Supporting food security in the 21st century through resource-conserving increases in agricultural production
© Uphoff; licensee BioMed Central Ltd. 2012
Received: 30 July 2012
Accepted: 9 October 2012
Published: 1 December 2012
The Green Revolution was accomplished under a set of demographic, economic, climatic and other conditions in the 20th century that have been changing and will surely be different and more difficult in the decades ahead. The suitability and sustainability of any given agricultural technology depends on factors like resource availability and productivity, energy costs, and environmental constraints. The achievements of Green Revolution technologies in the 1960s and 1970s came at a critical time of impending food shortages, and the world’s people would be worse off without them. However, the rate of yield improvement for cereal production has been slowing since the mid-1980s.
Looking ahead at the foreseeable circumstances under which 21st century agricultural producers must try to assure food security, there will be need for technologies that are less dependent on resources that are becoming relatively scarcer, like arable land and water, or becoming relatively more costly, like energy and petrochemical-based inputs. This paper considers agroecologically-based innovations that reduce farmers’ dependence on external inputs, relying more on endogenous processes and existing potentials in plants and soil systems. Such resource-conserving production represents a different approach to meeting food security goals.
While these innovations are not yet fully understood and are still being researched, there are good agronomic reasons to account for their effectiveness, and scientific validations are accumulating. Enough successes have been recorded from making changes in the management of plants, soil, water and nutrients that more attention from researchers, policy-makers and practitioners is warranted, especially given the need to adapt to, and to mitigate the effects of, climate change. The same agroecological concepts and management methods that are enhancing factor productivity in rice production are giving similar results with other crops such as wheat, finger millet, sugarcane, mustard, and tef.
Genetic potentials are the starting point for any and all agricultural production, and current efforts to improve food security and nutrition through plant breeding efforts should continue. However, future research and production strategies could beneficially seek to capitalize on biological processes and potentials existing within crops and in their supporting soil systems, rather than focusing so predominantly on making modifications in genetic factors. Scientific advances in the domains of microbiology, soil ecology and epigenetics could foreseeably assist farmers in meeting production and income goals with resource-economizing methods. It remains to be seen to what extent agroecologically-informed methods can help farmers meet expected agricultural production requirements to ensure global food security, but this direction deserves more attention and support.
KeywordsAgroecology Food security Green revolution Soil biota System of rice intensification
An overriding challenge for agricultural research and practice in the 21st century will be to produce more food and fiber with less investment of our land, labor, capital and (particularly) water resources. This large order must be met in the context of less favorable weather conditions for much if not most of our planet, as weather shifts and variability are becoming ever-more evident constraints for agricultural scientists, policy-makers, and practitioners.
Dr. Norman Borlaug and his generation of agricultural scientists gave leadership in the 20th century to meeting the challenge faced then of ‘feeding a hungry planet’. Fortunately, they achieved some quick and remarkable technological advances under the banner of the Green Revolution. It does not detract from their accomplishment of raising cereal yields substantially to note, however, that these gains were made mostly in Asia, and that the opportunities were not equally distributed across all sizes of landholding. A more crucial consideration at present is that these improvements have been slackening over the past 25 years.
Without the increases in production that resulted from the Green Revolution, millions of people would have suffered from sickness and hunger, and many would have died if there had not been significant increases in food availability in the latter part of the past century. This accomplishment is evident from a 50% decline in the relative real price of food over a four decade period.
But this favorable trend has been reversed, with food prices again rising in recent years. Moreover, we have to deal now with some very stark constraints foreseeable in this century. Many millions of agricultural producers, particularly in Africa, need to raise their production very substantially with the resources that they have at hand if life-saving levels of food security are to be achieved and maintained, to keep hunger, poverty and other woes from becoming more widespread.
Reckoning with a changing world
The world situation 50 years ago with rapid population growth presented an ominous, even dire, threat to the well-being of all people, rich and poor alike. In the 21st century, this pressure has fortunately abated as population growth rates have fallen dramatically over the last three decades. Still, the momentum of even decelerating population growth means that we must reckon with 9 to 10 billion people as the lowest peak population that can be expected in this century, and some of the poorest countries still have very rapid population growth.
It is good news that the ‘population bomb’ now appears unlikely to explode. A world population which stabilizes at less than 10 billion, and then possibly declines, is only half as large as what demographers were predicting when I began working on development issues over four decades ago. Deceleration of population growth, to be sure, brings some of its own challenges, as there may not be enough productive younger countrymen and women to support elderly populations. However, such problems are less difficult to cope with than the multiple ‘bad news’ trends that we need to grapple with now.
In this century, we face a threat to our welfare and even to our existence that is even more inexorable and potentially devastating than population growth - climate change. It is neither alarmist nor paranoid to point out that the continuation of our human species depends on remaining within the ranges of temperature, precipitation and other climate parameters within which our and other species have evolved.
While humans are unique in their ability to expand the range of environments in which they can live, drawing on our intelligence, culture and technology, the means for extension and adaptation of human habitats do not come free, and the ranges that are physiologically as well as economically tolerable are fairly narrow. There are significant economic and environmental costs as well as some social and cultural costs involved.
Agriculture as a sector is uniquely sensitive to, and dependent on, weather factors. As we think about our countries’ agricultural sectors in the future, we need to figure out how we can cultivate our crops, raise our livestock, and fish our water bodies with more resource-economizing methods, no longer using water, metals, chemicals and fuels as profligately as in the past. Furthermore, how can we devise ways to protect our soil systems, watersheds, forests, hydrological cycles and agroecosystems - indeed, how can we restore and replenish them?
Most of the concepts, principles, laws and even methodologies in our scientific domain have been developed within the realms of chemistry, physics and engineering, where closed-system thinking is realistic, indeed necessary. Biology, on the other hand, operates with the non-linear logic of open systems, where small inputs can produce large outputs, but also where huge inputs can give no output at all. While biology has inputs and outputs parallel to those that drive chemical and physical processes and that get channeled by engineering, its throughputs function quite differently.
