scholarly journals A NEW ERA FOR SUSTAINABLE FARMING SYSTEMS FOR GREECE, BASED ON CONVERGENCE OF SMART FARMING, AGRICULTURAL ROBOTICS AND GEOSPATIAL TECHNOLOGIES

2021 ◽  
Vol 06 (01) ◽  
pp. 114-133
Author(s):  
Dr. Avraam Mavridis ◽  
Dr. Athanasios Gertsis
Author(s):  
Alvaro Rocca ◽  
Francesco Danuso ◽  
Franco Rosa ◽  
Elena Bulfoni

2016 ◽  
Vol 72 (1) ◽  
pp. 5A-9A ◽  
Author(s):  
Adam Reimer ◽  
Julie E. Doll ◽  
Bruno Basso ◽  
Sandra T. Marquart-Pyatt ◽  
G. Philip Robertson ◽  
...  

1992 ◽  
Vol 7 (3) ◽  
pp. 122-128 ◽  
Author(s):  
Thomas L. Dobbs ◽  
David L. Becker

AbstractWe analyzed two sets of farm policy options, representing different ideological approaches to government involvement in agriculture, to estimate their effects on the relative economic attractiveness of “sustainable” and “conventional” farming systems. The mandatory supply control approach, through strict acreage limitations on program crops, represents a strong government role in commodity supply management. The Normal Crop Acreage approach, on the other hand, allows farmers greater flexibility in deciding what crops to grow. We used economic models of five pairs of case study farms in different agroclimatic areas of South Dakota, covering corn-soybean, spring wheat, and winter wheat growing regions. Mandatory restrictions on the planted acreage of “program” crops, including soybeans, were found to favor the conventional systems, because they induced high prices for crops that predominate in conventional systems, especially com, soybeans, and wheat. In principle, however, mandatory acreage controls could require compliance with certain sustainable agriculture practices. Normal Crop Acreage (NCA) proposals can encourage greater use of sustainable farming systems. Where conventional corn and soybean production is relatively profitable, as in parts of eastern South Dakota, NCA options by themselves appear insufficient to induce changeovers to sustainable cropping systems. In wheat growing areas of northern and western South Dakota, however, where the two systems oflen are about equally profitable, NCA policies could promote sustainable systems, particularly if deficiency payments are not reduced for harvesting legumes and other non-program crops on NCA base. To have this positive effect, NCA policies must be introduced gradually and structured to limit adverse effects on the markets for legumes and other non-program crops that are important in sustainable rotations.


1999 ◽  
Vol 39 (5) ◽  
pp. 605 ◽  
Author(s):  
R. C. Dalal ◽  
P. Lawrence ◽  
J. A. Doughton ◽  
J. Walker ◽  
R. J. Shaw ◽  
...  

Community awareness of the sustainable use of land, water and vegetation resources is increasing. The sustainable use of these resources is pivotal to sustainable farming systems. However, techniques for monitoring the sustainable management of these resources are poorly understood and untested. We propose a framework to benchmark and monitor resources in the grains industry. Eight steps are listed below to achieve these objectives: (i) define industry issues; (ii) identify the issues through growers, stakeholder and community consultation; (iii) identify indicators (measurable attributes, properties or characteristics) of sustainability through consultation with growers, stakeholders, experts and community members, relating to: crop productivity; resource maintenance/enhancement; biodiversity; economic viability; community viability; and institutional structure; (iv) develop and use selection criteria to select indicators that consider: responsiveness to change; ease of capture; community acceptance and involvement; interpretation; measurement error; stability, frequency and cost of measurement; spatial scale issues; and mapping capability in space and through time. The appropriateness of indicators can be evaluated using a decision making system such as a multiobjective decision support system (MO-DSS, a method to assist in decision making from multiple and conflicting objectives); (v) involve stakeholders and the community in the definition of goals and setting benchmarking and monitoring targets for sustainable farming; (vi) take preventive and corrective/remedial action; (vii) evaluate effectiveness of actions taken; and (viii) revise indicators as part of a continual improvement principle designed to achieve best management practice for sustainable farming systems. The major recommendations are to: (i) implement the framework for resources (land, water and vegetation, economic, community and institution) benchmarking and monitoring, and integrate this process with current activities so that awareness, implementation and evolution of sustainable resource management practices become normal practice in the grains industry; (ii) empower the grains industry to take the lead by using relevant sustainability indicators to benchmark and monitor resources; (iii) adopt a collaborative approach by involving various industry, community, catchment management and government agency groups to minimise implementation time. Monitoring programs such as Waterwatch, Soilcheck, Grasscheck and Topcrop should be utilised; (iv) encourage the adoption of a decision making system by growers and industry representatives as a participatory decision and evaluation process. Widespread use of sustainability indicators would assist in validating and refining these indicators and evaluating sustainable farming systems. The indicators could also assist in evaluating best management practices for the grains industry.


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