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Evaluating the Economic and Environmental Impacts of a Global GMO Ban

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DOI: 10.4236/jep.2016.711127    2,345 Downloads   3,907 Views   Citations

ABSTRACT

The objective of this research is to assess the global economic and greenhouse gas emission impacts of banning GMO crops. This is done by modeling two counterfac-tual scenarios and evaluating them apart and in combination using a well-know Computable General Equilibrium (CGE) model, GTAP-BIO. The first scenario models the impact of a global GMO ban. The second scenario models the impact of increased GMO penetration. The focus is on the price and welfare impacts, and land use change greenhouse gas (GHG) emissions associated with GMO technologies. Much of the prior work on the economic impacts of GMO technology has relied on a combination of partial equilibrium analysis and econometric techniques. However, CGE model-ling is a way of analyzing economy-wide impacts that take into account the linkages in the global economy. Here the goal is to contribute to the literature on the benefits of GMO technology by estimating the impacts on price, supply and welfare. Food price impacts range from an increase of 0.27% to 2.2%, depending on the region. Total welfare losses associated with loss of GMO technology total up to $9.75 bil-lion. The loss of GMO traits as an intensification technology has not only economic impacts, but also environmental ones. The full environmental analysis of GMO is not undertaken here. Rather we model the land use change owing to the loss of GMO traits and calculate the associated increase in GHG emissions. We predict a substan-tial increase in GHG emissions if GMO technology is banned.

1. Introduction

Genetically modified organism (GMO) is defined as one being produced via genetic modification as contrasted with conventional breeding [1] . GMO crops have been a lightning rod for controversy since their introduction into agriculture in the early 1990s. With the development of commercially viable genetically modified field crops (insect resistant corn and herbicide tolerant soybeans in particular), the controversy only intensified. Indeed the controversy is such that some public intellectuals including but not limited to economists, biologists, and philosophers have taken sides in the debate on GMO crops (examples are: Taleb et al. [2] , Dawkins [3] , Singer and Daar [4] ). Consumer fears about the danger of GMO crops including fears about the safety of genetically modified food for human consumption, the impact of GMO crops on the environment, and the effect of GMO crops on farms and farmers. These fears, along with some economic considerations, have led to significant regulatory obstacles to GMO crops worldwide.

That many consumers prefer non-genetically engineered varieties is not truly up for debate. What explains this preference is less clear. Part of the explanation seems to be that consumers do not just prefer non-GMO products, but actually fear the effects of genetic modification. Chiang et al. [7] report that a substantial percentage of consumers across the world believe that GMO crops are dangerous for human consumption. In a more recent study, Costa-Font and Mossialos [8] suggest that what they term dread of GMO crops is at least partially explained by lack of information. In the absence of information, consumers adopt a self-protective attitude that here is expressed as an anti-GMO attitude. This suggests that the preference for non-GMO emerges from a failure to communicate on the part of GMO advocates. In other work, Costa-Font and Gil [9] have found that meta-attitudes about science and technology can also explicate attitudes towards GMO crops.

The picture of why consumers distrust and dis-prefer GMO crops and genetically engineered food is a complex one. Whatever the explanation, consumer fear of GMO crops and preference for non-GMO varieties is a fact. This is reflected in global agricultural policy. GMO crops are heavily regulated everywhere in the world, with partial or full bans on cultivation in many European and Asian countries. In China, according to the ISAA, there is only one variety of GMO maize approved for cultivation, and no varieties of GMO soybeans. There are a larger number of varieties approved for import, though imports tainted by unapproved varieties have been a source of some contention [10] [11] . In Europe there are a variety of regulatory attitudes. In the EU in general, it is legal to import GMO crops and feed, so long as the GMO variety is one of the approved varieties. If shipments are found that include a certain percentage of an unapproved GMO variety, the shipment is refused [11] . The EU also approves a certain number of GMO crops, though the individual member states are allowed to opt- out, through a variety of regulatory mechanisms. France and Germany have outright bans on growing GMO crops of any kind. Spain and the Czech Republic, on the other hand grow approved GMO crops in significant percentages. The United States is the world’s leader in GMO crop planting and in the development of agricultural biotechnology. Indeed it is only very recently that the rest of the worlds’ GMO planted acreage overtook the United States [12] . According to the ISAA, there are currently 189 GMO varieties currently approved for cultivation in the United States (across a wide variety of crops). Regulation of GMO crops is managed by three federal agencies: The Environmental Protection Agency, the Department of Agriculture and the Food and Drug Administration [13] . Though the United States is the largest producer and user of GMO technology, there continues to be resistance and opposition to GMO crops. Most recently, legislation around GMO labeling requirements has been a locus [14] .

In what follows, we examine two distinct counterfactual scenarios. Both use the 2013 yield improvement estimates from Brookes and Barfoot’s data [15] . The first asks, “What would be different if there was no GMO technology?” The second asks, “What would be the impact if GMO adoption globally caught up to the United States?” By examining these scenarios individually as well as in combination, we can determine the economic and environmental impacts of banning GMO crops.

The first scenario is the most straightforward. It assumes that GMO penetration is exactly what it was as of 2013 in each region. This case asks what would be the economic and GHG impacts of switching from GMO to conventional, assuming that GMO crops would remain at their current level of penetration.

In the second scenario, we model the effects of increasing the penetration of GMO crops in the rest of the world to the penetration rate achieved in the US. This in turn provides a picture of the as yet unrealized potential benefits of GMO crops. While the first scenario asks “How much better off are we?”, the second asks “How much better off could we be?”

