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Agricultural activities generate a significant amount of pollutants

The NPF framework is used to identify and demonstrate the implications of narratives for the design of SB 700 . The framework identifies a basic structure of narratives and provides basic belief system linkages and preliminary hypotheses. The basic structures of a narrative include “a setting or context; a plot that introduces a temporal element .Providing both the relationships between the setting and characters, and structuring causal mechanisms; characters who are fixers of the problem , causers of the problem , or victims ; and the moral of the story, where a policy solution is normally offered”.This structure is grounded in a belief system that anchors the narrative “in generalizable content to limit variability” . From this premise, one can test hypotheses at both micro and meso levels . This framework fits with elements of Schneider and Ingram’s theory of policy design, which allows the NPF to be used to explore how narratives shape policy design. The key linkage is the concept of socially constructed target populations. This refers to the recognition of shared characteristics that distinguish a target population as socially meaningful, and the attribution of specific valence-oriented symbols and images to the characteristics” . Positive constructions label target populations as “deserving,” “honest,” and driven by “public interest.” Negative constructions label target populations as “undeserving,” “dishonest,” and “self-interested.” These portrayals are captured in the NPF by the discussion of characters as part of the narrative structure. Narratives utilizing the social constructions of target populations influence the other aspects of policy design including policy tools, agents,indoor vertical farming and implementation structures. This allows for meso-level hypotheses between narratives and different aspects of policy design.

Narratives serve to amplify our notions of who is “deserving” and “undeserving” of the benefits of government policy. The credibility of narratives depends on tapping into the preconceived ideas of groups in the larger social context . Policy tools “are elements in policy design that cause agents or targets to do something they would not otherwise do with the intention of modifying behavior to solve public problems or attain policy goals” . The choice of tools reflects the assumptions and biases about how different people and targets behave . Policy tools applied to deserving target populations emphasize the positive aspects of the group. Capacity-building and learning tools reward with benefits and penalize with burdens. These tools tend to see the group as being able to act independently of the policymaker. However, undeserving groups will be on the receiving end of a combination of sanctions and authority-laden tools. Undeserving target populations are treated in a coercive manner with respect to burdens. Thus, as a narrative portrays a target population in a more positive way, the more likely policy tools are to emphasize the positive aspects of this group. According to Schneider and Ingram , agents are “the means for delivering policy to target populations.” The implementation structure refers to the relationships among various agents and their connections to target groups. Policymakers reward deserving groups in a highly visible way. Strong statutes that clearly provide the reward directly in the legislation are used frequently. Placing burdens on the deserving groups usually entails an approach to implementation that seeks to build consensus and support for the policy.Agents and implementation structures tend to operate differently for undeserving groups. The assessment of burdens is done very visibly in a strongly worded statute.

The rewarding of benefits is done using a more decentralized process, although the statute may provide specific eligibility criteria . Thus, as a narrative portrays a target population in a more positive way, the more likely agents and implementation structures directly reward this group. Roe’s narrative policy analysis was applied to the materials making up the SB 700 database. In all, there were 202 discrete problem statements identified in the texts. The aggregation of these individual statements revealed four major patterns of problem-cause relationships. Narratives play an important role in shaping the social construction of populations targeted by SB 700. They capture the context of the struggle to end California agriculture’s exemption to air pollution permits. This struggle takes place in the state legislature and has a very partisan base. Democrats assemble a coalition of environmental and public health groups in support of SB 700. Republicans construct a coalition of various agricultural and municipal organizations to oppose the legislation. The following is a discussion of these four narratives and their varying constructions of target population. Thus, it is a combination of natural and demographic factors, along with a variety of mobile and stationary sources that emit harmful air contaminants in the valley. This narrative establishes two important ideas that carry through the rest of the policy discourse. The first is that air quality in the San Joaquin Valley is bad. Numbers play an important role in establishing air quality as a problem that needs to be solved. In particular, EPA has established national ambient air quality standards for ozone and PM-10. The San Joaquin Valley Air Control District is in serious non-attainment for PM-10 and severe non-attainment for ozone with the possibility of moving to extreme non-attainment . The second foundational element is that this poor air quality leads to adverse health and environmental impacts . These are the victims of the narrative. Ozone and particulate matter are associated with a variety of health effects including reduced lung function, permanent lung damage, increased risk of cardiac death, increased risk of lung cancer and heart disease, and aggravated asthma .

Of all these, the incidence of childhood asthma garners the most attention. According to figures from 2001, 16.4% of children in Fresno County were reported as having asthma . This is higher than the statewide rate of less than 10% and the national rate of 5.5% . Grossi et al. note, “Health officials cite the number of children with asthma in the valley when advocating for stricter pollution standards.” In addition to these figures, the authors of “Last Gasp” utilize personal vignettes to drive home the human toll exacted by exposure to high levels of these pollutants. Institutional sources are also indicted in the narrative. According to Deborah Stone , problems may be “caused by a web of large, long-standing organizations with ingrained patterns of behavior.” Some claim that the interaction of various government officials with one another and industry have led to delays in cleaning up the valley’s air. Grossi et al. note, “The valley’s last 30 years are littered with accounts of the federal government issuing proposals,edicts and threats to clean up the air, only to accept delays and compromises after meeting resistance. Industries, local elected officials, and even state regulators have had a hand in the process.” The EPA has the power to sanction noncompliance with the Clean Air Act; it has a history of backpedaling. In the 1990s, CARB underestimated vehicle pollution emissions and failed to act in a timely manner. The SJVAPCD has been accused of bowing to various industry pressures and not pursuing stronger emission reducing strategies . Natural and institutional forces aside, there is no shortage of “villains” contributing to the polluted valley air. Chief among these are passenger cars and trucks, gross polluters, and diesel trucks . All told, these and other mobile sources account for 56% of NOx and 41% of VOCs emitted in the San Joaquin Valley Air Basin.Emissions from sources such as farm diesel engines and dairy operations account for 54% of particulate matter and 25% of VOCs in the valley’s atmosphere.

In addition to these major categories, sprawling development encourages more driving and less environmentally friendly modes of transportation . Complex systems and institutional causes make finding policy solutions difficult. Stone notes “Complex explanations are not very useful in politics,hydroponic vertical farming precisely because they do not offer a single locus of control, a plausible candidate to take responsibility for a problem, or a point of leverage to fix a problem.” However, the complex cause narrative does provide some insights into the discourse surrounding SB 700. It establishes two ideas taken as givens by all participants in the discourse. Air pollution in the valley is bad and it is related to adverse health effects. Other narratives take these as facts not to be disputed. The narratives to follow emphasize selected pieces of the multi-causal chain and deemphasize others. This is done to accomplish the strategic ends of different actors in the policy process. Thus, the complex cause narrative acts as a context or backdrop for the coming discourse. In the complex cause narrative, federalism functioned to delay the process of cleaning up the air. In this narrative, the federal relationship will serve as an incentive for California to end agriculture’s exemption to Clean Air Act permits. This sets off a story of potential decline. On May 14, 2002, the EPA and Earth Justice Legal Defense Fund settled a lawsuit concerning whether or not EPA should regulate major agricultural sources of pollution. Under the settlement, the EPA found California’s exemption for agriculture violated Title V of the Clean Air Act. Thus, “if the state fails to revise its agricultural exemptions, increased pollution offsets will take effect on November 15, 2003, and California will lose its federal highway funding on May 15, 2004” . Pollution offsets would be imposed on new and modified sources. Business and industry would pay increasing bills to expand their activities. Loss of the highway funding would amount to around $2.4 billion for 2004. Thus by not ending the state’s agricultural exemption, state policymakers and citizens became the victims of this narrative. The ending of the exemption became imperative. While there were alternative solutions, the approach taken by SB 700 argues agriculture is a significant contributor to air pollution and should be required to play a larger role in the cleanup effort. Florez believed the exemption needed to be repealed and regulations on agricultural sources extended, “We’re not taking our cue from EPA. . . . If farmers’ argument is going to be that the EPA says we don’t need to go that far, that’s not acceptable. We are not interested in doing the minimum. We want to clean the air” . Florez believed that the additional EPA requirements announced in June 2003 supported his argument. Specifically, the EPA announced that farms must be included under new source review permits . Florez argued, “There is no way to avoid it.You have to remove it now to make sure the state can comply with all of the Clean Air Act” . As the clock ticked closer to the imposition of sanctions, wholesale repeal of the exemption gained momentum. As Fitzenberger states, “agricultural leaders knew some form of SB 700 had to pass. It is the only bill to lift the exemption, and failing to do so could lead to a loss of billions of dollars in highway funds and increased fees for some businesses” . This narrative is structured around intentional cause. This suggests that agriculture interests and their political supporters have willfully supported the exemption, and this allowed their contributions to poor air quality to grow . While numbers are used to detail the level of various pollutants emitted from agricultural sources, comparisons are used to put the numbers in context. According to SJVAPCD and CARB data, agricultural sources are the: “Largest source of nitrogen oxide and second largest source of sulfur oxide —precursors of smog; largest source of the volatile organic compounds and reactive gases —precursor to smog; and second largest source of particulate matter.” . Grossi et al. offer another unflattering comparison, “During summer, the $14 billion agriculture industry creates more lung-searing pollution than the valley’s eight highest-polluting large businesses combined” . And the significance is growing, “For one of the two major, smog-making pollutants, reactive organic gases, livestock waste is projected to pass cars in 2005. Farm equipment in 2005 will run second only to heavy-duty diesel trucks for nitrogen oxides, the other major smog ingredient” . Some supporters of SB 700 state this argument even more directly. They argue agriculture’s longstanding exemption from air permits has allowed the industry to “grow” its contribution to air pollution relative to other groups.

The impact of the yield-increasing technology  is more complicated

Breakthroughs in higher yields lead to faster spread and replacement of new varieties for some crops but not others. The positive and significant signs of the Yield Frontier variables in the wheat VT equations  demonstrate that when higher yielding wheat varieties appear in their provinces farmers turn their varieties over more frequently. The correlation between a higher yield frontier and more rapid turnover may explain why wheat yields outperformed other major grains during the reform period. In contrast, higher values of Yield Frontier variables in the rice and one of the maize equations are associated with slower turnover . Such a finding is consistent with our gap analysis and may reflect the fact farmers  in the mid- to late-reform period prefer adopting higher quality rice varieties, even though higher yielding varieties are available. The impact of the materials from the CG system is mainly a story of the China’s breeders using IRRI and CIMMYT varieties for the yield enhancement of their seed stock. If it can be assumed that, when China’s breeder incorporate foreign germplasm into its varieties, the material contributes to part of the rise in productivity, then the test of the direct impact of CG material is seen in the results of the TFP equation. If technology is important in all the TFP equations, by virtue of the fact that IRRI’s material is used more frequently by China’s rice breeders, compared to that used by wheat and maize breeders, it is making the largest contribution of the CG system to China’s TFP in the reform era.It is possible, however, that foreign material may be bringing in an extra “boost” of productivity, beyond its contribution to the varieties themselves,hydroponic grow table by increasing the rate of turnover of new varieties.Such an effect would show up in the VT equations. If the coefficients of the CG variables were positive and significant, they would indicate that the presence of material from CG centers makes the varieties more attractive to farmers and contribute to technological change in China in a second way.

In fact, there is not particularly strong evidence that increases in the presence of IRRI material is important in increasing the turnover of rice varieties . If farmers are, in fact, mainly looking for characteristics that are not associated with higher yields, it could be that IRRI material is making its primary impact on yields and only a secondary impact on the other traits that have been more important in inducing adoption in the reform period. A similar cautious interpretation is called for in the case of wheat and maize  where the standard errors are large relative to the size of the coefficient in all but one case. But although the contribution of CIMMYT wheat and maize germplasm to China, according to this analysis, may be smaller, in some provinces the contribution of CIMMYT’s material has been large and may have extraordinary effects on the productivity of some of China’s poorest areas. For example, the CG genetic materials contributes more than 50 percent of Yunnan Province’s wheat varieties and more than 40 percent of Guangxi Province’s maize varieties in the late 1980s and early 1990s. Yunnan and Guangxi Provinces are both very poor provinces and some of the poorest populations in China are in the mountainous maize growing areas. Elsewhere , we have shown that the impact of CG material in poor provinces, in general, is more important than its effect in rich areas—both directly and in some cases in terms of inducing more rapid turnover. Such a pattern of findings is consistent with a story that although the focus of the CG system on tropical and subtropical wheat and maize varieties has limited its impact on China productivity as a whole, it has played a role in increasing technology in poor areas, a chronic weakness of China’s research system .Our results for the TFP equation, presented in Table 4, also generally perform well. The goodness of fit measures  range from 0.80 to 0.85, quite high for determinants of TFP equations. In other work, in India for example, the fit of the specification was only 0.17 . The signs of most of the coefficients also are as expected and many of the standard errors are relatively low.15 For example, the coefficients of the weather indices are negative and significant in the TFP equations in the rice, wheat, and maize specifications . Flood and drought events, as expected, push down TFP measures, since they often adversely affect output but not inputs.

