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Frontiers of Agricultural Science and Engineering

ISSN 2095-7505

ISSN 2095-977X(Online)

CN 10-1204/S

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Front. Agr. Sci. Eng.    2022, Vol. 9 Issue (2) : 214-237    https://doi.org/10.15302/J-FASE-2021437
REVIEW
HARNESSING ECOLOGICAL PRINCIPLES AND PHYSIOLOGIC MECHANISMS IN DIVERSIFYING AGRICULTURAL SYSTEMS FOR SUSTAINABILITY: EXPERIENCE FROM STUDIES DEPLOYING NATURE-BASED SOLUTIONS IN SCOTLAND
Timothy S. GEORGE(), Cathy HAWES, Tracy A. VALENTINE, Alison J. KARLEY, Pietro P. M. IANNETTA, Robin W. BROOKER
Ecological Sciences Department, The James Hutton Institute, Invergowrie, Dundee, DD2 5DA, UK
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Abstract

● Diversification enhances nature-based contributions to cropping system functions.

● Soil management to improve production and ecosystem function has variable outcomes.

● Management of the production-system to use legacy nutrients will reduce inputs.

● Intercrops, companion crops and cover crops improve ecological sustainability.

● Sustainable interventions within value chains are essential to future-proof agriculture.

To achieve the triple challenge of food security, reversing biodiversity declines plus mitigating and adapting to climate change, there is a drive to embed ecological principles into agricultural, value-chain practices and decision-making. By diversifying cropping systems at several scales there is potential to decrease reliance on inputs, provide resilience to abiotic and biotic stress, enhance plant, microbe and animal biodiversity, and mitigate against climate change. In this review we highlight the research performed in Scotland over the past 5 years into the impact of the use of ecological principles in agriculture on sustainability, resilience and provision of ecosystem functions. We demonstrate that diversification of the system can enhance ecosystem functions. Soil and plant management interventions, including nature-based solutions, can also enhance soil quality and utilization of legacy nutrients. Additionally, this is facilitated by greater reliance on soil biological processes and trophic interactions. We highlight the example of intercropping with legumes to deliver sustainability through ecological principles and use legumes as an exemplar of the innovation. We conclude that there are many effective interventions that can be made to deliver resilient, sustainable, and diverse agroecosystems for crop and food production, and these may be applicable in any agroecosystem.

