.M./ WOLF, E.D.; WU, R.; SANFORD, J.C. 1987. High velocity microprojectiles for delivering nucleic acids into  living cells. Nature327: 70-73.
24.  LEBRUN, M.; LEROUX, B.; SAILLAND, A. 1996. Chimeric gene for  the transformation or plants. U.S. patent number 5,510,471.
25. LEBRUN, M.; SAILLAND, A.; FREYSSINET, G.; DEGRYSE, E. 2003. Muted 5 enolpyruvylshikimate-3-phosphate synthase, gene coding for said protein and transformed plants containing said gene. Bayer CropScience S.A. (Lyons, FR) Patent nº 6,556,587.
26. LUNA, S.V.; FIGUEROA, J.M.; BALTAZAR, M.B.; GOMEZ, L.R.; TOWNSEND, R.E.; SHOPER, J.B. 2001. Maize pollen longevity and distance isolation requirements for effective pollen control. Crop Sci. 41: 1551-1557.
27. MCLEROY, D.; ZHANG, W.; CAO, J.; WU, R. 1990. Isolation and efficient action promoter for use in rice transformation. Plant Cell2: 163-171.
28. MESSEGURE, J.; PEÑAS, G.; BALLESTER, J.; BAS, M.; SERRA, J.; SALVIA, J.; PALAUDEMÀS, M.; MELÉ, E. 2006. Pollen mediated  gene flow in maize  in real situations of coexistence. Plant Biotechnology Journal, 4: 633-645.
29. NIELSEN, K.M.; BONES, A.M.; SMALLA, K.; VAN ELSAS, J.D. 1998. Horizontal gene transfer from transgenic plants  to terrestrial bacteria – a rare event? FEMS Microbiology Reviews 22, 79-103.
30. ORGANIZATION FOR  ECONOMICAL COOPERATION AND DEVELOPMENT – OECD. 2003. Considerations for the safety assessment of animal feedstuffs derived from genetically modified  plants. Series on the Safety of  Novel Foods and Feeds, nº 9. 46 pp. Available at:
http://www.olis.oecd.org/olis/2003doc.nsf/LinkTo/NT0000426A/$FILE/JT00147696.PDF.
31. PATERNIANNI, E.; CAMPOS, M.S. 1999. Melhoramento do milho. In: BORÉM, A. (Ed.) Melhoramento  de espécies cultivadas. Viçosa: UFV, p. 429-486.
32. RAYNOR, G.; OGDEN, E.C.; HAYES, J.V. 1972. Dispersion and deposition of corn pollen from experimental sources. Agron J. 64: 420-427.
33. SOCIETY OF TOXICOLOGY. 2003. The safety of genetically modified foods  produced through biotechnology. Toxicol Sci 71: 2-8.
345. SYNGENTA SEEDS LTDA. Processo nº 01200.000062/2006-21 – Apêndice 3. Análise Western Blot  de extratos de folhas de plantas de milho derivado do evento GA21  usando seis diferentes anticorpos policlonais  anti-mEPSPS, p. 1833-1847.
35. SYNGENTA  SEEDS LTDA. Processo 01200.000063/2006-21 – Apêndice 9. Análise da composição química do grão e da forragem do milho  evento GA21  expressando a sintase do mutante duplo de milho 5-enopiruvinilshikimate-3-fosfato (mEPSPS). p. 2043-2014.
36. SYNGENTA SEEDS LTDA. Processo 01200.000062/2006-21 – Apêndice 11. Sintase 5-EnopiruvinilShikimate-3-Fosfato duplo mutante de milho (mEPSPS) expressa no milho  geneticamente modificado evento GA21: avaliação da homologia da sequência de aminoácidos com toxinas conhecidas. p. 2123-2225.
37. SYNGENTA SEEDS  LTDA. Processo 01200.000062/2006-21 – Apêndice 13. Digestibilidade in vitro da sintase 5-enolpiruvinilshikimate-3-fosfato (mEPSPS) das substâncias teste GA21-0104 e IPA21-0105 do  milho duplo mutante sob condições gástricas simuladas de mamíferos. p. 2277-2295.
38. SYNGENTA SEEDS LTDA. Processo 01200.000062/2006-21 – Apêndice 14. Efeito  da temperature na estabilidade da enzima dulo mutante de milho 5-enolpiruvinilshikimate-3-fosfato sintase (mEPSPS). p. 2296-2306.
39. SYNGENTA SEEDS LTDA. Processo 01200.000062/2006-21 – Apêndice 15. GA21-0104: Estudo de toxicidez por dose oral única em camundongo. p. 2309-2500.
40. SYNGENTA SEEDS LTDA. Processo 01200.000062/2006-21 – Apêndice 19. Grão de milho Evento GA21: Estudo de segurança de alimento integral em 90 dias em ratos. p. 2550-3917.