Perhaps the most robust and important finding of our analysis is that technology has a large and positive influence on TFP. The finding holds over all crops, and all measures of technology. The positive and highly significant coefficients on both measures of the rate of varietal turnover  show that as new technology is adopted by farmers it increases TFP . Following from this, the positive contributions of China’s research system and the presence of CG material both imply that domestic investments in agricultural R & D and ties with the international agricultural research system have contributed  to a healthy agricultural sector. Further analysis is conducted to attempt overcome one possible shortcoming of using VT as a measure of technological change. It could be that an omitted variable is obscuring the true relationship between VT and TFP. As varieties age, the yield potential may deteriorate . We add a variable measuring the average age of the varieties  to isolate the age effect from the new technology effect . Although we find no apparent negative age impact on TFP in any of the equations , in a number of the regressions, the coefficient ofVT variable in the TFP equation actually rises, a finding that reinforces the basic message of the importance of technology. The role of extension is less simple. The impact of extension can occur through its effect on spreading new seed technologies  and through its provision of other services enhancing farmer productivity . The positive and significant coefficients on the extension variable in all of the VT technology equations for all crops demonstrate the importance of extension in facilitating farmer adoption . Extension, however, plays less of an independent role in increasing the yield potential of varieties that have been adopted by farmers, perhaps an unsurprising result given the reforms that have shifted the extension from an advisory body to one that is supporting itself, often through the sale of seed .The long-termsustainability of agricultural systems concerns diverse groups of people. They emphasize different aspects of sustainability, from land steward- ship and family farms, to low external-input methods and food safety. Often there are two different themes: sustainability defined primarily in terms of resource conservation and profitability, and sustainability defined in terms of pressing social problems in the food and agriculture system.

Each of these perspec- tives has been illustrated by William Lockeretz1 and Miguel Altieri.2 In his review article on sustainability, Lockeretz documented primarily production-oriented components of sustainability. Altieri, on the other hand, has pointed out that concentration on only the technological aspects of sustainability results in, among other things, failure to distill the root causes of nonsustainability in agriculture. While sustainability efforts need to address both social and technical issues, they frequently overemphasize the technical, a problem we see originating in the way sustainability is often defined. Our purpose in this paper is to discuss concerns about current sustainability definitions and suggest a definition based upon a broader perspective.Among those working in sustainability there is often a feeling that we need to devote less time to talking about the meaning of sustainable agriculture and more time to implementing it. While this is an understandable position, especially for those directly involved in production agriculture, it also expresses a contradiction. How can we form an improved agricul- tural system if it has not yet been clearly conceptual- ized? Lockeretz1 queries, “Isn’t something backwards here?” and shows that, although there is a surge of interest in agricultural sustainability, “even its most basic ideas remain to be worked out.” There is no generally accepted set of goals for sustainable agricul- ture, and little agreement even on what and who it is we intend to sustain.3 Is it possible, for example, to both sustain production levels and preserve the natural environment? Who should we work to sustain – farmers, consumers, future generations – or should all of them be our priorities? Can we truly sustain one group without considering others? Without clarifying these goals the necessary changes in cultural, infra- structural, technological, and political arenas are difficult to negotiate. If we want sustainable agricul- ture to pursue a path differentiable from that of conventional agriculture, we need to explicitly state and gain some consensus on these goals. A clear, comprehensive definition of sustainability forms the necessary theoretical foundation for articulating sustainability goals and objectives.The emergence of agricultural sustainability reflects many people’s dissatisfaction with conventional agricultural priorities, especially the extent to which short-term economic goals have been emphasized over environmental and social goals. In response, a number of agricultural sustainability concepts have been developed under the terms “alternative,” “regen-erative,” “organic,” “low-input,” and “sustainable.” In this paper we refer to those definitions most com- monly espoused in the agricultural research commu- nity, definitions which are predominant in the literature and are used as the basis of sustainability programs.

We examine what priorities these defini- tions embody, how these priorities relate to those expressed in conventional agriculture,flood tray and how developing sustainability would benefit by broadening these priorities. Althoughsustainability definitions include a range of environmental, economic, and social characteris- tics, most focus somewhat narrowly on environment, resource conservation, productivity, and farm- and firm-level profitability. Charles Francis4 defines sustainable agriculture as a “management strategy” whose goal is to reduce input costs, minimize envi- ronmental damage, and provide production and profit over time. The National Research Council5 defines alternative agriculture as food or fiber production which employs ecological production strategies to reduce inputs and environmental damage while promoting profitable, efficient, long-term production. For Richard Harwood6 the three principles for sus- tainable agriculture are: “the interrelatedness of all parts of a farming system, including the farmer and his family; the importance of the many biological balances in the system; the need to maximize use of material and practices that disrupt those relation- ships.” According to Vernon Ruttan7 enhanced productivity must be a key factor in any sustainability definition. Rod MacRae, Stuart Hill, John Henning, and Guy Mehuys8 adopt a sustainability definition which emphasizes environmentally sound production practices. They note that sustainable agriculture today is characterized mainly by products and practices which minimize environmental degradation, although they also point out the potential to move beyond this restrictive application. In his review of sustainable agriculture definitions, Lockeretz1 stresses agronomic considerations although he does note the connection between changing production practices and associated socioeconomic transformations. Sustainabilitydefinitions such as the above focus on environmental conservation which is to be achieved through changing farm production practices without reducing farmers’ profits. They challenge some but not all of the assumptions that underlie agriculture’s nonsustainable aspects, generally neglecting questions of equity or social justice, or devoting little specific language to it. Altieri,2 for one, has challenged the narrowness of these approaches and their implicit assumption that taking care of the environmental, production, and economic aspects of sustainability automatically takes care of social aspects: “Intrinsic to these [agroecology] projects is the conviction that, as long as the proposed systems benefit the environment and are profitable, sustainability will eventually be achieved and all people will benefit.” Altieri has noted that without intervention on policy, research, and other levels, the more appropriate technology devel- oping in the name of sustainability will merely perpetuate and enhance the current differentiation between those members of society who benefit from agriculture and those who do not. Furthermore, the technology itself will not be developed and used unless we address the cultural, infrastructural, and political factors which shape how it is designed and implemented. These factors include scientific para- digms, fiscal policy, international trade, domestic commodity programs, and consumer preferences.Pursuing the dialogue on sustainability is essential in order to make visible the often invisible assump- tions and priorities which have governed agricultural research, policy, and business decisions leading to nonsustainable systems.

Farmers also need instances of trust as machinery rings to encourage them to share data

Data that farmers generate and collect are comparable to the business secrecies of other economic actors because the information from data means an advantage in knowledge and competition.However, as data are not physical and are easily duplicable, it was until today not possible to define a right on data ownership.Within the intellectual property law, it is difficult to dispense justice on a copyright law basis, concerning data that are regularly not the result of thinking, creating processes.Mere, unordered collections of “raw data” are not protected in this context, and also the GDPR does not apply in such cases.But farmers’ data in the normal cloud-based communication ways are exposed to several third parties.Data security, data ownership, and data safety, also for impersonalized data, need to be addressed for example by entering the corresponding parties into contracts so that impersonal data are as save as personal data are.Another possibility to personalize data is offered by the block chain technology itself and furthermore the use of NFT.Data stored in this way in a block chain still can be copied but the authenticity of data is safely defined.Furthermore, decentrality amongst clouds is recommendable to increase data security.Vogel summarizes, that data sovereignty is hardly guaranteed and whoever is in possession of the data can use it as wished.Undesirable market dynamics that could lead to extortion of individuals and the lack of criteria defining data sovereignty led the German Conference of Justice Ministers to reject the creation of defined data sovereignty.Contracts with the according service providers could bring data sovereignty to farmers but may also lead to unfavourable “lock-in” effects.To strengthen data sovereignty several activities took and still take place.There was an industry recommendation in Germany heading to assure full control of data sovereignty and rights of use to the farmer.On a European level, there is “The EU code of conduct on agricultural data sharing” heading the same aims and centralizing clear contracts between collaborative parties after the principles of the code.

The number of signatories representing farmers, industries, and cooperatives is gratifying and promising.However, still,vertical rack system several security issues on different layers of digital farming systems are present.Therefore, concepts are needed which provide suggestions of systems that give control to the data originators or trusted parties of them and provide open, simple, and interoperable solutions, facilitating the introduction and continuation in digitization for every farm size.In the authors’ point of view, absolute data sovereignty belongs to the farmers concerning any data which are generated in the fields of their responsibility.Farmers are the owners of these data, this needs to be legally protected and substantiated by unique identification methods of the corresponding data.In the near future, this needs to be taken care of, from the beginning of a cooperation, service, or machine purchase.The EU code of conduct is a good basis for the beginning of a legal process.Farmers are encouraged to use the “Code of conduct” for the critical examination of appropriate solutions.Defining the term IoT as a technology still seems misleading.Paraforos unites numerous definitions to the common denominator of a technological paradigm.One might consider IoT as an integrating network of technologies interacting and exchanging data in an ideally interoperable way.Kim categorizes the applications of IoT fourfold in management systems, monitoring systems, control systems, and unmanned machinery, which include respectively a perception layer where physical properties are recognized, the network layer realizing M2M communication, and the application layer where the data is being used or processed to information.Chaudhary conducted a case study on AGCO’s Fuse Technology’s ‘Connected Farm Services’ as a commercial IoT example covering farm management, standard field works, monitoring, and dealer telemetries.They mention as a major vulnerability issue the centrally connected network and the therefore comprehensive need of cyber security measures.IoT offers practical and also monetary benefits at farm level if it is tailored to the needs of the user as realized in the specific example of sugar cane production shown by van de Vooren.Increased invention and application of IoT solutions lead to a strongly increased number of devices and data traffic which reveals the transmission and computing limits of cloud solutions.

Therefore, applying edge and/or fog computing, data processing is being decentralized from the cloud, on or close to the data acquiring device, to the edge of the network, leveraging this problem.This results in a lowered latency by avoiding edge to cloud or edge to enterprise server round trips.By processing computing workload on edge devices or edge servers/gateways network congestion is minimized.Furthermore, data privacy and security are increased by installing access control options at the corresponding edge device/ gateway.Also, storage and intelligence capacities from the cloud can be mirrored on the edge servers.Fog computing is usually localized one level beyond edge computing in the network.Like this, a decentralized and redundant infrastructure evolves and leads to more independence from centralized cloud solutions.As it was mentioned by Jha and Patidar in a market report: “The global autonomous farm equipment market is projected to expand at over 10% CAGR through 2031, and top a market valuation of US$ 150 billion by 2031”.Numerous Start-Up companies all over the world develop robots and autonomous systems for agricultural purposes.Also here the amount of data that is and will be generated and has to be transferred, increases, and has to be processed in high quality and quantity to ensure continuous functionality to the autonomous systems also using AI.The actual working speed and efficiency of autonomous systems are still low, which makes working hours in narrow time windows of certain works even more crucial/critical.Furthermore, a full customer service is needed, which also is a matter of costs.For technical issues or hardware problems, a service technician needs to be present near-time, and also for remote services in case of software issues farmers need real-time online support.Thus, these solutions need a solid and seamless digital infrastructure to exploit the full potential of each device.Due to the competition of OEMs, whose interest in data sharing is limited, the development of infrastructure is always lagging behind the development of single devices.But to be forearmed for the use of autonomous systems, the infrastructure conceptualization and development should be forced.A nice example shows Saito by using XML standards for directing robots to target plants.Today AI in agriculture is used in decision support systems, expert systems, and agricultural predictive analytics.Digital twin methods are dealt with for modelling future scenarios and preventing disadvantageous circumstances.Furthermore, data over periods of decades could reveal regionally optimized crop rotations, cultivar selections, and cultivation strategies by the application of AI.