When trying to understand, maintain and improve open-system phenomena, we should guard against mindsets and assumptions that were derived from, and are appropriate to, closed systems. While engineering concepts can be applied to agriculture, this does not mean that agriculture should be seen or managed simply as an industrial enterprise. Although agricultural practice has many industrial characteristics and opportunities, it remains essentially biological. This becomes even more evident as we gain a better understanding of some microbiological dimensions of agriculture as discussed below.
When doing more of the same won’t do
The changing circumstances under which agriculture will be practiced in the 21st century are likely to make less effective and less economic the agricultural technologies that were successful in the preceding century, even with some modifications and evolutions. The foreseeable world presents us with rather different conditions and constraints than we had to deal with in the past.
As explained by Hayami and Ruttan , past changes in agricultural technology have been driven by changing factor proportions. These inexorably reshape and redirect our future technological paths, reflecting the relative amounts and productivities of land, labor and other resources. The added impacts now of climate change will make the need for different, even novel technological solutions even more certain.
Agriculture in the 21st century will have to deal with major alterations in the physical and institutional landscape:
Arable land per capita is declining. While different definitions of land quality can lead to different numbers, the combination of continuing population growth and land degradation is surely lowering this ratio. By some calculations, by the middle of the 21st century there will be about one-third as much cultivable area per person as 100 years earlier, falling from about 0.25 ha to 0.08 ha per person. Land-extensive strategies will thus become less tenable as the ratios of population-to-land continue to change substantially .
Supply of water, absolutely essential for agricultural production, is becoming less reliable as well as less available for farmers. This is a result of competing uses, of declines in water quality and of shifting weather patterns, so economizing on water is becoming an agricultural and social imperative; getting ‘more crop per drop’.
Energy costs in the 21st century will almost certainly be higher than in the 20th century, making energy-intensive production more costly. This applies to the mechanization of operations as well as to our present dependence on petroleum-based agrochemical inputs. Also, patterns of agricultural production and consumption that involve long-distance movement of commodities will become less economic as transport costs rise. This will make local production economically more competitive with distant agricultural operations that were previously considered to have a comparative advantage. Moreover, the increasing use of grains to manufacture biofuels in response to the rising prices for energy contributes to increased prices of food grains, which adversely affects particularly the food-insecure.
Environmental concerns are affecting the acceptability of various agricultural practices in many places. Negative externalities such as adverse effects on water, soil and air quality and biodiversity losses are becoming less tolerated than in the past, given larger and denser human populations and more urban political influence.
Pest and disease problems are likely to increase, partly in response to climate changes, but also with pest resistance to agrochemical controls as a factor. Despite a 14-fold increase in the amount of pesticides used in the US after World War II, the percentage of crops lost to pests increased in this period from 6% to 13% . The theory of ‘trophobiosis’ may help account for this phenomenon of chemical-induced vulnerability of crops to pest and disease losses .
Climate changes will make all of these other trends more challenging for agricultural producers. Altered temperature and rainfall patterns will not be felt equally because there will be winners and losers from change; but especially the poorer countries, and the more marginalized farmers within them, appear likely to bear the greatest brunt of new weather regimes and of the greater uncertainty and variability that these bring. ‘Extreme events’ are likely to become both more frequent and more extreme: droughts, storms, flooding, heat waves, cold periods, disadvantaging both producers and consumers at the same time.
To make matters worse, government capabilities to deal with these many problems appear less coherent, less stable, and less statesmanlike, with less commitment and less ability to achieve effective functioning of their economies, societies and administrations. Our legislative and governing bodies are increasingly beset by narrow partisanship and jockeying for short-term personal or factional advantages. Also, we are seeing in many parts of the world an attenuation of cultural and political inhibitions against large-scale use of violence - that genie which governments previously kept bottled up with at least some success.
Governments’ fiscal capacities are almost everywhere stretched to the breaking point. Accumulating debts and voter disaffection are reducing public-sector willingness and ability to invest in (or subsidize) inputs and improvements in agriculture, even though the central importance of food has not diminished. Farm subsidies and export restrictions in many countries, maintained as a result of governments’ political weakness rather than strength, continue to exert upward pressures on food grain prices that affect the food-insecure.
Furthermore, the forces of globalization, while they may open up many opportunities, seem also to contribute to socio-economic instability and inequity that make national governance ever more difficult. Simply the greater scale and complexity of modern societies and economies appears to be making our institutions and practices of governance less effective.
Slowing gains in agricultural productivity cast an ominous shadow over this whole scene. The rates of growth in cereal production during the 1970s and 1980s were truly remarkable, although we should notice that the rate of yield increase was even higher in the 1960s before Green Revolution technologies began taking effect. World grain production per capita, according to FAO and USDA statistics, peaked in 1984, with the rate of grain production increases falling ever since. The world’s total grain production has been stagnant or declining since the mid-1990s [5–7].
The global food crisis in 2007 to 2008 with its huge price jumps was prompted by multiple factors; but an underlying cause was the tightening of world food supplies relative to demand. It is true that with available resources and improved technology, more food could have been produced in recent years if there had been higher market prices for food. However, if food had been more expensive, this would have increased the extent of hunger and poverty in the world, both of which are still unacceptably pervasive.
All these considerations make it imperative to find ways to raise our agricultural productivity, to make our available resources, land, labor, water and capital more productive. We need to be enhancing food supply particularly on the basis of productivity gains rather than trying to evoke more food production through the incentive of higher prices, as this will increase food insecurity for millions of households.
There are ongoing efforts to improve food security through genetic improvements that focus on yield, resistance to various biotic and abiotic stresses, and improved nutritional value through biofortification. While some of these gains may be some years away, they are worth pursuing. But in the present and near future, we need to be achieving greater productivity of the key factors of production: land, labor, and especially water, as well as capital.