The only countries included in the second scenario are countries with GMO crops already planted. Obviously, it is possible that other countries in the future will permit GMO varieties, so our analysis represents a very conservative estimate of GMO benefits. While other countries likely would benefit from GMO crops, policy is political, not strictly economic. Thus, the estimates provided assume no complete policy changes from current policy.

2. Yield Contributions of GMO Crops

The data used for this study consists in a set of yield shocks for the three main GMO crops (soybeans, corn, and cotton) by country. These crops were chosen because they represent the vast majority of GMO acreage planted [12] . They are also the three crops with the fullest global data [15] and the greatest global economic impacts [16] [17] . The basic yield shock assumptions are drawn from Brookes and Barfoot [15] [18] review of the literature. These numbers are then combined with data on current GMO penetration in the United States and the rest of the world in order to produce estimates of realistic yield shocks by crop and country.

2.1. Derivation of Yield Shocks

The literature on yield impacts of GMO crops used in this work derives the yield improvement associated with GE traits. In order to derive shocks usable in the GTAP model, we must first derive the yield shocks for each trait. These are weighted by area, and the overall yield impact of GMO technology for the crop is determined. Finally, these weighted yield shocks are weighted according to the crop share in the GTAP crop grouping and an adjustment for regional aggregation. The derivation follows.

We define the yield of some country, Y, as the sum of the conventional yield and the GMO yield, weighted by their respective penetrations. Penetration here is understood as the proportion of the total area planted to each variety and is defined such that,

(1)

where is the penetration of conventional varieties and is the penetration of GMO varieties. The yield of the GMO varieties is defined in terms of the yield of conventional varieties and the GMO yield improvement such that,

(2)

where is the GMO yield, is the conventional yield and is the yield improvement. Thus by (1) and (2), (3) and (4) can be shown to be equivalent.

(3)

. (4)

Thus we have derived current yield in terms of conventional yield, GMO yield improvement and GMO penetration. In our first scenario, our aim is to determine the impact of switching over exclusively to conventional crops. In order to do so, we define an x such that

. (5)

That is, x is the fraction of the original yield obtained if GMO varieties are no longer available. By plugging in the identity in Equation (4), we put x in terms of yield improvement and GMO penetration.

. (6)

Equation (7) is equivalent to Equation (6), and gives the yield loss associated with switching over to exclusively conventional crops.

. (7)

Thus for instance, if the yield without any GMO crops would be 96% of current yield, then that counterfactual yield is 0.96% - 1% = −4% lower than current yield.

We consider also a scenario in which penetration of GMO crops increases. Our goal is to derive the change in yield given the change in penetration, yield improvement and the original penetration. We assume that only penetration changes-conventional and GMO yield remain as they were. The change in yield is given by Equation (8).

(8)

where is the yield after increased penetration and is the current yield, with and the respective penetrations. Equation (8) simplifies to Equation (9).

. (9)

From Equation (4) and Equation (9), we derive Equation (10).

. (10)

Thus the positive yield shock given an increase in penetration from to is as given in Equation (11).

(11)

where is the positive yield shock.

GMO crops do not always include only one trait. Indeed, in the United States, a majority of the corn (~75% [5] ) is stacked-trait. A single cultivar might include several kinds of insect resistance and herbicide resistance. There are three possibilities for interaction effects in GE traits-the trait impacts can be additive, more than additive or less than additive. The implicit assumption in Brookes and Barfoot’s work is that the traits are additive. Given the damage control framework for thinking about yield improvement [19] , additivity is a reasonable simplifying assumption. Thus the yield shock by crop for each country is simply the sum of the total yield shocks of every trait for a given crop. This is expressed in Equation (12).

(12)

where is the yield improvement associated with some trait j and is the penetration of that trait. Panels I, II, and III of Table 1 give the weighted yield shocks for corn, cotton, and soybeans by country.

These country shocks must then be converted into GTAP shocks. This happens in two steps. GTAP aggregates countries into regions and aggregates crops into categories. The first step, then, is to convert the country shocks by crop into regional shocks by

Table 1. Yield shocks for corn, cotton, and soybeans by country.

crop. This is done by weighting each country's shock by the proportion of the regions total planted area for the relevant crop. Once this has been accomplished, we can convert the regional shocks by crop into regional shocks by category. The final regional shocks for other coarse grains, soybeans, and other agriculture are reproduced in Table 2 in three panels.

2.2. Yield Impacts

The impact of GMOs on yield can be difficult to calculate. Not only are there structural and causal difficulties (which are specific to the type of study), but also year-to-year, the impact can be different. Since Bt traits increase yield through damage mitigation, pest pressure affects the difference between GMO and conventional yields. In a year with high pest pressure, the GMO crop will outperform the conventional variety much more than in a year with low pest pressure. For the same reason, there is considerable regional variation (see for instance [20] ). Studies take different approaches to identifying the yield impact due specifically to the inserted trait. Field trials, empirical results, econometric analyses and meta-analyses are the main approaches. Most studies summarize impacts at the national or global level. The yield impact assumptions in Brookes and Barfoot’s work are supported by the extant literature where available, and farmer survey data where not. We provide some context for the yield impacts given by Brookes and Barfoot.