However, to reach this, the form of data storage, transmission, and processing must orient on international standards to ease the interoperable interactions of systems that can reflects entire agricultural processes.Slurry application is an often delegated application for small and medium-sized farms today.Customers can order the service of a self propelled slurry applicator using precision farming technologies like auto-steer, online NIRS nutrient analysis, and site specific slurry application including section control, which farmers themselves would not invest for, for their own farms alone.If VRA is conducted, the data transmission goes via a USB stick.Which can be inconvenient, due to the risk of data and hardware loss, and can be time-consuming if changes in the application map are necessary.The data upload to the cloud can be tedious in rural areas because of narrow bandwidth and low mobile network coverage but also occur to be minimized by weak performance of the cloud services.FMISs lack interfaces for seamless data transmission and task execution.Task documentation also demands increased knowledge and skills of drivers to organize and overview data of multiple farms.The billing of the single tasks hereafter is done by hand and transferred to the computer manually for finalizing the invoicing.To summarize, high-tech machines and digital farming components are available and implemented but are barely used to their full potential up to automated documentation and billing, due to the lack of infrastructure and/or not interoperable or isolated components.To meet the responsibility for a critical infrastructure and the weather-dependent and therefore, time-critical conditions in agriculture, specific requirements concerning the digital infrastructure are to be fulfilled.If services or devices, which generate or need data, do not work at the application date, in most cases farmers will continue without it.This chapter aims to specify the requirements of regional and on-farm ICT infrastructures.Farmers’ independence of the susceptibility of centralized systems and the straightforward inclusion of small and middle scaled farms are the main focus.

For the application of field measures like seeding, plant protection, or fertilization, various information can be used and are required to achieve maximum efficiency.The existing, actual, and forecasted data of soil, plants, and weather conditions are decisive.Therefore, these agronomic data need to be easily accessible to farmers if they don’t acquire them themselves.The structure and the format of these data must further be readable and processible in farmers’ FMISs.The combination and systematic processing of these data should be straightforward via accessible algorithms and knowledge bases which are accessed and used by the management software of the farmers.Like this,mobile grow rack farmers have the information to make profound decisions which they need directly in crop management and field applications.Additionally, to existing data like yield maps or satellite images, these data are to be combined and supplemented in the prescription map by merging also dynamic and non-deterministic parameters by farmers as Heiß et al. showed in their work.Most FMISs and other digital farming components are and will be based on cloud computing solutions.Reasons are the advantages for the companies like better customer support, instant new updates, and decentral data management.However, to correspond to the need for resilience, centralized cloud-based services can become redundant and fail-safe by decentralization.In Fig.1 it is highlighted where decentralization can be realized.Decentralization is required within the cloud layer, by placing functionalities redundantly within further clouds ideally with geographically remote located servers.In the lower layer of fog computing, an additional, regional server location, driven by an MR or a local government institution , can be implemented to expand decentralization on a regional level.Server maintenance and corresponding storage, back up and computing capacities must be provided by the responsible institution.At the farm level, a farm server tailored to the farms’ needs is required.It must be able to define the access rights to farm data for third parties and has to ensure the required data protection and data privacy.The red arrows in Fig.1 show the current means of data acquisition, communication, and processing in the corresponding clouds: From sensor/ device to OEM cloud to FMIS and back or further to other destinations.

The path over the cloud is the preferred way in the suggested FDFS.Alternatively, and/or additionally, in case of disconnection or outage, data can be sent to the farm server and be processed there or on the district servers to maintain functionalities.For the interpretation of this data, a certain level of intelligence in offline software on the farm server or secondary servers is needed because farmers hardly deal with raw data.The prerequisite for the common communication path in Fig.1 and as well for the connection between farm and regional server locations is the expansion of broadband internet over landline connection and mobile network coverage especially to rural areas where farms are located.For realizing the resilient communication path , a local on-farm network is required to sustain data communication between sensors/devices and farm server/farm PC.To enable communication during internet outages between farmers, farmers and contractors/MR, etc., a network communication technology is required which ensures data communication over an area expansion that covers the region of the farmers, their partners, and contractors.Here only small and necessary amounts of data need to be sent for example to communicate basic data of an application task.Furthermore, especially for small and middle scaled farmers who have to communicate with different brands through MR and contractors, interoperability of digital technologies is a major requirement.This concerns all components of an FDFS beginning at data structures on sensor level and ending at interfaces to sales and purchase.Finally, the FDFS needs to ensure data safety and security.The more digitization proceeds the more important this requirement becomes.The systems must be protectable against unwanted and malicious access.Traceability of data must be given so that it is known to the farmers who use their data and for which purpose.Furthermore, information about the production process is offered to the customer which increases trust in farmers’ practices.

There are at least three major obstacles to more widespread use of the agricultural easement technique

Not included in these estimates were other agricultural acres protected by easements primarily for environmental purposes, such as wetlands, habitat and riparian corridors . Anecdotal evidence suggests that there are many thousands of such acres throughout the state, with easements acquired and held by local land trusts and open space districts, national conservation organizations such as The Nature Conservancy, and state and federal wildlife agencies . Of the 34 organizations, only 24 had acquired agricultural easements by 2000, reflecting that many new programs are still in the formative stage. The programs studied held 29,600 acres in non-agricultural easements and owned outright another 90,900 acres in natural resources and recreational areas, indicating that many programs pursue multiple conservation goals. Only about one-fifth of the total agricultural easement acres were cropland; four-fifths were grazing land. By comparison, cropland and grazing acres represent much larger and smaller shares, respectively, of California’s total farmland base — about one-third and two-thirds of the total . One explanation for the prevalence of grazing acres in easement programs is the relatively large size of cattle ranches and the preference of some programs to put an easement on one large ranch in a single transaction, rather than undertaking the more difficult task of seeking multiple easements from numerous owners of smaller cropland farms. Farms under easement are an infinitesimal share of California’s total 27 million agricultural acres. These are located in only 19 of the state’s 58 counties . They are concentrated in eight coastal counties from Mendocino to the north and Santa Barbara to the south, and in three adjacent Bay Area counties . The coastal counties alone contain more than 80% of all easement acres. Three Central Valley counties are also represented in the easement ranks. This geographical pattern is also notable for the regions that lacked any agricultural easement activity in 2000: the southern and northern thirds of the state. Just as striking is the absence of many important agricultural counties.

Among the 11 counties that lead the state in agricultural production value, each with at least $1 billion in market receipts in 1999,round plastic pots only three contained agricultural easements as of mid-2000 . Counties with farm market values of $1 billion or more in 1999 that did not have agriculture easements were Imperial, Kern, Riverside, San Diego, San Joaquin, Stanislaus, Tulare and Ventura. On the other hand, Sonoma and Marin — the top counties in agricultural easement acres — ranked 16th and 44th, respectively, in farm market value among all California counties. The pattern of varying easement activity among top agricultural counties can be explained, in part, by underlying differences in the conservation sentiments of local populations. For example, Central Coast voters have shown higher levels of support for environmental measures on statewide ballots than voters in inland and southern counties . As a result, citizen coalitions with land conservation or other environmental agendas are more likely to form in Central Coast communities, which may explain the relatively larger number of land trusts in these areas. Yet not all Central Coast counties have active agricultural easement programs. Santa Cruz, Santa Clara and Ventura counties, for example, had recorded no agricultural easements or far fewer than nearby areas as of mid- 2000. In interviews, conservation organization managers cited as reasons the higher costs of acquiring easements on farmland in some of these locations and the greater interest of local land trusts in conserving environmental lands and engaging in educational and other activities.Each of a dozen programs — 11 land trusts and one open space district — had acquired easements on 1,000 or more agricultural acres as of 2000. Their collective holdings totaled about 79,000 acres, 94% of the state total. Among the 12 programs are six coastal programs, three in adjacent counties, two in the Central Valley and one statewide program . The two largest programs combined held more than 46,000 farmland easement acres, or slightly more than half of the statewide total. Serving adjacent North Bay counties, Marin Agricultural Land Trust and the Sonoma County Agricultural Preservation and Open Space District have been the two most active farmland easement programs in California since the mid-1990s. More than 150 separate transactions were represented by these easements. In some cases, the number of separate transactions is a better measure than total acres of the organization’s achievements, since each transaction is the result of a complex process that includes extensive landowner negotiations.

Most of the 12 programs exclusively or primarily hold easements on grazing land. Only the Monterey, Yolo and South Livermore Valley land trusts are exclusively or primarily involved in acquiring and holding easements on cropland, although several others with large holdings in acres overall also have significant cropland acres. The crops grown on easement-protected land include artichokes, strawberries, vegetables and grapes in coastal counties, and field and orchard crops in the Central Valley.The first agricultural easement in California was acquired by MALT in 1983. In fact, most of the easements accumulated by all agricultural programs by 2000 had been acquired only in the previous 5 or 6 years, since the early and mid-1990s. The 12 leading programs quickly established successful records. Other programs in our sample had accomplished far less or had yet to acquire their first agricultural easements, although some had placed significant amounts of non-agricultural land under environmental easements. Each of the leading programs followed a unique path, but they have several underlying factors in common. The most critical element seems to have been early access to funds or other acquisition resources, in part a result of fortunate timing, location and community support. But success was also the result of the skill and persistence of program staff and community leaders in working with landowners and putting together the resources to complete easement deals.The coastal location of four programs gave them access to state conservation funds earmarked for this region. California state government for several decades has targeted the long, narrow Pacific coastline for special conservation measures, starting with the creation in 1972 of the Coastal Commission, a land use regulatory agency. A more beneficial action for landowners was the formation in 1976, by state legislation, of the Coastal Conservancy, which was given the non-regulatory task of preserving coastal areas through landowner compensation. State appropriations began to flow to local agencies after the 1988 passage of Proposition 70. This bond issue generated $776 million for state and local land conservation programs, mainly to acquire and improve parks and wildlife habitat. A small portion of the total, some allocated through the Coastal Conservancy, eventually was used to acquire easements on farmland that had other resource values .

At least four of the successful programs benefited from these actions shortly after their formations. MALT, the Sonoma Land Trust and the Monterey County Agricultural and Historical Land Conservancy, either independently or with their county governments, each received a $1 million grant from the Coastal Conservancy in the mid-1980s. All three land trusts, together with the Peninsula Open Space Trust , a few years later obtained Proposition 70 funds for easement activities. Two land trusts among the 12 leading agricultural programs have prospered from a different type of funding stimulus — local government mitigation of farmland loss, which requires urban development projects to pay for easements on comparable farmland. The Yolo Land Trust received its initial easements as the result of a mitigation ordinance passed by the city of Davis in 1995,the first such municipal action in California. The South Livermore Valley Agricultural Land Trust was formed and acquired many of its easements as the result of litigation,hydroponic bucket in which the city of Livermore successfully challenged a large residential project. Another trust that has concentrated on environmental easements, the Solano County Farmland and Open Space Foundation, also benefits from a mitigation arrangement as a result of litigation involving the city of Fairfield. The Sonoma County Agricultural Preservation and Open Space District is in a different funding category because of its countywide 0.25-cent sales tax, approved by voters in 1990. The district, which relies exclusively on this 20-year revenue source for its operations and purchases, was the only California entity with a dedicated tax for acquiring farmland easements until November 2000, when voters in Davis approved a parcel tax to fund a land conservation program that includes easements.Several of the other leading programs depended largely or primarily on landowner donations of easements, including Napa County Land Trust, Land Trust for Santa Barbara County, California Rangeland Trust and Sonoma Land Trust. All four have broader open space and conservation interests than just farmland protection, and their donated easements have come primarily from owners of large ranches who are generally motivated by the tax benefits or preservation of the environmental qualities of their properties. Beyond their formative years, most of the successful programs have been able to tap a variety of sources to fund easement acquisitions . External sources and landowner donations of easements were most frequently used, particularly grants from state and federal governments and from private foundations. Internal sources, including both private funds and public revenues, were less widely used. California’s strict rules for funding local government programs, especially the restricted property tax and two thirds voter approval requirements for new or increased taxes, severely limit the ability of communities to support easement programs with local taxes.The less tangible elements of program entrepreneurship were also important to the success of the leading programs. Even with early funding opportunities, the leaders of the better-funded programs had to apply skill, focus and persistence, and to work hard over long periods of time, to get their organizations going.

