The global human population is expected to reach ∼9 billion by 2050. Feeding this many people represents a major challenge requiring global crop yield increases of up to 100%. Microbial symbionts of plants such as arbuscular mycorrhizal fungi (AMF) represent a huge, but unrealized resource for improving yields of globally important crops, especially in the tropics. We argue that the application of AMF in agriculture is too simplistic and ignores basic ecological principals. To achieve this challenge, a community and population ecology approach can contribute greatly. First, ecologists could significantly improve our understanding of the determinants of the survival of introduced AMF, the role of adaptability and intraspecific diversity of AMF and whether inoculation has a direct or indirect effect on plant production. Second, we call for extensive metagenomics as well as population genomics studies that are crucial to assess the environmental impact that introduction of non-local AMF may have on native AMF communities and populations. Finally, we plead for an ecologically sound use of AMF in efforts to increase food security at a global scale in a sustainable manner.
The problem of producing enough food to feed the planet, and the need for increased food security, has become all too apparent in recent years. With a global human population exceeding 7 billion, and estimates of over 9 billion by 2050, global food production will have to be greatly increased (FAO, 2006; Godfray et al., 2010), especially in tropical and subtropical regions where population growth rate is increasing faster than in the rest of the world (The Future of Farming, 2011). Such yield increases exceed the current global capacity to produce food by prevalent farming practices, highlighting the need to develop new technologies and better apply long-known technologies, such as growth-promoting microbial symbionts of plants, in a more efficacious manner (Bennett et al., 2013).
Poor soil fertility, particularly the availability of nitrogen and phosphorus, is the most limiting to increasing crop yields (Tilman et al., 2002). Consequently, nitrogen-fixing bacteria and arbuscular mycorrhizal fungi (AMF) are the two key groups of soil microorganisms with a potential for improving nitrogen and phosphorus acquisition by crops, respectively (Cakmak, 2002; Conniff, 2013; Reid and Greene, 2013). Although significant advances are being made to get effective nitrogen-fixing bacteria to farmers in developing countries (i.e. the Bill and Melinda Gates Foundation-funded N2Africa; http://www.n2africa.org/), the application of AMF has not been well adopted or lived up to the promises, despite its enormous potential (Box 1).
In this perspective article, we consider how appropriate application of AMF could improve food security, by increasing the overall yield of important staple crops irrespective of the mechanism by which it occurs (e.g. improved phosphate acquisition, improved drought or disease resistance). By food security crops, we mean those crops that are grown because they can feed a significantly large number of people and because their yields fluctuate little during periods of major climatic perturbation. We are not intending to review here the mechanisms by which the AMF symbiosis could give a crop species more food security-enhancing properties such as increased drought resistance, disease resistance or by other systemic effects revealed by recent transcriptome profiling studies, although we recognize that these aspects are extremely important (e.g. see Salvioli and Bonfante, 2013; Zouari et al., 2014). Here, we outline two major challenges to (i) effectively and (ii) safely using AMF to significantly improve production of important food security crops, especially in the tropics. We believe that both these challenges can only be resolved by the adoption of community and population ecology approaches. We propose possible ways to overcome past hurdles in applying AMF inoculation technology by respecting the general community and population ecological principles. These perspectives are based on recent ecological, community and population genetic insights, coupled with recent technological advances that allow us to better understand the ecology of these important fungi. We focus particularly on the tropics because most tropical soils are acidic and very nutrient poor, especially in bioavailable phosphate. It is in these soils where we consider that AMF could make the largest contribution, but have been most overlooked.
