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WHAT IS CLIMATE SMART AGRICULTURE?

Friday, July 12, 2024

Introduction



As the United States agricultural system faces the challenges of feeding a
growing population, adapting to climate change, and reducing environmental
consequences, the concept of climate-smart agriculture (CSA) was established as
a comprehensive strategy to help address these issues. However, no standardized
framework exists to assess if CSA practices produce the desired benefits. This
article calls for developing a consistent, widely applicable, and standardized
framework to assess what makes a specific agricultural system or practice
"climate-smart” and analyzes agroforestry and prescribed grazing within said
framework.




BACKGROUND

Climate change and food insecurity are two complicated and interconnected
challenges that the world must address. With global population projected to
reach 9.7 billion by 2050, there is increasing pressure on production
agriculture and supply chain management to reduce food insecurity (Food and
Agricultural Organization of the United Nations [FAO], 2013). This challenge is
made more difficult by global climate change, driven by increasing anthropogenic
greenhouse gas (GhG) concentrations, of which a significant proportion are
attributable to agriculture (Environmental Protection Agency, 2024). Therefore,
a heightened focus on sustainable agriculture systems is necessary to guarantee
food security, improve environmental health, and respond to climate change; the
concept of CSA intends to contribute to addressing this ultimate challenge.




Agricultural systems and practices referred to as CSA are assumed to address at
least two of the interconnected challenges of feeding a growing population,
adapting to climate change, and reducing environmental harm (The World Bank,
2024). However, the lack of a standardized framework to assess if CSA practices
produce their desired benefits promotes an environment where the term CSA can be
arbitrarily applied to any agricultural system or practice assumed to have a
production, environmental, or climate benefit. For example, in 2024 the USDA
added 15 practices to its climate-smart conservation list eligible for
Environmental Quality Incentives Program (EQIP) funding, but many likely lack
tangible climate benefits (Schechinger, 2024). To ensure the paradigm of CSA
truly produces the tangible benefits needed to address food insecurity,
environmental sustainability, and climate change, a standardized framework
supported by global agricultural organizations should be adopted.




TOWARD A CLIMATE SMART AGRICULTURE FRAMEWORK

Many organizations have broadly defined CSA, including the World Bank, the FAO,
and the United States Department of Agriculture (USDA). These definitions are
connected by the central tenets of (1) increasing agricultural productivity, (2)
enhancing agricultural resilience, and (3) reducing GhG emissions (The World
Bank, 2024; FAO, 2024; USDA Northeast Climate Hub, n.d.).




Despite the agreement between agricultural organizations on the broad pillars of
CSA, no standardized framework exists to assess if practices or technologies
identified as "climate-smart” produce the desired benefits as defined by the
framework. A standardized framework would provide a common set of criteria for
evaluating the climate-smart attributes of agricultural practices in different
regions. A standardized framework would also enable producers, policymakers, and
researchers to consistently compare the effectiveness, tradeoffs, and
implementation barriers of various CSA systems and practices. The framework will
result in improved implementation of CSA goals, better policy development, and
more informed decision-making processes on a national scale.




Furthermore, it is difficult to effectively allocate resources without a clear
assessment of how a system or practice is identified as "climate-smart” or to
what degree it produces tangible "climate-smart” benefits. To maximize resource
allocation, the USDA, producers, policymakers, researchers, and other interest
groups must fully understand and consider the benefits, costs, and uncertainties
of CSA practices. This article subsequently provides examples of such an
assessment using examples of agroforestry and prescribed grazing systems, which
are often referred to as "climate smart.”




AGROFORESTRY DISCUSSION

When analyzing agroforestry systems and its five practices (alley cropping,
riparian forest buffers, silvopasture, windbreaks, and forest farming) through
the three-pillar CSA framework, strong scientific evidence supports that the
system increases productivity, enhances adaptation, and reduces emissions (USDA
National Agroforestry Center, n.d.a). When properly implemented and managed,
agroforestry systems simultaneously address the "production needs of farmers and
land-owners while providing environmental benefits to society” (Bishaw et al.,
2022).