To build a record of acquisitions, they had to look for funds from competitive sources and/or seek landowner donations. Program leaders had to match funding with landowner interests, a process that involved a time sensitive juggling of several interrelated factors: dealing with foundations and state government as funding sources, selecting or seeking out appropriate parcel candidates according to the trust’s priorities, matching available funding with available landowners and negotiating with landowners. Each easement transaction is process unto itself. One land trust manager estimated that the average direct cost of completing a transaction was $15,000 in staff time and other expenses. Another estimated that putting an easement together required several hundred hours in staff time. As much as funding or landowner donations, the critical resources in this process were the personal skill, focus and persistence of program leaders. The successful programs generally have small professional staffs, but they also rely extensively on the work of volunteer boards, which typically include members with expertise in law, resource management, agriculture, finance, land appraisal and other relevant areas. Land trusts with boards composed substantially of farmland owners, such as the Yolo and Merced trusts, are especially equipped to use board members’ local knowledge and personal contacts in persuasive discussions with other farmers and ranchers who own desirable parcels. Explaining this strategy, one land trust manager noted: “The [founders of the trust] knew that they couldn’t be an urban group going out to the farmers and telling them how to change their land. The message had to come from colleagues — other farmers and ranchers in the community.If you want to be effective in agricultural preservation, you need to get along with the people of the land. . . and that includes the Farm Bureau” .Despite recent achievements of the leading programs and general popularity of this non-regulatory technique for preserving farmland, agricultural easement programs have not yet caught on in a substantial way in most of California’s agricultural counties. The limited progress so far may be understandable, considering the still-new status of the technique as a farmland protection tool. In time, with greater familiarity and acceptance in agricultural and other community circles, and fueled by the achievements of the first active programs, there could be a rapid expansion in the number and geographical extent of programs and acres covered . This is not a certain scenario in the near future, however.It takes a high degree of citizen interest or local government support to form a land trust or open space district, qualities not currently present in many agricultural areas. Local and regional organizations run the easement programs, rather than more distant state government and other outside agencies, because successful easement transactions depend on close relations with landowners.

A range of development initiatives to support small-holder agriculture exist in India

Of those, the watershed development program has been the most employed strategy since the 1990s and has focused on socio-economic development through modernizing agricultural production in India’s drylands.The annual investments in WDPs were approximately 4 billion USD between 2009 and 2012 , indicating the program’s magnitude.Currently, it is amalgamated into a larger program under the ministry of land resources with a similar scale of funding.WDPs encourage the promotion of intensive production systems , which are perceived as ideal for developing countries.WDPs, therefore, have been identified as key drivers triggering rapid transitions in farming systems.A recent study mapped the transitions in agriculture and farming systems in a region in Telangana.It also analyzed the effect of transitions in farming systems on smallholder livelihoods in the last 20 years.The study region was subject to various development programs, of which WDPs were the predominant one.That study, in line with other literature , indicate that farming systems before 1997 were primarily subsistence-oriented, with mixed crop-livestock production and where livestock had diverse functions.However, the subsistence farming system dwindled between 1997 and 2015, and specialized and market-oriented production systems emerged.The role of livestock became limited to the food production function.This was also accompanied by a significant change in land use, where croplands increased by 45% at the expense of wastelands that decreased by 75%.Increased regional production with land-use change led to groundwater scarcity in the region.In the end, the study also reported that some HH broke the socio-economic and cultural barriers to climb the “livestock ladder” to engage in, e.g., dairy farming.However, other HHs became marginalized and/or dropped out of the agricultural sector.

A plethora of articles have been published in the early 2000s on the agricultural and economic benefits of WDPs.Later articles indicated sub-optimal program outcomes due to various social, technical,4x8ft rolling benches and institutional issues.However, there is little information about the characteristics of the emergent farming systems and their economic and/or environmental performance.As indicated by Kuchimanchi et al., the fact that rapid transitions have occurred in the area, that more intensive forms of agriculture with altered crop-livestock interactions have led to higher input use, production costs, and investments ; or that development usually entail multiple trade-offs and undesired effects , calls for further research.Therefore, the aim of this study is to gain insight into the characteristics of emerging farming systems and their economic performance in a dryland region of Telangana, India, that has undergone rapid transitions in farming systems.This knowledge will help enhance the customization of WDPs and other development programs and ensure that their impact is sustainable.The two study watersheds are in the Rangareddy and Nagarkurnool districts of Telangana, India.For this research, we considered the administrative boundaries of the villages falling within the watershed, given that the secondary data are aligned with administrative boundaries.The first watershed covers four villages inhabited by 1820 HHs, and the second covers three villages inhabited by 1186 HHs.The HHs in the region are primarily agrarian , and 8.5% are engaged in non-agricultural activities due to higher education or acquiring non-farm skill sets.The predominant land category in the study region is cropland.The study region falls within the Deccan Plateau and Eastern Ghat agro-ecological sub-region 7.2.The area is characterized by deep loamy and clayey mixed red and black soils, with medium to very high available water capacity and a growing season duration of 120–150 days.The climate is characterized by hot, moist summers and mild, dry winters, with an aridity index of 0.2 ≤ AI <0.5.It is therefore classified as a semi-arid region.These districts are drought-prone, with an annual rainfall of 500–700 mm.We collected data in a stepwise approach to characterize the farming systems existing within the study region.The first step consisted of conducting a HH survey in both study watersheds in 2015.It involved face-to-face interviews with household heads using a structured questionnaire.

The data collected in the survey provided an overview of the population: types of livestock reared and herd sizes; farm sizes and categories of farming HHs ; and caste groups present in the region.The caste system in India is a social hierarchical classification of communities based on occupation, which has evolved since ancient times.Based on the government classification, we considered the four main groups: forward castes , backward castes , scheduled castes , and scheduled tribes.Of the 3006 HHs surveyed, 241 had no cropland or reared livestock, and they were excluded from the study.In the second step, we used the data from the household survey to classify the HHs according to the farming system.Our classification method was adapted from studies by Ser´e and Steinfeld , Kruska et al., Notenbaert et al., Robinson et al., and Alvarez et al..The classification was based on two variables: ownership of cropland and dominant livestock species reared.We identified the following farming systems: crop without livestock , crop with dairy , landless with livestock , crop with small ruminants , and crop with diverse livestock , as described further in the Results section.We conducted five focus group discussions, in the third step, one for each farming system.The participating HHs were randomly selected from the survey list.These discussions were intended to gather information on various qualitative characteristics of each farming system.Within each farming-system category, 30 HHs were randomly selected, and 1–2 members of each household were invited to participate.The gender composition of the focus groups was mixed, with participation varying from 25 to 30 people per group.Measures were taken to ensure proper representation from all farm-size categories and social groups mentioned above.If the representation of one of these categories was lacking, we substituted a randomly selected household from the over-represented group with one from the under-represented group.Each focus group discussion lasted 2–3 h and was conducted in the native language.To ensure that the objective of the discussions would be met, a detailed list of questions was used to guide the discussions.The key questions involved characteristics of current farming systems, including cropping and livestock-holding practices, farm infrastructure and use, off-farm jobs, access to fodder and water resources, livestock markets, and animal healthcare.The presence of different groups in each focus group discussion allowed to contrast potential divergent views between groups ‘in situ’.However, and to avoid domination by the wealthy, elderly, or socially forward groups, and to ensure that sufficient time was allocated for documenting information,each focus group discussion was moderated by an experienced facilitator.

All discussions were documented on charts to maintain transparency and enhance interaction with participants.We ultimately combined the quantitative data from the household survey with qualitative data from the five focus-group discussions to characterize the different farming systems.In the final step, we collected data on the economic performance of various farming systems in the study region.Although five farming systems were identified and characterized, we limited economic data collection to the three systems with consistent income from agriculture , based on the information derived from the focus-group discussions.The HHs to be surveyed were selected according to a two-stage sampling process.In the first stage, we selected the village in each watershed with the highest presence of all farming systems.From the selected village i.e.Thalakondapalle, 75 HHs were randomly selected from the complete household list.The selection for the survey was finalized only after HHs expressed their willingness to participate.Those declining to participate were replaced by new HHs until a sample of 25 HHs per farming system was reached.We compared the distribution of castes and farm size among selected HHs to ensure that they were representative of the total regional population.Data on the economic performance of the 75 HHs were monitored once every fortnight from August 2015 to August 2016 across all agricultural seasons in India: monsoon season , winter , and summer.Each household was provided with a data-collection booklet to record data, which data collectors cross-checked at regular intervals.Herd size was expressed in tropical livestock units.The conversion factors were cattle , buffalo , sheep/goats , and poultry.Labor was analyzed according to family type , assuming two working units for nuclear families and five working units for joint families.For the caste grouping prevalent in India, we considered the four main groups: FC, BC, SC, and ST,flood and drain table based on the Indian government classification.We estimated total revenue, costs of production, and gross margins at the household level as follows.The total revenue earned by a household was calculated based on the total quantity of different crop and livestock products sold multiplied by the market price, as obtained from the survey.The total costs of production were calculated based the total input costs for crop or livestock production, hired labor, and rented farm machinery costs, but excluding capital costs.The total GM was obtained by subtracting total costs of production from total revenue.All economic calculations were performed in Indian rupees and then converted to US dollars at an exchange rate of 71 INR.

The statistical analysis was to determine differences among farming systems and to gain insight into factors determining economic performance of those systems.The statistical analyses were performed using the statistical program GenStat , with a significance level of 0.05.To explore whether land use or herd size of HHs would differ across the farming system and/or between watersheds, we performed some preliminary statistical analysis.That analysis showed relevant differences across farming systems only, but not between watersheds.Hence, we performed an ANOVA with a post hoc Tukey test to identify differences in terms of land use and herd size across farming systems.To explore the economic performance of the three farming systems and gain insight into the factors contributing to it, we undertook a two step approach: ANOVA with post hoc Tukey test to identify differences in economic performance across farming systems, and a general linear model for each farming system to identify factors contributing to the GM.In the GLM model, the dependent variable was GM, with the independent variables of herd size, farm size, caste, and family type , along with all two-way interactions.Caste, labor, and their two-way interactions were not significant in any of the farming systems, and they were therefore removed from the model.Given the skewed distribution indicated by the GLM, we followed the approach described by Kuchimanchi et al.for the statistical analyses, converting the values into their natural logarithms.To ensure that values of 0 would also be transformed, we added one unit to all values.Once the tests were run, the mean values and confidence intervals were then back-transformed and one unit was subtracted from each value.This system accounted for the highest proportion of HHs.Most of these HHs were either marginal or small farmers , with medium farmers constituting 21% and large farmers constituting only 2%.The HHs in this system owned very few bore wells, which were seasonally functional.Cropping was thus predominantly rain-fed, with limited irrigated crop production.Low water availability limited crop farming in this system to one agricultural season per year.Mono-cropping of cash crops was predominant.Farmers reported that cropping practices were intensive and required higher investments, as they grew mainly cash crops, rented farm machinery, and used hybrid seeds and inorganic fertilizers.They added that cash crops were preferred to food crops, given their higher market value.These HHs mainly sold the produce, and the crop residues were either burnt or tilled back into the soil.Participants in the focus groups added that increased drought conditions over the years had led to failed crops, reduced yields, and increasing debts.These HHs owned no livestock due to diminishing common property resources for grazing, less family labor, or limited capacity to hire labor or invest in leasing lands for grazing or bore wells.The limited availability of water resources further inhibited them from taking up dairy production.A lack of livestock resulted in greater use of inorganic inputs in crop farming, as livestock manure was unaffordable.Many HHs therefore opted to take off-farm jobs in order to earn income, although they noted that such jobs were not adequately available.Most of the HHs also depended on the public food-distribution system to meet their food needs, as they cultivated mainly cash crops.The second most prevalent category was the CD system.Most of the HHs in this system were medium and small farmers , with marginal farmers constituting 15% and large farmers constituting 12%.The HHs in this system grew cash crops in combination with food crops and perennial green fodder.

