Response to Professor Anthony Trewavas & Martin Livermore

Trevewas and Livermore clearly take the view that the loss of autonomy for poorer farmers associated with purchasing patented GM seeds is justified by a number of claimed benefits. 

However, in practice, GM farming is in crisis as resistant weeds have become widespread in response to the use of glyphosate-resistant GM crops and secondary and resistant pests are causing increasing difficulties for farmers growing insect-resistant GM crops.

Despite decades of investment and research, other products have not been delivered or have failed to reach the market place, due to poor performance and technical difficulties.

GM farming in the United States has not out-performed non-GM farming in Europe (Heinemann et al. 2013, Hilbeck et al. 2013). In the US, yields are falling behind and are more variable, pesticide use is higher, the number of farms is decreasing and there is greater monopoly control over inputs.

The implication that US farmers grow GM through choice because it is superior is questionable as seed catalogues show that the diversity of seeds on the market in the US has reduced significantly as a result of takeovers in the industry, with many varieties only available in combination with GM traits. In addition, the capacity to innovate on farm has reduced significantly. 

Although Trevewas and Livermore describe GM as a “cutting edge technology”, conventional breeding, in some cases enhanced by new technologies such as market assisted selection (MAS), has in fact delivered more crop improvements much faster and more cheaply, despite a significant diversion of resources away from conventional breeding towards GM research (Goodman, 2002; Knight, 2003; Jiang, 2013).

Organic and resource-conserving agriculture can improve farmers’ livelihoods, without creating dependency on patented GM seeds and associated chemicals (Bennett & Franzel, 2013).

However, research investment in these areas is relatively limited. Over-optimism about what GM can deliver has led to significant opportunity costs as other areas of research have been neglected.

The authors describe glyphosate, which is blanket sprayed on the market-leading GM crops which are tolerant to glyphosate, as “innocuous to human health” and “environmentally benign”.

This claim is not consistent with evidence in the scientific literature which suggests a number of mechanisms through which glyphosate and its common commercial formulation RoundUp may damage human health (see, for example: Koller et al. 2012; Mañas et al. 2009; Paganelli et al. 2010; Romano et al. 2010; Samsel & Seneff 2013; Thongprakaisang  et al. 2013).

Glyphosate accumulates in glyphosate-resistant GM soybeans (Bøhn et al. 2013). Regarding environmental impacts, there are particular concerns about impacts on amphibians (Relyea & Jones 2009; Wagner et al. 2013). 

Disturbingly, Trevewas and Livermore downplay the negative effects on wildlife of habitat loss due to blanket spraying, including impacts on iconic species such as the Monarch butterfly.

Whilst it is clear that other factors (e.g. deforestation) play a role in the Monarch’s decline it is surprising to see the role of the expansion of GM herbicide-resistant crops dismissed when it is widely acknowledged in the literature (Brower et al. 2012).

In addition to the negative impacts of blanket spraying GM crops with glyphosate, further milkweed habitat has been lost due to the large areas of grassland and rangeland that have been converted to biofuel crops, especially GM maize.

Studies have confirmed the link between milkweed habitat loss and glyphosate-treated fields (Harzler 2010, Pleasants and Oberhauser 2013) and the negative impact on the butterflies has been modelled, providing a convincing link between the decimation of habitat and loss of fecundity (Zalucki & Lammers 2010).

Messan and Smith (2011) conclude that herbicide has a large effect and that a reduction of herbicidal spraying is needed to stabilize the monarch butterfly population.

Trevewas and Livermore fail to acknowledge the seriousness of the problem of herbicide tolerant weeds (‘superweeds’) and the harm to farmers, or the problems associated with proposed responses.

The spread of glyphosate-resistant weeds in the United States is causing severe weed management problems, with nearly half of US farms affected (Fraser 2013).

The dramatic increase in glyphosate use that caused this would not have been possible without glyphosate-resistant GM crops.

The proposed response includes new GM crops tolerant to more toxic herbicides such as 2,4-D and dicamba, which will inevitably exacerbate the environmental problems associated with blanket spraying and create a new cycle of resistant weeds  (Mortensen et al. 2012).

Trevewas and Livermore also claim that widespread resistance has not developed to the Bt toxins expressed by insect-resistant GM crops.

However, reduced efficacy of Bt crops caused by field-evolved resistance has been reported now for some populations of 5 of 13 major pest species examined, compared with resistant populations of only one pest species in 2005 (Tabashnik et al. 2013; Van den Berg et al. 2013; Jin et al. 2013).