Each agroforestry practice has its own set of advantages and complexities (USDA
National Agroforestry Center, n.d.a). For example, alley cropping can support
soil stabilization, bioremediation, and biodiversity, which are important for
climate change adaptation and emission reduction (Udawatta et al., 2014);
however, root competition with grain or horticulture crops may hinder production
benefits (Garrett et al., 2022). Riparian forest buffers are effective at
helping farmers to become more resilient by improving water quality and reducing
farm runoff, but productivity and emission benefits are not well known (Schultz
et al., 2004; Effert-Fanta et al., 2019). Silvopasture can reduce methane
emissions, but more research is needed to optimize adaptation and production
benefits (Pent, 2020; Jose & Dollinger, 2019). Windbreaks excel at protecting
crops and enhancing productivity, but may cause plants to become less
drought-resilient (Ballesteros-Possu, et al., 2017; Smith, et al., 2021). Forest
farming provides farmers with additional products and income, but adaptation and
emission reduction benefits are unclear (Baker & Saha, 2016; Trozzo et al.,
2021).




The production pillar of the CSA framework comprises the agronomic production of
the system or practice and its economic feasibility. Research supports the
economic resilience of agroforestry systems in the Midwest relative to a
traditional maize-soybean rotation (Wolz & DeLucia, 2018). Agroforestry is also
supported by various Natural Resource Conservation Service (NRCS) implementation
incentives through EQIP (USDA National Agroforestry Center, n.d.b). Across the
Midwest, between 2017 and 2023, approximately $900,000 of EQIP-Farm Bill funds
were invested in agroforestry practices (USDA NRCS, 2024). Figures 2 and 3 below
show a further breakdown of how and where the funds were allocated. A
standardized CSA framework will help these funds be distributed as efficiently
as possible.








However, challenges and tradeoffs exist with agroforestry, including potential
resource competition between trees and crops, variability in environmental
services provided, and the need for comprehensive research on GhG sequestration
and legacy (Garrett et al., 2022). While some uncertainties and limitations
persist, the overall positive effects of agroforestry on enhancing farm
resilience make it a promising CSA candidate. As the Midwest recognizes the
viability of these practices, addressing challenges and conducting further
research will be crucial for optimizing the benefits of agroforestry in the
region. By using the unique advantages of each agroforestry practice and
addressing their respective limitations, stakeholders can collaborate toward
building resilient and sustainable agricultural systems that proactively address
climate change, while enhancing productivity and environmental stewardship.




PRESCRIBED GRAZING DISCUSSION

The three-pillar framework is also applied to prescribed grazing, where
livestock from several herds are combined and rotated among different pastures
to provide a "rest period for the pastures when the cattle are in a different
pasture” (USDA NRCS, n.d.a). Prescribed grazing involves "multiple human
dimensions as well as complex ecological processes” with the goal to support
"ecosystem sustainability and restore degraded ecosystems” (Briske, 2011).









In the context of the three-pillar framework, the CSA benefits of prescribed
grazing are less clear than for agroforestry. In terms of productivity benefits,
there is an absence of strong evidence describing how prescribed grazing can
improve forage quality and quantity, thereby improving animal health,
resilience, and productivity (Nelson, 2012).