Dairying is a very labour intensive enterprise but the cost paid by the farmers was not attractive for farm workers

The present study found that, lack of improved dairy genotypes was reported as the fourth important challenge of dairy production.The low production and reproductive performance of local dairy cows was mainly due to their low genetic potential.Lack of access to artificial insemination services, high prices of improved cows and heifers, and lack of capital were mentioned as the main limiting factors for the lack of improved dairy cows.Therefore, breeding programs which enable dairy farmers to crossbreed their indigenous cows with improved dairy breeds either through natural or AI services should be provided by the government and non-governmental organization.Alternatively, the government or NGO should supply farmers with crossbred genotypes with affordable prices to increase productivity together with improved feeding technologies.Lack of access to credit services was ranked as the 5th most serious problem to dairy production.It was reported that, lack of credit to allow farmers for investing in technological changes is a major constraint to intensification among smallholder dairy farmers.Use of formal credit was a major constraint due to lack of securities as most of the dairy farmers are resource poor.Generally, investment in improved inputs was found to be very low, except farmers who kept crossbred dairy animals.The locally available financial institutions such as state owned commercial banks, micro-finance institutes, and private banks provide credits to commercial businesses, and smallholder farmers lack access to credit services from these financial institutions due to lack of collateral security.Moreover, the farmers feared the high interest rate and short repayment period to borrow from bank.This discouraged farmers to borrow money from banks.Therefore, there is a need from the government to encourage financial institutions to provide access to affordable credit services and long-term repayment to help farmers invest in improved dairying inputs to improve productivity of their dairy animals and household nutrition and food security.

Another major constraint identified by respondents was low productivity of dairy cows.This was associated with lack of improved dairy breeds, which was again attributed to their high prices,hydroponic nft lack of or inefficient AI services and shortage of quality feeds, among others.Non-remunerative prices of milk and lack of preservative facilities especially during the long Orthodox Christians fasting periods and higher milk yields in the rainy season were reported as the main constraints for low milk prices.This result supports that of Debrah and Birhan , who reported the low milk prices and demand of milk was attributed to the long fasting season, whereby the Ethiopian Orthodox followers abstain from consuming milk for more than 150 days/year.Respondents reported that they are unhappy with the prices they were getting for milk during long fasting periods.Therefore, to overcome the low demand and fluctuations of milk prices, especially during the long fasting periods, value addition to milk in form of butter and cheese could make a better market for milk after fasting periods or for home consumption.Moreover, the farmers should be encouraged to establish dairy cooperative or milk collection center in order to have access to formal marketing and strong bargaining power in setting fair prices for their products, as well as to obtain improved inputs such as supplementary feeds, AI, credit, veterinary services and drugs at affordable prices through their cooperative.Shortage of water in the dry season was another constraint identified by farmers in the study area.Support from government and nongovernmental organization for water development such as well water and improving municipality water supply are suggested to mitigate shortage of cattle drinking water in the dry season.According to the respondents, the major causes of feed shortage were lack of land, shrinkage of communal grazing lands, severe scarcity of feed in the dry season, expansion of towns encroaching nearby grazing lands, high prices and unavailability of commercial feeds, lack of forage production, inadequate knowledge on how best use locally available feed resources, and lack of access to credit and capital problems.Hence, there is a need for introduction of alternative feeding system, such as efficient use of locally available feed resources, feed conservation, treatment of crop residues, adoption of Urea Molasses-Mineral-Blocks, concentrate supplementation to lactating cows when affordable, and on farm feed formulation from local feeds as substitute to costly commercial concentrates are suggested to alleviate the causes feed scarcity and ensure all year round feed availability, especially for lactating cows.

As indicated in Table 9, farmers’ revealed that high prevalence of endemic infectious and parasitic diseases, lack of routine vaccination, inadequate veterinary services, lack of proper disease prevention skills, transmission of diseases during communal grazing and high cost of treatment as factors associated with animal health problems.Therefore, training farmers’ and provision of adequate health care extension services on diseases control and best health practices, adequate veterinary services and drug supply, routine vaccination for the most common infectious diseases are suggested.The results presented in Table 9 revealed that lack and/or inefficient AI services, low conception to AI, high cost and unavailability of crossbred cows, more vulnerability of improved breeds to diseases, high management and feed scarcity were reported to be the critical factors for non-adoption of crossbred/improved cows.The study suggests improved access to AI, access to long term and low interest rate credit services for purchasing improved animals, and improving the efficiency of AI technicians to reduce the problem of low conception rate are areas that need to be highlighted for alleviation of the problem.The results of the current study indicated that lack of specific financial systems and policy support in relation to credit services, unavailability of rules for dairy animals to be used as collateral security for borrowing from financial institutes, and fear of the short-term repayment and high interest rate that discourage farmers from borrowing are the main influencing factors for access to credit services.For majority of the respondents it was impossible to buy crossbred cows due to critical limitation of capital.Thus, the government should encourage the local government controlled micro-finance institutes to provide long term and low interest rate credit services that fits the dairy farmers to acquire improved inputs and technologies that improve milk production and their income.Low milk price was also considered another challenge to dairy production.The possible influences reported by farmers were poor genetic merit of local cows, lack of crossbred animals, feed scarcity and lack of supplementation, diseases , and poor management practices.Therefore appropriate measure need to be taken to improve access to efficient AI services for crossbreeding the local breed along with improved husbandry practices in order to increase milk production and farmers income.As indicated in Table 9, the low prices of milk was reported to be associated with seasonal fluctuations in demand especially during the long fasting periods of Orthodox Christians, lack of milk collection center and dairy cooperative, and unavailability of appropriate milk processing technologies to add values to milk to increase its shelf-life during fasting periods, and lack of milk price policy based on the cost of production.

In Ethiopia, Orthodox Christians fast for more than 150 days per year.The long fasting periods are 55 days before Easter and 30 days before Christmas.Farmers sell their milk at farm gate to individual consumers or retailers with low and price fluctuations, due to lack of milk collection center and dairy cooperative, which have major influence on dairy farmer profitability.Therefore, dairy farmers should be encouraged to form dairy cooperative to develop formal milk value chain which function ethically and improve their bargaining power in terms of deciding fair prices and reduce price flactuations and income loss to them and off course for the benefits of milk users.At Agaro town, the existing dairy cooperative was not active and need to be strengthened by providing necessary technical and institutional support.The results of the current study further revealed that the labour shortage as constraint was reported to be associated with high cost of labour and its unavailability.Due to this most respondents relied on family labour for dairy management activities.The result showed that dry season hydroponic channel, shortage of municipality water supply during the dry season and labour shortage for feed and water collection for zero-grazed crossbred animals were reported to be the main associated factors for water shortage during the dry season.In this study, surveyed farmers practiced different coping strategies in response to the challenges they faced aimed at reducing the effects of these constraints to optimize productivity and sustainability of dairy production.Generally, farmers’ perceived effect of the identified challenges on dairy animals was poor productive and reproductive performance, whereas the impacts on farmers were reduced income, food insecurity, and increasing the vulnerability in their livelihoods.Respondents’ suggested supports needed from dairy development stakeholders and government to overcome the identified constraints for sustainability of their dairy farming is presented in Table 9.Generally, the supports needed by the respondents to alleviate the identified constraints to dairy production included breeding, economic, feed and nutrition, genetics, health, and marketing interventions.

The impact of climate change and climate variability on agricultural livelihoods in resource-dependent societies has led to numerous national and international initiatives that aim to improve decision-making through the application of weather/climate information services.This reflects the urgency of adapting to global climate change as highlighted by the Intergovernmental Panel on Climate Change report: Global warming at 1.5 degrees and the need for concerted and aggressive measures to ensure weather information services work at all levels of society.WIS involves the generation, provision, and contextualisation of information and knowledge about the condition of the atmosphere at a given place for up to about 14 days for decision-making at all levels of society, thus making it a sub-type of climate information service.Climate information service is a means through which vulnerability to climate change and climate variability might be reduced and improve the resilience of livelihoods.Although most studies indicate that the use of, and interest in, weather/climate information services have increased over the last decade, every empirical research continues to show that information is not used to its full potential.Overall, the empirical literature on weather and climate information services has revealed usability gaps influenced by many factors.Consequently, the World Meteorological Organization launched the Global Framework for Climate Services in 2012 to provide and facilitate access to weather and climate information services.Hence, the forecast information meets users’ varied requirements through observations and monitoring, research, modelling, prediction, capacity building, and the creation of user interface platforms.The information usability gap, a function of both how weather/climate information services are produced and how they are needed and applied by users in different decision-making contexts, is also narrowed.These, indeed, have resulted in an explosion in research on the use of WIS across regions in different sectors, including farming.In Ghana, climate change through global warming causes consequent variability in weather conditions in the form of increasing dry spell length and frequency, early or late rainfall onsets, and reduction in rainfall amount.The effects of climate change have a negative toll on agricultural production, the mainstay of most of the population.Since food crop production is primarily rainfed, the sector is vulnerable to the adverse effects of climate change.In this context, weather/climate information services support farmers’ adaptive decision-making under uncertain conditions.In Ghana, the weather/climate information service was provided only by the Ghana Meteorological Agency, the sole public organisation responsible for producing and disseminating forecast information.In recent times, business organisation and international NGOs are also providing forecast information.The provision of forecast information for farming includes seasonal onset, weekly and daily rainfall, and temperature conditions.The information is delivered mainly through radios, mobile text messages, workshops, TV, mobile phone, information centre, newspaper, community leaders, and social media.Yet, in most farming communities, the radio is the key medium for receiving weather/climate information because it is relatively cheaper and used without electricity supply.Smallholder farmers also often depend on their local knowledge by using various indicators like the appearance of a flowering plant to determine the pattern of rainfall.Farmers apply the information for land preparations, crop variety selection, changing cropping patterns, applying fertilizer, planning planting time, and managing crop risks.Even so, the uptake of forecast information for decision-making in farming is affected by multiple social-economic and cultural barriers.These include inadequate information on seasonal forecast, high levels of illiteracy, the lack of communication of information in the local language, and non-integration of farmers’ local knowledge into the production of forecast information.

Secure land increased farmers’ decision to participate in social groups by 30 percent

Six indices of social capital among the cocoa-based farming households are identified.The density of membership to associations is 0.636, which means that cocoa-based farming households belong to 6 out of 10 associations.Households belong to various associations in order to promote and protect their business interests.The degree of heterogeneity is considerably high in the area of study.This suggests heterogeneous characteristics such as different ethnicities, occupations, religion and neighbourhoods among the cocoa-based farming households.The decision-making value is fairly high in the associations, which implies that most of the cocoa farming household members are actively involved in decision making within the social group they belong.The meeting attendance value is 0.318, which means that the cocoa-based farming households do not attend most of the scheduled statutory meetings.This could be attributed to the fact that the households trekked an average of 0.70 km to designated meeting points.Hence, they only attend meetings whenever important decisions are to be made.The cash contribution value is 0.652, which means that the cash commitment to associations by cocoa-based farming households is relatively high.This shows that cocoa-based farming households are committed to contributing cash to their respective associations.Also, labour contribution has a value of 0.541, which means that the mean labour contribution is 54 days annually.This result compares favourably with Ajani and Tijani.The aggregate social capital, which is the multiplicative value of density of membership, heterogeneity index and decision-making index is 0.568.The result shows that a fairly high level of social capital exists among cocoa farming households in the study area.The factors that influenced the decision to participate in social groups are shown in Table 3.These characteristics include asset, age, years of education, gender, farm size,ebb and flow trays land tenure, loan interest rate, and extension visit.