Whilst they concede that Bt crops were never intended to give complete protection against pests, Trevewas and Livermore ignore the impact on farmers of a number of documented increases in secondary pests, which can increase significantly in numbers when targeted pests decrease (e.g. Zhao et al. 2011; Tay et al. 2013).

As a response to these problems, Trevewas and Livermore highlight research on the use of double-stranded RNA to switch off the expression of specific genes, as a new means of pest-control.

However, the use of RNA interference can give rise to unintended off-target effects and its efficacy and safety is far from being established (Heinemann et al. 2013; Lundgren et al. 2013). 

There is no scientific consensus on the safety of GM crops (ENSSER 2013) and there are limitations to all rat feeding studies conducted on both sides of the debate (Meyer & Hilbeck 2013).

There is also  evidence of commercial bias in the literature (Diels et al. 2011). Even if there were no such scientific disagreements, consumers have a right to choose to avoid GM crops for health, environmental or other reasons, such as objections to the patenting of seeds.

If consumer choice is to be maintained, the introduction of GM farming to a country or region adds the costs of segregation to the food supply chain, increasing costs across the board.

Failure to plant what consumers demand or to effectively segregate supplies means that US farmers have lost markets due to GM farming as exports elsewhere have been reduced (EuropaBio and BIO, 2012).

Whilst the industry argues that the answer is to weaken regulation, the alternative route of not planting GM food crops at all still remains open to most developing countries.

For example, India and China, despite growing GM cotton, are still rightly hesitant over planting crops such as GM brinjal (aubergine) or GM rice. Food security and trade issues are a big part of the debate, as countries seek to avoid dependency on imported GM seeds and associated chemicals.

References
Bennett M, Franzel S (2013) Can organic and resource-conserving agriculture improve livelihoods? A synthesis. International Journal of Agricultural Sustainability. 2013;11(3):193–215. 

Bøhn T, Cuhra M, Traavik T, Sanden M, Fagan J, Primicerio R (2013) Compositional differences in soybeans on the market: glyphosate accumulates in Roundup Ready GM soybeans. Food Chemistry. doi:10.1016/j.foodchem.2013.12.054.

Brower LP, Taylor OR, Williams EH, Slayback DA, Zubieta RR, Ramírez MI (2012) Decline of monarch butterflies overwintering in Mexico: is the migratory phenomenon at risk? Insect Conservation and Diversity 5(2):95–100.

Catangui MA, Berg RK (2006) Western Bean Cutworm, Striacosta albicosta (Smith) (Lepidoptera: Noctuidae), as a Potential Pest of Transgenic Cry1Ab Bacillus thuringiensis Corn Hybrids in South Dakota. Environmental Entomology 35:1439–1452.

Diels J, Cunha M, Manaia C, Sabugosa-Madeira B, Silva M (2011) Association of financial or professional conflict of interest to research outcomes on health risks or nutritional assessment studies of genetically modified products. Food Policy 36(2):197–203. doi:10.1016/j.foodpol.2010.11.016.

ENSSER (European Network of Scientists for Social and Environmental Responsibility) Statement: No scientific consensus on GMO safety. 21st October 2013. http://www.ensser.org/increasing-public-information/no-scientific-consensus-on-gmo-safety/ 

EuropaBio and BIO (2012) EU-U.S. High Level Working Group on Jobs and Growth: Response to Consultation by EuropaBio and BIO. http://ec.europa.eu/enterprise/policies/international/cooperating-governments/usa/jobs-growth/files/consultation/regulation/15-europabio-bio_en.pdf 

Fraser K (2013) Glyphosate Resistant Weeds – Intensifying. Stratus Research. 25th January 2013. http://www.stratusresearch.com/blog07.htm 

Goodman M (2002) New sources of germplasm: lines, transgenes and breeders. In: Memoria congresso nacional de fitogenetica. Saltillo, Coah., Mexico: Univ. Autonimo Agr. Antonio Narro. 28–41.

Hartzler RG (2010) Reduction in common milkweed (Asclepias syriaca) occurrence in Iowa cropland from 1999 to 2009. Crop Protection 29(12):1542–1544.

Heinemann JA, Massaro M, Coray DS, Agapito-Tenfen SZ, Wen JD (2013) Sustainability and innovation in staple crop production in the US Midwest. International Journal of Agricultural Sustainability 1–18.

Heinemann JA, Agapito-Tenfen SZ, Carman JA (2013b) A comparative evaluation of the regulation of GM crops or products containing dsRNA and suggested improvements to risk assessments. Environment International 55:43–55.

