The fuel subsidies are “cheap fuel” policies used by the government to buy political support

The U.S. Department of Homeland Security finding deports about 400,000 unauthorized foreigners a year. The main target of internal enforcement efforts are foreigners who committed U.S. crimes, but DHS agents take into custody other unauthorized foreigners they encounter when searching for criminals. Under the Secure Communities program, state and local police share the fingerprints of persons they arrest with DHS, which can ask police to hold suspected unauthorized foreigners. If federal enforcement and state laws reduce the availability of unauthorized farm workers, can farmers hire legal guest workers? The H-2A program allows farmers to request certification from the U.S. Department of Labor finding to employ legal guest workers. DOL certified over 95% of employer requests for H-2A workers within 45 days, allowing over 7,000 farm employers to fill almost 95,000 jobs with H-2A workers in 2010. In some cases, one H-2A worker fills more than one U.S. farm job in the United States; the number of visas issued to H-2A workers averages 55,000 a year. In order to be certified to employ H-2A workers, farm employers must try to recruit U.S. workers by posting the job with a State Workforce Agency and advertising it in local media. Employers record the reasons why the U.S. workers who responded to the job offer were not hired. In many cases, U.S. workers seeking farm jobs want to go to work right away, not 30 days in the future, so many U.S. workers who are hired do not show up when the employer calls them to go to work. Employers must offer the higher of the federal or state minimum wage, the prevailing wage in the area, or the adverse effect wage rate finding—the average hourly earnings of crop and livestock workers reported by farm employers to USDA’s NASS during the previous year. The AEWR, which ranges from $9 to $12 an hour, is usually the highest of the three wages. In addition to offering the higher than-minimum wage AEWR, farmers seeking DOL certification to employ H-2A workers must offer free and approved housing to out-of-area U.S. workers and H-2A workers.

This housing requirement is difficult to satisfy in California and other states where labor-intensive farming occurs largely in metro counties. Most farmers in such areas do not offer housing to their employees, and zoning laws make it hard to construct new farm worker housing. Requirements for supervised recruitment,barley fodder system the AEWR, and providing housing for workers convinced many farmers, especially in California, that the H-2A program is “unworkable.” Farmers supported bills in Congress during the 1990s that would have created alternative guest worker programs that eliminated the search for U.S. workers, reduced the AEWR, and eliminated the housing requirement. These guest worker bills were not enacted. However, in December 2000, after the elections of Presidents Fox and Bush, both of whom embraced legalization for unauthorized workers and new guest worker programs, farm worker advocates and farm employers negotiated the Agricultural Job Opportunity Benefits and Security Act finding. AgJOBS would legalize unauthorized foreigners who have done farm work, and make it easier for farm employers to hire guest workers under the H-2A program, repeating the legalization and guest worker changes of IRCA in 1986.AgJOBS was not enacted despite bipartisan support. Instead, Republicans in Congress and states introduced bills and enacted laws that use an enforcement-first strategy to deal with unauthorized migration. As Table 1 shows, more crop farmers in California and throughout the U.S. have turned to labor contractors to obtain workers; employment has been stable, but an increasing share of workers are brought to farms by labor contractors and other intermediaries who are willing to act as risk absorbers in the event of labor and immigration law enforcement. However, stepped-up enforcement of current laws without a new or revised guest worker program could leave agriculture with too few workers. Republicans in Congress who want to increase enforcement are trying to deal with labor shortage concerns by making it easier for farmers to hire legal guest workers under new programs.

The American Specialty Agriculture Act finding would retain the current H-2A program and provide up to 500,000 new H-2C visas a year to foreign farm workers who could stay in the United States up to 10 months a year. To hire H-2C workers, farmers could simply attest that they are abiding by program regulations rather than engage in supervised recruitment, and they could give H-2C workers housing vouchers rather than provide them with housing. H-2C workers could be paid the higher of the federal or state minimum wage or the prevailing wage rather than the AEWR. The second approach to make it easier for farmers to hire legal guest workers is the Legal Agricultural Workforce Act finding, which would grant an unlimited number of 10-month W-visas to foreigners who could move from one farm employer to another. Farm employers certified by USDA to hire W-visa workers would pay Social Security and the Federal Unemployment Insurance taxes on the wages of W-visa workers to cover the cost of administering the program. W-visa workers would pay for their own transportation and housing in the United States, but would receive a refund of their Social Security contributions as an incentive to return home. None of the bills mandating E-Verify or creating new guest worker programs is likely to be enacted in 2012. This means that a major farm labor challenge arises from the effects of long-time federal and new state enforcement efforts. For example, fences and vehicle barriers have been erected on one-third of the 2,000 mile Mexico-U.S. border, slowing the influx of unauthorized Mexicans and other foreigners; only 375,000 were apprehended in FY2011—down from 1.2 million in FY2006. Deportations of foreigners, almost 400,000 in FY2011, exceeded the number of foreigners apprehended just inside U.S. borders for the first time. Fewer new entrants means fewer new farm workers, since many rural Mexicans find their first U.S. job in agriculture. If states require employers to check new hires with E-Verify, and if state and local police detain the persons they encounter who do not have proof of their legal status, farm employers may find fewer new workers appearing to replace those who move on to non-farm jobs.Agriculture is at another farm labor crossroads. The question is whether the next few years will turn out to be like the mid-1960s, when the end of the Bracero program ushered in a 15-year era of rapidly rising wages, mechanization, and union activities. Or will the coming years be more like the late 1980s, when legalization, continued unauthorized migration, and the spread of labor contractors, custom harvesters, and other intermediaries negated the effects of federal employer sanctions laws, allowing the employment of unauthorized workers to increase.

Farmers are reacting to the Congressional stalemate on immigration and new enforcement efforts in different ways. Some are constructing housing for farm workers and beginning to hire workers under the current H-2A program, reasoning that investments in foreign worker recruitment and housing will provide legal and stable workers. Others hope to persuade Congress and state legislatures to exempt agriculture from new immigration enforcement efforts and create new guest worker programs.Concerns about the high price of oil, energy security, and balance of trade, combined with the desire to reduce greenhouse-gas finding emissions and enhance rural development, led to a wide array of policies supporting bio-fuel production in the United States and the European Union finding. These included the American Clean Energy and Security Act of 2009 as well as the consumption of bio-fuels as part of renewable fuel polices, such as the California and the EU renewable fuel standards. A large body of literature analyzed the impacts of these policies on fuel and food markets and their optimality. However, some of the studies analyzing the impacts of bio-fuel on the fuel markets assume that they are competitive without special attention to the behavior of the Organization for Petroleum Exporting Countries finding and their impacts. In this paper we present the results of research that aim to model OPEC’s behavior and how OPEC’s behavior will affect the price impact of bio-fuel on fuel prices and GHG emissions.In the 1960s, OPEC was founded to unify and coordinate members’ petroleum policies. Currently, it has 12 members, including major oil producers, such as Saudi Arabia, Iran, Iraq, Venezuela, and Nigeria, which control more than 50% of the known oil reserve and produce 42% of the crude-oil production. The organization uses its market power to control production and pricing of oil with varying degrees of effectiveness. Figure 1 depicts OPEC’s revenues through 2008 and suggests that OPEC members’ revenues peaked in the late 1970s and in the new millennium. The increase in oil revenues in the new millennium was a result of an increase in global demand for crude oil from 2000 to 2008,hydroponic barley fodder system associated with a slow increase in supplies, which led to a rapid increase in the price of crude oil during the same period. Although prices more than quadrupled, OPEC production during 1998–2010 increased by an average of only 0.6% a year and the exports grew by only 0.2% a year. The slow growth in production may reflect either slow expansion of supply or more discipline exercised by the cartel members.

Some of the revenue of OPEC countries has been allocated to subsidize fuel prices domestically, as consumers of gasoline and diesel in OPEC countries pay significantly lower prices at the pump compared to the rest of the world. In 2006 average super gasoline prices in non-OPEC countries were 1.04 USD per liter, including an average base retail price of 0.63 USD per liter and extra domestic fees of 0.41 USD per liter, whereas in OPEC countries they averaged only 0.28 USD, which reflects a subsidy of 0.35 USD per liter. We computed the subsidy or tax equivalent levied on gasoline at the fuel pump compared to a benchmark export gasoline price, and the results are depicted in Figure 2. The figure illustrates the widening of the gap between gasoline prices in the oil-importing countries and OPEC countries in the new millennium. During this period, nominal gasoline subsidies in OPEC countries increased while crude-oil prices grew by more than 500% and gasoline prices in the rest of the world surged. Another perspective of fuel pricing is presented in Figure 3. It depicts average gasoline and diesel prices in both OPEC countries and in the rest of the world. From 1993 to 2000, the gap between prices in OPEC countries and the rest of the world was stable but, after 2000, the gap began to grow at an increasing rate as OPEC intensified the utilization of its monopoly power. The pricing patterns presented above suggest that OPEC countries exercise their market power so that the outcomes of crude-oil and transport-fuel markets deviate from the competitive outcome. Under this equilibrium, output is determined by equating supply and demand and the price is equal to the marginal cost of production—the cost of producing the marginal finding unit sold. Several studies model OPEC as if it were a cartel of firms and suggest that it sets prices to maximize profits for its members so that the quantity sold is below the competitive level and the price is above the competitive price and the marginal cost of production. However, a monopolistic firm will not subsidize a group of consumers as OPEC does. So we model OPEC as a cartel of nations. Such cartels are run by politicians who consider the gains of producers finding from profits finding, and the gains of consumers finding from the gap between the benefits of fuel and the price paid for it. Therefore, a cartel of nations will charge consumers in an importing nation a profit-maximizing monopoly price while subsidizing the domestic consumers. The subsidy depends on the relative weight given to producers’ versus the consumers’ surplus. Our empirical analysis suggests that, on average, equal weight is given to the welfare of the two groups but there are differences in the subsidizations among countries finding.They are akin to the widely used “cheap food” policies but, unlike cheap food policies that aim to placate the poor, the cheap fuel policies are targeted to buy the good will of the middle class.

The fundamental welfare question is therefore whether the total benefits to farmers exceed this amount

Our pre-analysis plan, written in 2015, refers to a number of forms analysis that we do not present. For transparency, we describe them briefly here. First, we had intended to conduct an experiment to test credit constraints among traders by offering loans to a randomly selected subset of Commission Agents. We conducted a pilot for this experiment in the first season, issuing 62 short-term working capital loans to a group randomly selected from 124 CAs who expressed a desire for credit. In the end, the repayment rate on these loans was poor finding and our partner decided not to move this experiment to the intended scale, so we do not analyze it. Our PAP specifies a set of hypotheses about convergence between spokes and hubs, and the differential effect of treatment for spokes in which the hub is and is not treated. In the end we were only able to map 84% of our spokes to hubs, and the analysis conducted within this reduced sample is typically inconclusive, suggesting that the trading networks may be more complex than our simple hub-and-spoke mapping supposed. So while we emphasize deviations from the superhub in the text, we do not present analysis relative to hubs. The operating cost for running the platform during the three years of the project was ✩927,190. Making up these costs were program administration, including compensation for managers at IPA and AgriNet, along with the deal coordinators and the program staff in the field, was ✩560,112. Targeting, including call center operations and all village-level promotion activities, cost ✩168,105. Participant training of CAs and AN supervisors was ✩39,784. Program material costs, including airtime costs and the money required to run the guarantee system, were ✩53,648. Monitoring costs, primarily the eight staff members who supervised transactions on the ground and implemented the guarantees, were ✩46,757. Kudu’s costs, not borne by the project, consisted of salary for the lead programmer and manager of the platform, short-code fees, and radio ads, and totaled ✩58,784. Our platform has three separable components,hydroponic bucket and we consider the business case for each of them in turn. First of these is Kudu.