The negative signs of marginal effects reduce probability of household participation in social groups while positive signs increase the probability of participation.Assets of households significantly affects the probability of participating in social groups.An additional unit of households’ asset decreased the decision to participate in social groups by 10.9 percent.This implies that increase in asset ownership decreases probability to participate in social groups.The age of household head significantly affected the probability of participating in social groups.A year increase in age of household head increased the decision to participate in social groups by 54.8 percent.This could be attributed to the fact that social groups might prefer older farmers to their younger counterparts, because older farmers are more responsible and secured to participate.In addition, due to some cultural beliefs in Africa, younger people might be prevented from participating in social groups.Years of education of household head significantly affected the probability of participating in social groups.An increase in years of education of household head increased the decision to participate in social groups by 7.7 percent.This implies that education gives farmers the ability to access and comprehend information regarding the terms and conditions required to participate in social groups.The gender of household head significantly affected the probability of participating in social groups.A male household head increased the decision to participate in social groups by 17 percent.This could be attributed to the fact that male headed families are willing to take more risk than female headed families.In addition, due to some social-cultural values and norms of Africans, male farmers have more freedom to participate in different social groups compared to the female farmers.The farm size of household significantly affected the probability of participating in social groups.An increase in hectares of farm size increased the decision to participate in social groups by 28 percent.The result implies that farmers with large farms possess the ability and collateral to participate in social groups.Land tenure status of household head significantly affected the probability of participating in social groups.This could serve as a push factor to participate in social groups in order to put resources to optimum use.

Loan interest rate significantly affected the probability of participating in social groups.A one percent increase in interest rate decreased the decision to participate in social groups by 46.6 percent.This implies that high interest rate constitutes a hindrance to loan access.Extension contacts significantly affected the probability of participating in social groups.A contact of household with extension agents increased the decision to borrow by 5.4 percent.This is because extension services could provide farmers with essential information regarding participation in social groups.The results of the factors influencing cocoa-based farming households’ level of participation in social capital groups are presented in Table 3.These include age of household head, years of education, membership in agricultural organization, off farm income, land tenure, interest rate, distance to credit sources, extension visits, decision making, cash contribution, and labour contribution.The age of household head significantly affected level of participation in social groups.A year increase in age of household head increased the level of participation in social groups by 3.164 units.This could be ascribed to the fact that as farmers get older, they become more productive and increase their level of participation in social groups.Years of education of household head significantly affected level of participation in social groups.An increase in years of education of household head increased the level of participation in social groups by 0.662 units.This is because education equips farmers to make informed decisions about their level of participation in social groups.Membership in agricultural organisations significantly affected level of participation in social groups.Being a member of agricultural organisation increased the level of participation in social groups by 2.085 units.This is attributed to the fact that membership in an agricultural organisation increases access to credit.Non-farm income significantly affected level of participation in social groups.An increase in non-farm income of households decreased the level of participation in social groups by 0.041 units.This is because farmers that earn substantial amounts of non-farm income would less likely need external funds.Land tenure significantly affected level of participation in social groups.Households with secure land increased the level of participation in social groups by 1.858 units.This could serve as a push factor to farmers to increase their level of participation in social groups.

Loan interest rate significantly affected level of participation in social groups.A one percent increase in loan interest rate decreased the level of participation in social groups by 1.225 units.High interest rates constitute a hindrance to the level of participation in social groups.Distance to credit source significantly affected level of participation in social groups.A kilometre increase in the distance to credit source decreased the level of participation in social groups by 0.010 units.Farmers who live near the social group’s designated building have a location advantage, which increases their level of participation in social groups.Extension visits significantly affected level of participation in social groups.Households’ contact with extension agents increased the level of participation in social groups by 0.768 units.Extension services provide essential information to farmers regarding participation in social groups.Decision-making significantly affected level of participation in social groups.An increased unit of the decision-making index increased the level of participation in social groups by 1.424 units.This is ascribed to the fact that decision making keeps individuals abreast of the association’s benefits.Cash contribution significantly affected level of participation in social groups.A naira increase in cash contribution increased the level of participation in social groups by 9.923 units.This implies cocoa-based farming households who made adequate financial contributions to social groups have access to substantial amounts of credit compared to households who did not.Labour contribution significantly affected level of participation in social groups.An increase in labour contribution increased the level of participation in social groups by 3.353 units.This implies that cocoa-based farming households who make adequate labour contributions in social groups have access to substantial amounts of credit compared to households who do not.To test for validity of the instrumental variables used in the 3SLS estimation procedure, a correlation analysis between aggregate social capital, farm productivity and food security with the proposed instruments was carried out.The proposed instruments were length of residency, charity donation, membership in religious group,4×8 flood tray and membership in ethnic groups.The results of the correlation analysis are presented in Table 4.The membership in ethnic groups has significant correlations with aggregate social capital, but an insignificant correlation with farm productivity and food security.It also has the highest correlation coefficient with the social capital.This conforms to the findings of Adepoju and Oni.

The basic model is shown in the first column of Table 6.The rationale behind this model is to examine the farm productivity of the households while they are not involved in social capital activities.The Chi2 showed that the econometric modelling is appropriate and correctly specified.Age of household head significantly influenced farm productivity of the cocoabased farming households.This implies that a unit increase in age of household head decreased households’ farm productivity by 0.836 kg/₦.This is attributed to the fact that ability to do farm work and farm output reduces with ageing.Household size significantly influenced farm productivity of the cocoa-based farming households.This implies that a unit increase in household size increased households’ farm productivity by 0.865 kg/₦.This is attributed to the fact that family labour available for farming could increase farm output.The results agree with Atagher.Primary and secondary education significantly influenced households’ farm productivity.The implication of this is that a unit increase in primary and secondary education increased households’ farm productivity by 0.014 and 0.113 kg/₦, respectively.This could be traced to the fact that education empowers farmers to access required skills and to utilise existing resources on the farm to boost their productivity.Farm size significantly influenced farm productivity of the cocoa-based farming households.This implies that a unit increase in the farm size increased households’ farm productivity by 0.214 kg/₦.This is ascribed to the fact that resources on large farms would increase farm productivity.Interest rate significantly influenced farm productivity of the cocoa-based farming households.This implies that a percentage increase in interest rate decreased households’ farm productivity by 0.346 kg/₦.This is because high interest rate discourages farmers from applying for loans and the amount of the loans farmers receive.Correspondingly, this reduces the quantity and quality of farm inputs that the farmer buys and negatively affects productivity farmer.Loan time lag significantly influenced farm productivity of the cocoa-based farming households.This implies that a unit increase in loan time lag decreased households’ farm productivity by 0.660 kg/₦.This is because long loan time lags would delay the procurement of a loan, which implies that farm inputs will not be available to the cocoa farmers at the right time, quantity and quality.This affects productivity of the farmers due to the seasonal nature of agriculture.This model suggests that households’ social-economic characteristics, farm specific and credit variables play a significant role in improving farm productivity.The second column of Table 6 shows the inclusion of six additive forms of social capital variables identified in this study.These include density of membership, decision making, cash contribution, labour contribution, meeting attendance and heterogeneity.The rationale behind the model is to examine the farm productivity of the households while they are involved in social capital activities.This new model has a better farm productivity level as reflected in a Chi2 of 45.34.This suggests that households’ farm productivity improve as members become involved in the affairs of their social groups.This model shows that the effect of social capital on farm productivity can be traced to meeting attendance, decision making, membership density, and cash contribution.This finding is line with the findings of Balogun et al..Meeting attendance significantly influenced farm productivity of the cocoa-based farming households in the study area.This implies that a unit increase in attendance of meetings increased households’ farm productivity by 6.959 kg/₦.This is because farmers who recurrently attended group meetings have access to resources and information to improve their productivity.Decision making significantly influenced farm productivity of the cocoa-based farming households.This implies that a unit increase in active participation in decision of the group decreased households’ farm productivity by 4.824kg/₦.This means that farmers’ involvement in association matters is of no benefit to their farm productivity.Density of membership significantly influenced farm productivity of the cocoa-based farming households.This implies that a unit increase in the number of groups to which a farmer belongs increases productivity by 0.450 kg/₦.This is attributed to the fact that farmers’ commitment in many social groups enhances their access to loans, which can be used to increase their productivity.

Pollination is critically important for sustaining the world’s terrestrial biota

Geomembranes are generally welded in the field.The seam is considered a critical point for possible injuries and future leaks in the barrier system.Rollin et al.reported that the total number of faults in geomembranes occurred in landfills, ponds and basins, and 55% of them were found at the seams.Stark et al.evaluated seams made by industry and in the field of a polyolefin geomembrane for a water reservoir project.According to the authors, the seams made by industry can minimize dirt and moisture in the seam, ambient temperature changes and wind.After good statistical data work, the results of this research showed that the seams made by industry were 9% stronger than field seams for peel strength and 10% stronger for shear strength.Moreover, seams according to industry data showed less variability.Lavoie et al.evaluated two different HDPE geomembrane samples exhumed from a municipal landfill leachate pond and a sewage treatment aeration pond.The authors conducted thermal, physical and mechanical analyses.The thermogravimetric analyses showed an altered decomposition behavior for the landfill leachate pond sample, probably caused by the interaction with the leachate.The sewage pond sample presented low stress cracking resistance and low tensile elongation at break, compatible with the dynamic mechanic analysis , which showed an increase in the stiffness.Ewais and Rowe studied an HDPE geomembrane with 1.0 mm of the thickness of about five years immersed in synthetic leachate at different temperatures and in air and water at 55 ◦C.The authors observed changes in the sample’s stress crack resistance values before chemical degradation and before antioxidant depletion for temperatures lower than 70 ◦C.The major SCR value decrease was noted for the sample immersed in leachate at 55 ◦C, reaching 26% of the SCR value of the virgin sample.

This behavior was attributed to morphological changes during aging that affected the interlamellar connections due to the annealing that increased the strength of the inter-lamellar connections and the proposed chain disentanglement mechanism.HDPE geomembranes are often utilized as a flow barrier in landfills, mining facilities, canals, waste liquid ponds,mobile vertical farm and farm ponds.This research evaluated three exhumed high-density polyethylene geomembrane samples from two different shrimp farming ponds after 8.25 years of field exposure for the first pond and 3.0 years of field exposure for the second pond.Thermoanalytical and physical analyses were used to understand the final conditions of the HDPE geomembrane samples.Analyses such as thickness, density, carbon black content, melt flow index , tensile properties, stress crack resistance, oxidative-induction time , thermogravimetry,differential scanning calorimetry,and dynamic mechanical analysis were performed.Using an HDPE geomembrane as a liner of a shrimp farming pond is limited to some places globally, such as the northeast region of Brazil.This work aims to provide new data on the HDPE geomembrane performance in shrimp farming pond applications.This work evaluated three high-density polyethylene geomembrane samples exhumed from two different shrimp farming ponds in the northeast of Brazil with 0.8 mm of nominal thicknesses.The samples called “CAM” and “CAM1′′ represent the same geomembrane installed in a shrimp farming pond and were collected after 8.25 years of field exposure.The CAM sample was exhumed from the bottom liner and had been in contact with the salinized water.The CAM1 sample was exhumed from the same pond as the CAM sample, but it was taken from the slope liner and had been in contact for 8.25 years with environmental conditions.The third sample was exhumed from another shrimp farming pond after 3.0 years of service.This pond has the particularity of being covered with an agricultural plastic film.Figs.1 and 2 show, respectively, the shrimp farming pond representing the CAM and CAM1 samples and the shrimp farming pond representing the CAM2 sample.Table 1 presents the salinized water parameters used for shrimp cultivation.

However, nesting habitats and foraging resources for pollinating insects have decreased severely due to intensification in agricultural landscapes.Developing effective mitigation tools to counteract pollinator losses is essential for satisfactory pollinator diversity and sustainable agriculture.In Europe, agri-environment schemes are among the most valuable instruments to reduce the pressure of agriculture on the environment.The new Common Agricultural Policy of the EU also aims at increasing their share by targeting one-fourth of the direct payments to subsidise eco-schemes.AES offer two main tool types to support biodiversity and thus pollination, i.e.productive and non-productive schemes.Organic farming is one of the most favoured productive management systems where farming intensity is reduced with a preference for mechanical methods over agrochemicals.In their meta-analysis, Tuck et al.found that organic farming increased overall species richness by 30 %, with plants benefiting the most.Pollinator insects also profit from organic farming.Flower strips are flower-rich non-crop landscape features created at arable field edges.The annual or perennial strips are formed to enhance invertebrate pest control and pollination by providing forage, shelter, and nesting places.As AES schemes differ in concept, they should be evaluated against each other to prioritise them for benefits to biodiversity.Functional trait-based assessments offer an effective tool for studying community functionality, redundancy and stability in agroecosystems.Different management types can support various arthropod taxa by maintaining specific plant functional traits and high functional trait diversity.Plant traits associated with visibility, quantity, and quality of floral resources are the most important traits shaping pollinator communities.For example, plants with large, conspicuous inflorescences attract pollinators efficiently , while floral patterns resulting from UV reflection are also important signals to several major pollinator groups.Nectar is the primary reward for pollination; therefore, spatial and temporal variation in nectar volume influences pollinator behaviour and survival.As land-use significantly affects pollination-related flower traits , their diversity can indicate the quality and quantity of floral resources and can be used to evaluate AES schemes for pollinators.Different field parts with different management regimes can support biodiversity and pollination to varying degrees.The interior of arable fields covers the largest area of agricultural landscapes; therefore, its ecological condition may be decisive for biodiversity at the landscape scale.Intensive management within field interiors favours plants with ruderal strategies , and selects for species with early flowering and selfing.Crop edges are also shown to be keystone transitional zones for pollinators and support increased plant diversity compared to field interiors as they are expected to contain both typical arable weeds and species originating from grassy margins.