Keywords diversification      ecological principles      legumes      plant management      soil management      soil ecosystem services     
Corresponding Author(s): Timothy S. GEORGE   
Just Accepted Date: 23 March 2022   Online First Date: 26 April 2022    Issue Date: 25 May 2022
 Cite this article:   
Timothy S. GEORGE,Cathy HAWES,Tracy A. VALENTINE, et al. HARNESSING ECOLOGICAL PRINCIPLES AND PHYSIOLOGIC MECHANISMS IN DIVERSIFYING AGRICULTURAL SYSTEMS FOR SUSTAINABILITY: EXPERIENCE FROM STUDIES DEPLOYING NATURE-BASED SOLUTIONS IN SCOTLAND[J]. Front. Agr. Sci. Eng. , 2022, 9(2): 214-237.
 URL:  
https://academic.hep.com.cn/fase/EN/10.15302/J-FASE-2021437
https://academic.hep.com.cn/fase/EN/Y2022/V9/I2/214
Ecological target Target interventions Benefits Trade-offs References
Enhanced within-field diversity •Farmer/grower tolerance of weeds
•Companion cropping
•Diverse margins
Enhanced resource use efficiency, system resilience to stress, maintained crop productivity, reduced herbivory and disease, improved food web, more functional diversity, reduced agrochemical input, more pollinators, improved N fixation and AMF symbiosis, more earthworms and decomposition. See also benefits of non-chemical weed control below Potential for competitive weeds to establish [213]
Non-chemical weed control •Late sowingcrops
•Stale seed bed
•Increased seed rate
•Weed-competitive
•Mechanical weed reduction
Improved N fixation by legume weeds, retention of nutrients in weed biomass, reduced pollution of agrochemicals, diversity of carbon inputs to soil, more diverse food web supporting regulating ecosystem functions Labor intensive weed control [14,15]
Integrated pest and pathogen management •Increased habitat diversity
•More abundant/diverse natural enemies
•Higher crop diversity
•Pesticide alternatives
Insect pest suppression, reduced pesticide use, maintained crop productivity, reduced herbivory and disease, more diverse food web, more functional diversity, reduced agrochemical input, more abundant/diverse pollinators Differential effects of abiotic stress on trophic levels could disrupt pest controlEmergence of biocontrol-resistant pest variants [1621]
Diversified cropping with legumes •Legumes in rotations
•Understory sowing
•Intercropping
Diversification of the supply chain increasing resilience to global shocks, reduced inputs of nutrients (particularly N), enhanced nutritional security, provision of alternative to animal protein, reduced imports of environmentally damaging grain legume production from some regions Under yielding of legumes and slow breeding progress [27,22,23]
Cover cropping •Autumn/winter soil cover
•Soil cover between rows
Reduced erosion and loss of nutrients in winter, greater recycling of nutrients, reduced input of fertilizer, improved habitat diversity to support food web Use of soil to produce a crop without a harvestable product. If utilizing potential for developing biorefining or green manure-loss of beneficial processes [12]
Reduced tillage •Fewer cultivations
•Non-inversion tillage
•Zero cultivation
•Zero traffic
Improved soil physical conditions (in the long-term), improved water retention and release, increased C sequestration (variable results), improved AMF networks, maintenance of biopores, stratification of resources in the root zone Reduced yield, abiotic stress. Acidification of root zone. Change in weed burden [24,25]
Use of legacy nutrients •Reduced fertilizer inputs
•Nutrient efficient genotypes
•Inoculation with AMF, PGPR
Greater cycling of nutrients, stimulation of rooting traits, positive impacts on microbiome function associated with plants and other organisms, improved stoichiometric balance of soil Interference of complex trophic interactions.Carbon loss to priming of nutrients. [26]
Use of alternative organic fertilisers and carbon addition •Compost•Green manure•Animal manure•Seaweed•Rock phosphate•Sewage sludge•Biochar Reduced need for fertilizer input, immobilization of excess and toxic elements, reduced pollution of water and atmosphere by GHG, combinations of sources can help manage stoichiometry and toxic element availability, increased microbial activity/soil biological processes Immobilization of nutrients.Release of C as CO2Transportation costs (economics and environmental).Addition of toxic elements [2735]
Reliance on microbial function •Recruitment of Functional rhizosphere microbiome
•Mycorrhizal inoculation
•Rhizobia inoculation
Reduced need for fertilizer inputs, enhanced pest, and pathogen resistance, increased nutrient use efficiency and use of legacy nutrients, potential for reduced GHG emissions and enhanced C sequestration, stimulation of rooting traits Potential for promotion of antagonistic or pathogenic microbes [28,3644]
Adaptation of crop genotypes •Nutrient use efficiency
•Pest and pathogen resistance
•Interactions with microbiome
•Adaptation to tillage practice
•Enhanced C dynamics
•Weed tolerance
Reductions in inputs of fertilizers, pesticides, and traffic; tolerance to insect pests and pathogen; tolerance to weed understory; increased nutrient use efficiency; increased tolerance to reduced tillage; selection of beneficial microbial interactions (AMF); altered C dynamics promoting priming or sequestration; adaptation to growing in mixed systems such as intercropping Negative interaction between cycling of legacy nutrients and sequestration of carbon.Trade-off between traits benefitting monoculture and mixed cropping systems [4452]
Tab.1  Summary of benefits and trade-offs of major ecological target interventions in cropping systems designed to enhance sustainability
Fig.1  Network diagram of interactions necessary for applying ecological principles to sustainable agriculture. Sustainable management of agroecosystems capitalizes on the ecosystem functions resulting from the complex ecological network of interactions within diversified agroecosystems. Adopting integrative approaches to promoting diversity maintains long-term ecological functioning, including soil quality, nutrient, carbon and water cycles, primary production, microbe-plant associations, pest and pathogen regulation, pollination and arable food web resilience, thereby enhancing crop production while relying less on agrochemical inputs. These influences and interdependencies between different elements of the field-scale agroecological system are illustrated in this figure, summarized as follows:Organic matter inputs and internally generated sources of organic matter increase SOC, providing resources for detritivores and microorganisms and improving soil biophysical structure (1);Reduced tillage also improves soil structure both directly by less disturbance and indirectly through the enhanced bioturbation effects of earthworms and the binding properties of fungal hyphae and roots (2). The increased soil microbial biomass (3) enhances nutrient turnover through decomposition processes and includes a diversity of functional groups, for example, growth promoting bacteria that produce enzymes and antioxidants, AMF and rhizobia that enhance P uptake and N capture and antagonists which reduce pathogen pressure;Cover crops can be used to reduce losses over winter and release