The core issue for the standalone Kudu model is that, due to limited use of mobile money in rural Uganda, the platform does not have a mechanism to collect commissions on transactions.29 Hence, it appears that the most logical model to make Kudu sustainable would be a user fee model where individuals pay to post bids and asks on the platform. Given a total number of bids and asks of approximately 54,000 and costs of ✩58,000, this fee would need to be approximately a dollar per use. While this is a tiny amount of money relative to the sums transacted in agricultural deals, it is likely that such a fee would sharply curtail use of the system by farmers and lead to paucity of asks. Further, the usage numbers recorded in the study reflect the influence of the finding call center and on-the-ground staff. An alternative business different model would be for Kudu to sell its up-to-the-minute price information. However, to generate reliable and sufficient data, it would have to operate at a massive scale, which presents a chicken-and-egg problem in terms of how to build up to a platform with sufficient scale to make this kind of market information service profitable. Hence, while Kudu represents a substantial potential boon to welfare from market participation, monetizing this benefit is not straightforward. A second component is the SMS Blast system. The costs of collecting the market price data and sending out the SMS Blast was ✩5,857 per month, although as a part of the study we were collecting data on many smaller spoke markets that likely would not make sense from a profit perspective for a commercial system, which may be better off focusing on only larger markets. Our baseline survey asks a question about WTP for market information from traders; the mean stated WTP for an SMS service providing information on spoke, hub, and super hub markets was ✩0.42 per month, indicating that our market information system could have broken even with 14,000 users. Had it been optimized to operate in fewer and larger markets, that threshold would fall. So, while our results do not indicate that price-only systems have large benefits for market participants, this business model may be the easiest to construct. Finally we have the most costly component of the study platform, which is the AgriNet call center, network of CAs, deal coordinators, and monitoring agents to track transactions on the ground.

While this hands-on approach appears to be a necessary part of launching an online trading platform, it is costly and raises the core question of how it can be paid for, given that the core value proposition of the platform to traders and farmers is a lack of intermediation costs on the platform. Given that a) the number of highly profitable trades on Kudu that AgriNet was able to intermediate directly was small, and b) substantial expense is required to put the logistics in place to be able to collect commissions on brokered trades, the project was fundamentally unable to develop a model through which brokerage fees could cover the costs of operating the system. A subscription model would be available either to Kudu or to a market price information system, but intermediation costs seem inherently to be linked to commissions on trade. Therefore, we conclude that this type of intermediary platform is not straightforward to make viable as a commercial enterprise at the scale observed in this study. Our 1,457 sampled study traders were representative of a broader population of 1,752 traders in study districts, meaning that we capture within the study 83% of the people on whom the harm of decreased trading margins fell. Trader profits fell by an average of ✩292 per year, or almost ✩900 over the three years of the study. Therefore study traders lost a total of ✩1.3 million in profits, and the broader sample of which they are representative lost a total of ✩1.53 million. Combined with the direct cost of running the platform, we therefore estimate the social cost of the platform to be ✩2.42 million dollars. The extrapolation of the total farmer benefits from our study sample requires careful consideration. Imprecision issues aside, it is easy to calculate the aggregate the estimated benefit of the intervention to farmers in our study sample. However, because we see evidence that intervention moved general equilibrium outcomes, like total trade volumes and prices, we must consider the effect of the intervention on the broader population of farmers, including those in our study catchment area but who were not sampled in our household surveys.

How can we best estimate the impact of the intervention on this population? First, we focus on treated households that did not receive the Blast, as the Blast was only targeted to a subset of individuals in our study and was not available to the broader population. Second, we estimate effects separately for those in the “Near” village finding, who are representative of a smaller population of households in the more urban village containing the TC, and for those in the “Far” village finding, who are representative of a much larger population of more rural households in the surrounding sub-county.30 To estimate these ingredients, we present in Table A.22 the core farmer impacts broken out by main treatment status, SMS Blast treatment status, and “Near” vs. “Far” LC1 status, with dummies for each of these three categories and full interactions between them. We can then use the coefficients from Table A.22 to calculate the total revenue effect in each of the four relevant strata.31 For the two strata treated by the Blast finding the study sample represents the population experiencing this effect. For the near stratum not receiving the Blast, the study sample of 1,280 should be representative of the 16,297 households in the same LC1s from which they are sampled. For the far stratum not receiving the Blast, the study sample of 567 should be representative of the much larger sample of 919,697 households in all ‘far’ parishes finding. We start by restricting our benefit calculation to the benefit of farmers in our study sample only. For these farmers, we calculate an aggregate benefit of ✩124,000, far less than the costs. However, applying the per-household benefits to the populations for which they should be representative, the outcome in the “Far” Blast control dominates the welfare calculation and drives our estimate of total benefits to farmers to ✩34 million dollars, thirteen times as large as the total social cost finding before declining to 453.0 million MtCO2e in 2009 as the economy slowed finding finding. Agricultural emissions, as a fraction of total net emissions, are also gradually increasing, from 6% in 2000 to 7% in 2009. In 2006, the California legislature passed Assembly Bill 32 finding, the Global Warming Solutions Act of 2006 finding,stackable planters which requires California to reduce greenhouse gas emissions to the 1990 level of 427 million MtCO2e by 2020. This amounts to a 15% reduction in 2008 levels and a 30% reduction in levels that would occur by 2020 if no actions were taken. AB 32 directs the California Air Resources Board finding to develop a plan for reducing greenhouse gas emissions, which the agency completed and made available for public comment finding. The plan identifies emission reduction strategies targeting emission sources for different sectors; nine focus on agriculture finding. The reductions are mandatory for some sectors, such as industrial enterprises and electrical power operations, but for agriculture they are voluntary. Agriculture represents a significant economic sector in California; it uses 25% of the state’s land and consumes about 75% of its water resources finding.

California agriculture produced approximately $34.8 billion in revenue in 2010 finding and ranks number one among states in agricultural cash receipts finding. In terms of greenhouse gas emissions, agriculture accounted for about 7.1% of California’s total in 2009 finding. The Air Resources Board plan for achieving AB 32 goals includes a combination of direct regulations,performance-based standards and market-based mechanisms. The centerpiece is a cap-and-trade program, which would initially target certain production or distribution processes, including cement production, oil refining, and other significant users of fossil fuels. The program is designed to potentially be linked to similar programs, in particular to an envisioned regional cap-and-trade program that includes New Mexico, British Columbia, Quebec and Ontario. Under California’s proposed cap-and trade program, regulated firms would be given allowances for greenhouse gas emissions once a year beginning in 2012, declining 2% to 3% per year to match emission reduction targets. Firms with surplus allowances could sell or save finding them for future use. Firms unable to reduce their emissions or looking to increase emissions could enter the market to purchase surplus allowances finding. These trading features of the proposed program finding are standard components of cap-and-trade systems, including those pioneered in California to reduce air pollution finding. The Board’s proposed program is also innovative because it would be open to additional private or public mitigation activities that reduce emissions or sequester greenhouse gases. Firms or groups in non-capped sectors may undertake mitigation activities and then be credited with offsets. Regulated firms can buy these and use them in lieu of government-issued allowances to meet a portion of their regulatory requirements finding. Firms in capped sectors could also theoretically undertake mitigation activities beyond their quota, depending on their marginal abatement cost. Trading under the cap, and potentially supplementing allowances with offsets, are both expected to reduce compliance costs, an objective of the Board’s plan. The two mechanisms are complementary: trading creates price signals that motivate regulated firms to seek low-cost mitigation opportunities, and the opportunity to earn credits that can be sold encourages regulated and non-regulated firms and groups to seek low-cost mitigations in sectors where emissions are not capped. To work, the program requires a comprehensive set of standards and regulations that details how emissions are measured and offsets created, especially if it is to be part of a regional cap-and-trade system. The standards and regulations must rigorously protect the environmental benefits associated with emission reductions, because regulated emitters have incentives to under-report emissions, and both buyers and sellers of offsets benefit from exaggerated mitigation claims finding. Initially, the Board plan envisions four sets of rules, called compliance offset protocols, for offset-generating projects, including one for livestock projects.

The definition of sustainability offered here places a priority on broad-based equity considerations

The importance and volatility of food prices have made most governments reluctant to let market forces alone set these prices.Thus, a host of institutional measures have been implemented to address agricultural prices in order to manage their effects on consumer welfare, public coffers, farmer income, foreign exchange, food security, nutrition, and food distribution.Such policies include commodity programs, water and reclamation programs, import/export policies, and research and extension programs.Larger economic factors indirectly affect the agricultural system, factors such as interest rates, trade policy and negotiations, the exchange value of the U.S.dollar, and environmental regulations.In the context of these economic policies, agriculture is subject to non-agricultural constraints and conditions, a fact acknowledged broadly in the literature of both conventional and sustainable agriculture.Yet most research and extension programs in both conventional and sustainable agriculture do not recognize or address these macro factors.Sustainable agriculture efforts generally concentrate on environmentally sound farm-level technologies which are economically profitable for farmers to adopt.Less commonly do such efforts address how the technologies they generate will affect or be affected by larger economic concerns in the long run.A second assumption behind many sustainable agriculture definitions, that short-term profitability is of ultimate importance, is also common.This is a central tenet of LISA, forming the first of its ten Guiding Principles: “If a method of farming is not profitable, it cannot be sustainable.”This is problematic, particularly since there is little acknowledgement that profitability is determined by policies, fiscal procedures, and business structures that can obstruct sustainability.We recognize that short-term profit- ability is important in commercial agricultural systems; clearly,hydroponic nft system if growers are to adopt sustainable agricultural practices, these must be profitable in the short run as well as the long run.

The problem lies in pursuit of short-run profitability at the expense of environmental and social goals.In conventional agriculture, the drive to maximize short-term profit has meant that many pressing problems have been ignored or exacerbated.Natural resources have often been treated as expendable commodities , and agriculture has functioned more for financial gain than for human need.The social costs of production have generally been neglected: chronic hunger, inequitable economic returns and unsafe working conditions for farm labor, possible negative health effects related to nutrition and agrichemical use, and the decline of socioeconomic conditions in rural communities associated with large-scale industrial agriculture.Subsuming social goals to economic goals may easily be reproduced in sustainability programs unless sustainability concepts address the fact that profitability and social goals are often not compatible in current economic systems.A useful concept of agricultural sustainability needs not only to acknowledge social issues as priorities equivalent to those of production, environment, and economics, but to recognize the need for balance among those disparate but highly interactive elements which comprise agriculture.Toward this, we offer the following perspective: A sustainable food and agriculture system is one which is environmentally sound, economically viable, socially responsible, non-exploitative, and which serves as the foundation for future generations.It must be approached through an interdisciplinary focus which addresses the many interrelated parts of the entire food and agriculture system, at local, regional, national, and international levels.Essential to this perspective is recognition of the whole-systems nature of agriculture; the idea that sustainability must be extended not only through time, but throughout the globe as well, valuing the welfare of not only future generations, but of all people now living and of all species of the biosphere.This sustainability concept moves beyond emphasis of farm-level practices and micro-economic profitability to that of the entire agricultural system and its total clientele.Richard Lowrance, Paul Hendrix, and Eugene Odum16 describe a model which approximates a whole-systems approach.They see four different loci or subsystems of sustainability: 1) farm fields where agronomic factors are paramount; 2) the farm unit wherein micro-economic concerns are primary; 3) the regional physical environment where ecological factors are central; and 4) national and international economies where macroeconomic issues are most important.

Their model demonstrates that focusing on only one level of the agricultural system neglects others that are equally essential.A whole-systems perspective fosters an understanding of complex interactions and their diverse ramifications through- out agriculture and the systems with which it articulates.This understanding is at the root of sustainability.Vernon Ruttan17 describes an ever-widening comprehension of “whole system” as he delineates three waves of social concerns which have arisen about natural resource availability, environmental change, and human well-being.In the late 1940s and early 1950s the first wave focused on whether resources such as land, water, and energy were sufficient to sustain economic growth.The second wave, in the late 1960s and early 1970s, focused on the effect of growth-generated pollution on the environment.The most recent concerns, manifest since the mid-1980s, also center on adverse environmental effects, but the key distinction is the transnational issues such as global warming, ozone depletion, and acid rain.As agriculture and its impacts become increasingly globalized, the need for a whole-systems perspective, particularly in terms of decision-making, become increasingly critical.Dahlberg 9 observes that although the impacts of modern industrial society are global, the data and analytical tools we use to assess those impacts are limited by national, disciplinary, or sectoral boundaries.Our educational and research institutions tend to mirror this shortcoming,with the result that the larger system contexts of research questions are infrequently investigated and poorly understood.Difficulties in apprehending and resolving problems whose constituents are grounded in several interrelated systems are compounded by the international community’s disparate, competitive political and economic systems.Nations act to promote their own priorities but affect, often negatively, globally shared resources and globally interdependent societies.Although nations and other sociopolitical groups generate impacts beyond their borders, they are generally incapable or unwilling to assess and react equitably to the results of their actions.Pierre Cross on and Norman Rosenberg 18 note the inadequacy of information feedback about significant environmental problems in modern societies, an inadequacy which characterizes feedback about social problems as well.