Challenge 1: AMF are everywhere! A major ecological challenge to effectively using AMF in agriculture
We argue that there is a major ecological challenge to effectively using AMF to increase crop production, where agronomists cannot afford to ignore microbial community and population ecology. Thousands of published studies conducted in pots with sterile soil, where inoculated versus non-inoculated plants were compared, form the basis of the well-known potential of AMF to improve plant growth. However, all soils in which crops are cultivated already contain diverse communities of AMF and all globally important food crops naturally become colonized by AMF independently from inoculation. Consequently, expecting that introducing AMF to an already established AMF community will lead to consistent increases in crop yield is utterly simplistic. We already know that microbial community structure and diversity can greatly affect plant productivity and interactions among these microorganisms can even allow persistence of less beneficial microbes (Rosendahl, 2008; Bever et al., 2013; Hart et al., 2013). It is unsurprising, therefore, that there are very few published field trials with AMF that have given consistently promising results with a major food crop that is responsible for feeding a significant proportion of the global human population (perhaps with one exception; Box 2). There are additional reasons for poor adoption of mycorrhizal technology (Box 1). We propose that a better understanding of the ecology and population biology of AMF, and how introduced AMF interact with existing AMF communities and populations, is essential to developing effective AMF inocula for increasing yields of the globally important crops, namely rice, wheat, cassava, maize and potatoes.
We identify four areas where ecologists could contribute significantly to a more effective use of AMF:
Understanding the survival and colonizing ability of introduced AMF in the presence of an existing AMF community.
Understanding the adaptability of AMF to environmental conditions that the fungus has not previously experienced.
The importance of within-AMF species genetic variation and how it affects plant growth.
The need to identify whether the effect on crop yield of introduced AMF is direct or indirect, through changes to the pre-existing AMF community.
Do introduced AMF actually establish?
Understanding how introduced AMF interact and coexist with the local AMF community and whether this directly leads to changes in crop production is key to a successful application of AMF in agriculture. Remarkably, few field studies have directly linked yield increases with successful colonization by an introduced AMF. One field study in which yield increases were observed, with parallel increases in AMF colonization, revealed that one out of two introduced AMF inoculants may have successfully established and persisted 2 years following inoculation (Pellegrino et al., 2012). The pending question is whether that particular isolate was directly responsible for the increase in biomass of the target plant or even of the higher mycorrhizal colonization observed in those roots. Nowadays, high-throughput sequencing offers a more powerful, sensitive and also quantitative technique to track the fate of the introduced AMF, both temporally and spatially and also determine whether the establishment of the AMF is influenced by the native AMF community (Figure 1a). It remains to be seen whether effective inoculation of crops with AMF will lead to significant levels of colonization by the introduced fungus, but as we explain below, this may not necessarily be important if the effects are indirect via the resident AMF community.
Do AMF inoculants have to be preadapted to a particular soil or crop species?
Very little is known about adaptation of AMF to environmental conditions (Johnson et al., 2013). A common assumption for field applications is that to be effective, the fungus has to be adapted to a given soil type or crop. Indeed, as high nutrient levels can reduce colonization by AMF, it could be more difficult for AMF to establish in more nutrient-rich soils. However, some AMF species appear to have an extremely large geographic range, suggesting a lack of specialization to certain environments (i.e. Funneliformis mosseae and Rhizophagus irregularis in Rosendahl et al., 2009 and Box 3). In fact, some field studies successfully used in vitro-grown R. irregularis from arid Spanish soil in extremely nutrient-poor tropical acidic soils and with a plant (cassava) that the fungus had not previously experienced (Ceballos et al., 2013).
The question of environmental adaptation in AMF has only been tangentially approached (Johnson et al., 2010). Johnson et al. (2010) provided the first evidence, in natural ecosystems, of possible local AMF community adaptation to soil mineral nutrient levels. However, recent laboratory evidence suggests a genetic mechanism that could allow for the rapid adaptation in AMF to a change of environment (Angelard et al., 2014). Strains of R. irregularis that had been maintained for ∼12 years on carrot roots exhibited rapid genetic change following a shift to potato and showed a very large range of phenotypic responses to a change of host. Thus, to understand whether AMF need to be adapted to a given environment, we also need to understand the mechanisms by which AMF can become adapted to a new environment.
Finally, we see little available experimental data on whether AMF that have evolved in a given environment will be more effective in that environment. Thus, we believe that in order to more effectively use AMF, it is necessary to understand the role that selective adaptation has in the effectiveness of AMF in given soils or crops.