The more resources which are require for meeting people’s food needs, the fewer resources are available for meeting other needs, for investment in human resources, for housing and infrastructure, for expanding research and development in other fields. Resources expended in food production cannot be used to improve output and well-being in other sectors. This makes the quest to find ways to produce more food with fewer resources important for the whole world as we head into an uncertain, fairly ominous future.
Capitalizing on existing biological opportunities
Making improvements in our global ability to meet people’s needs for sustenance will not solve all of the many problems that face our governments and societies around the world. But if we cannot produce and provide sufficient food to everyone - if we tolerate large pockets of hunger and misery, and have large domains of desperation with loss of hope for the future - most of the other problems that loom on the global agenda will remain beyond solution.
The limited and, in many respects, shrinking resources that are available for agricultural production dictate that we intensify our production practices rather than continue with the land-extensive strategies that expanded in the 20th century, relying heavily on mechanization and economies of scale. In the 21st century, these strategies for food production, being energy-intensive and chemical-dependent, will become less attractive and indeed less economically viable as factor proportions and relative prices change.
The word ‘intensification’ when applied to agricultural production has usually referred to an intensification of input use. The logic of such intensification - and the cost-benefit analysis that guides it - has been to compare how much more of what inputs will yield how much more in resulting outputs? If the value of the resulting outputs from production is sufficiently greater than the cost of the inputs needed to produce them, this represents a net gain. This strategy has been bolstered by plant-breeding efforts which have developed genotypes that are more responsive to additional inputs of water, fertilizer, and agrochemicals. There has been an underlying assumption that we always need to increase inputs to raise production, with the expectation that a greater increase in outputs will result to justify the expenditure.
Current agricultural development efforts focus particularly on improving G to achieve maximum increases from the resources invested. A management-oriented strategy, conversely, starts with the best available G, focusing on how to improve those factors that constitute the E for their crops’ growing environments both above and below ground. The logic of cost-benefit analysis is turned on its head when we try to calculate a ratio between reduced inputs and greater output. This may be why agroecological alternatives are widely viewed with skepticism.
Raising food production, especially for the food-insecure
An agroecological innovation that has demonstrated remarkable gains in food output is the System of Rice Intensification (SRI) developed in Madagascar [9–11]. This methodology for raising the productivity of all the resources devoted to rice production (land, labor, seeds, water and capital) departs from the intensification strategy that relies on new varieties with genetic improvement and then on greater external inputs.
The yield effects of intensifying crop management with SRI methods have been a matter of some controversy among rice scientists, for example [17–20]. But governments in China, India, Indonesia, Cambodia and Vietnam, where two-thirds of the world’s rice is produced, have become satisfied from their own evaluations that factor productivity is greatly enhanced by SRI changes in rice crop management. Two of the world’s most eminent rice scientists, Dr. MS Swaminathan and Prof. Yuan Long-ping, have satisfied themselves from their own evaluations that SRI methods lead to more productive rice plants and have recommended SRI use in their respective countries, India and China .
In 2007 the Ministry of Agriculture and Rural Development in Vietnam, after three years of evaluations, concluded and declared that SRI represented a ‘technical advance’. At that time, fewer than 10,000 Vietnamese farmers were using SRI methods. Four years later, in 2011, the Ministry announced that over 1 million Vietnamese farmers were using most or all of the recommended SRI practices - with higher yields, less water, lower production costs, and improvements in environmental quality . See news report at http://qdnd.vn/qdndsite/en-US/75/72/182/156/189/164012/Default.aspx.
The management changes introduced with SRI include: use of younger seedlings if the rice crop is established by transplanting (note: direct-seeding is also beginning to be used with the other SRI practices); greatly reduced plant populations by planting single seedlings in widely-spaced hills; no continuous flooding of paddy fields; controlling weeds with a mechanical weeder that aerates the soil; plus enhancement of the soil’s organic matter as much as possible.
Review of SRI management impacts on yield, water saving, costs of production, and farmer income per ha in 13 countries
Farmers (N) or Trials/Area
Conven-tional yield (t/ha)
SRI yield (t/ha)
Yield increase (%)
Water saving (%)
Impact on cost per ha (%)
Impact on income per ha (%)
Coverage of evaluation and agency doing study [source of data]
Aga Khan Foundation program in Baghlan district 
2-year study by NGOs and Syngenta under IRRI program auspices 
5-province study done for GTZ 
Study of all 3-year SRI users by CEDAC 
Village study by China Agricultural University in Sichuan province 
Total area 2004 to 2010 : 301,967 ha
Additional income: US$320 million
Provincial Department of Agriculture data, 2004 to 2010 
IWMI-India programme study in W. Bengal 
Andhra Pradesh state
Evaluations by AP state university ANGRAU 
On-farm trials managed by Nippon Koei TA team, 2002 to 2006 
Mwea irrigation scheme trials, 3 replications 
Mwea irrigation scheme trials, 4 replications 
Timbuktu region under Africare program 
8.7 times more
FFS results in Kachin and Shan States, 3 years 
District agricultural extension program, Morang 
Far Western region
10 communities, evaluation by NGO 
IWMI study in 2 districts 
MARD FFS results from 13 districts 
Total N and Averages
It is understandable that SRI results have been received with some incredulity. However, the bases for these increases in productivity are becoming better understood. The most evident factor is the greater root growth induced by SRI methods (Figure 1b). Less visible but now being documented are the methods’ impacts on soil biota that provide benefits to rice crops [42–45]. Similar benefits are now being seen when SRI methods have been adapted to other crops such as wheat and sugarcane [46, 47], finger millet, mustard, tef, and some legumes and vegetables. This adds credibility to the remarkable results that have been reported for rice.