Accounting for the system-wide implications of local actions should be a primary objective for sustainable agricultural systems.The tools to facilitate such an accounting can only be developed within a whole-systems perspective.We believe it is inadequate to exclude social justice as a priority and that there is an ethical requirement for greater equity in the agricultural system.Some have combined concern for how we treat the environment with how we treat our fellow human beings.For those focusing on the latter, it is essential to look beyond sustaining our environmental and economic ability to produce agricultural goods.It is equally important to ensure that those goods are produced and distributed in an equitable manner.A concern with this human values aspect of agriculture involves a sweeping rather than localized concept of who constitutes “us.” Typically, resource conservation is dis- cussed in terms of its implications for farmers’ profit- ability or our descendants’ food-producing capabilities.The sustainability definition offered in this paper does not limit equity considerations to these groups.A concern with equitable social relations in agriculture requires defining “us” in terms of all fellow humans – not only farmers and future generations, but also farm workers, consumers, non-farm rural residents, Third World urban poor, and others.Sustainability in this sense is framed in terms of both inter generational and intragenerational equity.Thus, issues such as farm worker rights and inner-city hunger are as central as issues of soil erosion and groundwater contamination to the goals of agricultural sustainability.One of the most profound challenges facing agriculture is creating a decision-making process which will fairly resolve equity issues.Such a process must assess competing interests; evaluate agriculture’s costs and benefits,nft channel and the recipients of each; decide fairly what the compromises must be; recognize and encourage shared goals and common ground.In most discussions of sustainability either environmental quality or social justice issues are emphasized, but neither can be sup- ported wholly at the expense of the other.Nourishing humans, ensuring social justice, and providing a reasonable quality of life cannot be accomplished if agriculture’s resource base and environmental constraints are neglected.Likewise, few would argue that environmental considerations should be pursued at the expense of satisfying basic human needs.An equitable agricultural system must foster a decision-making process which is truly democratic, one which identifies not only what the costs and benefits are but how to distribute them fairly among all sectors of society.Many sustainability definitions, particularly those which guide applied sustainable agriculture programs, are based on the primacy of farm production and short-term profitability.

As sustainable agriculture programs have increasingly been incorporated into long-established agricultural institutions they have manifested the largely unquestioned intellectual assumptions and infrastructural constraints which characterize their parent institutions.This is problematic because conventional agricultural institutions have fostered many technologies and policies counter to sustainable agriculture goals.23 Such institutions have, for example, contributed to concentration within agriculture; have not generally benefited agricultural labor; and have systematically failed to examine their impact on the environment, the structure of rural households and communities, and the consequences of rural resident displacement.24 To situate new pro- grams designed to address these problems within the framework which produced them is of questionable value unless steps are taken to change the nature of that framework, for it determines the way its re- searchers see the world, pose questions, and define problems.When agriculture is viewed in a whole-systems context and sustainability is defined comprehensively, it is clear why the current popular focus on farm production practices is insufficient for achieving agricultural sustainability.Developing non-chemical pest management methods, for example, will effectively reduce pesticide use only if economic structures and policies encourage their adoption by farmers.More importantly, one cannot conclude that improved production practices will transform the agricultural system into one that meets all environmental, economic, and social sustainability goals.Social goals must be addressed explicitly.This is why production techniques such as organic farming, while a likely component of a sustainable food and agricultural system, cannot be thought of as synonymous with sustainable agriculture.Given the conventional institutional context of most state and federal sustainable agriculture programs it is not surprising that they tend to focus research on conventional priorities such as production practices and efficiency and have not, for the most part, aggressively addressed social and economic issues.Sustainability priorities – and the definitions which embody them – must be expanded to encompass the many factors affecting production and distribution as well as the larger environmental, economic, and social systems within which agriculture functions.This has been the focus of the Agroecology Program since its inception in 1982.Through conferences and publications* we have worked to expand the discussion and practice of integrating these aspects of sustainability.

Recently, the University of California Sustainable Agriculture Research and Education Program has broadened its agronomic focus to include social, economic, and policy issues.SAREP defines sustain- able agriculture as integrating “…three main goals – environmental health, economic profitability, and social and economic equity.”Their grant program, which encourages research and education on social, economic, and public policy issues affecting food and agriculture, could become a model for other sustain- able agriculture programs such as LISA.We believe that it is important to continue exploring the meaning of agricultural sustainability.Before an improved agricultural system can be developed the biases and structures that have led to agricultural problems must be closely examined and concrete goals articulated, based upon a broadened concept of agricultural sustainability.The concept of sustainability offered in this paper emphasizes that social goals are as important as environmental and economic goals, and widens the opportunity to move beyond the narrow agricultural priorities expressed in the past.It is based upon the whole-systems, interactive nature of all aspects of the agricultural system – that problems and their resolutions must be conceived not only in terms of their immediate time frames and local impacts, but just as importantly, in terms of their future time frames and their global impacts.It encourages emphasis on optimum production over maximum production, the long term along with the short term, the public’s best interest over special interests, and the contextualization of disciplinary work within interdisciplinary frameworks.Our hope is that this definition helps advance the discussion on developing a food and agriculture system that is sustainable for everyone.Global warming attributed to the anthropogenic emissions of greenhouse gases has increased the global temperature by ∼0.89 °C in the 20th century.Approximately 13% of total GHG emissions were contributed from agricultural lands and N2O emission from agriculture accounted for 61% of total anthropogenic N2O emissions.

The limited extent of ownership change may have limited the effects found in this study

Measuring costs per unit of output, the authors find that privatization increased the efficiency of firms operating in both competitive and non-competitive environments, and that the efficiency gains from privatization were significantly greater in non-competitive environments than in competitive ones.These results provide a uniquely controlled setting in which to study the effect of competition on relative efficiency, and also the relative importance of agency issues and soft budget constraint issues in publicly-owned firms.Since public firms should become less relatively less efficient than prive firms as competition increases, because soft budget constraints shield them from competitive pressures, and relatively more efficient as competition increases, because the observable performance of other firms reduces agency issues, the fact that efficiency gains from privatization attenuated with the level of competition provides evidence that the effects of agency issues dominated the effects of soft budget constraints in this study.The study also documents the existence of subsidies to public firms prior to privatization – amounting to 12.7% of GDP in Mexico – suggesting that reductions in agency-related issues due to competition had to surmount substantial soft budget constraint issues that presumably increased with the level of competition that firms faced.Because La Porta and Lopez-de-Silanes separates ownership effects by competition level, examines a large number of firms, and is exceptionally careful and thorough in its approach, it is one of the most persuasive studies in providing evidence of the effects of competition on ownership efficiency.The vast majority of studies that examine public and private efficiency differences in noncompetitive settings are studies of privatization efforts that compare the performance of enterprises before and after state ownership.

A complication in studying privatization programs is that ownership effects could take place gradually,nft hydroponic and might not be adequately captured just after privatization takes place.Additionally, the announcement of a government’s intentions to privatize sometimes preceded the actual transfer of ownership by several years, during which the perception of ownership transferrability and a period of “shake-out”could increase public firm efficiency.Lastly, privatization programs are typically accompanied by other regulatory changes – in particular, many governments shielded state-owned firms from competition, and undertook market liberalization measures either concurrently with privatization, or after a grace period during which newly privatized firms are shielded from competition.Unless these liberalization effects are separated, studies may compare public monopolies to private firms operating with limited competition, and thus conflate the effects of competition and ownership on efficiency.Of the 9 studies in non-competitive environments in our review, 5 study privatizations of telecommunications firms.Within this industry, Wallsten and Boylaud and Nicoletti both find no ownership effects from privatization, while Ros , Ramamurti , and Boles de Boer and Evans find that private firms are more efficient than state-owned firms.Wallsten studies the privatization of telecom monopolies in 30 countries across Africa and Latin America, from 1984 to 1997.Controlling for competition changes and other concurrent programs that may have affected firm efficiency, he finds no effect of privatization on labor productivity in the absence of additional regulatory measures.When privatized firms are faced with price regulation from an independent regulator, though, privatization yields efficiency benefits.This result is consistent with theory: By keeping prices low, regulators essentially create the pressure for efficiency that competition does, which differentially affects private firms if public firms face soft budget constraints.

Boylaud and Nicoletti study telecom privatizations in 23 OECD countries from 1991 to 1997, and similarly conclude that ownership did not affect labor productivity, when controlling for the level of competition and also the time to liberalization.However, both the number of competitors and decreases in the time to liberalization are associated with increases in productivity.The authors interpret the effects of time to liberalization as being due to the effects of potential competition, which may have stimulated managers and employees in public firms to increase efforts to avoid unemployment as profit margins were reduced.Such responses may be partially attributable to an anticipated reduction in cross subsidization across internal groups, which the authors describe as common prior to privatization.However, diminished agency issues would only occur when actual competitors emerged, and the separately significant effect of the number of competitors provides evidence that agency issues are important.Notable in this study is the fact that the government “generally maintained the largest single share of the PTOs capital and sometimes retained special voting rights in the privatised enterprises.”Indeed, some studies find that ownership change is only effective when firms are fully privatized.Ros , Ramamurti , and Boles de Boer and Evans all find productivity improvements in telecom firms following privatization.Ros studies a mix of firms that were either privatized during the period from 1986 to 1995, or were private throughout the period, and measures ownership effects on labor productivity while controlling for competition.Ramamurti finds significant ownership effects in 3 of 4 telecoms studied, but does not separate competition and ownership effects, and acknowledges that the level of competition may have changed after privatization.Boles de Boer and Evans provide a case study of the 1990 privatization of Telecom New Zealand, and study efficiency changes during the period from 1987, when the market was liberalized, to 1993, when the first actual competitors entered.

As a case study, the evidence the auhtors present is inherently less generalizable than that of other studies.On the other hand, the authors are less restricted to use variables that are common across all firms being studied, and can be precise about the levels of competition and other contextual details of the privatization.The study measures productivity as the level of output per cost of inputs, where inputs include labor, material inputs, and capital.They find that productivity increased by 10% per year during the study period, and that unit costs reduced by 5.8% per year.Like Ramamurti , the authors do not separate the effects of competition and ownership in their examination; however, competitors only emerged in the final year of the study, and potential competition due to deregulation was present throughout.A concern permeating all the telecom studies is that the effects of ownership are averaged across both the monopoly conditions and conditions of limited competition following market liberalization, making it impossible to isolate the precise market conditions under which these effects occur.Caves and Christiansen provides some evidence on ownership effects in a static competitive environment, by comparing two Canadian railroads – one private, one state owned – who were each other’s sole competitors for many decades.Measuring the cost of inputs per unit of output, they find that the state-owned railroad was initially less productive than the private one, but find no significant differences between the two by the end of the 19- year study period.Since the railroads began to compete 30 years prior to the study period, their findings suggest that efficiency improvements may take a very long time to adjust to a change in the level of competition.Assuming this is true, the privatization studies that average efficiency effects across short periods of time during which monopolies were exposed to competition may be best placed as studies reporting relative efficiencies under monopoly conditions.Both Caves and Christiansen and Ramamurti make another contribution to the analysis: While they both study railroads that faced little or no direct competition , both argue that the railroads they study faced substantial indirect presure from other forms of transportation that competed for both passengers and freight.Ramamurti explicitly documents the market share of the Argentinian railroad he studies, and finds that only 8% of freight and intercity travel were handled by the railroad, along with 15-20% of suburban travel.Since ameliorating agency issues requires the observation of direct competitors, both studies exist in a non-competitive environment for agency purposes.However, indirect competitive pressure reduced prices and profit margins, and thus expand the efficiency gap between public and private firms due to soft budget constraints.With both unmitigated agency issues and exacerbated soft budget constraint issues, theory would predict the efficiency gap between these railroads to be at their largest.