Linear non-crop landscape elements such as grassy margins along field edges are less intensively managed than field interiors and also provide important shelter and forage resources for various taxa in agricultural landscapes.The overall performance of AES schemes on pollination should be quantified by assessing all characteristic parts of the agricultural fields.Landscape-scale factors should also be considered beside local factors when studying the effects of AES schemes on pollinators and their services.The effectiveness of AES varies by landscape heterogeneity that has two main components.Compositional heterogeneity describes the relative amount of habitats in the landscape, whereas configurational heterogeneity refers to their spatial arrangement.Most studies assessed the effect of landscape composition on pollinator communities and found that pollinator abundance and richness were higher in landscapes comprising more high-quality habitats.The role of landscape configuration is less studied, though it may also be very important as landscapes with smaller fields have higher structural connectivity and more edges providing more floral resources for pollinators.Given this research gap, here we focus on the role of the less studied configurational heterogeneity by assessing landscape-scale mean arable field size.Our study presents a trait-based approach to estimate the potential of two agri-environmental schemes to support pollinators based on floristic composition.For this, we studied plant traits associated with pollinator attraction and reward accessibility.We calculated community-weighted trait means and functional trait diversity in organic and conventional winter wheat fields complemented with sown flower strips and compared them to conventional fields along a gradient of landscape configurational heterogeneity.We tested whether management intensity and landscape heterogeneity select for specific pollination-related plant traits, and result in differing trait diversity by using literature data on species traits.Our specific hypotheses were the following: Pollination-related plant trait diversity is reduced with increasing mean field size within the landscape.Flower strips and organic farming maintain functionally more diverse plant trait composition than control conventional fields.Pollination-related plant trait diversity decreases from grassy margins to field interiors in both conventional and organic fields.We considered only insect-pollinated plant species that may attract pollinators and provide nectar resources.We assessed the following traits: flower size, flower colour, UV pattern in the flower,vertical farming racks reward quantity, and flowering duration.Trait values were collected from the BiolFlor database and identification books.Flower size was expressed as flower diameter.For zygomorphic flowers, the mean of the longest and shortest diameter was calculated.In the case of compact inflorescences that can be regarded as one functional pollination unit, we used the size of the whole inflorescence.We expressed flower colours on a continuous wavelength scale.White-flowered species got the mean value of the visible light spectrum.The presence of UV pattern in the flower was treated as a binary variable.In the case of reward quantity, we considered only nectar resources because of no available information about pollen resources for the majority of the species.Nectar quantity was provided on an ordinal scale with four categories.

The average flowering duration was coded as a continuous variable.For each transect, we calculated the total number and average percentage cover of insect-pollinated plant species.We quantified transect-level community-weighted means for each trait by averaging trait values weighted by species abundance.We tested the effects of management type , transect position , mean field size on the species richness and cover of insect-pollinated plant species, Rao’s quadratic entropy and the CWM and FD values for each trait by using linear mixed-effects models.We used generalized mixed-effects models for species richness with Poisson error distribution and log link function.For each response variable, we started with a model with all two-way interactions of the fixed effects and then selected the minimum adequate model from all possible nested models with the minimum Akaike Information Criterion value.The effect of years was not assessed per se but was treated as a random effect in the analyses.The field, farmer, and landscape identities were also used as random effects nested within each other and crossed with year.We used log transformation for cover values and square root transformation for CWM and FD values if necessary to fulfil test assumptions.We restricted our assessment on those 151 transects that harboured at least one insect-pollinated plant species for flower colour analyses to have meaningful results.We derived marginal and conditional coefficients of determination of the models to estimate the variance explained by the fixed effects and the entire model including both fixed and random effects using the MuMIn.We conducted multiple GLMM tests, therefore, we controlled for the false discovery rate.Post hoc pairwise comparisons were made with the em means package , and were presented in the figures.All analyses were conducted in the R environment.We found that flower strips and organic farming outperformed conventionally farmed fields, as they had the highest insect pollinated plant species richness and supported higher trait diversity favourable for pollinators.Flower strips were superior with the highest cover of insect-pollinated plants and the highest ratio of flowers showing UV patterns.Although annual flower strips doubled the insect-pollinated plant species richness in the grassy margins, the benefits of flower strips completely diminished in neighbouring field interiors.In contrast, organic field interiors could be considered the most favourable pollinator habitat among the studied field interiors based on plant pollination traits.Thus organic farming can enhance pollinators at a larger spatial scale with more environmentally friendly crop production on the whole area of the arable land.We did not find any effect of configurational heterogeneity expressed as mean arable field size.We showed that organic farming outperformed conventional farming practices regarding insect-pollinated species richness, flower attractiveness, and food resources provided for pollinators.This is primarily due to lower overall farming intensity in organic fields.Even organic field interiors offer abundant and diverse flower resources to pollinators compared to conventional farms.Thus, we can consider organic farming the most beneficial method based on pollinators’ resources.In contrast, intensively managed conventional fields supported the lowest richness of insect-pollinated plant species showing that only a few plant species could establish here randomly.Annual flower strips sustained the most favourable vegetation for pollinators, considering the quantity and quality of flower resources.They had six times higher cover of insect-pollinated plants than the edges of the other two farming methods.

Features that focus on pigs vary from features of live pigs to features of meat

We assessed that the first 50 publications contain sufficient information for answering the research questions and thus were used as exclusion criteria. The primary studies with their authors and publication year are included in the appendix . To get insight into the relevance of the topic for this SLR, the results of the broad and narrow search results are grouped by year of publication and presented in Fig. 1 and Fig. 2, respectively. When looking at the number of primary studies published for the broad search query, it seems that there are downward trends in 2010 and between 2014 and 2018. This is however due to the high number of publications that were found and the exclusion criteria that affected publication in those years disproportionately. Many publications were excluded because they were outside of the 50 most relevant publications. However, there is a consistent and sharp increase in the number of publications since 2018 both for the narrow and broad search queries. To get insight into the focus of the primary studies, we have categorized the studies by topic . The categories clearly indicate that majority of the studies were on pig health. Most studies focussed on the presence, spread, or outbreak of diseases, and few studies focussed on the causes and prevention of boar taint. In the selected primary studies, pig health and the performance of pig production were researched often. The production performance was investigated by analysing various parameters, such as the DNA of pigs,rolling bench fat composition of pig meat, meat quality, and muscle thickness. This shows that the production performance of pig farming was mostly measured using the attributes of the meat measured after the animals are slaughtered. Besides pig health and pig production results, other topics were researched.

Several feeding strategies have been developed and evaluated. Further, research was done to test if the origin of meat could be traced and on-farm environmental influencers, such as disease spread in manure and temperature effects on pigs. The narrow search query focused more on the application of ML and the topics of research are summarised in Table 7. According to the search results, most of the research focussed on performance related issues, such as pig performance, feeding strategy, and genetics. Pig health is the second most researched area, focusing mainly on diseases. The trend of using ML for disease detection through image and video analysis is reflected in the number of primary studies found on this topic. Pig detection and behaviour analysis were also performed using ML. Feeding strategy was analysed using basic statistical analysis and using ML. There were also primary studies that focus on detecting the origin of meat, detecting stress in pigs. A detailed description of the topics of research per primary study is shown in Appendix B. As can be seen in Table 8, a variety of data were used for research in the pork industry. Data were largely collected from body and tissue . The rest of the data reported refers largely to measurements of the external characteristics of the animals and their living environment or feed . There were also primary studies that used data on manure and micro-arrays. The type of data used per primary study is shown in Appendix E. The results of the analysis of data from the second search query focused on the application of ML to pig farming are shown in Table 9. The table shows the widely used features used in research. The features used can be grouped into features on pigs and features on climatic conditions.Pork meat information, images and recordings, growth, occupancy and reproduction, genetics, and pig movement have been used to build and validate models. The features on climatic data consist of data about indoor or outdoor climatic conditions, or both. Data used in those primary studies consist of outside temperature, indoor temperature, and relative humidity. The features used per primary study are shown in Appendix H.

The location of data gathering provides insight into the main sources of research data. We have categorized the locations where data are gathered into groups , which shows that most of the data is gathered at farms and slaughterhouses. The farms were sometimes conventional farms where a specific group of animals was monitored closely; other times, they were experimental farms used for precisely monitoring growing conditions and pig behaviour. Slaughterhouses serve as one of the main data gathering locations. The quality and composition of meat are important indicators of production performance; therefore, data from slaughterhouses where these indicators are routinely measured, are important sources of data. Other locations of data gathering for research include laboratories , externally collected data, previous research, or large database where data are shared. Further, data was collected at distribution centres, urban abattoirs, and there was a case of data from a virtual simulation. The data gathering location per primary study is shown in Appendix C. To get an overview of data analysis methods used in the primary studies, the algorithms or principles used were calculated as shown in Table 11. Least squares regression was used most often, followed by logistic regression. The primary studies found by the broad search query did not often use complex algorithms; instead, they applied variations of the linear regression model. All data analysis methods used are shown in Appendix F. All primary studies found by the second search query used ML algorithms. Random forest algorithm was used most, followed by neural networks and support vector machine, as is shown in Table 12. Compared to the primary studies found by the broad search query, those found by the narrow search query used more complex analysis models.

The algorithms used per publication are shown in Appendix G. Eight studies using models based on random forest and/or neural networks recorded an R-squared accuracy scoring higher than 0.7. The challenges stated include difficulty in scaling into large-scale farms due to differences in the environment between the experimental setup and large scale farm, and other features that influence the performance. Table 13 shows what has been studied, and if the research subjects were pigs, it shows the size of the group of pigs studied. A total of 26 primary studies considered live pigs, from which measurements were made. The number of pigs used for research varies significantly, from 5 to 908,582 pigs. Three primary studies considered farms as a whole, focusing on the growing environment of the pigs. Further, data on meat quality and faecal samples were used by some studies. There were also studies that used externally collected data, virtual experimental data, RNA pools, and liver pasts. Appendix D shows the research group types and sizes per primary study. Much research has been using data on genetics, pig breeds, meat quality after processing, disease recognition, and factors influencing diseases. Research that focused on the prevention of negative aspects of the final product is, for example, research done on boar taint and the attempt to reduce it. Boar taint in meat results in a lower price for the carcass. A variety of challenges have been stated in the studies regarding ML. The largest challenge is making the algorithms perform consistently high for all situations. Many studies reported that it was feasible to define a well performing model for the specific research setup and condition the model is trained and tested on but it was in general not possible to guarantee the same level of performance in practice. Mostly, more data and more features are required in order to improve the overall performance of the models developed.The original aim of this study was to review the literature on the use of advanced data analytics techniques in real-life business scenarios. We tried diverse search strings in order to find studies that are not based on experimental set-up be based on the use of data sources from real-life production chains. But the number of results we obtained was low.