2.2.1. Corn Yield

Corn yield impacts in the United States have been the most researched of any GMO

Table 2. Yield shocks for coarse grains, soybeans, and other agriculture by country.

trait in any region. Nolan and Santos [21] provide an overview of this research. They find that yields fall by approximately 7% in the switch from stacked to conventional. This is in keeping with the estimates provided by Brookes and Barfoot. Shyrock [22] reviews the literature and finds yield impacts varying between 6.6% and 10.3% between 2005-2010, though this is already weighted by area (thus the 2010 figure is highest because of the greater penetration achieved by that point). This suggests slightly higher yield impacts then those adopted in this work.

In the Philippines, more recent work finds that Bt corn led to 33% and 45% higher predicted yields in 2003 and 2007 respectively [23] . The improvement in the Philippines is especially sensitive to yearly factors (weather, pest pressure, etc.). The 18% figure used by Brookes and Barfoot is a relatively conservative one. In Argentina, other literature confirms the 5.5% figure used in this work―Burachick [24] reports that Bt corn improves yields by 5% to 9%. No work has been done specifically on Uruguayan Bt corn yields. For this reason, Brookes and Barfoot assume Uruguay benefits as Argentina does. A similar approach is taken for Paraguay. Colombia, where farm survey data is used, does not have a large extant literature. For Brazil, earlier field trial data suggested that Bt corn produced yield 24% higher than conventional varieties [25] . Brookes and Barfoot rely on more recent farmer surveys for their figure, which is more conservative. In Spain, other work estimating the economic impact of Bt corn on farms uses a slightly lower number (around 9%) [26] . However, the value used in Brookes and Barfoot”s work comes from a more recent study. The Czech Republic and Portugal do not have a lot of literature on Bt corn yield improvement, so it is difficult to put the estimates in context. In South Africa, the yield figures used correspond to the accepted figures in the literature around the benefits of Bt corn (see for instance Kruger et al. [27] in their discussion of pest resistance).

2.2.2. Soybean Yield

The assumption that first generation soybeans provide no yield advantage in most of the world is consistent across the literature. In general, herbicide tolerance provides no yield improvement. The adoption of herbicide tolerant soybeans is not a function of yield improvement, but rather a function of cost and time savings [28] [29] . There are only two assumptions made by Brookes and Barfoot with respect to soybean yields. The first is that farmers in the United States who have planted second generation soybeans have experienced yield gains [15] . The technology is new, so there is not a large amount of data yet available for the rest of the world. The second is that Bolivia experiences a yield improvement with herbicide tolerant soybeans. This is confirmed in further work by Smale et al. on the impact of soybeans in Bolivia [30] .

2.2.3. Cotton Yield

In the United States, there are two major types of Bt cotton planted: Bollgard 1 and Bollgard 2. The figures used by Brookes and Barfoot are conservative. They use yield increases around 10%, which corresponds to work by Verhalen et al. [31] . Other pieces of the literature support yield increases from 15% up to 25% and even higher depending on year and region [20] [32] [33] . In Argentina, the primary work done on yield improvement in cotton is the work cited by Brookes and Barfoot. However, they acknowledge using the lower of the estimates in the data (30% yield improvement) rather than the higher numbers found in Qaim and De Janvry (35% yield improvement) [34] . Brazil's figures are based on as yet unpublished farm survey data―it is therefore difficult to put the figures into context. In Colombia, the figures used in this work are conservative.

Earlier farm survey work found an average yield improvement of 35% for Bt over conventional [35] . In Mexico, the main work on GMO yield improvement for cotton was done by Traxler, who noted in 2004 that the improvements due to GMO are highly variable year to year [36] . In South Africa, econometric analysis by Gouse et al. [37] find varying yield improvements for Bt cotton depending on farm size. These improvements range from around 14% to around 46%. Other work using farm survey data found farmers using GMO varieties obtained yields at least 56% greater than farmers using conventional varieties through three seasons of planting [38] . The work on GMO yield improvement in Burkina Faso is the work cited in Brookes and Barfoot’s data―there is no other literature to put these numbers in context. In China, the figures used here align with the overall consensus―that China experiences roughly 10% yield improvement for Bt over conventional varieties [39] . Some work finds slightly lower figures, closer to 6% [40] . The difference can be explained by regional and seasonal differences in the data being used. In India, earlier work found GMO yield improvements of 37% on average across three seasons [41] . Other studies confirm this magnitude of yield improvement [42] , though some work points to even higher yield improvements (80%) [43] . In Pakistan, the yield improvement for Bt over conventional used here is in line with other empirical analysis [44] .

3. Modeling Framework

3.1. Computable General Equilibrium

Computable General Equilibrium (CGE) models are economic models that attempt to solve for the equilibrium conditions in the economy, by modeling the behaviors of three agents: households, firms, and the government. Based on the assumptions about these behaviors (e.g. profit maximizing firms, or utility maximizing households), a CGE model determines demands for and supplies of goods and services endogenously, while it takes into account resource constrains. The CGE models stand in contrast to partial equilibrium models in the way they approach the relationships among markets. In partial equilibrium models, the focus is commonly on a single market or a few markets in isolation from the other parts of the economy. In general equilibrium analyses, the goal is to determine the equilibrium conditions across the whole global economy. This means accounting for linkages across markets in an economy including both product and factor markets is much more important in general equilibrium approaches. The CGE models are used for economy-wide analysis. They are necessarily built out of input-output tables representing all goods and services produced, consumed, and traded given primary factors of production including labor, land, capital, and resources. A typical input-output table represents the extent to which industries are reliant on the outputs of other industries. It also captures the links between the economic agents represented in the model: firms, households, and the government. Together these tools arguably capture the linkages that characterize specific economies. Another important piece of any CGE model are the elasticities―these parameters capture a wide variety of responses to change across an economy (for instance, relevant here are elasticities that capture the conversion of land in response to changing agricultural commodity prices).Obviously solving for the global general equilibrium requires a considerable amount of data and computational power.