Indeed, Ramamurti finds that privatization resulted in a 370% increase in labor productivity,nft system and explicitly documents the existence of railroad subsidies to the state-owned Argentinian railroad prior to privatization.Caves and Christiansen, who paradoxically find no significant differences by the end of their study, also point out that the state’s role was “restricted to that of a stockholder”in their study – no subsidies were provided to the state owned railroad.Both of these studies point to the potential relevance of state subsidies in reducing efficiency gains, particularly in environments where firms face substantial competitive pressure.Ehrlich et al conduct a very careful study of 23 airlines with varying ownership types, and estimate a model wherein productivity is endogenously and separately determined for each airline.The authors include several robustness checks using alternate specifications, and do not consistently find level differences between the cost efficiencies of private and public airlines across all specifications.However, they find that private firms have a relatively higher rate of cost reduction over time in each specification that they test.To examine whether ownership effects vary with competition levels, the authors separately test the efficiency of the subset of airlines in the US, Canada, France, and the UK, arguing that that they exist in competitive environments because there are more domestic competitors within these nations.Although the authors find qualitatively similar results for these airlines, it is unclear whether airlines in those four countries might not face very different competitive environments from airlines that are the sole carriers for their countries, to the extent that airlines compete internationally, and also because – as the authors themselves point out – the International Air Transport Association coordinated fares and erected barriers to entry for all airlines during the period of study.Also notable in this study is the fact that both private and public airlines have historically been subject to soft budget constraints via “bailouts”,so that state-owned airlines may not be subject to a widened efficiency gap at higher competition levels in this industry.Funkhouser and MacAvoy study firms in a variety of industries in Indonesia, and compare their efficiencies by computing the ratio of each firm’s average costs to the appropriate industry average.Although they find no differences at the 5% level, private firms are significantly more efficient at the 10% level.Cullinane, Song, and Gray use a method that is increasingly popular in the recent literature to estimate cost efficiency: stochastic production frontier function estimation.Rather than looking at the cost of producing a unit of each output separately, or creating an index to evaluate the cost of all outputs simultaneously, the method establishes an efficient frontier of production using the data available, and evaluates each firm’s efficiency based on its distance from the frontier.The authors study 15 container ports in Asia, and find no significant differences in efficiency based on ownership.Of the 7 studies reviewed that study competitive environments, only 3 found that private firms were more efficient than state-owned firms.Of those 3, Vining and Boardman and Diboky both used measures of efficiency that are sensitive to revenue gains; it is unclear whether the measures used in Chen and Yeh are price-sensitive or not.As the evidence in Section 1.3.1 suggests, the efficiency of private firms may be overstated using price-sensitive measures, when markets are not highly competitive.Diboky and Chen and Yeh are similar in other respects.Both studies use Data Envelopment Analysis to estimate the technical efficiency of public and private firms that contemporaneously exist over the study period.Diboky studies results for 300 insurance firms in Germany that compete directly with each other; Chen and Yeh examine 34 domestic banks in Taiwan that face additional competition from 67 banks that are partially foreign-owned.Diboky measures firm “outputs”as gross premiums and net income, while Chen and Yeh measure quantities of loan services and portfolio investment.Chen and Yeh find that private banks outperform public banks; Diboky finds that public banks were substantially less efficient than either private or “mutual”banks of mixed public and private ownership.Vining and Boardman study a variety of industries whose four-firm concentration ratios vary from 14% to 43%, suggesting that the competitive environment in their study bordered on monopolistic competition, by the standards of this review.In such an environment, their use of efficiency metrics such as sales per employee and sales per asset may have caused private firms to appear more efficient than state-owned firms for reasons of higher prices, rather than lower unit costs.

Agricultural pesticides are often detected in rural homes

A related anaerobic process is nitrate-dependent iron oxidation; a recent review has highlighted, in the context of this process, how the simultaneous presence of nitrate-reducing and iron-reducing areas can potentially be important to nitrogen cycling.Under anaerobic conditions, iron can also be linked to ammonium oxidation.If reactions that generate N2O are active in any of the above processes, they may be stimulated or suppressed by different forms of iron, such as the two indices examined in this study.The degree of this influence under different conditions will then determine the importance of iron relative to other soil properties.Our treatments consisted of two contrasting values for soil moisture and addition of amendments.This was done in order to explore the importance of iron across a wide range of conditions while at the same time avoiding a cumbersome dataset.It is clear from Figure 1 that the importance of iron can change between the two limits of each treatment variable.For example, between 50 and 100% WHC under ammonium fertilization, iron moves from a position of modest relevance to become the highest-ranked driver.Since our results show the importance of iron only at two distinct values, we do not know how its importance under intermediate conditions changes between the two end values.Even without such intermediate data, the differences between contrasting treatments can aid in understanding the mechanisms at work in generating N2O.In the above example, the importance of iron rises markedly under ammonium fertilization as soil moisture increases from 50 to 100% WHC; FeP surpasses FeA in strength as well.

As mentioned earlier, ammonia is oxidized to hydroxylamine, and this can react with iron to produce N2O.In a wetter soil,dutch buckets solutes are more mobile, which can lead to greater production of hydroxylamine as well as greater contact of hydroxylamine with iron.FeP is also likely to be more soluble than FeA.Any combination of these effects might elevate the importance of iron and change which form is more relevant in explaining the associated N2O data.The overall position of iron among other drivers of N2O emission is determined by both its reactivity and the presence of processes subject to its influence.Ample opportunity for inquiry exists for defining the extent of the relationship between iron and N2O in managed as well as unmanaged ecosystems, and this can provide useful practical and theoretical information.For example, including iron in current models of N2O emission may strengthen their predictive ability.In addition, inasmuch as certain indices of iron can be related to its physical or chemical characteristics, observing the relationship between a given index and N2O production, and how this changes under different conditions, may provide insight into the specific reactions at work.As stated earlier, production of N2O is generally accepted to be a microbial affair, and it is logical to assume that the factors that regulate the activity of N2O-producing microorganisms should be the same factors that regulate N2O production.This is not incorrect, but is perhaps a somewhat restrictive rendering; a more accurate framework might include ‘‘biotic-abiotic reaction sequences’’that generate N2O, such as those outlined above.Indeed, ‘‘the complex interactions that occur between microorganisms and other biotic and abiotic factors’’ have been suggested to be a key part of further understanding greenhouse gas production and improving predictions.Pesticide drift, which is the off-target movement of pesticides, is recognized as a major cause of pesticide exposure affecting people as well as wildlife and the environment.In the United States in 2004, > 1,700 investigations were conducted in 40 states because of drift complaints, and 71% of the incident investigations confirmed that drift arose from pesticide applications to agricultural crops.Pesticide drift has been reported to account for 37–68% of pesticide illnesses among U.S.agricultural workers [California Department of Pesticide Regulation 2008; Calvert et al.2008].Community residents, particularly in agricultural areas, are also at risk of exposure to pesticide drift from nearby fields.

Alarcon et al.reported that 31% of acute pesticide illnesses that occurred at U.S.schools were attributed to drift exposure.The occurrence and extent of pesticide drift are affected by many factors, such as the nature of the pesticide 2010], equipment and application techniques , the amount of pesticides applied, weather , and operator care.Pesticide applicators are required to use necessary preventive measures and to comply with label requirements to minimize pesticide drift.Pesticide regulations such as the Federal Insecticide, Fungicide, and Rodenticide Act and EPA’s Worker Protection Standard require safety measures for minimizing the risk of pesticide exposure , and many states have additional regulations for drift mitigation.Better understanding about the magnitude, trend, and characteristics of pesticide poisoning from drift exposure of agricultural pesticides would assist regulatory authorities with regulatory, enforcement, and education efforts.The purpose of this study was to estimate the magnitude and incidence of acute pesticide poisoning associated with pesticide drift from outdoor agricultural applications in the United States during 1998–2006 and to describe the exposure and illness characteristics of pesticide poisoning cases arising from off-target drift.We also examined factors associated with illness severity and large events that involved five or more cases.Participating surveillance programs identify cases from multiple sources, including health care providers, poison control centers, workers’ compensation claims, and state or local government agencies.They collect information on the pesticide exposure incident through investigation, interview, and medical record review.In California, on some occasions, such as large drift events, active surveillance is undertaken for further case finding by interviewing individuals living or working within the vicinity affected by the off target drift.Although the SENSOR-Pesticides program focuses primarily on occupational pesticide poisoning surveillance, all of the SENSOR-Pesticides state programs except California collect data on both occupational and nonoccupational cases.In California, PISP captures both occupational and nonoccupational cases.SENSOR Pesticides and PISP classify cases based on the strength of evidence for pesticide exposure, health effects, and the known toxicology of the pesticide and use slightly different criteria for case classification categories.This study restricted the analyses to cases classified as definite, probable, possible, or suspicious by SENSOR-Pesticides and definite, probable, or possible by PISP.

We also performed analyses restricted to definite and probable cases only.Because the findings from these restricted analyses were similar to those that included all four classification categories , only the findings that used the four classification categories are reported here.In this study, a drift case was defined as acute health effects in a person exposed to pesticide drift from an outdoor agricultural application.Drift exposure included any of the following pesticide exposures outside their intended area of application: a) spray, mist, fumes, or odor during application; b) volatilization, odor from a previously treated field, or migration of contaminated dust; and c) residue left by offsite movement.Our drift definition is broader than U.S.EPA’s “spray or dust drift” definition, which excludes post application drift caused by erosion, migration, volatility, or windblown soil particles.A drift event was defined as an incident where one or more drift cases experienced drift exposure from a particular source.Both occupational and nonoccupational cases were included.An occupational case was defined as an individual exposed while at work.Among occupational cases, agricultural workers were identified using 1990 and 2002 Census Industry Codes : 1990 CICs, 010, 011, 030; 2002 CICs, 0170, 0180, 0290.Figure 1 presents the process of case selection.We selected cases if exposed to pesticides applied for agricultural use including farm, nursery, or animal production, and excluded cases exposed by ingestion, direct spray, spill, or other direct exposure.We then manually reviewed all case reports and excluded persons exposed to pesticides used for indoor applications , persons exposed within a treated area , and persons exposed to pesticides being mixed, loaded, or transported.Drift cases therefore represented the remaining 9% and 27% of all pesticide illness cases identified by the SENSOR-Pesticides and PISP, respectively.We also searched for duplicates from the two programs identifying California cases.Because personal identifiers were unavailable, date of exposure, age, sex, active ingredients, and county were used for comparison.A total of 60 events and 171 cases were identified by both California programs.These were counted only once and were included only in the PISP total.Drift events and cases were analyzed by the following variables: state, year, and month of exposure, age, sex, location of exposure, health effects, illness severity,grow bucket pesticide functional and chemical class, active ingredient, target of application, application equipment, detection of violations, and factors contributing to the drift incident.U.S.EPA toxicity categories ranging from toxicity I to IV were assigned to each product.

Cases exposed to multiple products were assigned to the toxicity category of the most toxic pesticide they were exposed to.Illness severity was categorized into low, moderate, and high using criteria developed by the SENSOR Pesticides program.Low severity refers to mild illnesses that generally resolve without treatment.Moderate severity refers to illnesses that are usually systemic and require medical treatment.High severity refers to life-threatening or serious health effects that may result in permanent impairment or disability.Contributing factors were retrospectively coded with available narrative descriptions.One NIOSH researcher initially coded contributing factors for all cases.Next, for SENSOR-Pesticides cases, state health department staff reviewed the codes and edited them as necessary.Any discrepancies were resolved by a second NIOSH researcher.For PISP cases, relatively detailed narrative descriptions were available for all incidents.These narratives summarize investigation reports provided by county agriculture commissioners, who investigate all suspected pesticide poisoning cases reported in their county.After initial coding, the two NIOSH researchers discussed those narratives that lacked clarity to reach consensus.Data analysis was performed with SAS software.Descriptive statistics were used to characterize drift events and cases.Incidence rates were calculated by geographic region, year, sex, and age group.The numerator represented the total number of respective cases in 1998–2006.Denominators were generated using the Current Population Survey micro-data files for the relevant years.For total and nonoccupational rates, the denominators were calculated by summing the annual average population estimates.A nonoccupational rate for agriculture-intensive areas was calculated by selecting the five counties in California where the largest amounts of pesticides were applied in 2008.For occupational rates, the denominators were calculated by summing the annual employment estimates including both “employed at work” and “employed but absent.” The denominator for agricultural workers was obtained using the same 1990 and 2002 CICs used to define agricultural worker cases.Moreover, in California, where data on pesticide use are available, incidence was calculated per number of agricultural applications and amount of pesticide active ingredient applied.Incidence trend over time was examined by fitting a Poisson regression model of rate on year and deriving the regression coefficient and its 95% confidence interval.Drift events were dichotomized by the size of events into small events involving < 5 cases and large events involving ≥ 5 cases.This cut point was based on one of the criteria used by the CDPR to prioritize event investigations.Illness severity was dichotomized as low and moderate/high.Simple and multi-variable logistic regressions were performed.Odds ratios and 95% CIs were calculated.To our knowledge, this is the first comprehensive report of drift-related pesticide poisoning in the United States.We identified 643 events involving 2,945 illness cases associated with pesticide drift from outdoor agricultural applications during 1998–2006.Pesticide drift included pesticide spray, mist, fume, contaminated dust, volatiles, and odor that moved away from the application site during or after the application.