AMF species versus within-species diversity
AMF species richness is a major contributor to maintaining plant species diversity and ecosystem functioning (van der Heijden et al., 1998a). Many field investigations have also demonstrated that crops respond differently to inoculation with different AMF species. Most of these studies demonstrating differential effects of AMF species on plants have used one individual AMF isolate as a representative of the species. However, one study shows that larger variation in plant biomass can be induced by randomly choosing two different isolates of the same species, rather than inoculating with two different species (Munkvold et al., 2004). Furthermore, variation in plant growth caused by different AMF individuals from one population has been shown to have a genetic basis, highlighting genetic variation in AMF populations as a major source of variation (Koch et al., 2006). Furthermore, a fivefold difference in the growth of rice was observed by inoculating with genetically different R. irregularis isolates (Angelard et al., 2010). This calls for further studies on the functional implication of genetic diversity in AMF populations as it may be possible to breed and select more effective AMF for crop plants.
We also stress that genetic variation in crop species also needs to be considered as AMF genotype-by-crop genotype interactions may exist where crop varieties respond differently to a range of different AMF genotypes. Different plant genotypes are known to respond differently to AMF inoculation, but so far the interaction has not been investigated in sufficient detail (Hetrick et al., 1995; An et al., 2010).
Direct versus indirect effects of AMF inoculation
Agricultural soils have been shown to harbour diverse AMF communities (Smith and Read, 2008). Ecological studies have clearly shown that different species of AMF induce different effects on plant growth (van der Heijden et al., 1998b). Thus, it appears likely that alterations to the AMF community could potentially alter the yield of a crop without necessarily changing overall colonization levels caused by adding an additional AMF species. Introducing a non-indigenous AMF is a biotic disturbance that could alter resident AMF community structure (Figure 1a). There is no information, however, on whether AMF inoculation that results in improved crop yield is actually because of a direct effect of the introduced AMF on the plant or indirectly through a change in the local AMF community (Figure 1a). It is, therefore, highly pertinent to understand the mechanisms that govern AMF community composition in response to application of non-indigenous AMF. This is a key ecological issue in need of thorough consideration for an ecologically sustainable use of AMF (see Challenge 2). Furthermore, variable effects on crop yield of AMF application, using the same inoculum in different places, might be determined by their indirect effect on local AMF communities, which might differ in these places.
At present, there is almost no information about what determines the community composition of AMF in a given environment and, indeed, whether there are abiotic or biotic factors that allow us to predict which AMF taxa will form a given assemblage in a given locality. Without understanding of such basic ecological patterns, which we largely take for granted in plant and animal assemblages, it is impossible to even start predicting how a given AMF community might react to the introduction of an additional AMF inoculum. One way to address this is if community ecologists describe AMF community structure over a wide variety of well-described agroecosystems to identify the environmental variables that determine AMF community assemblages. With this knowledge, for a large number of sites, it would then be possible to select sites with given environments and AMF assemblages and perform experiments to observe both crop responses and AMF community responses to inoculation with one uniform inoculum. With modern molecular techniques, this very large experiment is technically possible and we see this as critical for predicting how a given AMF inoculum will affect already existing AMF assemblages.
Challenge 2: Ecological impact of introducing non-native AMF
The second major challenge we highlight is the need to understand the ecological impact of introducing AMF into soils in which they previously did not occur. This was first addressed in a landmark publication that called for caution in global dispersal of AMF inoculants and stressed the need for environmental impact studies (Schwartz et al., 2006). Recent development of new techniques means this can now be assessed and, owing to new findings, additional factors need to be taken into consideration. Without conducting the research that we highlight below, it is impossible to assess the safety and dangers associated with introducing non-native AMF. The recent developments in the analysis of microbial communities, populations and genomes make it feasible to address the following questions:
Does an introduced AMF alter the composition and/or structure of the naturally occurring AMF community?
Do introduced AMF persist and spread in the environment?
If the introduced AMF species already occurs locally, are we introducing new genetic material (new alleles) into an existing AMF population?
Will the introduced fungus undergo genetic exchange with the local AMF population and what are the functional consequences?