3.2. GTAP-BIO Model

The model used in this work is an extension of the Global Trade Analysis Project (GTAP) framework developed originally by Thomas Hertel [45] . There are two parallel features of GTAP: the model, which attempts to capture the structural features of the global economy and the database built from social accounting matrices for countries that are then aggregated by region. The GTAP database is unique. It contains country input and output data, along with other empirical data representing relationships among markets and industries, and relationships between countries. The database is updated periodically, and new versions are created that attempt to capture the most up to date information on the state of the global economy. It is worth noting that the GTAP model used in this paper is a comparative static model-thus we are comparing the current economic situation to the economic situation given certain changes. The changes are not changes “over time” but rather counterfactual comparisons. Since its creation, a number of advancements, both in the modeling techniques and in the collection of data have made GTAP one of the preeminent CGE modeling frameworks and data bases. The information for the GTAP database is drawn from a number of sources. These include the World Bank, the UN Statistics Division, as well as individual country’s statistic’s departments. Some of these advancements include the disaggregation of land by agro- ecological zone (AEZ) [46] .

As biofuels began to experience a revival in interest and production (based on the aggressive goals of the Renewable Fuel Standard), they were integrated into both the GTAP database and model, leading to the GTAP-BIO model [47] . This version of the model and the database capture not just the biofuels themselves, but also the secondary byproducts of biofuel production (e.g. dried distiller’s grains). This model was subsequently used to quantify the economic and environmental impacts not just of agricultural policy and trade policy, but also of a variety of other kinds of public policy (energy, water, etc.) [48] - [50] .

In a more recent work, Taheripour and Tyner have calibrated the model using empirical evidence on global land use change in the post-biofuel boom world [51] . The authors modify the elasticities of transformation for the types of land in the model (forest, pasture, and crop) and modify the structure of land supply as shown in Figure 1. As in all research using the GTAP-BIO framework, the time horizon is medium term.

Figure 1. Land supply trees in new and old GTAP-BIO models (source: Taheripour and Tyner, 2013).

In the original model, all land use types are in the same nest-the assumption underlying this decision is that forest and pasture have the same ease of transformation to cropland. The new two-level nest implicitly assumes that pasture is easier and less expensive to convert than forest.

The two level nest version of the model is used in this work. Using this model allows us to account for the effect of GMO yield shocks on land use change in the presence of global biofuel production. It also allows us to quantify more accurately the land use impacts of falling yields, which is of critical importance for this work.

The database used in this work is the most recent available. It represents the global economy in 2011. There are 19 regions, some of which are composed of individual countries, others of which aggregate country level data. Goods and services are aggregated into 52 categories, which include individual commodities (e.g. soybeans) as well as aggregated categories (e.g. coarse grains).

3.3. Implemented Closure

Only two major modifications to the model’s closure are made. The first is required in order to shock yields, and mostly technical. The basic model sets a limited number of variables as exogenous, with the rest being determined by the model (or endogenously). Since yield is not one of the exogenous variables, we swap yield with a technological change variable that is exogenous. The other modification is that biofuel production is fixed in the EU, Brazil and the United States at their base level. These three regions produce the vast majority of global biofuels in the 2011 database (approximately 89%).

The economics of biofuels are complicated. In particular, it is not the case that biofuel production is dictated by straightforward production cost and demand. In the United States, for instance, biofuel production is dominated by the Renewable Fuel Standard (RFS).Whether or not biofuel policy would change in the face of falling yields is beyond the scope of this work. Instead, we assume that biofuel production from the main producing regions remains constant, as the focus here is not on biofuels, but on GMO yield shocks. This also allows us to compare our counterfactual scenarios for price, welfare and the environment with the actual world more readily. We do note that fixing biofuels production quantity makes this analysis technically a partial equilibrium analysis. However, since we are still using a CGE framework we consider our work here to fall under the broad heading of general equilibria and to contribute to the general equilibrium literature.

3.4. Scenario Description

In what follows, we examine two distinct scenarios. Both use the 2013 yield improvement estimates from Brookes and Barfoot’s data. We propose here to examine two counterfactuals. The first asks, “What would be different if there was no GMO technology?” The second asks, “What would be the impact if GMO adoption globally caught up to the United States?” By examining these scenarios individually as well as in combination, we can derive conclusions about both the current and future value, both economic and environmental, of GMO crops.

The first scenario is the most straightforward. It assumes that GMO penetration is exactly what it was as of 2013 in each region. This case asks what would be the economic and land use GHG impacts of switching from GMO to conventional. By shocking each country with a weighted negative yield shock, we reduce the yield in those countries to the conventional yield. This first scenario provides the current benefits due to GMO crops.