Although the incidence for cases involved in small drift events tended to decrease over time, the overall incidence maintained a consistent pattern chiefly driven by large drift events.Large drift events were commonly associated with soil fumigations.Occupational exposure.Occupational pesticide poisoning is estimated at 12–21 per million U.S.workers per year.Compared with those estimates, our estimated incidence of 2.89 per million worker-years suggests that 14–24% of occupational pesticide poisoning may be attributed to off-target drift from agricultural applications.Our study included pesticide drift from outdoor applications only and excluded workers exposed within the application area.Our findings show that the risk of illness resulting from drift exposure is largely borne by agricultural workers, and the incidence was 145 times greater than that for all other workers.Current regulations require agricultural employers to protect workers from exposure to agricultural pesticides, and pesticide product labels instruct applicators to avoid allowing contact with humans directly or through drift.Our study found that the incidence of drift-related pesticide poisoning was higher among female and younger agricultural workers and in western states.These groups were previously found to have a higher incidence of pesticide poisoning.It is not known why the incidence is higher among female and younger agricultural workers, but hypotheses include that these groups are at greater risk of exposure, that they are more susceptible to pesticide toxicity, or that they are more likely to report exposure and illness or seek medical attention.However, we did not observe consistent patterns among workers in other occupations.This finding requires further research to identify the explanation.

Well-curated GGB databases play an important role in the data lifecycle by facilitating dissemination and reuse

The AgBioData consortium was formed in 2015 in response to the need for GGB personnel to work together to come up with better, more efficient database solutions. The mission of the consortium, comprised of members responsible for over 25 GGB databases and allied resources, is to work together to identify ways to consolidate and standardize common GGB database operations to create database products with more interoperability. FAIR principles have rapidly become standard guidelines for proper data management, as they outline a road map to maximize data reuse across repositories. However, more specific guidelines on how to implement FAIR principles for agricultural GGB data are needed to assist and streamline implementation across GGB databases. The results were used to focus and foster the workshop discussions. Here we present the current challenges facing GGBs in each of these seven areas and recommendations for best practices, incorporating discussions from the Salt Lake City meeting and results of the survey. The purpose of this paper is 3-fold: first, to document the current challenges and opportunities of GGB databases and online resources regarding the collection, integration and provision of data in a standardized way; second, to outline a set of standards and best practices for GGB databases and their curators; and third, to inform policy and decision makers in the federal government, funding agencies, scientific publishers and academic institutions about the growing importance of scientific data curation and management to the research community. The paper is organized by the seven topics discussed at the Salt Lake City workshop. For each topic, we provide an overview, challenges and opportunities and recommendations. The acronym ‘API’ appears frequently in this paper, referring to the means by which software components communicate with each other: i.e. a set of instructions and data transfer protocols.

We envision this paper will be helpful to scientists in the GGB database community, publishers, funders and policy makers and agricultural scientists who want to broaden their understanding of FAIR data practices.Biocurators strive to present an accessible,ebb flow tray accurate and comprehensive representation of biological knowledge . Biocuration is the process of selecting and integrating biological knowledge, data and metadata within a structured database so that it can be accessible, understandable and reusable by the research community. Data and metadata are taken from peer-reviewed publications and other sources and integrated with other data to deliver a value-added product to the public for further research. Biocuration is a multidisciplinary effort that involves subject area experts, software developers, bio-informaticians and researchers. The curation process usually includes a mixture of manual, semi-automated and fully automated workflows. Manual biocuration is the process of an expert reading one or several related publications, assessing and/or validating the quality of the data and entering data manually into a database using curation tools, or by providing spreadsheets to the database manager. It also encompasses the curation of facts or knowledge, in addition to raw data; for example, the role a gene plays in a particular pathway. These data include information on genes, proteins, DNA or RNA sequences, pathways, mutant and nonmutant phenotypes, mutant interactions, qualitative and quantitative traits, genetic variation, diversity and population data, genetic stocks, genetic maps, chromosomal information, genetic markers and any other information from the publication that the curator deems valuable to the database consumers. Manual curation includes determining and attaching appropriate ontology and metadata annotations to data. This sometimes requires interaction with authors to ensure data is represented correctly and completely, and indeed to ask where the data resides if they are not linked to a publication. In well-funded large GGB databases, manually curated data may be reviewed by one, two or even three additional curators.

Manual biocuration is perhaps the best way to curate data, but no GGB database has enough resources to curate all data manually. Moreover, the number of papers produced by each research community continues to grow rapidly. Thus, semi-automated and fully automated workflows are also used by most databases. For example, a species-specific database may want to retrieve all Gene Ontology annotations for genes and proteins for their species from a multi-species database like UniProt . In this case, a script might be written and used to retrieve that data ‘en masse’. Prediction of gene homologs, orthologs and function can also be automated. Some of these standard automated processes require intervention at defined points from expert scientist to choose appropriate references, cut off values, perform verifications and do quality checks. All biocuration aims to add value to data. Harvesting biological data from published literature, linking it to existing data and adding it to a database enables researchers to access the integrated data and use it to advance scientific knowledge. The manual biocuration of genes, proteins and pathways in one or more species often leads to the development of algorithms and software tools that have wider applications and contribute to automated curation processes. For example, The Arabidopsis Information Resource has been manually adding GO annotations to thousands of Arabidopsis genes from the literature since 1999. This manual GO annotation is now the gold standard reference set for all other plant GO annotations and is used for inferring gene function of related sequences in all other plant species . Another example is the manually curated metabolic pathways in Ecocyc, MetaCyc and PlantCyc, which have been used to predict genome-scale metabolic networks for several species based on gene sequence similarity . The recently developed Plant Reactome database has further streamlined the process of orthology-based projections of plant pathways by creating simultaneous projections for 74 species. These projections are routinely updated along with the curated pathways from the Reactome reference species Oryza sativa . Without manual biocuration of experimental data from Arabidopsis, rice and other model organisms, the plant community would not have the powerful gene function prediction workflows we have today, nor would the development of the wide array of existing genomic resources and automated protocols have been possible. Biocurators continue to provide feedback to improve automated pipelines for prediction workflows and help to streamline data sets for their communities and/or add a value to the primary data.

All biocuration is time consuming and requires assistance from expert biologists. Current efforts in machine learning and automated text mining to pull data or to rank journal articles for curation more effectively work to some extent, but so far these approaches are not able to synthesize a clear narrative and thus cannot yet replace biocurators. The manual curation of literature, genes, proteins, pathways etc. by expert biologists remains the gold standard used for developing and testing text mining tools and other automated workflows. We expect that although text-mining tools will help biocurators achieve higher efficiency, biocurators will remain indispensable to ensure accuracy and relevance of biological data. GGB databases can increase researchers’ efficiency, increase the return on research funding investment by maximizing reuse and provide use metrics for those who desire to quantify research impact. We anticipate that the demand for biocurators will increase as the tsunami of ‘big data’ continues. Despite the fact that the actual cost of data curation is estimated to be less than 0.1% of the cost of the research that generated primary data , data curation remains underfunded .Databases are focused on serving the varied needs of their stakeholders. Because of this, different GGB databases may curate different data types or curate similar data types to varying depths, and are likely to be duplicating efforts to streamline curation. In addition, limited resources for most GGB databases often prevent timely curation of the rapidly growing data in publications.The size and the complexity of biological data resulting from recent technological advances require the data to be stored in computable or standardized form for efficient integration and retrieval. Use of ontologies to annotate data is important for integrating disparate data sets. Ontologies are structured, controlled vocabularies that represent specific knowledge domains . Examples include the GO for attributes of gene products such as subcellular localization, molecular function or biological role,flood and drain tray and Plant Ontology for plant attributes such as developmental stages or anatomical parts. When data are associated with appropriate ontology terms, data interoperability, retrieval and transfer are more effective. In this section, we review the challenges and opportunities in the use of ontologies and provide a set of recommendations for data curation with ontologies.To identify current status and challenges in ontology use, an online survey was offered to AgBioData members. The survey results for ontology use in databases for each data type are provided in Table 1 and a summary of other survey questions such as barriers to using ontologies are provided in the supplementary material 1. In addition, the ways ontologies are used in data descriptions in some GGB databases are described in supplementary material 2. To facilitate the adoption of ontologies by GGB databases, we describe the challenges identified by the survey along with some opportunities to meet these challenges, including a review of currently available ontologies for agriculture, ontology libraries and registries and tools for working with ontologies.

A key component of FAIR data principles is that data can be found, read and interpreted using computers. APIs and other mechanisms for providing machine-readable data allow researchers to discover data, facilitate the movement of data among different databases and analysis platforms and when coupled with good practices in curation, ontologies and metadata are fundamental to building a web of interconnected data covering the full scope of agricultural research. Without programmatic access to data, the goals laid out in the introduction to this paper cannot be reached because it is simply not possible to store all data in one place, nor is it feasible to work across a distributed environment without computerized support. After a brief description of the current state of data access technology across GGB databases and other online resources, we more fully describe the need for programmatic data access under Challenges and Opportunities and end with recommendations for best practices. Sharing among AgBioData databases is already widespread, either through programmatic access or other means. The results of the AgBioData survey of its members indicate that GGB databases and resources vary in how they acquire and serve their data, particularly to other databases. All but 3 out of 32 GGB databases share data with other databases, and all but two have imported data from other database. Some make use of platforms, such as Inter Mine , Ensembl and Tripal , to provide programmatic access to data that is standard within, but not across the different options. Other databases develop their own programmatic access or use methods such as file transfer protocol . Finally, some databases provide no programmatic access to data. A number of infrastructure projects already exist that support AgBioData data access needs, most of which have been adopted to some degree by different GGB platforms . A more recent approach to facilitate data search, access and exchange is to define a common API that is supported by multiple database platforms. An example of this is BrAPI , which defines querying methods and data exchange formats without requiring any specific database implementation. Each database is free to choose an existing implementation or to develop its own. However, BrAPI’s utility is restricted to specific types of data. Alternatively, the Agave API provides a set of services that can be used to access, analyse and manage any type of data from registered systems, but is not customized to work with GGB databases.Aside from primary repositories like GenBank, model organism and specialty databases remain the primary means of serving data to researchers, particularly for curated or otherwise processed data. These databases represent different community interests, funding sources and data types. They have grown in an ad hoc fashion and distribute data in multiple formats, which are often unique to each database and are may be without programmatic access. Below, we lay out some of the challenges and opportunities in programmatic data access faced by GGB researchers using the current landscape of databases. Exploration of these use cases yielded a set of common data access requirements under five different themes, summarized in Table 7.Large comparative genomic portals exist but have limitations in their utility for specialized communities, such as not incorporating data from minor crop species or crop wild relatives or rarely handling multiple genomes for the same species.

Young women were clearly identified as high-risk targets for SH

Gender harassment was reported by 30% of female crew members, of which 9% also reported unwanted sexual attention and 1% reported sexual coercion. The relative prevalence of these SH categories mirrored the pattern in prior California studies, although the rates of workers reporting SH in our study were considerably lower than the rates reported in those studies . This may be explained by regional and crop-specific differences. For example, working conditions in Napa vineyards are generally considered better than those in other agricultural sectors, with workers offered above average wages and benefits . Additionally, we considered harassment only at a worker’s current company, not throughout the worker’s overall agricultural or working career, which could have resulted in a lower reporting rate compared to previous studies. The low rates of unwanted sexual attention and sexual coercion in our study were far lower than those found in other studies. Such low rates reflect well on the Napa industry, but they may also, despite the anonymity of responses, indicate a reluctance among women to admit severe harassment when participating alongside co-workers and in a study coordinated as we did this one. The small number of women reporting unwanted sexual attention or sexual coercion meant we were not able to consider an analysis of the relationship between the severity of SH with the other variables measured. Instead, we focused on two types of group comparison based on the presence or absence of SH: women reporting any type of harassment versus women reporting no harassment, and crews where SH was reported versus crews where SH was absent . We analyzed average scores or counts except for crew gender ratio, SH awareness training and relatives in crew. For these three variables, we classified female participants into additional groups based on the percentage of females in a crew, the percentage of crew members that were SH-trained and the presence or absence of relatives in a crew. Thus, female participants were assigned either to a low-female group or a high-female group and either to a low-SH-trained group or to a high-SH-trained group , using a median split.