For some years, skeptics rejected SRI because they considered some of its reported results to be impossible. The top yields reported from Madagascar were characterized as being above the biological maximum achievable with rice . However, in the 2011 kharif season in the Indian state of Bihar, five first-time SRI farmers in one village (using hybrid varieties) matched or exceeded the previous world-record yield for paddy of 19 tons/ha. According to Bihar Department of Agriculture data, one achieved a yield of 22.4 tons/ha, almost ten times the average paddy yield for the state. The dry weight was an unprecedented 20.16 tons/ha . These measurements, made with standard methods and with hundreds of observers looking on, have been officially accepted.
The controversy over SRI maximum yields has unfortunately deflected attention from the large differences in average yields, which should have been the central focus of discussion. SRI methods have often enabled poor farmers to double, triple or even quadruple their yields, not just individually but on a village level, without having to purchase new varieties or agrochemical inputs [49–52]. Such resource-limited farmers started at very low levels of production, it is true. But for them, to go from 1 ton per hectare to 4 tons, or from 2 tons to 8 tons, without added costs of production, makes a huge difference in their food security and well-being. For the 2011 kharif season, the Bihar Department of Agriculture in India has calculated an average SRI yield of 8.08 tons/ha on 335,000 hectares across all 38 districts of the state. This was more than three times the state-wide average of 2.5 tons/ha.
It has been argued that the ‘best management practices’ (BMP) recommended by scientists can give better results than reported from SRI practices . However, the evidence and analysis presented to support this claim are seriously flawed . More importantly, the paddy yields reported above from Bihar state show the argument to be simply wrong; SRI methods can surpass what best conventional practices can achieve by yielding more productive phenotypes. The five Bihar farmers who got SRI yields matching or exceeding the previous world record got less than half as much yield from their hybrid varieties when these were grown on the same farms, with the same soil and same climate, using conventional crop management methods.
The contention that BMPs are superior to SRI disregards the fact that many millions of small and marginal farmers do not have access to, or cannot afford, the new seeds and other inputs required for what are considered as BMP. For hunger and poverty to be reduced, we need methods that substantially improve farmers’ productivity with the resources and means that they have at hand. A variety-based, input-dependent strategy of agricultural development has inherent limitations for reducing world hunger and food insecurity in a significant way.
Experience with SRI methods has directed our attention to the symbiotic relationships between plants and soil microbes, which parallel the growing realization that humans and other members of the animal kingdom are themselves thoroughly interdependent with, and for that matter, dependent on microorganisms, referred to collectively for humans as the human microbiome. The microbiomes of plants are no less important. Appreciating this fact re-focuses our thinking from engineering and chemical solutions to capitalizing more upon biological and ecological processes and potentials.
It has long been known that the root zones (rhizospheres) of plants are domains of intense and mutually beneficial interaction between plant roots and soil organisms [56, 57]. Research has shown that certain soil organisms in fact inhabit the leaves, sheaths and stalks of rice plants, that is, their phyllosphere; and controlled trials have demonstrated that this ‘infection’ of above-ground plant tissues by soil bacteria is associated with the plants having larger canopies and root systems, higher levels of chlorophyll and more photosynthesis in their leaves, greater water-use efficiency, and higher yield [15, 58].
Moreover, the presence of soil rhizobia in the tissues of leaves and sheaths of rice plants has been seen to up-regulate certain genes that produce proteins supportive of photosynthesis and other functions in the canopy; and these same microorganisms, in the roots of rice plants, enhance the expression of genes in tissues there that produce proteins conferring greater protection against pathogens . Plant growth and performance are thus assisted by the presence and influence of soil microbes.
Signaling between roots and shoots via phytohormones has been shown to contribute to higher yield with reduced fertilizer inputs and to healthier plants that resist pathogens . Even more surprising may be the results of replicated trials in which rice plants grown from seeds inoculated with a certain fungus (Fusarium culmorum) have been found to have five times more root growth in their early days after germination, and their root hairs emerge two days sooner. The fungus, when residing in seeds, enhances the plants’ ensuing growth and robustness .
The contributions that symbiotic endophytes, microbes living mutualistically within plant tissues and cells, can make to crop performance and health are becoming more evident . Learning how to utilize and benefit from positive microbial influences could possibly enhance crop productivity in parallel with the improvements that are expected to be made in human health as a result of contemporary research on the human microbiome. Research on the microbiomes of crop plants should be similarly productive.
Focusing research on ecological rather than only on species productivity
These findings suggest that we consider making some shifts in the predominant focus for agricultural research. Present strategies are based on ever-increasing use of inputs in conjunction with making improvements in genotypes, with a species focus. There is reason to explore more how improving crops’ environments above and below ground through changes in plant, soil, water and nutrient management can elicit more beneficial expression of crops' genetic potentials, recognizing that these are affected by ecological factors.
Previously, agricultural researchers have focused separately on individual species of plants or animals in isolation from other species. Finding ways to capitalize upon symbiotic relationships among various species -- considering sets of species together in ecological perspective, such as with the ‘push-pull’ crop management system developed in East Africa to deal with striga infestation -- can create multiple benefits at low cost .
Soil scientists have been evaluating plants' performance often under axenic soil conditions, where all life in the soil has been eliminated by fumigation or sterilization. If the effects of soil organisms are studied, possibly just one or two species would be added back to look at their effect under what are called gnotobiotic conditions in otherwise axenic soil. This latter word is curious because ‘axenic’ is constructed from Greek semantic roots which mean ‘without strangers’ (a + xenos). This formulation implies that soil organisms are to be considered as strangers or foreigners within their own natural habitat .
Future agricultural research, in light of recent findings, will do well to examine the performance of crops and livestock within their ecological contexts. Species improvement should be attempted in the context of interactions with other species rather than in isolation. This is one way in which we can ‘re-biologize’ agriculture, having been guided for the past half century more by the disciplines of chemistry and engineering in league with the science of genetics. The disciplines of microbiology, soil ecology, and epigenetics will, foreseeably, become more prominent within the agricultural sciences, focusing in particular on understanding better how genetic potentials are expressed (epigenetics), appreciating that it is phenotypes and not genotypes that we consume as food.