nutrients to the following crop which also benefits from improved soil structure particularly in reduced tillage systems (4). Efficient nutrient uptake leads better resilience to pests and pathogens and competitive ability against weeds, resulting in less reliance on crop protection chemicals (5). Healthy crops also provide better quality resource to pollinating insects (5) bringing further benefit to crop yields;Crop diversification, including co-cropping, intercropping, companion planting and rotation diversity (6), improves the efficiency of production in low-input systems through resource complementarity leading to more efficient nutrient uptake, better quality of carbon inputs to the soil and also through a reduction in weed, pest and pathogen pressure; and finallyNative plant biodiversity (weeds flora and seminatural habitats (7)) increases the activity of natural enemies and pollinators, reducing pest pressure and increasing yield and quality of insect pollinated crops.Utilizing the complementarities and synergisms between all of these components of agroecosystems represents a potential nature-based solution to the conflict between food production and environmental protection and has the potential to enhance sustainable food production alongside biodiversity conservation and environmental protection (reproduced by kind permission of CABI Reviews)[54].
Fig.2  Centre for Sustainable Cropping: a long-term platform to assess within-field species and functional diversity for multiple benefits. The picture is reproduced with permission from the James Hutton Institute. The Centre for Sustainable Cropping, based at Balruddery Farm near Dundee, Scotland is a long-term experimental platform established in 2009 with the goal to design and test an integrated cropping system for multiple benefits. Best practice options are combined in the integrated system to optimize crop yield, biodiversity and ecosystem services, while reducing the environmental footprint of crop production by minimizing agrochemical inputs and the loss of non-renewable resources. The Centre for Sustainable Cropping comprises a 42 ha block of fields in a six-course rotation of potato, winter wheat, winter barley, winter oilseed rape, faba beans and spring barley, in a split-field design with a 6-m wide grass buffer strip separating the two treatments: the integrated system (Int) in one field half is compared directly against standard commercial practice (Com) for each crop in the other.
Target Management practice
Soil biophysical quality Direct drilling (cereals and beans), non-inversion till (OSR)Organic matter amendments (10 t·ha−1 green waste compost and crop residue inputs)Tied-ridging in potato to reduce erosion/runoffCover crops over winter (oil radish and rye)
Plant nutrients Legume undersowing/co-cropping (clover in OSR and barley)Soil N Supply calculations for optimized mineral N input ratesCover crops to reduce over winter losses
Crop protection Blight forecasting using Hutton criteria and spore monitoringPesticide dose reductions based on HGCA response curvesBiofortification with minerals to boost disease resilienceWildflower margins for enhanced natural enemy control of pests
Biodiversity Targeted weed control aiming for 10% cover beneficial speciesWildflower margins for invertebrate and bird resourcesReduced crop protection applications through IPM
Tab.2  Integrated management: combining proven best practice options into a single cropping system
Fig.3  Variation in soil physical properties in response to soil tillage, across three different depths, in Mid-Pilmore Tillage trial. Physical properties are affected differently depending on the tillage system used, depth of the cultivation and depth at which the soil sample is taken. At 2–7 cm sampling depth, the no-tillage samples separate from the more disturbed plots, and at 25–30 cm sampling depth, no-tillage and inversion plow with compaction diverge.
Fig.4  Complexity of the below ground environment and influence of trophic interactions: ① earthworms create biochemical and physical niches. Linkages between microorganisms are able to exploit soil pore space and aggregate organization. Protozoa and bacteria degrade larger molecules that nematodes would otherwise cannot degrade due to physically or biochemically limitations. Small molecules disperse more readily in pore water microsites. ② Root hairs increase plant root exudation and create physical niches for biological interactions. Plant-bacteria-protozoa priming establish a beneficial nutrient loop. ③ Phosphatases (in this picture phytases) are released by mycorrhizae, bacteria, plant roots and nematodes, hydrolyze complex phosphorus molecules, increasing biological availability of P. ④ A mineralization hotspot where a nematode community and bacteria release phosphorus, nematodes translocate nutrients and bacteria to the plant in the absence of roots. ⑤ Top-down process from the plant induced hormonally, benefits from mycorrhizae and bacteria mineralization. ⑥ Lateral mediating process from nematodes to bacteria to protozoa create both hormonal and mineralization hotspots, herbivory increases root exudation and nutrients are exchanged between plant and organisms. ⑦ Protozoa create a hormonal hotspot which increases lateral root growth. Mobile organisms such as collembola migrate, generating crosstalk with neighboring microcommunities, and other nutrient processing tools. ⑧ Bottom-up stimulation from bacteria and protozoa in a phosphorus surplus zone create a hormonal hotspot which promotes plant root growth which benefits microbial community[38].
Fig.5  This schematic diagram highlights the cornerstone role which legume crops have in the functional diversification of cropping systems, and delivering improved ecosystem services, especially provisioning and regulating services. Two distinct functional forms of legume crops (green text boxes), are highlighted (i.e., woody legumes are not accounted here). These two dominant forms mediate the delivery of an important complex array of nutritionals and non-nutritionals as key ecosystem provisions (peach text box). These include secondary metabolites, other bioactives and structural elements (e.g., fiber) that affect soil functions (yellow text box) and regulate of key chemical cycles (e.g., nitrogen, carbon, phosphorus, water via N-leaching, carbon sequestration and greenhouse gases), and other ecosystem functions such as human and animal well-being and health, including biodiversity and natural, and low-input means, wherever possible, of pest control (blue text box). The diagram also aims to emphasize the increasing role of biorefining-based approaches means by the utility of legume use may be rendered more commercially competitive. Collectively, the more effective management of legumes from cropping and processing to marketing and consumption can help achieve better human, organismal and, thereby, ecosystem functions, where greater natural resource and capital use efficiency is achieved in a circular-economic mode through transformational optimizing of renewable (i.e., biologically fixed) nitrogen use and management.
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