Descriptive data for harassed and non-harassed female participants show that harassed women in our study differed on two antecedent variables. As in other industries ,what is a vertical farm harassed women were significantly younger than non-harassed women; women under 40 years of age accounted for two-thirds of reported harassment cases in our study. Second, 89% of women reporting the more severe categories of harassment were seasonal employees. More female seasonal workers than permanent workers reported gender harassment, although this relationship was not statistically significant . Harassed and non-harassed women did not differ significantly in the presence of relatives on their crews, the duration of their employment, crew size, crew gender ratio or the number of members in their crew that had received SH awareness training . Harassed women had significantly higher turnover intentions and lower overall job satisfaction compared to non-harassed women, supporting prior research on the negative impact of SH on morale and worker productivity. We compared descriptive data for SH+ and SH− crews on hostile sexism and male work outcomes. Mean scores for hostile sexism were significantly higher in SH+ crews compared to mean scores in SH− crews, supporting the theory that sexist attitudes contribute to a climate of SH tolerance . This complemented our finding of a higher incidence of gender harassment over other types of SH. The hostile sexism questionnaire can thus be considered an attitudinal measure of the behavioral gender harassment component of the SEQ, as hostile sexist attitudes appeared to be enacted as behavioral harassment towards women workers. Turnover intentions for male members of SH+ were significantly higher and job satisfaction was lower than they were for males in SH− crews. We could not determine whether dissatisfied male workers were more likely to perpetrate SH or if witnessing SH adversely affected male workers; however, the latter has previously been concluded in other research .

We identified several variables associated with the presence of SH in agricultural work crews, and we demonstrated that SH is associated with a decline in work outcomes. The type of design we employed in this study cannot verify causation between variables, only association. However, these statistical associations, together with consideration of the literature on SH in other industries, provides grounds for healthy speculation as to how agricultural companies might address SH among their workers.The oldest woman reporting SH was 47; most harassed women in this sample were 40 years or younger. Despite the lack of statistical differences in SH incidence between seasonal and permanent female workers, the severe forms of SH were overwhelmingly reported by seasonal workers. While recognizing that all workers are at risk of SH, companies should therefore be especially vigilant of the risk to young and seasonal female workers.Changing the structure of work crews is unlikely to reduce SH. In our study, harassed women worked in crews that were large and small, with or without relatives, and with considerable variation in gender ratio. Harassed women were just as likely to be working on crews with a high percentage of females as on crews with a low percentage of females . This was unexpected, as meta-analyses have demonstrated gender ratios to be a significant predictor of SH . However, the gender ratio effect may be small, and as SH occurs in a range of organizational settings , the characteristics of SH perpetrators may be more important. For example, perpetrators in male dominated workplaces tend to be co-workers, whereas perpetrators in female-dominated workplaces are more likely to be supervisors . The questionnaire we used in our study did not ask women about the perpetrators, but the unimportance of crew gender ratio indicates the possibility that SH may have originated not only from inside the crews but from outside, such as from supervisors or other company employees. Our presumption that the crew level is the most relevant company unit for SH was too optimistic. We often observed multiple crews working in the same vineyard, and they often mixed during work breaks; SH could therefore have originated from other crews, especially as the SH reported in our study was primarily verbal and gestural in nature.

Crew membership was also probably more fluid than our study design conceived. Women were asked about SH only during their current employment, but these women did not necessarily work continually in the same crew configuration. If gender ratio is an important antecedent of SH in agriculture, we predict it will be at the level of the company rather than at the level of the work team.Our results, as supported by the literature , indicate that an improvement in organizational climate is a more effective method for tackling SH than a restructuring of work crews. The hostile sexist attitude of both men and women in a crew was significantly associated with the presence of SH. Companies can expect to reduce SH by changing or neutralizing these attitudes. However, shifting these attitudes may be difficult to accomplish, as indicated by our finding that previous SH awareness training was not related to a decrease in reported SH. Similar poor efficacy of SH awareness training has been reported in prior research , suggesting that improvements are needed to the structure and administration of awareness training for agricultural workers. Unless these changes are made, other organizational climate variables, such as the internal management of complaints and the overall social climate of a company , are more likely to be effective in reducing SH. There is still value in conducting training, as it has been shown to make women more likely to report SH and it makes workers more aware of what is acceptable behavior . Since we did not collect details on which training programs the workers received, we cannot comment on the efficacy of one training program over another. Harassed females reported lower job satisfaction and higher intention to quit their jobs, illustrating that SH is likely resulting in companies losing female workers and experiencing other negative effects associated with poor worker satisfaction. The same reduced outcomes were reported by male workers in crews where harassment was occurring, suggesting that SH may be impacting not only the targets but also the co-workers. Dissatisfaction among men as a result of SH thus also has the potential to negatively affect company performance. The current study demonstrated that workplace sexual harassment of female vineyard workers affects the well being and retention of all workers in an agricultural sector where there is a paucity of quantitative data on the issue. Furthermore, this study illustrated that female workers in entry positions to the industry are most at risk of SH, illustrating that SH is a barrier for women seeking to enter the agricultural workforce. Thus, SH has the potential to significantly affect the stability of the labor pool in a time of labor shortage and to incur economic costs not only for workers but also for agricultural organizations seeking to train and retain stable work crews. Incidence of SH in our study was lower than that previously reported for farm workers, but our results should be treated with some caution; there may have been some under reporting due to our method of data collection and our relatively small sample size. This study also measured SH in one region and one crop only, and incidence rates may not generalize to other agricultural regions and sectors. Workplace policies and practices that reduce or eliminate hostile sexist attitudes appear to have the most promise for reducing SH in agriculture. However,vertical strawberries vertical system accomplishing these goals with limited resources and within a company’s traditional organizational structure may be challenging.

Future studies may seek to consider in more detail how organizational climate can be effectively addressed in the agricultural sector, the effectiveness of different SH awareness programs and the characteristics of perpetrators of SH towards women. In response to a shift toward specialization and mechanization during the 20th century, there has been momentum on the part of a vocal contingent of consumers, producers, researchers, and policy makers who call for a transition toward a new model of agriculture. This model employs fewer synthetic inputs, incorporates practices which enhance biodiversity and environmental services at local, regional, and global scales, and takes into account the social implications of production practices, market dynamics, and product mixes. Within this vision, diversified farming systems have emerged as a model that incorporates functional biodiversity at multiple temporal and spatial scales to maintain ecosystem services critical to agricultural production. This essay’s aim is to provide an economists’ perspective on the factors which make diversified farming systems economically attractive, or not-so-attractive, to farmers, and to discuss the potential for and roadblocks to widespread adoption. The essay focuses on how a range of existing and emerging factors drive profitability and adoption of DFS, and suggests that, in order for DFS to thrive, a number of structural changes are needed. These include: 1) public and private investment in the development of low-cost, practical technologies that reduce the costs of production in DFS, 2) support for and coordination of evolving markets for ecosystem services and products from DFS and 3) the elimination of subsidies and crop insurance programs that perpetuate the unsustainable production of staple crops. This work suggests that subsidies and funding be directed, instead, toward points 1) and 2), as well as toward incentives for consumption of nutritious food. Each year, more than 50,000 people in the U.S. die from hospital-acquired bacterial infections, millions experience episodes of food borne illness, and reported cases of “superbugs” such as Methicillin-resistant Staphylococcus aureusand vancomyc in-resistant enterococci are on the rise. For those who acquire a resistant infection in their food, in their community, or in a hospital, resistance is associated with a longer duration of treatment, the use of more potent antibiotics, and longer hospital stays. This, in turn, means increased health care costs and costs to society due to antibiotic-resistant infections. Antibiotic resistance is contributing to the scope and severity of this health care crisis, and at least some of the responsibility for antibiotic resistance sits on the shoulders of industrial livestock production. In livestock operations, low or sub-therapeutic doses of antibiotics are used to promote growth, in addition to their use to prevent and control disease. Today, more antibiotics are used in livestock production and the production of milk and eggs than in humans. While the use of sub-therapeutic doses of antibiotics is regulated less stringently in the United States than in the European Union, there is movement toward and potential for such regulation.

Agricultural mechanization is the use of any mechanical technology and increased power to agriculture

The implication is that increases in agricultural production have to be met through increases in agricultural productivity, and less through expansion of cultivated area. Another worsening factor is the climate change and global warming. Some studies predict that global warming will significantly and negatively affect African agriculture. They also indicate that the use of irrigation reduces the harmful impact of global warming. In addition, irrigation use is a catalyst of improved technology adoption, which will have a substantial impact on food security.The author’s understanding of food security is informed by Sen’s entitlement theory. Farmer’s access to food can be seized either through the output markets or through increases in productivity levels and improvements in food storage. As elicited by the “sell low, buy high” puzzle, the mark-up is usually very high and a significant number of households in rural Mozambique may not afford to purchase food during the lean season. Therefore, it becomes crucial to enhance both agricultural productivity and farmer’s ability to store food. Selective mechanization, improved storage, and other improved agricultural technologies play an essential role in ensuring farmers’ food entitlements. Previous attempts to mechanize the agricultural sector in the post-colonial period have failed, one of the reasons being the 16-year civil war that started a year after the independence in 1975. Moreover, the government established tractor-hire schemes had serious planning,vertical grow shelf management, and training problems, denting the image of agricultural mechanization in general. Agricultural mechanization is also mistakenly perceived as tractor mechanization.

This includes the use of tractors, animal-powered and human-powered implements and tools , as well as irrigation systems, food processing and related technologies and equipment. Although not addressed in this paper, the use of jab planters has been shown to significantly reduce labor requirements. Information on the economic impact of selected improved agricultural technologies is needed to target interventions efficiently and equitably, and to justify investment in such technologies.This paper assesses the impact of improved agricultural technologies by constructing a counterfactual comparison group. In this setting, a comparison of the outcome variable is made between farmers using a given technology and their counterparts with similar observable co-variates .The use of tractor mechanization is significantly correlated with road infrastructure. The distance to the nearest tarred road is three times higher among households who did not use tractors, relative to their counterparts. Remarkably, among the 2 percent of the population that used a tractor, 49 percent accrues to Maputo province, and 32 percent to Gaza province, both located in the south, a region of relatively lower agricultural potential, but of better road infrastructure. The remaining 19 percent are distributed across the other 8 provinces, which includes agro-ecological zones of higher agricultural potential, but relatively poorer road infrastructure. Unsurprisingly, adoption rates rise with increases in both landholding size and livestock flocks for all four improved technologies. Households with larger landholdings will potentially have higher production and thus feel compelled to invest in improved granaries. The use of animal traction or tractor mechanization is also cost-effective in larger fields. Additionally, the adoption of animal traction and tractor mechanization require some initial investment, and asset endowment is positively and significantly correlated with household welfare.

With regard to access to credit, the difference between treated and untreated households was only significant for the adoption of tractor mechanization, and marginally significant for the use of animal traction. This result, however, is an artifact of a low data variation as not many households could access the emerging rural credit market. Furthermore, a tractor can be used as collateral, a bottleneck for many rural households in accessing to the credit market. Membership to farmers’ association is also significantly correlated with the use of improved agricultural technologies. The number of farmers using tractor mechanization is three times higher among members of an association. Similarly, there are twice as many farmers using improved seeds among members of a farmers’ association.Figures 1A through 4A show the distribution of propensity scores for all four technologies. Treated and untreated households overlap very well, suggesting that the overlap assumption is plausible. Additionally, the assessment of the overlap assumption was complemented by the analysis of normalized differences. The results are presented in Table 2, and they show that normalized differences are in general smaller than 0.25 . Exceptions are the variables on head’s age and tropical livestock units. However, this outcome did not affect the estimation results because these two variables were dropped from the stepwise logit model due to their low explanatory power. The results on the stepwise logit model are not reported to save space, but are available from the author upon request.Table 4 presents the estimation results of the impact of selected improved agricultural technologies, contrasting the results obtained through three econometric approaches. With the exception of animal traction, the impact of improved agricultural technologies is consistently positive and significantly different zero. The impact is greater for tractor mechanization, followed by the use of improved seeds, and finally the use of improved granaries. Farmers that used animal traction and experienced losses in 2004/05 agricultural season may be enticed to abandon such technology, especially if they rented the animals and the implements. This is probably one of the reasons why “adoption rates” of improved agricultural technologies are usually very low: some farmers abandon the technology after some unsuccessful adoption attempts. Policies to sustain adoption of improved agricultural technologies should be put in place. Irrigation investments fall in that category.The significance of improved granaries underscores the relevance of post-harvest losses, and reducing these losses potentially results in higher household income in light of opportunities for inter-temporal price arbitrage; and improved food entitlements and farmer’s nutritional status. The author speculates that the benefits from an improved granary might outstrip by far its construction costs, considering that it will be used for more than a year.