Some implications for plant breeding
SRI practitioners have found that the greatest yields obtained with their methods have come from what are called high-yielding varieties (HYVs) or hybrids. So, agroecological approaches do not negate the basis for genetic research. The world-record yield reported above was with a hybrid variety with application of some inorganic fertilizer, although there was primary reliance on organic fertilization, that is, on integrated nutrient management . It is also true, however, that many local or indigenous varieties also respond well to SRI management, with some giving yields over 10 tons/ha. (The world average is about 4 tons/ha.) Since the market price for local varieties is often higher because of consumer taste and other preferences, growing ‘unimproved’ cultivars with SRI practices can be more profitable than using HYVs.
The kind of plant breeding that Norman Borlaug and his colleagues undertook has been very successful and deserves our appreciation. But it may not be as suitable a strategy for the emerging conditions that will be faced in the decades ahead. Both breeding and management are essential for success, combining the effects of G and E; that is clear. But since the 1990s there have been diminishing returns from breeding strategies, whereas over the past decade we have been seeing from SRI experience that very great impacts on yield can be achieved by making changes in crop management, as apparently this has beneficial impacts on crops’ relationships with their microbial symbionts [43, 45].
One can find very little in the Green Revolution literature that examines the contributions of roots and soil biota to plants’ health and growth. These are the factors that SRI experience and its extrapolation to other crops are pointing to as very potent. For decades, plant breeders have sought through genetic improvements to raise the Harvest Index (HI), that is, the proportion of plant biomass that is found in the edible portion. But the focus has all been on above-ground plant organs. The biomass in plant roots has not even been considered when calculating HI.
The abundant growth of roots has been largely ignored or even deprecated by plant breeders, much as profuse tillering has been disapproved. The prolific growth of roots and shoots was thought to be wasteful and in competition with - rather than supportive of - grain production. (I have been told, twice, by a senior agronomist in the US that ‘roots are a waste’, because they lower the Harvest Index). However, crops in this current century will need to be more naturally resistant to pest and disease assaults and to be buffered from drought, from rain and wind damage, and from temperature stresses. Root development and more abundant, more diverse soil biota are likely to become more appreciated for their promotion of crop resilience and for their enhancement of productivity in the face of climate-change pressures.
Future research opportunities and modes of operation
There is widespread agreement on the need for ‘another Green Revolution’, but the operational shape and direction of this effort remains to be determined. Agricultural scientists have begun to investigate and evaluate SRI methods only in the last few years, and these methods are rapidly spreading to other crops with similar effects. SRI ideas and methods were developed inductively by a Jesuit priest  based on observations and field experimentation, so there are surely many opportunities for scientists to make improvements and to determine limitations in this methodology.
The symbiotic relationships between crops and beneficial microorganisms appear to be a particularly fruitful area for research [43, 61]. Studying rhizosphere biology can illuminate changes in underground dynamics that occur when plants are grown using SRI methods. For example, spatial and temporal variations in redox gradients can lead to qualitative and quantitative changes in microbial populations and activity [42, 66]. Recent analysis has underscored the importance of optimizing redox potential which has its basis in soil biology as much as soil chemistry and soil physics .
Research at the Indian Agricultural Research Institute has shown that SRI methods of cultivation not only increased water productivity (with a 27% saving of irrigation water in these trials), but they also enhanced soil microbial activity, micronutrient uptake, and the N content in both soil and grain, compared to conventional transplanting methods [45, 68]. Biofertilizers and microbial inoculants when used with SRI management may further contribute to the prolific growth of roots and facilitate nutrient mobilization and uptake in rice, with improvements in grain quality. Much research remains to be done.
Along with a refocusing of research in microbiological directions, it should be noted that SRI experience encourages agricultural scientists to work more closely with practitioners, both farmers and NGO personnel, who presently have more knowledge of this innovation than anyone else. Advances in the future are likely to come from observations, experience and thinking from many sources, not just from the formal agricultural disciplines.
There is no reason to think that SRI and other agroecological concepts and practices will replace all other kinds of agriculture; agricultural change does not proceed so discontinuously. Norman Borlaug reasonably insisted that agricultural development be science-based. This means that innovations should be examined and evaluated objectively and systematically, although this does not mean that all innovations must originate from the formal scientific community, or that knowledge and data coming from sources other than credentialed scientists should be excluded from consideration.
Norman Uphoff has been on the faculty of Cornell University since 1970 as a professor of government and (since 1990) of international agriculture. From 1990 to 2005, he served as director of the Cornell International Institute for Food, Agriculture and Development (CIIFAD), and he is currently director of the Cornell Institute for Public Affairs (CIPA), while also senior advisor to the SRI International Network and Resources Center (SRI-Rice) based in CIIFAD.
This paper updates a presentation made at a forum organized by the Norman Borlaug Foundation at the 2010 BioVision Alexandria International Conference, held at the Alexandria Library in Egypt in April 2010. Inputs from Dr. Radha Prasanna, senior scientist in the Indian Agricultural Research Institute, New Delhi, are gratefully acknowledged.