41. SIQUEIRA, J.O.; TRANNIN, I.C.B.; RAMALHO, M.A.P.; FONTES, E.M.G. 2004. Interferências no agrossistemas e riscos ambientais de culturas transgênicas tolerantes  a herbicidas e protegidas  contra  insetos. Cadernos de Ciência e Tecnologia 21: 11-81.
42. TAYLOR, M.; HARTNELL, G.F.; RIORDAN, S.G.; NEMETH, M.A.; KARUNANANDAA, K.; GEORGE, B.; ASTWOOD, J.D. 2003. Comparison of broiler performance when fed diets containing grain from roundup ready (NK603), yieldgard x roundoup ready (MON810  x NK603), non-transgenic control, or  commercial corn. Pout. Sci. 82: 443-453.
43. U.S. FOOD AND DRUG ADMINISTRATION – FDA. 2007. Toxicological principles for the safety assessment of food ingredients: Rek 2000.
http://www.cfsan.fda.gov/~rek/red-toca.html.
44. WATANABE, E.; MARIN, V.A.; NUTIN, M.R. 2003. Avaliação  da segurança alimentar. In: BORÉM, A.; GIUDICE, M.P.; COSTA, N.M.B. (Ed). Alimentos geneticamente modificados. Viçosa, Editora Folha de Viçosa, 302 pp.
45. WATSON, S.A.; RAMSTAD, P.E. 1987. Corn: chemistry and technology. St. Paul: American Association of Cereal Chemists, 1 ed. 604 pp.
IX. Bibliography consulted
1. ALTIERI M. A. 2005. The myth of coexistence: Why transgenic crops are not compatible with agroecologically based systems of production. Bull. Sci. Technol. & Soc. 25: 361-371.
2. ASTWOOD, J.D.; FUCHS, R.L. 2001. Status and safety of biotech crops. In BAKER, D.R.; UMETSU, N.K. (editors) Agrochemical discovery: insect, weed and fungal control. Am.Chem. Soc Symp. Series: nº 774, p. 152-164.
3. AUMAITRE A. 2000. New feeds from genetically modified plants: substantial equivalence, nutritional equivalence, digestibility, and safety for animals and the food chain. Livestock Prod. Sci. 74: 223A.
4. DONKIN, S.S.; VELEZ, J.C.; TOTTEN, A.K.; STANISIEWSKI, E.P.; HARTNELL,  G.F. 2003. Effects of feeding silage and grain from glyphosate-tolerant or insect-protected corn hybrids on feed intake, ruminal digestion and milk production in dairy cattle. J. Dairy Sci, 86: 1780-1788.
5. FOSBSCH, A.; SCHUBERT, D.; LECHTENBERG, B.; GILS, M.; SCHMIDT, R. 2003. A comprehensive characterization of  single-copy T-DNA insertions in the Arabidopsis thaliana genome. Plant  Mol. Biol. 52: 161-175.
6. GARCIA, M.A.; ALTIERI, M.A. 2005. Transgenic crops: implications for biodiversity and  sustainable agriculture. Bull. Sci. Technol & Soc. 25: 335-353.
7. GRAEF, F.; STACHOW, U.; WERNER, A.; SCHÜTE, G. 2007. Agricultural practice changes with cultivating genetically modified herbicide-tolerant oilseed rape. Agricult. Syst. 94: 111-118.
8. HARRISON, L.A.; BAILEY, M.R.; NAYLOR, M.; REAM, J.; HAMMOND, B.; NIDA, D.L.; BURNETTE, B.; NICKSON, T.E.; MITSKY, T.; TAYLOR, M.L.; FUCHS, R.L.; PADGETTE, S.R. 1996. The expressed protein in glyphosate-tolerant soybean, 5-enolpyruvylshikimate-3-phosphate synthase from Agrobacterium sp. strain CP4, is rapidly digested in vitro and  is not toxic to acutely gavaged mice. J. Nutr. 126: 728-740.
9. LADICS, G.R.; HOLSAPPLE, M.P.; ASTWOOD, J.D.; KIMBER, I.; KNIPELS, L.M.J.; HELM, R.; DONG, W. 2003. Workshop overview: approaches  to the assessment of the allergenic potential of food from genetically modified crops. Toxicol. Sci. 73: 8-16.
10. LATHAM, J.R.; WILSON, A.K.; STENBRECHER, R.A. 2006. The mutational consequences of plant transformation. J. of Biomed. Biotech. 2006: 1-7.
11. MCCLELLAN, R.O. 1999. Human health risk assessment: an historical overview and alternative paths followed. Inhal. Toxicol. 11: 477-518.
12. ORGANIZATION FOR ECONOMICAL COOPERATION AND  DEVELOPMENT – OECD. 2006. OECD Guidelines for the Testing of Chemicals. Section 4. Health effects. Joint Meeting of the Chemicals Committee and the Working Part on Chemicals, Pesticides and Biotechnology. OECD Environment, Health and Safety Publication. Organization for Economic Cooperation and  Development. http://www.oecd.org.