Effects on AMF communities of introducing non-native AMF
An obvious question is whether the introduction of a non-native AMF significantly alters either the diversity or the composition of the existing AMF community. A number of studies have used pyrosequencing of rDNA amplicons from roots or soil, giving the first picture of AMF diversity in communities (Lindahl et al., 2013; Öpik et al., 2013). However, the technology needs to be suitable for large sample numbers and high replication, as well as for having the appropriate bioinformatics tools to handle very large data sets (Pagni et al., 2013). At the time of writing, Illumina MiSeq technology produces ∼30 million paired-end 300 bp reads, which means that a ∼550 bp concatenated amplicon sequence should give a very large number of informative reads, making it possible to work with considerable sequence coverage per amplified sample (Smith and Peay, 2014). Pooling of barcoded amplicons from large numbers of samples into single libraries will allow large-scale studies on AMF communities from inoculated and non-inoculated soils. New more robust clustering algorithms are also being developed, such as DBC454, that are efficient for the processing of large data sets (Pagni et al., 2013).
A much greater challenge is the ecological interpretation of any changes to the local AMF community. Although a decrease in AMF diversity is likely to be considered as a negative environmental impact, we still do not understand which aspects of AMF diversity (richness, evenness) favour crop growth. The experimental approach suggested above (end of Challenge 1) for investigating direct versus indirect effects should help to unravel this problem.
Persistence and invasiveness of introduced AMF: a population genomics approach
AMF inoculants are difficult to trace in field experiments. Therefore, it has been difficult, in practice, to measure either the persistence or the invasiveness of an introduced AMF. Consequently, there is no data available on this topic (Figure 1b). A further practical problem is that the same fungal species may already be present in the native AMF community, which means that a large number of molecular markers used for tracing the fungus may already exist at the field site. However, we propose that it is potentially possible to study invasiveness and persistence of one particular AMF species, namely R. irregularis (Box 3), by adopting a population genomics approach, even though this fungus is already present in many agricultural fields.
With the recent publication of the reference genome of R. irregularis isolate DAOM 197198 (Tisserant et al., 2013), it is now easier to undertake partial genome sequencing of multiple R. irregularis isolates and obtain a set of specific polymorphic markers to discriminate introduced R. irregularis strains from local ones. The technique known as random amplified polymorphic DNA sequencing is a powerful, and also an extremely reliable, high-throughput method for identifying large numbers of polymorphisms across genomes of different individuals (Baird et al., 2008). Potential marker identification would then be based on polymorphisms between the introduced R. irregularis strain and polymorphisms of a large number of R. irregularis isolates whose genomes were sequenced.
Introduction of non-native genetic material into existing AMF populations: the need for population genomics
Introducing non-native AMF at sites where the same AMF species occurs could result in the introduction of new or very different genetic material into existing fungal populations even though no new species is introduced. However, based on our knowledge of AMF genetic variation, these newly introduced individuals could potentially be genetically very different from those that are already present. This can be considered highly relevant because we already know that genetically different isolates of one AMF species can cause large differences in plant growth, even if they originate from the same population (Koch et al., 2006; Angelard et al., 2010).
To know the likelihood of adding new alleles into indigenous AMF populations, we believe that a detailed study of global population genomics of an AMF species is urgently needed. The fungus R. irregularis is an ideal candidate (Box 3). Some information on the population genetics of this fungus already exists and is intriguing. In a study of a Swiss R. irregularis population, where isolates originated from 1 small field (100 × 100 m2), genetic differences among isolates were very large (Koch et al., 2004; Croll et al., 2008). However, there were very few alleles in a Canadian isolate (DAOM 197198) that did not already exist in the Swiss population. This leads to the question whether R. irregularis populations might be locally extremely diverse, but globally not much richer. If true, it would mean that introducing inoculants of R. irregularis into soils from which the inoculant does not originate may pose little risk for the introduction of significant amounts of new genetic material (Figure 1b). However, only thorough population genomics studies using high-throughput polymorphism detection approaches (such as random amplified polymorphic DNA sequencing) on globally distributed R. irregularis isolates can help answer this question.
Genetic exchange between introduced AMF, the existing population and its consequences
It has been demonstrated that the fungus R. irregularis anastomoses with genetically different individuals of the same species, giving rise to genetically novel progeny, whose effects on plant growth differ from those of the parents (Croll et al., 2009; Angelard et al., 2010; Colard et al., 2011). Thus, anastomosis between an introduced AMF and local AMF of the same species would potentially allow non-native alleles to mix with the local population. This has the potential to change how the local AMF population affects plant growth and its competitive ability to coexist with the other species in the existing AMF community (Figure 1b).