- Hayami Y, Ruttan VW: Agricultural Development: An International Perspective. 1985, Johns Hopkins University Press, Baltimore,Google Scholar
- UN Environmental Program: The Environmental Food Crisis: environment’s Role in Averting Future Food Crises. 2005, http://www.grida.no/publications/rr/food-crisis/, Nairobi,Google Scholar
- Pimentel D: Techniques for Reducing Pesticides: Environmental and Economic Benefits. 1997, John Wiley, Chichester, UK,Google Scholar
- Chaboussou F: Healthy Crops: A New Agricultural Revolution. 2004, Jon Anderson Press, Charnley, UK,Google Scholar
- Pingali PL, Hossain M, Gerpacio RV: Asian Rice Bowls: The Returning Crisis?. 1997, CAB International, Wallingford, UK,Google Scholar
- Dyson T: World food trends and prospects to 2025. Proc Natl Acad Sci (US). 1999, 9: 5929-5936.View ArticleGoogle Scholar
- Uphoff N: Agricultural futures: What lies beyond ‘modern agriculture’?. Trop Agric Assoc Newsletter. 2007, 27: 13-19. http://www.bioscienceresource.org/cms/documents/TAA%20%20Bunting%20Lecture.pdf,Google Scholar
- Reichardt W, Dobermann A, George T: Intensification of rice production systems: opportunities and limits. Rice in the Global Food System. Edited by: Dowling NG, Greenfield SM, Fischer KS. 1998, 127-144. International Rice Research Institute, Los Baños,Google Scholar
- Uphoff N: Opportunities to achieve resource-conserving increases in agricultural productivity: learning from the System of Rice Intensification (SRI). New Life Sciences: Future Prospects – Proceedings of BioVision Alexandria 2010. Edited by: Serageldin I, Masood E, El-Faham M, El-Wakil M. 2011, http://www.bibalex.org/BVA2012/attachments/staticpages/file/Publications/BVA2010_Web.pdf, Biblioteca Alexandrina, Alexandria,Google Scholar
- Stoop WA, Uphoff N, Kassam A: A review of agricultural research issues raised by the system of rice intensification (SRI) from Madagascar: opportunities for improving farming systems for resource-poor farmers. Agric Syst. 2002, 71: 249-274. 10.1016/S0308-521X(01)00070-1.View ArticleGoogle Scholar
- Uphoff N, Kassam A: Case study: System of Rice Intensification. Agricultural Technologies for Developing Countries: Final Report, Annex 3. 2009, European Parliament, Brussels,Google Scholar
- Hameed KA, Mosa AKJ, Jaber FA: Irrigation water reduction using System of Rice Intensification (SRI) compared with conventional methods in Iraq. Paddy Water Envir. 2011, 9: 121-127. 10.1007/s10333-010-0243-1.View ArticleGoogle Scholar
- Lin XQ, Zhu DF, Chen HZ, Cheng SH, Uphoff N: Effect of plant density and nitrogen fertilizer rates on grain yield and nitrogen uptake of hybrid rice (Oryza sativa L.). J Agric Biotech & Sust Dev. 2009, 1: 44-53.Google Scholar
- Mishra A, Salokhe VM: Seedling characteristics and early growth of transplanted rice under different water regimes. Exper Agric. 2008, 44: 1-19.View ArticleGoogle Scholar
- Thakur A, Uphoff N, Antony E: An assessment of physiological effects of system of rice intensification (SRI) practices compared to recommended rice cultivation practices in India. Exper Agric. 2010, 46: 77-98. 10.1017/S0014479709990548.View ArticleGoogle Scholar
- Zhao LM, Wu LH, Li YS, Lu XH, Zhu DF, Uphoff N: Influence of the System of Rice Intensification on rice yield and nitrogen and water use efficiency with different N application rates. Exper Agric. 2009, 45: 275-286. 10.1017/S0014479709007583.View ArticleGoogle Scholar
- Dobermann A: A critical assessment of the system of rice intensification (SRI). Agric Syst. 2004, 79: 261-281. 10.1016/S0308-521X(03)00087-8.View ArticleGoogle Scholar
- Sheehy JL, Peng SB, Dobermann A, Mitchell PL, Ferrer A, Yang JC, Zou YB, Zhong XH, Huang JL: Fantastic yields in the system of rice intensification: fact or fallacy?. Field Crops Res. 2004, 88: 1-8. 10.1016/j.fcr.2003.12.006.View ArticleGoogle Scholar
- Sinclair TR, Cassman KG: Agronomic UFOs. Field Crops Res. 2004, 88: 9-10. 10.1016/j.fcr.2004.01.001.View ArticleGoogle Scholar
- Stoop WA, Kassam AH: The SRI controversy: a response. Field Crops Res. 2005, 91: 357-360. 10.1016/j.fcr.2004.07.023.View ArticleGoogle Scholar
- Uphoff N: Comment to ‘The System of Rice Intensification: time for an empirical turn’ [NJAS: Wageningen Journal of Life Sciences 57 (2011) 217–224]. NJAS: Wageningen J Life Sci. 2012, 59: 53-60. 10.1016/j.njas.2012.02.001.Google Scholar
- Castillo GE, Minh NL, Pfeifer K: Oxfam America: learning from the System of Rice Intensification in Northern Vietnam. Scaling Up in Agriculture, Rural Development and Nutrition. 2012, Brief No. 15, International Food Policy Research Institute, Washington DC,Google Scholar
- Thomas V, Ramzi MA: SRI contributions to rice production dealing with water management constraints in northeastern Afghanistan. Paddy Water Envir. 2011, 9: 101-109. 10.1007/s10333-010-0228-0.View ArticleGoogle Scholar
- Husain AM, Chowhan G, Barua P, Razib Uddin AFM, Ziaur Rahman ABM: Final Evaluation Report on Verification and Refinement of the System of Rice Intensification (SRI) Project in Selected Areas of Bangladesh (SP 36 02). 2004, Report to IRRI/Bangladesh Programme from BRAC, POSD, SAFE and Syngenta/Bangladesh Ltd, Dhaka, Bangladesh,Google Scholar