13. RIAZ, T.; HOR, H.L.; KRISHNAN, A.; TANG,  F.; LI, K.B. 2005. WebAllergen: a web server  for predicting allergenic proteins. Bioinf. 21: 2570-2571. http://weballergen.bii.a-star.edu.sg/
14. U.S. FOOD AND DRUG ADMINISTRATION – FDA. 2001. Toxicology testing hank: principles, applications, and data interpretation. Marcel Dekker, Inc. New York: 428 p.
15. U.S. FOOD  AND DRUG ADMINISTRATION – FDA. 2006. Recommendations for the early food safety evaluation of new- pesticidal proteins produced by new plant varieties intended for food use. Center for Food Safety and Applied Nutrition. http://www.cfsan.fda.gov/~dms/bioprgu2.html.
16. U.S. NATIONAL RESEARCH COUNCIL. 1983. Risk Assessment in the Federal Government: managing the process. Commissionon Life Science. Committee on the Institutional Means for Assessment of Risks to Public Health. National Academy Press, Washington, DC: 1-8.


Walter Colli
President of CTNBio


Dissenting Votes:
The following CTNBio members, Doctors Graziela Almeida Silva (Permanent Sector  Subcommission for Human Health), Kenny Bonfim (Permanent Sector  Subcommission for Human Health), José Maria Gusman Ferraz (Permanent Sector Subcommission for the Environment) and Leonardo Melgarejo (Permanent Sector Subcommission for the Environment) voted against the commercial release of GA21  corn.
Doctor Paulo Yoshio Kageyama (Permanent Sector Subcommission for the Environment), author of the technical opinion, issued an opinion against  the product based on:
1. The genetic and molecular characterization of GA21 was either insufficient  or  inadequate: new tests and data would  be necessary.
2. Allergenicity tests, as well as the nutritional analysis of  GA21  corn, were insufficient.
3. Comparison studies of GA21  with isogenic maize are necessary to assess aspects of plant survival, flowering, pollen grain morphology, genetic compatibility and pollinating  rate.
4. Studies of horizontal transfer  of gene mepsps gene are necessary for adventitious plants and rhizosphere bacteria.
5. Studies shall be conducted on  the impacts  of GA21-herbicide corn technology on non-target  organisms.
6. Studies on environmental impact are necessary including data  on reaction of  fauna communities  to GA21 corn culture  on different Brazilian ecosystems and with the use of  glyphosate-based  herbicides.
7. Studies are necessary to identify the  succession effects of glyphosate-resistant corn-soybeans  in the same area of studies and on the possibility of developing plants  that are resistant to glyphosate-based  herbicide.
8. Applicant shall submit  more scientifically reliable results  in what regards the 24  experiments enclosed, with a discussion on the  uncertainties identified.
Doctor Leonardo Melgarejo (Permanent Sector Subcommission for the Environment), author of the technical opinion, issued an opinion against  the product based on:
1. There are important risks associated to evidences  of likely genome  disorders associated to  lack of  precision in the biobalistic method and sustained  by international scientific literature.
2. The genetic stability of the transgene  through several generations is  not sufficiently demonstrated.
3. Absence of harmful effects for health derived  from GA21 corn  is  not sufficiently demonstrated.
4. No satisfactory answers to issues  1, 3, 6 and 7 of  Annex II of CTNBio Regulating Resolution no. 5 were made available.
5. The maintenance of nutritional and biologic features of corn  after insertion of the transgene  is  not consistently demonstrated, and  the possible interactive effects between Brazilian environment – plant metabolism were discarded.
6. Studies related to agronomic efficacy were contradictory and equivocated, aggravated  by lack of data obtained during planned releases authorized  by CTNBio.
7. There is large risk potential to which family farmers are submitted given the unavoidable contamination of their crops by a transgene whose stability and innocuousness are not yet established.
8. There is a large and growing potential for an expansion of tolerant and resistant plants, with impacts on the increasing use of the chemical product harmful to the environment.
9. Environmental impacts were not correctly assessed  and make room for concerns related to corn culture sustainability, mainly in the part under  the control of family farmers.
10. Environmental impacts were assessed without regard to direct and indirect impacts  of the new technology on its  whole over the non-target fauna and flora, water  and  soil, as  well as on the systems therein established.
11. Environmental impacts were superficially assessed, with no  scientific basis and lacking adequate answers to  issues 3, 4, 7, 8, 10 and 12  of Annex IV  of CTNBio Regulating Resolution no. 05.
12. Brazil has already expressed its decision to  abide to the Precaution Principle, sanctioned by the Cartagena Protocol, effective as of  January 22, 2004, as well as the Article  1 of Law no. 11,105/2005.


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