However, currently not all countries are experiencing the full potential benefits of GMO technology. Our assumption is that relatively low penetration in other countries is not due to those countries capping the optimal planted area of GMO crops to the current penetration. Indeed as the ISAA data shows [12] , GMO planted acres have been steadily increasing in the rest of the world. Not only that, but while the United States has some of the highest levels of GMO penetration, United States farmers do not derive unusually large yield increases, relative to other countries [52] . Thus the slower adoption must be due to other causes, whether due to restrictive agricultural policy (in the form of partial bans), or the relatively slow dissemination of technology. We model the effects of increasing the penetration of GMO crops in the rest of the world to the penetration rate achieved in the US. This in turn provides a picture of the as yet unrealized potential benefits of GMO crops. While the first scenario asks “How much better off are we?”, the second asks “How much better off could we be?”

In order to set the penetration of GMOs in the rest of the world, the United States is used as a baseline. Another approach would be to select penetration levels that seem reasonable on a country-by-country basis. While that might seem a more complete approach, in the end it would require more somewhat arbitrary assumptions than using a country with high GMO penetration as a starting point. Actual adoption might be higher or lower than predicted by basing penetration off of the United States. The literature on technology adoption is significant but parsing it and selecting an appropriate econometric model falls outside the scope of this work. Penetration in the second scenario is set at the current level of US penetration unless the country already has a higher level, in which case the higher level is retained.

The only countries included in the second scenario are countries with GMO crops already planted. Obviously, it is possible that other countries in the future will permit GMO varieties, so our analysis represents a conservative estimate of GMO benefits. While other countries likely would benefit from GMO crops, policy is political, not strictly economic. Thus, the estimates provided assume no complete policy changes from current policy.

Finally, there are other concerns that are not addressed here?for instance, the overall yield impact of increasing penetration of GMO crops. What is the impact on yield improvement of higher penetration? Are conventional yields boosted by high penetration of GMO crops? Again, the appeal here is to minimal but explicit assumptions. The assumption here is that yield improvement is not sensitive to penetration level, so again it is a conservative case.

There are two ways of thinking about the results of these simulations. The first is to consider them independently, as they were presented above. This consists in interpreting each simulation as an independent counterfactual. We can also combine the results of the two cases to gain a different perspective on overall GMO impacts. The original results for scenario 1 are negative and for scenario 2 positive. However, if we consider scenario 2 as an opportunity lost, we can change the signs of some of the results and add them to scenario 1 results to get combined GMO impacts. This approach can be taken for GHG emissions and welfare impacts. It cannot however be used for commodity and food price impacts.

For each of these scenarios, we also performed simulations fixing food supply. This was done in response to concerns that the model will lower food consumption in the presence of a yield shock in an unrealistic way [53] . As is to be expected, the economic impacts are slightly larger and the land use conversion is slightly greater. However, fixing food does not change the results in which we are interested in a substantial way. Thus the detailed results of those cases are not reported here. We provide some of the main results in appendix A.

4. Results

The results of this work are divided into three sections. We begin by examining the results of the first scenario-that is, the simulation in which we model the disappearance of GMO technology. This is followed by a similar summary of the second scenario (higher GMO penetration). The third section presents the combination of the outcomes from the two scenarios. The full results of the simulation cover a wide range of outcomes. In the following we present selected economic and environmental impacts. Each section covers global outcomes, United States’ outcomes, and outcomes for the rest of the world.

4.1. Scenario 1

4.1.1. Economic Impacts

Global outcomes

Global production of agricultural crops does not fall much, as the GMO commodities make up a relatively small proportion of global production. Only corn, soybeans, and cotton are included in GMO varieties, and those represent a relatively small (but increasing) share of the global total. The crop for which production falls the most in percentage terms is soybeans (1.40%), which is largely driven by the fact that it is a separate commodity in the version of GTAP used for this study. Sorghum has the greatest gains (1.13%), again mainly because it is a separate commodity. For sorghum, it is also starting from a small base, which grows as it substitutes for corn.

The supply price of these commodities is affected more significantly. This is an economically intuitive result. The supply price of other coarse grains (which includes corn) increases by 3.49%, and the supply price of soybeans increases by 4.05%. Table 3 summarizes the impact on supply and supply prices at the global level. The lowest price

Table 3. Impacts on global crop prices and supplies, Scenario 1.

increases are for rice (1.58%) and wheat (1.90%), and those lower increases are related to the fact that wheat and rice are food grains, while coarse grains, sorghum, and soybeans are used for animal feed. There is less substitution between food and feed crops.

Overall, the price of food is less significantly affected (increasing by only 0.8%). This is because the price of food includes not only the constituent commodities, but also costs of labor, processing, packaging, etc. Of course, although the change in price is small, the absolute numbers are significant. In 2010, according to the World Bank and the Food and Agriculture Organization, total expenditure on food totaled approximately $6 trillion. Thus a 0.8% price increase amounts to close to $49 billion dollars (if consumption quantities remained fixed, which they do not). There is a global welfare loss of $8.5 billion, though as with food price, a closer analysis of each region is important in understanding the dynamics of the welfare change.

US Outcomes

In the United States, production is affected more than the global average. Table 4 summarizes the supply effects of GMO disappearance. This is to be expected, as the United States has high GMO penetration relative to the rest of the world. Again we note the impact on sorghum, which is driven by the same features in the US as it is globally. It is a substitute for other coarse grains, starts from a small base, and has no acreage planted to GMO (so experiences no yield loss). Palm oil supply increases for analogous reasons. It is a substitute for soybean oil and has no GMO varieties, so yields do not fall. Even crops without GMO improvements experience both a reduction in supply and an increase in price. For instance, wheat and rice have no significant acreage planted to GMO varieties. Regardless they both experience supply decreases, of 3.35% and 2.42% respectively. The limiting factor is agricultural land. Without GMO traits, more land is needed to produce the affected commodities, so less is available for all other agricultural crops. Of course, while the price impacts are largest for the commodities that are directly affected by yield loss (with price increases of 6.74% for coarse grains and 6.48% for soybeans), the effects on price are not limited to those commodities. Sugar experiences a surprising price increase of 5.1%. Though the commodity price impacts are considerably above the global average, the effect on food prices is less so. This is explained by greater consumption of processed foods, whose prices are less affected for the reasons described above. However, while the relative numbers are small, total U.S.