- Anthofer J: The potential of the System of Rice Intensification (SRI) for poverty reduction in Cambodia. 2004, http://www.tropentag.de/2004/abstracts/full/399.pdf, Phnom Penh: Summary of report prepared for GTZ, Berlin,Google Scholar
- Tech C: Ecological System of Rice Intensification (SRI) Impact Assessment (2001–2003). 2004, Report of the Cambodian Center for Study and Development in Agriculture (CEDAC), Phnom Penh,Google Scholar
- Xu XL, Li XY, Li H: Socioeconomic impact analysis of SRI in China.China Rural Economics (in Chinese). 2006, English version available: http://scholar.google.com/scholar_url?hl=en&q=http://ciifad.cornell.edu/SRI/countries/china/cnciadeng.pdf&sa=X&scisig=AAGBfm1lE2WtonKhHMxx_5aPAnSAuB5QXA&oi=scholarr,Google Scholar
- Zheng JG, Zhou L, Chi ZZ, Jiang XL: Agricultural water savings possible through SRI for future water management in Sichuan, China. 2011, http://www.google.com/#hl=en&sclient=psy-ab&q=zheng+Zhou+Chi+Jiang+Agricultural+Water+Savings+SRI&oq=zheng+Zhou+Chi+Jiang+Agricultural+Water+Savings+SRI&gs_l=hp.3…126.23924.0.244188.8.131.52.184.108.40.2062.7794.25j35j5j1.66.0.les%3B.1.0…1c.CDwSwJjZcg4&pbx=1&bav=on.2,or.r_gc.r_pw.r_qf.&fp=7e9041a74f73c7f&biw=1179&bih=600. Data from Sichuan Provincial Department of Agriculture., paper for Crop Research Institute, Sichuan Academy of Agricultural Sciences, Chengdu,Google Scholar
- Sinha SK, Talati J: Productivity impacts of the system of rice intensification (SRI): A case study in West Bengal, India. Agric Water Manage. 2007, 87: 55-60. 10.1016/j.agwat.2006.06.009.View ArticleGoogle Scholar
- Satyanaryana A, Thiyagarajan TM, Uphoff N: Opportunities for water saving with higher yield from the system of rice intensification. Irrig Sci. 2007, 25: 99-115.View ArticleGoogle Scholar
- Sato S, Uphoff N: A review of on-farm evaluations of system of rice intensification methods in Eastern Indonesia. CAB Reviews: Perspectives in Agriculture, Veterinary Science, Nutrition and Natural Resources. 2007, 2: 54-View ArticleGoogle Scholar
- Ndiri JA, Mati BM, Home PG, Odongo B, Uphoff N: Comparison of water savings of paddy rice under System of Rice Intensification (SRI) growing rice in Mwea, Kenya. Intl J Curr Res Rev. 2012, 4: 63-73.Google Scholar
- Nyamai M, Mati BM, Home PG, Odongo B, Wanjugo R, Thuranira EG: Improving crop productivity and water use efficiency in basin rice cultivation in Kenya through SRI. Agric Engin Intl: CIGR Journal. 2012, 14: 1-9.Google Scholar
- Styger E, Attaher MA, Guindo H, Ibrahim H, Diaty M, Abba I, Traore M: Application of system of rice intensification practices in the arid environment of the Timbuktu region in Mali. PaddyWater Envir. 2011, 9: 137-144.Google Scholar
- Kabir H, Uphoff N: Results of disseminating the System of Rice Intensification with Farmer Field School methods in northern Myanmar. Exp Agric. 2007, 43: 463-476.View ArticleGoogle Scholar
- Uprety R: Economic analysis of System of Rice Intensification (SRI) methods in Morang district of Nepal, main season, 2005. 2006, Report from the District Agricultural Development Office, Ministry of Agriculture, Biratnagar, Nepal,Google Scholar
- FAO-EU: FAO-EU Food Facility Programme: after One and a Half Years in Nepal. 2010, FAO, Lalitpur, Nepal,Google Scholar
- Khadka RB: Project Completion Report of EU Food Facility Project. 2011, FAYA-Nepal, Dhangadhi, Kailali, Nepal,Google Scholar
- Turmel MS, Espinosa J, Franco L, Pérez C, Hernández H, González E, Fernández G, Rojas C, Sánchez D, Fernández N, Barrios M, Whalen JK, Turner BL: On-farm evaluation of a low-input rice production system in Panama. Paddy Water Envir. 2011, 9: 155-161. 10.1007/s10333-010-0227-1.View ArticleGoogle Scholar
- Namara R, Bossio D, Weligamage P, Herath I: The practice and effects of the system of rice intensification (SRI) in Sri Lanka. Qtly J Intl Agric. 2008, 47: 5-23.Google Scholar
- Dung NT, Minh LN: System of Rice Intensification - Advancing Small Farmers in Mekong Region. 2008, Report prepared by the Plant Protection Department (PPD)/Ministry of Agriculture and Rural Development (MARD) and East Asian Regional Office, Oxfam America,Google Scholar
- Uphoff N, Anas I, Rupela OP, Thakur AK, Thiyagarajan TM: Learning about positive plant-microbial interactions from the System of Rice Intensification (SRI). Aspects Appl Biol. 2009, 98: 29-54.Google Scholar
- Anas I, Rupela OP, Thiyagarajan TM, Uphoff N: A review of studies on SRI effects on beneficial organisms in rice soil rhizospheres. Paddy Water Envir. 2011, 9: 53-64. 10.1007/s10333-011-0260-8.View ArticleGoogle Scholar
- Lin XQ, Zhu DF, Lin XJ: Effects of water management and organic fertilization with SRI crop management practices on hybrid rice performance and rhizosphere dynamics. Paddy Water Envir. 2011, 9: 33-39. 10.1007/s10333-010-0238-y.View ArticleGoogle Scholar
- Priyanka S, Singh YV, Prasanna R, Shivay YS: Influence of methods of crop establishment and rice varieties on nutrient uptake and soil properties. under review, Research report for Indian Agricultural Research Institute, New Delhi,Google Scholar
- Prasad A: Going against the grain: The system of rice intensification is now being adapted to wheat – with similar good results. 2008, Outlook Business, New Delhi,Google Scholar