Hilbeck A, Lebrecht T, Vogel R, Heinemann JA, Binimelis R (2013) Farmer’s choice of seeds in four EU countries under different levels of GM crop adoption. Environmental Sciences Europe 25(1):12. 

Jiang G-L (2013) Plant Marker-Assisted Breeding and Conventional Breeding: Challenges and Perspectives. Advances in Crop Science and Technology. 1(3):e106.

Jin L, Wei Y, Zhang L, Yang Y, Tabashnik BE, Wu Y (2013) Dominant resistance to Bt cotton and minor cross-resistance to Bt toxin Cry2Ab in cotton bollworm from China. Evolutionary Applications. 6(8):1222–1235. 

Knight J (2003) Crop improvement: A dying breed. Nature 421(6923):568–570. doi:10.1038/421568a.

Koller VJ, Furhacker M, Nersesyan A, Misik M, Eisenbauer M, Knasmueller S (2012) Cytotoxic and DNA-damaging properties of glyphosate and Roundup in human-derived buccal epithelial cells. Arch Toxicol.  86: 805-813.

Lundgren JG, Duan JJ. RNAi-Based Insecticidal Crops: Potential Effects on Nontarget Species. BioScience. 2013;63(8):657–665.

Mañas F, Peralta L, Raviolo J, et al (2009) Genotoxicity of glyphosate assessed by the Comet assay and cytogenetic tests. Environ Toxicol Pharmacol. 28: 37?41.

Messan K, Smith K (2011) Short and Long Range Population Dynamics of the Monarch Butterfly (Danaus plexippus). Technical report of the Mathematical and Theoretical Biology Institute. http://mtbi.asu.edu/files/MTBIpaper_ButterflyGroup.pdf 

Meyer H, Hilbeck A (2013) Rat feeding studies with genetically modified maize - a comparative evaluation of applied methods and risk assessment standards. Environmental Sciences Europe 25(1):33.

Paganelli A, Gnazzo V, Acosta H, López SL, Carrasco AE (2010) Glyphosate-Based Herbicides Produce Teratogenic Effects on Vertebrates by Impairing Retinoic Acid Signaling. Chem Res Toxicol. 23(10):1586–1595.

Pleasants JM, Oberhauser KS (2013) Milkweed loss in agricultural fields because of herbicide use: effect on the monarch butterfly population. Insect Conservation and Diversity 6(2):135–144.

Relyea RA, Jones DK (2009) The toxicity of Roundup Original Max to 13 species of larval amphibians. Environ Toxicol Chem. 28(9):2004–2008.

Romano RM, Romano MA, Bernardi MM, Furtado PV, Oliveira CA (2010) Prepubertal exposure to commercial formulation of the herbicide Glyphosate alters testosterone levels and testicular morphology. Archives of Toxicology 84(4): 309-317.

Samsel A, Seneff S (2013) Glyphosate’s Suppression of Cytochrome P450 Enzymes and Amino Acid Biosynthesis by the Gut Microbiome: Pathways to Modern Diseases. Entropy 15(4):1416–1463. doi:10.3390/e15041416.

Tabashnik BE, Brévault T, Carrière Y (2013) Insect resistance to Bt crops: lessons from the first billion acres. Nat Biotech. 31(6):510–521.

Tay WT, Soria MF, Walsh T, et al. (2013) A Brave New World for an Old World Pest: Helicoverpa armigera (Lepidoptera: Noctuidae) in Brazil. PLoS One 8(11). 

Thongprakaisang S, Thiantanawat A, Rangkadilok N, Suriyo T, Satayavivad J (2013) Glyphosate induces human breast cancer cells growth via estrogen receptors. Food Chem Toxicol. 59:129–136. 

Van den Berg J, Hilbeck A, Bøhn T (2013) Pest resistance to Cry1Ab Bt maize: Field resistance, contributing factors and lessons from South Africa. Crop Protection 54:154–160. doi:10.1016/j.cropro.2013.08.010.

Wagner N, Reichenbecher W, Teichmann H, Tappeser B, Lötters S. (2013) Questions concerning the potential impact of glyphosate-based herbicides on amphibians. Environmental Toxicology and Chemistry. 32(8):1688–1700. doi:10.1002/etc.2268.

Zalucki MP, Lammers JH (2010) Dispersal and egg shortfall in Monarch butterflies: what happens when the matrix is cleaned up? Ecological Entomology 35(1):84–91. 

Zhao JH, Ho P, Azadi, H (2011) Benefits of Bt cotton counterbalanced by secondary pests? Perceptions of ecological change in China. Environ Monit Assess. 173:985–994.

 

Figures

Figure 1.

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