We were unable to find any study that fused data from the whole production chain except one by Ma et al. . Ma et al. developed an intelligent feeding equipment and network service platform,roll bench using sensors, software, and monitoring units. This system helped in optimizing feeding methods and improving pig management. We considered, therefore, two search strings, a broad and a narrow search string: the former focussing on general data analytics and the second on machine learning. In both cases, we used more generic terms and relied on exclusion criteria to select the relevant studies. We consulted five scientific databases in this SLR, namely: Science Direct, Scopus, Web of Science, Springer Link, and Wiley. We did not consult Google Scholar initially which returned 16,300 publications, a vast majority of which were irrelevant, and thus filtering out the relevant publications was infeasible. The exclusion criteria we selected ensured that only publications that are accessible and of high quality were considered. The exclusion criterion on year of publication was based on our initial test search results. While research performed 20 years back is likely outdated, the set year allowed us to get a clear view of the trend in the studies published. This made it clear, for instance, that the number of primary studies increased substantially from 2018 onwards, particularly on the application of machine learning in the pork sector. When analysing the results of the SLR, we grouped the attributes such as features, data types, or algorithms we found. Grouping the results allowed us to derive clear conclusions. The detailed results are however included as appendices to this study. As can be seen in the increasing number of primary studies since 2018, the application of ML will be important in the pork sector in the future. When looking at the algorithms used in this context, studies that used features and data on images and recordings often used neural networks, specifically convolutional neural networks algorithm. For example, Cowton et al. , Mukherjee et al. , and Fernandes et al. focused on pig recognition and deviations in behaviour. Studies that used pork meat information often had random forest as best performing algorithm. The focus of the research using pork meat information was to investigate growth performance or the state of health .

What is striking in our review is that most of the research conducted use only groups of pigs selected for an experiment. Most of the studies are conducted in large pig farms; however, the numbers of animals studied within the farms were often small, indicating the studies were conducted on an experimental basis and not on the entire herd. While the focus on a selected group of pigs helps to accurately track and monitor pigs, it does not reflect the real-life situation. Therefore, it remains unclear whether the solutions found in research could be applied in real-life business cases. Out of the 41 primary studies we considered through the broad search query, only 10 involve more than 500 pigs, and of which only two, performed by Naatjes et al. and Haraldsen et al. , used real-time data from farm management systems. Research based on real-life data is scarce and most studies focussed mainly on isolated and one-off problems. We suggest that future research should consider the complexity encountered in real-life circumstances and the integration of data analytics within the management systems so that the analytical results can be used within routine business processes. The Republic of Botswana has an installed capacity of 550 MW with an estimated population of 2.3 million of inhabitants. It is reported that the country has one of the highest national electrification rates in Africa determined as 60 % with 77 % of the population connected to electricity in urban areas and 37 % connected in the rural areas. According to Statistics Botswana, it is stipulated that the Government has set national electricity access target of 82% by 2016 and 100 % by 2030. With an average energy demand of more than 400 MW, Botswana relies mainly on fossil fuels energy sources such as coal, fuel wood, and petroleum and an imported power from South Africa to meet needs of the population. Additionally, the country is also known for its particularity in renewable energy sources such solar, wind and various forms of bio-energy such as bio-fuels and biomass wastes.

Organic fertiliser application was slightly increased in KE-C and GH-NC while it was reduced in KE-NC2

In the non-certified case studies, rather small percentages of farms fully followed the rules of OA. In KE-NC1, the case study with the most promising approach, up to 42% of farmers worked organically, without any certification, while in GHNC and KE-NC2 only 16% and 28% did, respectively. Remarkably, in four case studies, the share of smallholder farmers in the control group that did not use conventional inputs was below or around 10%. In KE-NC1, the rate was about 21% . This is contrary to literature, where organic-by-default is often indicated to be common among smallholder farmers in SSA . This indicates the increasing availability and usage of conventional inputs as found by De Bon et al. and Andersson and Isgren . Especially pesticide use among smallholders is far more widespread than commonly assumed . Getting accustomed to conventional input use may lead to a decreased willingness of smallholder farmers to convert to an entirely organic system and agroecological principles . However, input use in SSA varies substantially between countries , therefore these results cannot be extrapolated to other countries. Farmers replacing conventional inputs with either preventive or curative agroecological practices can address nutrient and pest management issues under organic management. These practices include, among others, applications of botanical pesticides, such as neem; preventive practices can involve a more diverse rotation, agroforestry or intercropping systems.We specifically analysed whether the interventions led to an increased uptake of a) practices substituting conventional inputs for pest, disease and weed management, b) practices for substituting mineral fertilisers, and c) further agroecological practices.

Looking at the effect of the interventions on the uptake of AOM practices, our data shows no widespread systematic adoption in any of the case studies.Among the agroecological practices,hydroponic barley fodder system only the diversity of crop rotations was affected positively in GH-NC and KE-NC1 while it was even less diverse in KE-C and KE-NC2. For the remaining components of AOM, we did not find consistent differences between the intervention and control groups. While at least one of the interventions led farmers to adopt POM, AOM was not adopted widely in any of the case studies, despite that all of the interventions aimed at such an adoption. This shows the importance of considering innovation dynamics and transition time frames when introducing organic agriculture to smallholder farmers, as their decision-making is dynamic, multi-dimensional and contextual . Transferring information and skills to famers via group trainings is an important component of capacity development, but needs to be embedded in a long-term process and governance structure, which allows a group of smallholder farmers to learn and explore practices on their own farms and identify ways of combining practices that fit into their specific production system. Compared to applying mineral fertilisers, herbicides and pesticides, agroecological practices are usually knowledge-intensive and require understanding of complex ecological principles . In order to understand the low uptake rates of organic farming practices by farmers in the organic intervention groups, we analysed a) motivations to convert to organic agriculture and b) the implementation challenges as perceived by the farmers. In the two certified organic case studies , high potential economic returns motivated farmers to practice organic farming , while non-financial reasons were less apparent. In the non-certified case studies, the primary motivation to practice organic farming was non-financial with the exception of GH-NC, where 54% of the responding farmers had primarily financial reasons. The differences in motivations and expectations are partly driven by the implementation approach of the intervention. For instance, in KE-NC1, much time was prior invested to make farmers aware of the non-financial benefits of organic farming such as human and environmental health.

While in most case studies, little difference between the responses of adopters and non-adopters could be observed, farmers adopting organic management practices in KE-NC2 and GH-NC had a higher share of financial motivations . The most prominent challenges that the organic intervention farmers faced were: pest and disease damage during crop cultivation and post harvest stages , lack of stable markets , inadequate training and extension services , unavailability of inputs and additional labour required due to weeding . The importance of the challenges was perceived differently in the various case studies. Generally, the Ghanaian farmers perceived the agronomic challenges as more important than the Kenyan ones. Furthermore, our assessment of uptake of farmers is reflected in severity of the challenges, as farmers in KE-C and KE-NC1 who were exposed to these interventions perceive the challenges as overall less severe . While there is only little empirical evidence reported in literature about motivations and challenges of organic farmers in SSA , the technical challenges, such as weed infestation and damage by pests and diseases, are similar to those found in Switzerland by Home et al. although the Swiss farmers in their study reported that these barriers were less severe than they had estimated before conversion to organic. Following the analysis of the effects of the interventions on the adoption of practices, we analysed how OA, as a production system, performed. For this, we compared all farms in each case study, those who worked organically with those who did not, regardless of whether they were part of the intervention group or not . We analysed the differences in yields, inputs, labour and gross margins of the four most widely grown crops in each of the five case studies, using an entropy balancing approach for estimating a sound counterfactual . Among the total of 20 crops analysed from the five case studies, we found four organically managed crops with significantly higher and four crops with significantly lower yields . Input cost was significantly higher for three crops each, while inputs were significantly lower for eight crops and labour was lower for six crops . This resulted in higher gross margins for four organically managed crops, while only one crop had significantly lower gross margins under organic management . Comparing the two certified case studies, farmers practicing OA performed very differently in their productivity and profitability.

Except for reduced cocoa input costs , no significant differences in yields and gross margins between organically and conventionally grown crops could be observed in GH-C. Contrary, we observed higher yields for the economically most relevant crops , while banana yields were lower in KE-C. Input cost was reduced or stayed similar, while labour cost was increased for coffee and macadamia nut in KE-C. Despite labour cost was higher, the gross margins of coffee and macadamia nut increased by 336% and 185%, respectively. Less pronounced differences were found in the non-certified case studies: in GH-NC, yields of organic farms were similar to conventional farms for the four crops, almost no purchased inputs were used and labour was reduced for maize , groundnuts and millet . Gross margins of organically managed crops were at similar levels to their conventional counterparts, except in the case of maize . In KE-NC1, however, organically managed brassica and maize yields were lower than for conventional farmers but other crops were not significantly affected. Maize input cost was significantly lower while labour costs were lower for beans, maize and roots. Overall, no significant differences in gross margins were observed in KE-NC1. On the other hand, in KE-NC2, pea yields were higher, while the other crops remained unaffected by organic management. In this case study, organic farmers significantly reduced input cost for mango while labour cost for peas was higher. In terms of gross margins, there were no significant differences, except for peas . Except for macadamia nut in KE-C,livestock fodder system the organically grown crops in our case studies were not sold with/did not generate a price premium. To assess the importance of local and international markets for organic produce, we therefore tested the impacts of a general 20% price premium for the organic farmers for sensitivity analysis . Assuming an organic price premium, POM gross margins would be higher than the conventional counterpart for bananas in GH-C, coffee in KE-C, beans and maize in GH-NC, roots in KE-NC1, and beans and peas in the case of KE-NC2. The high variability of organic yields and gross margins through organic farming is mostly consistent with findings of meta-studies that are mainly based on data from high-income countries . The methodological difficulties of comparing organic smallholder producers in low-income countries and the resulting uncertainty resulting from the definition of a sound counterfactual led even to a higher uncertainty of impacts of organic agriculture on smallholder yield and profits. Some authors identify strong yield increases due to organic agriculture , while others criticise methodological flaws.

We observed positive effects of organic farming practices at farm level productivity in one of the five case studies . Higher farm level gross margins could neither be achieved in the other certified case study nor in the three non-certified case studies . As, at least in GH-C, organic price premiums were originally supposed to be realised, the farm-level gross margins were analysed under the assumption that at least 20% of price premium could be realised due to the organic management. For the pooled sample over all five case studies, OA had significantly positive impacts on gross margins . Under such an assumption, the organic farmers in four of the five case studies would have realised higher gross margins than the farmers who managed their farms conventionally. Besides KE-C, GH-C , GH-NC and KE-NC1 would also have performed better, while for KE-NC1, there was no significant difference observed. For the pooled sample, OA had significantly positive impacts on gross margins . Our results show that there is no one silver bullet for increasing profitability among smallholder farmers . Profitability increasing effects observed over all the five case studies can be associated with labour input in general and specifically with the number of hours spent on pruning as one of the key specific good agricultural practices for the perennial crops such as macadamia nut, mango and cocoa. When used, the application of organic fertilisers had significantly positive impacts, while conventional fertilisers and pesticides affected the revenues rather negatively. Organic insecticides did not have significant yield effects while copper did. Contrary to findings from field trials , further organic and agroecological management practices resulted mostly in no remarkable economic benefits assessed for the farmers in our study . This could signify that the levels of inputs and practices applied by farmers in our study were still low and not optimal as supported by on-station long-term trial findings in Kenya . Contrary to results from field studies and meta-studies, which report the productivity of organic agriculture crop-specifically , our study shows that contextual factors such as the governance and capacities of smallholder cooperatives are important factors determining the agronomic and economic performance of OA, too.

Many authors suggest that capacity development measures, which are implemented alongside organic projects, are responsible for a large share of the revenue increases that were observed in other studies . In our study, we therefore, controlled for the number of training events from both government and non-governmental organisers. Overall, organic farms had similar numbers of training events and extension visits by NGO and government agents in all case studies, except in KE-C, where the number of governmental and total trainings was even lower than for conventional farms . Government trainings were generally rated lower by organic farmers than by conventional farmers in KE-NC1 and KE-C. On average, NGO trainings were rated better in terms of effectiveness compared to the governmental-based trainings. This indicates a potential for improvement and strengthening of trainings and extension services offered by governmental agents. This further indicates that there are large differences in the perceived quality of NGO training provided to the farmers. There is a great diversity of smallholder farmers in Africa. Much of the on-going controversial discussion about OA is due to a lack of a clear classification and the very heterogeneous characteristics and performances that one can realise on farms that may all be called “organic” on a superficial level . Therefore, based on the results from our study, we propose a terminology for organic farms that can bring more transparency in the debate and can be used to assess the current situation and design tailored public and private policy interventions. Fig. 4 distinguishes organic farming systems according to a) the degree they follow the principles of OA  and b) the intention to work organically .