The impact of improved seeds on maize is about 2 000 Meticais/ha, and 5 180 Meticais/ha for tractor mechanization . The estimates of the impact can also be regarded as shadow prices. Specifically, during the 2004/05 agricultural season, the use of tractor mechanization would be profitable for the farmer whenever the market cost of hiring a tractor was below $212/ha. Likewise, the market price of improved maize seeds required to sow 1 hectare of maize should be lower than $80. Taking into account that mean household income in 2004/05 was about $137 per adult equivalent , and that less than 5 percent had access to credit, understanding why adoption of improved technologies is extremely low becomes trivial. Even if improved agricultural technologies were riskless, a bulk of farmers would not be financially capable of investing in such technologies, much less irrigation. There is certainly an ample scope to enhance the impact of improved seeds and tractor mechanization, considering that less than 5 percent use irrigation or inorganic fertilizers, and about half of the tractors used in Mozambique are located in Maputo province, and more than 3/4 of all tractors are located in the south. If the Mozambican government wants to achieve the much talked-about green revolution, then huge investments on basic infrastructure and irrigation may pave the way for higher adoption rates and profitability of improved agricultural technologies. The bad news is that climate change and global warming is a translucent reality, potentially with severe implications to African agriculture. In the Mozambican agriculture context, the implication is that any effort to foster adoption of animal traction, improved seeds, tractors, and other improved technologies should be accompanied by investments on irrigation or water conservation technologies. Furthermore, drought-tolerant improved seeds will also significantly increase both agricultural production and productivity amidst low irrigation use and recurrent drought spells across the country.Hundreds of reports and articles begin with a variation on the same apocalyptic exhortation: The combination of population growth, food price volatility,vertical hydroponic and climate change demands a new agricultural revolution to expand and secure the global food supply. The bio-technologies frst deployed in the Green Revolution are still being constantly improved; food prices, however, stay stubbornly high and many fear a yield plateau. The new revolution, they argue, is digital technology. In a recent article about the use of artifcial intelligence in agriculture, for example, Wired gushed about “an explosion in advanced agricultural technology, which Goldman Sachs predicts will raise crop yields 70 percent by 2050” . Goldman, for their part, estimate that digital agricultural technologies will become a $240 billion market by 2050 . X, Google’s “moonshot” venture, recently hailed the arrival of “the era of computational agriculture” . Traditional agribusinesses have found themselves competing with Silicon Valley giants, venture capitalists, scrappy startups, intergovernmental organizations, non-governmental organizations , and research institutions to develop and market a dizzying array of new technologies to feed “the next two billion” and save the world. “Digital agriculture” is a heterogeneous suite of information-rich, computationally-complex, and often capital-intensive methods for improving the efficiency of agricultural land and the profit margins of sectoral actors.

Digital technologies have come to play a role in every stage of the agricultural cycle under capitalism, from input management to marketing produce, pricing commodities futures to pest control. However, while it is true that these technologies increase efficiency, we contest the notion that they will provide a long-term solution to the looming crises of the global food system. For what the narrative of an agricultural techno-revolution elides is how the methods of industrialized food production create these challenges in the frst place. We interpret the rise of digital technologies in agriculture as the continuation of a process dating back to the Green Revolution, namely, to reconfigure agrarian life in a manner amenable to increased profits, especially for actors further up the value chain. For the proponents of digital agriculture, the transition is between two technologically-paved pathways to profit: innovations in high dimensional computing supersede innovations in breeding. A purely technological perspective is insufficient and depoliticizes analyses of far-reaching changes to agricultural production, changes which have an effect on the rest of the capitalist economy . Nevertheless, this has not stopped digital agriculture’s boosters from frequently claiming that it heralds a “fourth agricultural revolution.”1 However, digital agriculture has received limited critical attention from social scientists. The vast majority of critical work on the ascendancy of global technology mega-firms and new information-centric accumulation strategies looks at their effects in non-agrarian industrial and service sectors. However, the generation of profits in these sectors depends in part on keeping inputs for production and reproduction— like food—artifcially cheap . By perpetuating an unsustainable regime of cheap food, digital agriculture technologies support the continued expansion of an equally unsustainable global urban system.We argue that the rise of digital agriculture is emblematic of an intensifying relationship between zones of agrarian production and extraction on the one hand, and zones of agglomeration, industrial production, and service provision on the other. A body of neo-Lefebvrian scholarship describes these apparently distinct zones as co-constitutive, entangled in a dialectic of extended and concentrated urbanization . In this framework, the growth imperative of capitalism requires the transformation of vast landscapes beyond the ‘city’ to increase extraction and agricultural output, the product of which is drawn back inward to fuel growth. In this reading, the socio-metabolic process of urbanization is increasingly generalized, to the point that some have argued for thinking of contemporary urbanization as a ‘planetary’ process. With this in mind, this article interrogates the political economy of digital agriculture and reinterprets the digitalization of the food system through the lens of extended–concentrated urbanization. We begin by introducing digital agriculture and the limited social scientific literature on the topic. Next, we critique the mainstream rhetoric surrounding digital agriculture, which makes a Malthusian argument for the need to feed a burgeoning global population in the face of climate change. Then, beginning from the observation that the crucial role of information is under-analyzed in the extended–concentrated urbanization framework, we build a theoretical argument for how digital agriculture challenges the urban–rural binarism. We locate the framework’s origins as a reaction to earlier threads of globalization theory, which emphasized the supposedly immaterial nature and deterritorializing effects of information and communications technologies .

The data for workers in these sectors come from the March Current Population Survey

Apprehensions by the U.S. border patrols dropped from 876,803 in 2007 to 556,032 in 2009. Because immigrants often send money home, we can use remittances from the United States to Mexico to infer whether the number of immigrants changed substantially during a recession. Figure 2 shows quarterly remittances to Mexico in millions of U.S. dollars as reported by Banco de México . The figure shows that remittances increased during the relatively mild 2001 recession but decreased substantially during the 2008–2009 Great Recession. These data again support the view that the number of Mexican immigrants to the United States fell during the Great Recession but not during the previous, milder recession. Moreover, Warren and Warren estimated that the net change of undocumented immigrants was negative during the Great Recession, which was related to a sharp decrease of new undocumented immigrants. The United States Department of Agriculture, Economic Research Service estimated number of full- and part-time agricultural workers fell from 1.032 million in 2007 to 1.003 million in 2008 and 1.020 million in 2009, before rising to 1.053 million in 2010.5 That is, the number of workers in 2008 was 3% to 5% lower than in the years before and after the Great Recession. Presumably the share of workers dropped by even more in seasonal agriculture, which employs most of the undocumented workers.Our agricultural workers data comes from the National Agricultural Workers Survey.The NAWS is a national, random sample of hired seasonal agricultural employees, who work primarily in seasonal crops.The NAWS is an employer-based survey. That is, it samples worksites rather than residences to overcome the difficulty of reaching migrant farm workers in unconventional living quarters.

These employers are chosen randomly within the U.S. Department of Agriculture’s 12 agricultural regions .Surveyors randomly select 2,500 employees of these growers to obtain a nationally representative sample of crop workers. Surveyors interview the more than 2,500 crop workers outside of work hours at their homes or at other locations selected by the respondent. The NAWS has a long,vertical growers visible history within farming communities, and the survey design incorporates questions aimed at data validation about legal status. Respondents receive a pledge of confidentiality and a nominal financial incentive for participation. As a result, only one to two percent of workers in the overall sample refuse to answer the legal status questions. The NAWS contains extensive information about a worker’s compensation, hours worked, and demographic characteristics such as legal status, education, family size and composition, and workers’ migration decisions. We dropped workers from the sample who were missing any relevant variable, 23% of the original survey sample. The NAWS is conducted in three cycles each year year to match the seasonal fluctuations in the agricultural workforce. Unfortunately, the public-use data, which we use, suppresses information about the cycle and aggregates the 12 regions into 6 regions. As a result, our data set consists of repeated annual cross sections of workers from 1989 through 2012. Column 1 of Table 1 presents national summary statistics for the variables used in our empirical analysis. Columns 2 and 3 provide data for California and for the rest of the country, because 37% of the sample works in California. Compared to workers in the rest of the country, Californian workers tend to have less education; have more farm experience; are more likely to be non-native, Hispanics; and are more likely to work in fruit and nut crops and less likely to work in horticulture.

After analyzing the effects of recessions on agricultural workers, we replicate the analysis for workers in construction, hotels, and restaurants, which also employ many immigrants.In March of each year, workers in the basic CPS sample are administered a supplemental questionnaire in which they are asked to report their income such as hourly wage rate and additional labor force activity such as hours worked in the previous week.8 Because information on immigration is available only since 1994, our sample period is 1994–2013. We include all workers who are 18 years and older.Three recessions occurred during our 1989–2012 sample period . The economy recovered quickly from the first of these recessions in 1990–1991. The second, 2001 recession was also relatively mild. However, the third recession, the 2008–2009 Great Recession, was much more severe and had longer-lasting economic and labor market effects than the first two. We analyze the effects of recessions on hourly earnings, the probability of receiving a bonus, and weekly hours of work of employed workers. For workers paid by time, hourly earnings are a worker’s hourly wage. For piece-rate workers, we use the workers’ reported average hourly earnings. The bonus dummy equals one for workers who receive a money bonus from an employer in addition to the wage, and zero otherwise. Weekly hours of work are the number of hours interviewees reported work at their current farm job in the previous week. The explanatory variables in all these equations are the same. The explanatory variables include all the usual demographic variables: age, years of education, years of farm experience, job tenure , gender, whether the workers is Hispanic, whether the worker was born in the United States, and whether the worker speaks English.The specification uses a legal status variable to capture the bifurcated labor markets for documented and undocumented workers. It also includes crop and regional dummies.

We have seven main explanatory variables: dummies for each of the three recessions, the recession dummies interacted with the legal status dummy , and regional unemployment rates for workers in all sectors of the economy. We use separate dummies for each recession to allow for differential effects across the recession . The interaction terms capture whether employers treat undocumented workers differently than legal workers during a recession. We include the unemployment rate because it peaks after the end of each recession . We do not report the unemployment rate interacted with the undocumented dummy because we cannot reject that its coefficient is zero in any equation. We treat all these variables as exogenous to the compensation and weekly hours of individual agricultural workers. We start by examining the effects of recessions on NAWS workers’ hourly earnings. Column 1 of Table 2 presents regression estimates for the ln hourly earnings equation. The coefficients on the demographic variables have the expected signs and are generally statistically significantly different from zero at the 5% level. Undocumented workers’ hourly earnings are 2.1% less than those of documented workers. Females earn 6.4% less than males. Hispanics earn 4.9% less than non Hispanics. Unlike most previous studies, we find a statistically significant effect of education. English speakers earn 3.9% more than non-English speakers. The coefficients on the recession dummies reflect the effect of the recession on documented workers. Documented workers’ hourly earnings rose 1.8% during the 1990–1991 recession, 4.2% during the 2001 recession, and 6.9% during the Great Recession. We draw two conclusions about the effects of recessions on documented workers. First, the hourly earning effect of the Great Recession was larger than that of the relatively minor recessions, which is consistent with literature on business cycles and the farm labor market in the 1970s . Second, in all recessions, documented workers’ wages rose, which suggests that recessions cause the hired-agricultural-worker supply curve to shift leftward relatively more than did the demand curve. The sum of the coefficients on the recession dummy and its interaction with the undocumented dummy captures the effect of a recession on undocumented workers. The 1990–1991 recession did not have a statistically significant effect on undocumented workers.