Regarding the second CSA pillar of enhanced resilience, the USDA prescribed
grazing management objectives of improving biodiversity, soil health, and water
quality are analyzed (USDA NRCS, n.d.b). For example, additional research
regarding wildlife responses to prescribed grazing is needed in developing
countries because wildlife effects widely vary depending on the species
(Schieltz & Rubenstein, 2016). Likewise, more studies are needed to assess plant
communities’ responses to prescribed grazing and understand long-term ecological
outcomes and benefits (Russell & Bisinger, 2015). Furthermore, the relationship
between grazing management and soil health is limited by a lack of scientific
evidence (Derner et al., 2018). Using prescribed grazing to manage fine fuel
loads is not a clear-cut tool, as weather and site conditions complicate this
relationship (Briske, 2011). Finally, the most transparent relationship exists
between riparian and watershed quality and reduced livestock grazing; however,
additional research is still needed to specify the effects of prescribed grazing
on riparian areas (Krall & Roni, 2022).




Although the USDA does not list GhG emissions reductions as a prescribed grazing
management objective, some literature suggests that prescribed grazing can
reduce atmospheric GhG concentrations through increased carbon and methane
sequestration (USDA NRCS, n.d.b). For example, the FAO claims that improving
grazing management can increase soil carbon stocks and sequestration (FAO,
2013). Researchers from Colorado State University performed a synthesis of
hundreds of studies and concluded that "management practices introduced
intending to increase forage production tend to lead to increases in soil C
stocks” (Conant et al., 2017). Therefore, it is evident that prescribed grazing
has some quantifiable indirect emission reduction capabilities through carbon
sequestration; however, more research is needed to better quantify these
benefits and link the potential emissions reduction benefits of prescribed
grazing to the USDA-defined management objectives.

Across the Midwest, between 2017 and 2023, approximately $17.5 million of
EQIP-Farm Bill funds were allocated to prescribed grazing (USDA NRCS, 2024).
This large investment highlights the regional applicability of prescribed
grazing practices in the Midwest. Figures 5 and 6 below show a further breakdown
of how and where the funds were allocated.











While prescribed grazing offers many benefits, there is substantial uncertainty
in its effectiveness in achieving CSA objectives (Nelson, 2012). Further
research is needed to better understand the production, resilience, and
emissions benefits of prescribed grazing and help clarify its role in CSA.
Overall, prescribed grazing has the potential to reduce environmental impacts
from the livestock sector, but the scientific literature does not adequately
support the assumptions of prescribed grazing management objectives as CSA.




CONCLUSION

CSA is a promising paradigm for addressing environmental challenges by
increasing productivity, enhancing resilience, and reducing emissions. However,
the definition and assessment of CSA practices lack standardization, hindering
their widespread adoption and effective implementation. Developing a
standardized CSA framework for assessing systems and practices is crucial for
evaluating their effectiveness, comparing different approaches, and guiding
decision-making processes and resource allocation. The Growing Climate Solutions
Act (GCSA) and the Inflation Reduction Act (IRA) gives the USDA some authority
to govern the CSA framework; however further development is needed to create a
common criterion for stakeholders to assess the climate-smart attributes of
agricultural systems and practices (GCSA, 2021; IRA 2022).




By applying the consistent three-pillar framework, we can better understand the
potential of CSA practices in addressing climate change and promoting
sustainable agriculture. Our initial assessment revealed that a significant body
of scientific research supports that agroforestry accomplishes many of the CSA
goals when properly implemented and managed; however, the benefits of prescribed
grazing lack scientific consensus and require further research. It is important
to note that for both agroforestry and prescribed grazing, the effectiveness of
the systems is dependent on site-specific conditions and management.




In conclusion, a consistent, widely applicable, and standardized framework for
assessing CSA will facilitate informed decision-making, improve resource
allocation, and enhance stakeholder collaboration. By promoting the adoption of
CSA practices, the United States can move closer to achieving environmental and
food security goals in a changing climate. It is recommended that this framework
is continually developed and used as a model for the USDA, producers, and
researchers to assess agricultural systems, practices, and technologies to
determine if they qualify as "climate-smart.”






By: Messerges, O. and T. Ford. "What is Climate Smart Agriculture?" farmdoc
daily (14):128, Department of Agricultural and Consumer Economics, University of
Illinois at Urbana-Champaign, July 11, 2024.
 

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