Table 4. Impacts on US crop prices and supplies, Scenario 1.

expenditure on food in 2013 was $1.6 trillion dollars. Food prices increase by 0.81%, which would amount to $13 billion dollar increase in food cost [54] .

The welfare effects in the United States are substantial, with a welfare increase of $1.24 billion. This is somewhat counterintuitive at first glance, since the United States is a major user of GMO technology. A closer look at the welfare decomposition provides insight into the mechanism at work here. Though the United States loses due to the loss of GMO technology (by $1.86 billion), it gains due to changes in the terms of trade (by $3.59 billion). The gains due to the terms of trade reflect the fact that in the absence of GMO crops crop prices go up in the world market in favor of the United States. The U.S. is one of the most productive agricultural areas in the world and a major agricultural commodity exporter. If GMO technology disappears everywhere, then the rest of the world becomes much more dependent on U.S. agricultural production.

Rest of the World Outcomes

China experiences by far the largest welfare loss in the first scenario. China has a welfare loss of $3.63 billion dollars. There are two primary reasons for this welfare loss. The first is simply the loss associated with the loss of the GMO technology-this accounts for around $1.1 billion dollars of welfare decrease. The other piece is the loss due to terms of trade. China loses $2.4 billion dollars in trade, primarily in soybean and coarse grain imports. This is unsurprising, as China is the largest commodity importer in the world. The Middle East and North Africa’s welfare loss is driven by an analogous dynamic-their reliance on imports for grain leaves them vulnerable to supply decreases and price increases. The European Union also experiences a similar effect. Even though the EU does not generally import varieties with GM traits, the fact that global production is higher than it would be without GM traits means that EU imports come at a lower cost. Thus, when the GM varieties disappear, the EU must pay higher import costs and suffer welfare losses of $0.96 billion. Food prices in the EU are relatively unaffected, with only about a 0.34% increase in overall expenditure. Other regions with substantial welfare loss are India, with a welfare loss of $2.23 billion and Japan with a welfare loss of $1.03 billion. India’s welfare loss is driven by the loss of yield due to GMO technology. Unlike the United States, India’s exports are not able to overcome the welfare loss. The first column of Table 5 summarizes the welfare losses and gains of this scenario by region.

As we see in Table 5, there are “winners” and “losers” from an overall welfare perspective. Apart from the United States, Brazil and South America are the biggest winners.

Table 5. Welfare impacts by region for scenarios 1 and 2 and their combination (million USD).

Even though Brazil and South America both have relatively high GMO penetration, like the United States they have a welfare gain through the terms of trade effect as other countries must pay more for their commodity exports. However, we note here what will be true for all of the simulations: the welfare impacts of banning GMO crops are quite small. If we compare the welfare impact of the GMO ban as compared to, say, the biofuels mandate (a welfare loss of $43 billion according to Hertel et al. [55] ), we see that banning GMO crops does not damage global welfare very substantially. Indeed this should hardly surprise us-the values are directly in keeping with the literature on GMO benefits [17] . Nevertheless, we report the welfare results as well as their global distribution, as the variation in welfare by region is noticeable. It is important however to keep in mind the scale of these losses.

Food prices increase most in South Asia. India experiences the highest food price increases, with a 2.2% increase in prices. In the rest of South Asia (grouped together as a single region in the model), food prices increase by 1.3%. These numbers are notably higher than the global average of 0.78%.Other regions with high relative food price increases are East Asia (1.14%) and Brazil (0.97%). These food price increases are driven by higher consumption of raw commodities, rice in particular, and lower consumption of processed food.

4.1.2. Land Use Change

The first block of Table 6 provides the land use change numbers for scenario 1 by region. As is to be expected, a considerable amount of land is converted to cropland from other uses. Falling yields on existing cropland means producers must expand their production area to meet demand. Global cropland increases by about 3.1 million hectares with 2.5 million hectares coming from pasture land and the balance (around 0.6 million hectares) coming from global forest loss. The greatest conversion of forest to cropland occurs in Sub-Saharan Africa, which also experiences the greatest increases in cropland. Other major areas of forest loss are India and the EU. Some regions actually experience increases in forested area. Brazil, South America, Central America and China all experience gains in forested area, though these gains are offset at the global level by losses in other regions.

Table 6. Land use change for scenarios 1 and 2 and their combination (in 1000 hectares).

One of the main problems with land use conversion to cropland is that when forest or pasture is converted to cropland, much of the carbon that has been sequestered over the years is released into the atmosphere. In addition, future sequestration is foregone. In the biofuels literature, this indirect or induced land use change and its associated emissions has been an important and controversial topic. Thus land use conversion to cropland has associated emissions increases. With the growing focus on greenhouse gases emissions, this is an important issue worth addressing. Fortunately, the results of the GTAP-BIO simulation allow us to calculate emissions changes associated with the land use change.