We propose that to assess this risk, experiments are urgently needed to determine whether an introduced AMF exchanges DNA with an existing AMF population. A population genomics approach would involve: (1) genetically characterizing polymorphisms that occur in the introduced fungus, as well as in the local fungi, to develop strain-specific markers; (2) checking the absence of the markers at the introduction sites; (3) following inoculation, single spores of the fungus would have to be isolated from the field site to look for co-occurrence of markers specific to the introduced fungus and markers specific to the existing population. We consider the detection of genetic exchange in the field and its consequences to be technically challenging, but feasible with current knowledge of the R. irregularis genome and powerful high-throughput polymorphism detection tools.
We conclude that ecological approaches at community and population scales, made possible by metagenomics and population genomics tools, can pave the way to a better informed agronomic utilization of AMF. As we point out, modern molecular techniques are already available for these studies and it is the responsibility of microbial ecologists and agronomists to take up these challenges, as their contribution could help lead to practical solutions to the problem of producing more food in a sustainable manner.
An GH, Kobayashi S, Enoki H, Sonobe K, Muraki M, Karasawa T et al. (2010). How does arbuscular mycorrhizal colonization vary with host genotype? An example based on maize (Zea mays) germplasms. Plant Soil 327: 441–453.
Angelard C, Colard A, Niculita-Hirzel H, Croll D, Sanders IR . (2010). Segregation in a mycorrhizal fungus alters rice growth and symbiosis-specific gene transcription. Curr Biol 20: 1216–1221.
Angelard C, Tanner CJ, Fontanillas P, Niculita-Hirzel H, Masclaux F, Sanders IR . (2014). Rapid genotypic change and plasticity in arbuscular mycorrhizal fungi is caused by a host shift and enhanced by segregation. ISME J 8: 284–294.
Baird NA, Etter DP, Atwood TS, Currey MC, Shiver AL, Lewis ZA et al. (2008). Rapid SNP discovery and genetic mapping using sequenced RAD markers. PLoS One 3: e3376.
Bennett AE, Daniell TJ, White PJ . (2013). Benefits of breeding crops for yield response to soil microorganisms. In de Bruijn FJ, (ed) Molecular Ecology of the Rhizosphere. Wiley: New York, NY, USA, pp 17–27.
Bever JD, Broadhurst LM, Thrall PH . (2013). Microbial phylotype composition and diversity predicts plant productivity and plant–soil feedbacks. Ecol Lett 16: 167–174.
Bécard G, Fortin JA . (1988). Early events of vesicular arbuscular mycorrhiza formation on Ri T-DNA transformed roots. New Phytol 108: 211–218.
Börstler B, Raab PA, Thiéry O, Morton JB, Redecker D . (2008). Genetic diversity of the arbuscular mycorrhizal fungus Glomus intraradices as determined by mitochondrial large subunit rRNA gene sequences is considerably higher than previously expected. New Phytol 180: 452–465.
Cakmak I . (2002). Plant nutrition research: priorities to meet human needs for food in sustainable ways. Plant Soil 247: 3–24.
Ceballos I, Ruiz M, Fernández C, Peña R, Rodriguez A, Sanders IR . (2013). The in vitro mass-prodcued model mycorrhizal fungus, Rhizophagus irregularis, significantly increases yields of the globally important food security crop cassava. PLoS One 8: e70633.
Colard A, Angelard C, Sanders IR . (2011). Genetic exchange in an arbuscular mycorrhizal fungus results in increased rice growth and altered mycorrhiza-specific gene transcription. Appl Environ Microbiol 77: 6510–6515.
Conniff R . (2013). Superdirt. Sci Am 2013: 76–79.
Croll D, Giovannetti M, Koch AM, Sbrana C, Ehinger M, Lammers PJ et al. (2009). Nonself vegetative fusion and genetic exchange in the arbuscular mycorrhizal fungus Glomus intraradices. New Phytol 181: 924–937.