- ICRISAT-WWF: Sustainable Sugarcane Initiative: improving Sugarcane Cultivation in India – Training Manual. 2008, ICRISAT-WWF Dialog Project on Food, Water and Environment, Intl Crop Research Inst for Semi-Arid Tropics, Patancheru, Hyderabad, India,Google Scholar
- Diwakar MC, Kumar A, Verma A, Uphoff N: Report on the world-record SRI yield in kharif season 2011. Nalanda district, Bihar state, India. 2012, 53-56. Agric Today, New Delhi,Google Scholar
- Uphoff N: Agroecological implications of the System of Rice Intensification (SRI) in Madagascar. Envir Dev & Sust. 1999, 1: 297-313.View ArticleGoogle Scholar
- Cook G, O’Connor T: Rice aplenty in Aceh. 2009, 10–11. http://www.caritas-europe.org/module/FileLib/RiceaplentyinAceh.pdf, Spring, Caritas,Google Scholar
- Singh MP: Organic rice cultivation transforming lives of Damoh farmers. The Hindu. Nov. 28, 2011. http://www.thehindu.com/sci-tech/agriculture/article2668286.eceGoogle Scholar
- Lyman J, Lyman J, Rasmei S, Than YK, Chantea L: Rice production in the Family Food Production project. 2007, Posted on SRI website: http://sri.ciifad.cornell.edu/countries/cambodia/camldsrpt07.pdf, Report of LDS Charities, Phnom Penh,Google Scholar
- McDonald AJ, Hobbs PR, Riha SJ: Does the System of Rice Intensification outperform conventional best management? A synopsis of the empirical record. Field Crops Res. 2006, 96: 31-36. 10.1016/j.fcr.2005.05.003.View ArticleGoogle Scholar
- Uphoff N, Stoop WA, Kassam AH: A critical assessment of a desk study comparing crop production systems: the example of the ’system of rice intensification’ vs ‘best management practice’. Field Crops Res. 2007, 108: 109-114.View ArticleGoogle Scholar
- Turnbaugh PJ, Ley RE, Mahady M, Fraser-Liggett CM, Knight R, Gordon JI: The Human Microbiome Project. Nature. 2007, 449: 804-810.View ArticlePubMedPubMed CentralGoogle Scholar
- Pinton R, Varanini Z, Nannipieri P: The Rhizosphere: Biochemistry and Organic Substances at the Soil-Plant Interface. 2007, CRC Press, Boca Raton, FL, 2,View ArticleGoogle Scholar
- Mukerji KG, Manoharachary C, Singh J: Microbial Activity in the Rhizosphere. 2006, Springer, Berlin,View ArticleGoogle Scholar
- Chi F, Shen SH, Chang HP, Jing YX, Yanni YG, Dazzo FB: Ascending migration of endophytic rhizobia, from roots to leaves, inside rice plants and assessment of benefits to rice growth physiology. Appl Environ Microbiol. 2005, 71: 7271-7278.View ArticlePubMedPubMed CentralGoogle Scholar
- Chi F, Yang PF, Han F, Jing YX, Shen SH: Proteomic analysis of rice seedlings infected by Sinorhizobium meliloti 1021. Proteomics. 2010, 10: 1861-1874.View ArticlePubMedGoogle Scholar
- Mattoo AK, Abdel-Baki A: Crop genetic responses to management: evidence of root-shoot communication. Biological Approaches to Sustainable Soil Systems. Edited by: Uphoff N, Ball A, Fernandes ECM, Herren H, Husson O, Laing M, Palm CA, Pretty JN, Sanchez PA, Sanginga N, Thies JE. 2006, 221-230. CRC Press, Boca Raton, FL,View ArticleGoogle Scholar
- Rodriguez RJ, Freeman DC, McArthur ED, Kim YO, Redman RS: Symbiotic regulation of plant growth, development and reproduction. Communic & Integr Biol. 2009, 2: 1-3.View ArticleGoogle Scholar
- Uphoff N, Chi F, Dazzo FB, Rodriguez RJ: Soil fertility as a contingent rather than inherent characteristic: Considering the contributions of crop-symbiotic soil biota. Principles of Sustainable Soil Management in Agroecosystems. Edited by: Lal R, Stewart B. 2012, in press, Taylor & Francis, Boca Raton, FL,Google Scholar
- Khan Z, Hassanali A, Pickett J: Managing polycropping to enhance soil system productivity: a case study from Africa. Biological Approaches to Sustainable Soil Systems. Edited by: Uphoff N, Ball A, Fernandes ECM, Herren H, Husson O, Laing M, Palm CA, Pretty JN, Sanchez PA, Sanginga N, Thies JE. 2006, 575-586. CRC Press, Boca Raton, FL,View ArticleGoogle Scholar
- Uphoff N, Ball A, Fernandes ECM, Herren H, Husson O, Laing M, Palm CA, Pretty JN, Sanchez PA, Sanginga N, Thies JE: Biological Approaches to Sustainable Soil Systems. 2006, CRC Press, Boca Raton FL,View ArticleGoogle Scholar
- Laulanié H: Le système de riziculture intensive Malgache. Tropicultura. 1993, 11: 110-114. reprinted in 2011, 29:3, 183–187, as English translation,Google Scholar
- Mishra A, Uphoff N: Morphological and physiological responses of rice roots and shoots to varying water regimes and soil microbial densities. Arch Agron Soil Sci. 2012, 58: 1-27.View ArticleGoogle Scholar
- Husson O: Redox potential (Eh) and pH as drivers of plant/soil/microorganism systems: A transdisciplinary overview pointing to integrative opportunities in agronomy. Plant Soil. http://rd.springer.com/article/10.1007/s11104-012-1429-7Google Scholar
- Priyanka S, Singh YV, Prasanna R, Bhatia A, Shivay YS: Pattern of methane emission and water productivity under different methods of rice crop establishment. Paddy Water Envir. 2011, 9: 1-12.View ArticleGoogle Scholar
This article is published under license to BioMed Central Ltd. This is an Open Access article distributed under the terms of the Creative Commons Attribution License (http://creativecommons.org/licenses/by/2.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.