4.1.3. Land Use Emissions

The first column of Table 7 shows the global emissions effects of land use change by type of land use change for the first scenario. At the global level, the total emissions due to land use conversion are about 0.9 billion tons CO2 equivalent for this scenario. In other words, if GMO technology were not available, there would be approximately 0.9 billion tons CO2 equivalent more greenhouse gas emissions than there are currently. It is important to note that these emissions effects are only capturing one way in which the loss of forestland has negative environmental outcomes. There likely are other ecosystems losses that are not included here.

4.2. Scenario 2

4.2.1. Economic Impacts

Global Outcomes

World supply of agricultural commodities is not significantly affected by the increased yield from scenario 2. Soybean supply increases the most (0.84%), as it has the greatest increase in penetration of all GMO crops. As mentioned above, it is also a single category, so in percentage terms its changes will inevitably be more significant than aggregated commodity categories like coarse grains. In turn, other oilseed crop supplies fall. As these are substitutes for soybeans, increased production of soybeans leads to substitution. Similar effects are observable in global commodity prices. The price of all commodities falls, but by less than 0.5%, with the exception of soybeans. Soybeans experience a 1.3% decrease in price. Global food price is barely affected at all in the second scenario, experiencing a very slight decrease (0.11%). Global welfare increases by $1.3 billion. As in scenario 1, the single global welfare number does not tell the whole story, as it fails to account appropriately for regional winners and losers.

Table 7. Emissions from land use change for scenarios 1 and 2 and their combination (billion grams CO2 equivalent).

US Outcomes

Unlike in scenario 1, the US experiences slight impacts relative to the rest of the world. This is to be expected. The approach we took in modeling scenario 2 means that the United States experiences no yield improvements. Thus the production effects in the United States are negligible. Total supply of all commodities stays even or falls-most notably for soybeans, where supply falls by 1.3%. Imports from other soybean producers become more affordable, thus lowering domestic production. This might not seem especially significant, but 1% of total US soybean production is close to 33 million bushels. Still, relative to total production, the effects are not important. Falling production and prices indicate that cheaper supply is now coming from other regions. In fact, a closer look at the terms of trade effects and the harvested area reveals that the increase in yields in the rest of the world changes to some extent the locations of agricultural production. United States producers move out of oilseed production and into wheat, rice and other coarse grains. As mentioned before, wheat and rice have little to no area planted to GMO varieties. Thus no country is gaining any advantage relative to the United States in those crops, explaining the increase.

The United States is a loser in net welfare in the second scenario. The United States experiences welfare losses of $492 million. The vast majority of those losses come from trade. As production in the rest of the world increases, the United States loses out to other exporters.

Rest of the World Outcomes

As in the first scenario, China experiences the most significant welfare impacts. This time, however, China gains $0.73 billion. The mechanism is analogous to the first scenario. China benefits from the rising supply (and falling price) of grains and oilseeds. In particular, the decreased price of soybeans is a particular boon to China.

Other beneficiaries are the Middle East and North Africa ($0.47 billion) and the EU ($0.37 billion). This is no surprise; just as for China, the mechanisms for loss and gain are roughly symmetrical in scenario 1 and scenario 2. Brazil and South America experience the largest losses in welfare ($89.2 million and $96.5 million, respectively). There is symmetry to the results of scenario 1 and scenario 2: welfare gains in scenario 1 are matched by welfare losses in scenario 2, and vice versa. The second column of Table 5 gives the overall welfare effects by region for this scenario.

Food price effects are negligible across the world-the most significant drop in food price occurs in the Brazil (0.38%).

4.2.2. Land Use Change

As global yields improve, we anticipate less area planted to crops. This is what we observe in the simulation results. Global cropland decreases by about 0.8 million hectares. Forests cover 0.06 million more hectares, and pasture for livestock covers the other 0.74 million hectares currently devoted to crops. The European Union and Sub Saharan Africa experience the largest increases in forestland (0.02 million hectares and 0.53 million hectares, respectively). Though Brazil experiences the greatest decreases in cropland (0.46 million hectares), most of that land is converted to pasture, rather than forest. The second block of Table 6 represent land use change by region for this scenario

4.2.3. Land Use Emissions

As in the previous scenario, the land use conversion has emissions impacts. Since the conversion is now from cropland to other uses, the emissions impacts are negative. A counterfactual world with higher GMO penetration is a world with less GHG emissions. Simply by increasing the penetration of GMO crops in countries currently using GMO to the United States” level of penetration, greenhouse gas emissions fall by 0.2 billion tons CO2 equivalent. The second column of Table 7 summarizes the global sources of emissions decrease.

4.3. Combination of Scenarios 1 and 2

4.3.1. Economic Impacts

Lastly, we consider the scenarios together. We recall that the previous results have all been understood relative to the actual world. Scenario 1 considers the world in the absence of GMO technology; scenario 2 considers the world with increased GMO penetration. Having considered these scenarios separately, we now take them together. Here our goal is not to compare counterfactual worlds to the actual world, but rather to consider the future. One way of thinking about this is to consider this as an estimation of the cost of banning GMO crops. Instead of comparing the ban to the current world, which assumes that the penetration of GMO crops will remain static, we compare the outcomes in the case of a ban to the outcomes in the case of a likely future scenario. In this case, we understand scenario 2 as the plausible alternative outcome. Based on the rising penetration of GMOs worldwide, it is not unreasonable to assume that penetration will reach the levels it has attained in the United States. In fact, it would not be unreasonable to assume that GMO penetration far exceeds the penetration we model here. That being said, given the number of unknown variables, this seems a reasonable way to conservatively estimate of the future costs of a GMO ban (or the future benefits of GMOs).