Croll D, Wille L, Gamper HA, Mathimaran N, Lammers PJ, Corradi N et al. (2008). Genetic diversity and host plant preferences revealed by simple sequence repeat and mitochondrial markers in a population of the arbuscular mycorrhizal fungus Glomus intraradices. New Phytol 178: 672–687.
FAO. (2005). A review of cassava in Africa with country case studies on Nigeria, Ghana, the United Republic of Tanzania, Uganda and Benin. Proceedings of the Validation Forum on the Global Cassava Development Strategy vol. 2. FAO Publications: Food and Agriculture Organization of the United Nations: Rome, Italy.
FAO. (2006) World Agriculture: Towards 2030/2050 (Interim Report). FAO Publications: Food and Agriculture Organization of the United Nations: Rome, Italy.
FAO. (2010). http://www.fao.org/ag/AGP/AGPC/gcds/index_en.html (last accessed date 21 October 2014).
Friesen DK, Rao IM, Thomas RJ, Oberson A, Sanz JI . (1997). Phosphorus acquisition and cycling in crop and pasture systems in low fertility tropical soils. Plant Soil 196: 289–294.
Gianinazzi S, Vosátka M . (2004). Inoculum of arbuscular mycorrhizal fungi for production systems: science meets business. Can J Bot 82: 1264–1271.
Gilbert N . (2009). The disappearing nutrient. Nature 461: 716–718.
Godfray HCJ, Beddington JR, Crute IR, Haddad L, Lawrence D, Muir JF et al. (2010). Food security: the challenge of feeding 9 billion people. Science 327: 812–818.
Gross G . (2010). Fears over phosphorus supplies. Curr Biol 20: 386–387.
Hart M, Forsythe J, Oshowski B, Bücking H, Jansa J, Kiers ET . (2013). Hiding in a crowd-does diversity facilitate persistence of a low-quality fungal partner in the mycorrhizal symbiosis? Symbiosis 59: 47–56.
Hetrick BAD, Wilson GWT, Gill BS, Cox TS . (1995). Chromosome location of lycorrhizal responsive genes in wheat. Can J Bot 73: 891–897.
Howeler RH, Sieverding E . (1983). Potentials and limitations of mycorrhizal inoculation illustrated by experiments with field-grown cassava. Plant Soil 75: 245–261.
Johnson NC, Angelard C, Sanders IR, Kiers ET . (2013). Predicting community and ecosystem outcomes of mycorrhizal responses to global change. Ecol Letts 16: 140–153.
Johnson NC, Wilson GWT, Bowker MA, Wilson J, Miller RM . (2010). Resource limitation is a driver of local adaptation in mycorrhizal symbioses. Proc Natl Acad Sci USA 107: 2093–2098.
Koch AM, Croll D, Sanders IR . (2006). Genetic variability in a population of arbuscular mycorrhizal fungi causes variation in plant growth. Ecol Lett 9: 103–110.
Koch AM, Kuhn G, Fontanillas P, Fumagalli L, Goudet J, Sanders IR . (2004). High genetic variability and low local diversity in a population of arbuscular mycorrhizal fungi. Proc Natl Acad Sci USA 101: 2369–2374.
Lindahl BD, Nilsson RH, Tedersoo L, Abarenkov K, Carlsen T, Kjoller R et al. (2013). Fungal community analysis by high-throughput sequencing of amplified markers—a user’s guide. New Phytol 199: 288–299.
Munkvold L, Kjoller R, Vestberg M, Rosendahl S, Jakobsen I . (2004). High functional diversity within species of arbuscular mycorrhizal fungi. New Phytol 164: 357–364.
Öpik M, Zobel M, Cantero JJ, Davison J, Facelli JM, Hiiesalu I et al. (2013). Global sampling of plant roots expands the described molecular diversity of arbuscular mycorrhizal fungi. Mycorrhiza 23: 411–430.
Pagni M, Niculita-Hirzel H, Pellissier L, Dubuis A, Xenarios I, Guisan A et al. (2013). Density-based hierarchical clustering of pyro-sequences on a large scale-the case of fungal ITS1. Bioinformatics 29: 1268–1274.