Hourly earnings for undocumented workers rose by 3.4% during the 2001 recession and 1.9% during the Great Recession. In contrast to the pattern for documented workers, the undocumented workers’ earnings rose by less during the Great Recession than during the 2001 recession. Thus, not only do undocumented workers earn less than documented workers do in general, but their hourly earnings rise less during recession than do the earnings of documented workers. That is, the wage gap between documented and undocumented workers widens during recessions. In addition to hourly earnings, 28% of the workers in our sample receive bonus payments , which supplement relatively low wage payments . These deferred payments play a similar function to that of efficiency wages in other sectors . We use a binary indicator equal to one if a worker receives a money bonus. Column 2 of Table 2 shows the results of a regression using a linear probability model . For documented workers, the probability of receiving a bonus did not rise during the two relatively minor recessions but increased by 5.8 percentage points during the Great Recession. Thus, the Great Recession not only raised documented workers’ hourly earnings, but it raised the probability that they received a bonus substantially. For undocumented workers, the probability of receiving a bonus fell by 2.9 percentage points during the 1990–1991 recession and rose by 9 percentage points during the Great Recession. Again, this result is consistent with the theory that the Great Recession caused a large supply side shock. Thus,vertical grow for both documented and undocumented workers, the Great Recession had a larger, positive effect on the probability of receiving a bonus than did earlier recessions. The unemployment rate has a statistically significant effect on the probability of receiving a bonus payment. A one percentage point increase in the unemployment rate raised the probability of receiving a bonus by 0.9 percentage points.Because our data set includes information about only employed workers, we cannot directly observe the effect of a recession on total employment. However, we can examine the effect on workers’ weekly hours. When employers have difficulty recruiting workers, they have employees work more hours per week to compensate for an unusually small workforce. For documented workers, weekly hours fell by 2.2 hours during the 1990–1991 recession, but rose by 1.1 hours during the 2001 recession, and 2.3 hours during the Great Recession. For undocumented workers, weekly hours were not statistically significantly affected during the two relatively minor recessions, but rose by 2.6 hours during the Great Recession—more than for documented workers. An increase in the overall unemployment rate by 1 percentage point lowered the weekly hours by 0.3 hours. Thus, an increase in the overall unemployment rate lowered weekly hours, but weekly hours rose during relatively large recessions.We conducted five robustness checks. First, we estimated all three equations separately for documented and undocumented workers. That is, we allowed all the coefficients to vary between these two groups instead of only the recession dummies.

The coefficients on our seven key recession variables were virtually unchanged . Second, we estimated all three regressions eliminating all newcomers , about 3,300 people or 7.5% of the sample, to see if compositional changes in the workforce during recessions are driving our results. However, the coefficients were virtually unchanged . Third, we estimated all three regressions leaving out the unemployment rate. Doing so had negligible effects on the other recession variable coefficients . Fourth, we excluded the crop dummies, in case they are endogenous. The recession variable coefficients were unaffected .Do recessions have different effects in agriculture than in other sectors of the economy that employ many undocumented immigrants, such as construction, hotels, and restaurants? To answer this question, we constructed a comparable data set based on the March Current Population Survey for 1994–2013. We can look at the effects from only two recessions, 2001 and the Great Recession, because the CPS does include certain key variables prior to 1994. It also lacks a variable on bonus payments. In contrast to the NAWS, the CPS data does not record whether an immigrant is undocumented. Therefore, we focus on immigrants in general and form interaction terms between immigrant status and the recession dummies. Otherwise, we use as similar a set of demographic variables as possible. Table 4 presents the regression results for the ln wage and weekly hours in the three sectors. In none of these three sectors did either recession affect the wages of non-immigrants or of immigrants. Presumably, wages are sticky in these sectors, partially due to union and other contracts and minimum wage laws. The unemployment rate had a statistically significant effect only in the construction sector, and that positive effect is small, as in the agricultural sector. The 2001 recession did not affect the weekly hours in these sectors.

The tools to facilitate such an accounting can only be developed within a whole-systems perspective

Our educational and research institutions tend to mirror this shortcoming,8 with the result that the larger system contexts of research questions are infrequently investigated and poorly understood. Difficulties in apprehending and resolving problems whose constituents are grounded in several interrelated systems are compounded by the international community’s disparate, competitive political and economic systems. Nations act to promote their own priorities but affect, often negatively, globally shared resources and globally interdependent societies. Although nations and other sociopolitical groups generate impacts beyond their borders, they are generally incapable or unwilling to assess and react equitably to the results of their actions. Pierre Crosson and Norman Rosenberg 18 note the inadequacy of information feedback about significant environmental problems in modern societies, an inadequacy which characterizes feedback about social problems as well. Accounting for the system-wide implications of local actions should be a primary objective for sustainable agricultural systems. The definition of sustainability offered here places a priority on broad-based equity considerations. We believe it is inadequate to exclude social justice as a priority and that there is an ethical requirement for greater equity in the agricultural system. Some have combined concern for how we treat the environment with how we treat our fellow human beings.19, 20, 21,22 For those focusing on the latter, it is essential to look beyond sustaining our environmental and economic ability to produce agricultural goods. It is equally important to ensure that those goods are produced and distributed in an equitable manner. A concern with this human values aspect of agriculture involves a sweeping rather than localized concept of who constitutes “us.” Typically, resource conservation is dis- cussed in terms of its implications for farmers’ profit- ability or our descendants’ food-producing capabilities. The sustainability definition offered in this paper does not limit equity considerations to these groups. A concern with equitable social relations in agriculture requires defining “us” in terms of all fellow humans – not only farmers and future generations, but also farm workers, consumers, non-farm rural residents, Third World urban poor, and others.

Sustainability in this sense is framed in terms of both intergenerational and intragenerational equity. Thus,greenhouse vertical farming issues such as farm worker rights and inner-city hunger are as central as issues of soil erosion and groundwater contamination to the goals of agricultural sustainability. One of the most profound challenges facing agriculture is creating a decision-making process which will fairly resolve equity issues. Such a process must assess competing interests; evaluate agriculture’s costs and benefits, and the recipients of each; decide fairly what the compromises must be; recognize and encourage shared goals and common ground. In most discussions of sustainability either environmental quality or social justice issues are emphasized, but neither can be sup- ported wholly at the expense of the other. Nourishing humans, ensuring social justice, and providing a reasonable quality of life cannot be accomplished if agriculture’s resource base and environmental constraints are neglected. Likewise, few would argue that environmental considerations should be pursued at the expense of satisfying basic human needs. An equitable agricultural system must foster a decision-making process which is truly democratic, one which identifies not only what the costs and benefits are but how to distribute them fairly among all sectors of society.Many sustainability definitions, particularly those which guide applied sustainable agriculture programs, are based on the primacy of farm production and short-term profitability. As sustainable agriculture programs have increasingly been incorporated into long-established agricultural institutions they have manifested the largely unquestioned intellectual assumptions and infrastructural constraints which characterize their parent institutions. This is problematic because conventional agricultural institutions have fostered many technologies and policies counter to sustainable agriculture goals.Such institutions have, for example, contributed to concentration within agriculture; have not generally benefited agricultural labor; and have systematically failed to examine their impact on the environment, the structure of rural households and communities, and the consequences of rural resident displacement.

To situate new pro- grams designed to address these problems within the framework which produced them is of questionable value unless steps are taken to change the nature of that framework, for it determines the way its re- searchers see the world, pose questions, and define problems. When agriculture is viewed in a whole-systems context and sustainability is defined comprehensively, it is clear why the current popular focus on farm production practices is insufficient for achieving agricultural sustainability. Developing non-chemical pest management methods, for example, will effectively reduce pesticide use only if economic structures and policies encourage their adoption by farmers. More importantly, one cannot conclude that improved production practices will transform the agricultural system into one that meets all environmental, economic, and social sustainability goals. Social goals must be addressed explicitly. This is why production techniques such as organic farming, while a likely component of a sustainable food and agricultural system, cannot be thought of as synonymous with sustainable agriculture. Given the conventional institutional context of most state and federal sustainable agriculture programs it is not surprising that they tend to focus research on conventional priorities such as production practices and efficiency and have not, for the most part, aggressively addressed social and economic issues. Sustainability priorities – and the definitions which embody them – must be expanded to encompass the many factors affecting production and distribution as well as the larger environmental, economic, and social systems within which agriculture functions. This has been the focus of the Agroecology Program since its inception in 1982. Through conferences and publications* we have worked to expand the discussion and practice of integrating these aspects of sustainability. Recently, the University of California Sustainable Agriculture Research and Education Program has broadened its agronomic focus to include social, economic, and policy issues. SAREP defines sustain- able agriculture as integrating “…three main goals – environmental health, economic profitability, and social and economic equity.”Their grant program, which encourages research and education on social, economic, and public policy issues affecting food and agriculture, could become a model for other sustain- able agriculture programs such as LISA. We believe that it is important to continue exploring the meaning of agricultural sustainability. Before an improved agricultural system can be developed the biases and structures that have led to agricultural problems must be closely examined and concrete goals articulated, based upon a broadened concept of agricultural sustainability. The concept of sustainability offered in this paper emphasizes that social goals are as important as environmental and economic goals, and widens the opportunity to move beyond the narrow agricultural priorities expressed in the past.

It is based upon the whole-systems, interactive nature of all aspects of the agricultural system – that problems and their resolutions must be conceived not only in terms of their immediate time frames and local impacts, but just as importantly, in terms of their future time frames and their global impacts. It encourages emphasis on optimum production over maximum production, the long term along with the short term, the public’s best interest over special interests, and the contextualization of disciplinary work within interdisciplinary frameworks. Our hope is that this definition helps advance the discussion on developing a food and agriculture system that is sustainable for everyone. While aggregate growth in an economy may improve the welfare of both wealthy and poor households,vertical agriculture the latter are most usually rural, and rural households have employment and incomes that depend disproportionately on agriculture. It is natural to wonder if growth in aggregate agricultural income has a different effect on the welfare of poorer households than does growth elsewhere in the economy. The question is an important one for many policy issues. Faced with continuing extensive poverty, many development agencies and scholars have suggested the need to refocus growth on agriculture , arguing that the alternatives of redistributing income generated outside of agriculture or migration out of agriculture to urban areas are difficult to achieve and create other problems. Of course, we are not the first to wonder whether growth in agriculture may be more effective than growth in the rest of the economy in reducing poverty; an extensive theoretical and empirical literature already exists on the subject which we discuss in Section 2. The theoretical literature focuses on the different transmission mechanisms of an exogenous gain in agricultural productivity on poverty, while the empirical literature analyzes the reduced form relationship, and generally documents a stronger association between poverty reduction and growth originating in agriculture compared to growth originating in non-agriculture, with the exception of Latin American countries. In this paper we tackle this question by comparing changes in the level and distribution of household expenditures due to growth in both aggregate agricultural and aggregate non-agricultural income. We use growth in household expenditures as the outcome of interest because we believe expenditures to be the best available indicator of material well-being; also, these are the data generally used for poverty calculations for most low-income countries. However, our analysis differs from most other studies in several aspects. First, we consider growth in expenditures across the entire distribution rather than the simple poverty headcount ratio, giving a richer picture of the effect of sectoral growth on welfare. Second, we use the deciles as defined within each country, rather than a common international benchmark of expenditures.

To correct the underlying assumption that deciles of very different countries have similar relationship with agriculture, we then pursue some heterogeneity analysis. Finally, we tackle the issue of simultaneity between sectoral income and expenditures using an instrumental variable approach, allowing us to take a stand on the causality of sectoral growth on welfare. The simple regression we would like to estimate relates expenditure growth for differently positioned households to growth in sectoral income, the latter weighted by its share in total aggregate income; this is described in Section 4. The question of whether the poor benefit more from agricultural income growth than growth in other sectors could then be answered simply by examining the relative size of the coefficients on aggregate income growth from agriculture and from other sectors. In practice, there is a series of challenges we must face before estimating such a regression. First, we do not have household level data that would allow us to make comparisons across countries. Instead, we use data from the World Bank’s Povcal Net project and consider estimates of household expenditures from different expenditure deciles; in effect we construct a panel of ten representative ‘households’ for each country, each representing an expenditure decile.1 We discuss these data in Section 3.1. Second, the resulting ‘panel’ is extremely unbalanced, since the underlying expenditure surveys are conducted at irregular intervals. This creates some important accounting issues when we turn to estimation, treated in Section 4.1. Third, some countries, some years, and perhaps some deciles can naturally be expected to have different expenditure growth rates for reasons unrelated to sectoral income growth. A global financial shock may cause expenditure growth to slow for everyone; households’ risk attitudes or time preferences may imply different rates of expenditure growth across deciles ; the endowments of a particular country or some aspect of the structure of its economy may imply systematically different rates of expenditure or income growth even over long periods; and variation in the global price of agricultural commodities will change the composition of income across sectors for many countries. We attempt to deal with these kinds of alternative sources of variation in expenditure and income growth in a fairly agnostic manner, by using fixed effects and related methods for dealing with what Wooldridge calls “unobserved effects.” So: we account for aggregate cross-country shocks using a collection of time effects; and for systematically different rates of expenditure growth across the distribution we use a set of decile fixed effects. We would be inclined to also use a complete set of country fixed effects to deal with differences in endowments, but with these we reach the limits of our dataset; instead we employ a set of continent fixed effects, which in practice seems to be effective. Fourth, the stochastic process governing country-level agricultural income exhibits more time-series variance than does income from other sectors.