In considering the scenarios relative to each other, we consider the welfare effects and land use/emissions effects. Clearly the commodity price impacts and food cost impacts would be higher, but it is not possible to directly combine those results.

In order to compare the welfare costs of a future GMO ban, we take the welfare results from scenario 1 and subtract the welfare impacts from scenario 2. This gives the welfare impact of a GMO ban given the welfare impacts of the increased GMO penetration from scenario 2. Global welfare loss is $9.8 billion. China is especially hard hit, with welfare losses accounting for more than 40% of global welfare loss. The third column of Table 5 gives the difference in welfare impact by region.

Here the winners and losers of the GMO ban are made even clearer than in either scenario taken alone. Besides China, India and the Middle East and North Africa are the hardest hit, with Brazil and the United States reaping significant rewards. Given the regulatory approaches of the various regions represented here, the results are somewhat surprising. On the whole, as GMO penetration increases in GMO using countries, a GMO ban hurts low GMO penetration regions more and more. Export heavy regions are also the regions with the most significant penetration of GMO crops. Importers in turn rely on the marginal production of these GMO using producers. When the GMO varieties disappear, it is the importers who must meet their demand with higher prices that are adversely impacted the most.

4.3.2. Land Use Change

A similar procedure allows us to determine the land use effects of a future GMO ban. The third block of Table 6 summarizes the land use impacts of the future GMO ban. From the first column of this table, it is clear that much of the conversion of forest to crop is occurring in either the developing world or in places with at-risk forests to begin with. Sub Saharan Africa has the largest forest loss, losing about 0.3 million hectares of forest. India also loses significant forested area (also around 0.3 million hectares).

4.3.3. Land USE Emissions

The global emissions outcomes combining scenario 2 and scenario 1 is approximately 1.1 billion tons of CO2 equivalent (see the last column of Table 7). It is clear from these results that GMOs are a significant factor in the “greening” of agriculture. After energy production, agriculture is the largest source of greenhouse gas emissions. This level of emissions is about three times the land use change emissions from the entire US ethanol program. The emission reduction impact of GMO varieties is rarely mentioned in the GMO debate.

5. Conclusions

The objective of this paper was to quantify the economic and environmental impacts of banning GMO crops. Using a well-known CGE model (GTAP-BIO), two counterfactual scenarios were examined to reach these goals. The first is a GMO ban, while the second is an increase in total GMO penetration. The economic impacts include welfare, price, and supply impacts. The environmental impacts focus on land use change and associated emissions change.

As GMO finds wider and wider usage, there is a corresponding growth in the popular hysteria surrounding the technology. Environmental activists push for GMO bans, without adequately considering the impacts such bans might have. The losses associated with a global ban would be twofold: the losses actually realized and the potential losses when compared to an alternative adoption schema. These losses are also not merely economic. To frame the debate as environmentalists on one side, and capitalists (and purveyors of capitalist apologetics) on the other, a more complex issue is oversimplified. There are environmental gains associated with GMO technology, and while the welfare effects of GMO technology are not, as it turns out, especially substantial at the global level, the environmental effects are. Both sides of the GMO debate are done a disservice if these effects are ignored.

While the welfare impacts are not substantial at the global level, there are economic effects worth noting. In particular, the supply price and food price increases are extremely region specific. While the United States does not even experience a 1% food increase, countries like India and other South Asian nations do see their food prices increase more noticeably (2.2% and 1.3%). These are parts of the world where food and beverage expenditure is already a greater share of total household consumption, and so the effect of the food price increase is in fact amplified. It is a luxury to be relatively unaffected by a GMO ban, or at least to have your pocketbook hit less hard. Interestingly, the welfare and supply effects suggest that in the case of a GMO ban, the world becomes more dependent on US agriculture. This might not be a desirable outcome for nations other than the United States. Indeed, the United States is the country that benefits most from a GMO ban, either present or future.

The welfare impacts are in line with the impacts estimated in the rest of the literature [17] . Because they are the results of a global GMO ban of all three main crops, they are slightly greater than studies which have focused on one region, or one crop’s benefits. However, the overall economic impacts of GMO crops have been discussed at great length, both at the micro and macro level.

What have been more sparsely covered in the literature are the land use change impacts. Indeed Barrows et al. [56] in their examination on land use change and GMO point to the need for a full general equilibrium analysis to assess the impacts of land use change on price, supply but also on greenhouse gas emissions. Our findings suggest that avoided land use change (and thus avoided increases in emissions) is one of the most important benefits associated with GMO technology. Following the completion of the latest talks in Paris, countries have expressed a willingness to lower overall emissions, and GMO technology is one of the ways that agriculture can help this aim. Agriculture would have to find alternative approaches to lowering emissions, and these are not immediately obvious without fundamentally altering the agricultural landscape (e.g. banning meat).

This work is among the first to use the updated 2011 data from GTAP. Thus it is run using the most recent global economic information. Undertaking to model, a global GMO ban requires that global data be used, and preferably the best global data available―this allows this work to provide a fuller picture of the world impacts.

Cite this paper

Mahaffey, H. , Taheripour, F. and Tyner, W. (2016) Evaluating the Economic and Environmental Impacts of a Global GMO Ban. Journal of Environmental Protection, 7, 1522-1546. doi: 10.4236/jep.2016.711127.

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