Apr 1, 2026
Soil Health: Regenerative Agriculture - Old Practices and New Applications
In the past several years public interest in RA has increased along with other similar designations such as sustainable agriculture, organic agriculture, etc. (Figure 1). These and similar interests tend to go in cycles, and these systems are commonly treated as new, novel, and revolutionary. There is a consistent theme and set of practices among each of these systems and they are not all new. I describe them briefly in the following sections.
Regenerative agriculture (RA) is a systems approach to crop production that emphasizes rebuilding soil health, enhancing biodiversity, and increasing the resilience of farming systems by supporting natural ecological processes. Many RA practices are grounded in old agronomic principles that predate modern conventional/chemical agriculture (CA) and remain relevant in contemporary agroecosystems (Giller, et al., 2021).

Figure 1. The frequency of key terms in books (3-year rolling averages). Source:
Google NGram Viewer, Corpus ‘English 2019’ which includes books
predominantly in the English language published in any country (Giller et al.,
2021).
Crop rotations and diversification
Crop rotation has long been recognized as a beneficial agronomic practice, and it is central to RA systems. Rotations disrupt pest and pathogen life cycles, improve nutrient cycling, and stabilize crop yields. The inclusion of legumes contributes to biologically fixed nitrogen and diverse root systems, which can reduce fertilizer requirements and benefit subsequent crops (Solberg, 1958; Troeh, et al., 1999; Tilman et al., 2002).
Organic residues and manures returned to soil
The incorporation of crop residues, green manures, compost, and animal manures replenishes soil organic matter (SOM) and soil organic carbon (SOC). As they decompose, they provide slow-release nutrients, and support soil biota. Returning organic materials enhances microbial activity, improves soil structure, and benefits soil waterholding capacity. Farmers have been utilizing these practices to sustain soil productivity for centuries (Lal, 2004).
Minimal or reduced tillage
Reduced tillage and no-till practices protect soil structure, reduce erosion, and support soil biological communities. Limiting physical disturbance promotes soil aggregation, porosity, and water infiltration, contributing to improved soil stability. Reduced tillage has long been a component of soil conservation and soil-building strategies for many years, particularly in the past 90 years since the Dust Bowl (Solberg, 1958; Troeh, et al., 1999).
Cover crops
Cover crops planted between cash crops protect soil from erosion, scavenge nutrients, add biomass, and can suppress weeds. Living roots and added organic inputs stimulate microbial activity and promote a more diverse soil microbiome. In irrigated crop production systems this practice is more challenging and expensive due to the extra water demand and special practices for a crop with no cash value. Thus, it is impractical in most cases.
Mulching and residue management
Surface residues and organic mulches help conserve soil moisture, moderate soil temperatures, and in some cases reduce weed pressure. Mulching creates a favorable microclimate for beneficial soil organisms and contributes to soil protection (Solberg, 1958; Troeh, et al., 1999). This is also a centuries-old practice (Lal, 2004) but difficult to implement in many irrigated crop systems.
Agroforestry, hedgerows, and diversified landscapes
Some regenerative systems integrate trees, shrubs, or hedgerows with crops and livestock to enhance biodiversity and nutrient cycling and potentially diversify farm income. However, these practices are not feasible in all agricultural production systems, including irrigated crop production systems in the desert Southwest (Solberg, 1958). They have been found to be more feasible in tropical and subtropical regions.
Integrated pest management (IPM) and soil biology
Regenerative agriculture emphasizes the use of natural enemies, habitat for beneficial organisms, and reduced reliance on synthetic inputs. Most of these principles align with established IPM practices that have been successfully used for decades, including in Arizona crop production systems (Stern et al., 1959; Naranjo and Ellsworth, 2009).
Nutrient cycling and long-term soil organic matter (SOM)
Building or maintaining SOM is a primary objective of RA systems. Stable SOM improves soil structure, aeration, infiltration, and water-holding capacity. Maintaining SOM has long been recognized as a critical goal in CA systems as well (Tilman et al., 2002; Lal, 2004).
Agroecosystem management
Effective management is essential to the success of any crop production system and this is true in both RA and CA systems. Successful implementation requires integrating cropping system (agroecosystem) knowledge with careful planning, monitoring of soilplant relationships, and nutrient management to maintain yield stability and long-term sustainability. Efforts to do this practically and effectively are central to the management of crop production systems in the desert Southwest. We have realized good progress over many decades, yet it is always good to review and consider where we can continue to improve.
References
Giller, R.E., H. Renske, J.A. Andersson, and J. Sumberg. 2021. Regenerative agriculture: an agronomic perspective. Outlook on Agriculture, Vol. 50(1) 13–25.
Lal, R. 2004. Soil carbon sequestration to mitigate climate change. Science. 304: 1623-1627.
Naranjo, S.E. and P.C. Ellsworth. 2009. Fifty years of the integrated control concept: moving the model and implementation forward in Arizona. Pest Manag Sci 2009; 65: 1267–1286
Solberg, E.D. 1958. Planning for stability in a great area. In: Yearbook of Agriculture, 1958. p 532-536. United States Department of Agriculture, Washington, D.C.
Stern, V.M., R.F. Smith, R. van den Bosch, and K.S. Hagen. 1959. The integrated control concept. Hilgardia 29:81-101.
Tilman, D.; Cassman, K.G.; Matson, P.A.; Naylor, R.; Polasky, S. 2002. Agricultural sustainability and intensive production practices. Nature. 418: 671-677.
Troeh, F.R., J.A. Hobbs, and R.L. Donohue. 1999. Soil and Water Conservation: Productivity and Environmental Protection. Prentice Hall.