Pellegrino E, Turrini A, Gamper HA, Cafà G, Bonari E, Young JP et al. (2012). Establishment, persistence and effectiveness of arbuscular mycorrhizal fungal inoculants in the field revealed using molecular genetic tracing and measurement of yield components. New Phytol 194: 810–822.
Reid A, Greene S . (2013) How Can Microbes Help Feed the World?. American Society of Microbiology: Washington, DC.
Rosendahl S . (2008). Communities, populations and individuals of arbuscular mycorrhizal fungi. New Phytol 178: 253–266.
Rosendahl S, McGee P, Morton JB . (2009). Lack of global population genetic differentiation in the arbuscular mycorrhizal fungus Glomus mosseae suggests a recent range expansion which may have coincided with the spread of agriculture. Mol Ecol 18: 4316–4329.
Salvioli A, Bonfante P . (2013). Systems biology and ‘omics’ tools: a cooperation for next-generation mycorrhizal studies. Plant Sci 203-204: 107–114.
Schwartz MW, Hoeksema JD, Gehring CA, Johnson NC, Klironomos JN, Abbott LK et al. (2006). The promise and the potential consequences of the global transport of mycorrhizal fungal inoculum. Ecol Lett 9: 501–515.
Sieverding E . (1991) Vesicular-Arbuscular Mycorrhiza Management in Tropical Agrosystems. Deutche Gesellschaft für Technische Zusammenarbeit (GTZ): Eschborn, Germany.
Sieverding E, Howeler RH . (1985). Influence of species of VA mycorrhizal fungi on cassava yield response to phosphorus fertilization. Plant Soil 88: 213–221.
Smith DP, Peay KG . (2014). Sequence depth, not PCR replication, improves ecological inference from next generation DNA sequencing. PLoS One 9: e90234.
Smith SE, Read DJ . (2008) The Mycorrhizal Symbiosis. Academic Press: San Diego, CA, USA.
The Future of Farming. (2011) Final Project Report. The Government Office for Science: London, UK, p 211.
Tilman D, Cassman KG, Matson PA, Naylor R, Polasky S . (2002). Agricultural sustainability and intensive production practices. Nature 418: 671–677.
Tisserant E, Malbreil M, Kuo A, Kohler A, Symeonidi A, Balestrini R et al. (2013). Genome of an arbuscular mycorrhizal fungus provides insight into the oldest plant symbiosis. Proc Natl Acad Sci USA 110: 20117–20122.
van der Heijden MGA, Boller T, Wiemken A, Sanders IR . (1998a). Different arbuscular mycorrhizal fungal species are potential determinants of plant community structure. Ecology 79: 2082–2091.
van der Heijden MGA, Klironomos JN, Ursic M, Moutoglis P, Streitwolf-Engel R, Boller T et al. (1998b). Mycorrhizal fungal diversity determines plant biodiversity, ecosystem variability and productivity. Nature 396: 69–72.
Zouari I, Salvioli A, Chialva M, Novero M, Miozzi L, Tenore GC et al. (2014). From root to fruit: RNA-Seq analysis shows that arbuscular mycorrhizal symbiosis may affect tomato fruit metabolism. BMC Genom 15: 221.
IRS and AR gratefully acknowledge the financial support from a Swiss National Science Foundation Joint Research Project (project number IZ70Z0_131311/1) that allowed the development of these ideas and constructive comments from three anonymous reviewers.
The authors declare no conflict of interest.
About this article
Cite this article
Rodriguez, A., Sanders, I. The role of community and population ecology in applying mycorrhizal fungi for improved food security. ISME J 9, 1053–1061 (2015). https://doi.org/10.1038/ismej.2014.207
This article is cited by
Spatial variability and environmental drivers of cassava—arbuscular mycorrhiza fungi (AMF) associations across Southern Nigeria
Nature Ecology & Evolution (2022)
Mycorrhizal inoculation increases fruit production without disturbance of native arbuscular mycorrhizal community in jujube tree orchards (Senegal)
Improved genotypes and fertilizers, not fallow duration, increase cassava yields without compromising arbuscular mycorrhizal fungus richness or diversity
A historical perspective on mycorrhizal mutualism emphasizing arbuscular mycorrhizas and their emerging challenges