ReseaRch aRticle
Journal of Soil and Water ConServation
Implementing nonpoint source pollution programs: Insights from
interviews with agency professionals
Bonnie l. Keeler , taylor hohensee, Meghan anderson, and erin Niehoff
Center for Science, technology, and environmental Policy, Humphrey School of Public affairs, university of Minnesota, Minneapolis,
Minnesota, uSa
ABSTRACT
Nutrient pollution from agriculture remains a leading cause of water quality impairments in
the United states despite decades of policy interventions. the authority to implement water
quality policies falls to states, with significant variation in the development and execution of
programs designed to reduce nutrient pollution. Few studies have evaluated how states
implement these programs, limiting insights into how policy actors can improve the design
and delivery of water quality policies. state agency professionals have unique insights into
the implementation of programs designed to address nutrient runoff. here we report on
interviews with agency staff involved in six water quality programs across three Us states. We
asked interviewees to reflect on the implementation of each program and share
recommendations for how policies could be adapted to other states or contexts. Respondents
identified several insights relevant to successful policy implementation. they stressed the
need for strong partnerships between state and local agencies, robust technical tools for
monitoring and compliance, and adaptable strategies that account for regional and operational
differences. agency staff noted that voluntary policies are more politically feasible but less
effective, while mandatory policies can achieve broader compliance when robust enforcement
mechanisms are in place. in addition to implementation challenges, agency staff were asked
to reflect on the equity implications of agricultural policies. Many programs fail to account for
barriers faced by small-scale, minority, and underrepresented farmers, including limited access
to land and resources. this research provides actionable insights for policymakers, emphasizing
the importance of balancing flexibility and resource allocation to create more effective and
sustainable water quality programs.
INTRODUCTION
Despite years of effort, policies to reduce non-
point source pollution have had limited success
in improving water quality (Dubrovsky and
Hamilton 2010; Lintern et al. 2020). More than
half of US stream and river miles and 40% of
lakes are still considered impaired (US EPA
2024b). Agricultural runoff is the largest source
of pollution to rivers and streams and the third
leading source for lakes in the United States (US
EPA 2024a).
States have implemented voluntary and regu-
latory approaches to reduce the impacts of agri-
culture on water quality. These include
encouraging farmers to adopt best management
practices (BMPs) such as cover crops and riparian
buffers (Liu et al. 2017; Schramm et al. 2024;
Shahady 2022) and regulating nutrient manage-
ment by mandating the quantity or timing of
fertilizer application. Efforts to document the
impact of state-level nonpoint source pollution
programs have proven challenging due to the
inability to identify specific sources of water pol-
lution, lag times between policy interventions and
measurable nutrient reduction impact, and the
resources required to monitor water quality out-
comes (Tomczyk et al. 2023). Additional chal-
lenges include insufficient monitoring or
enforcement, low adoption rates, limited resources
to oversee or execute programs, and investments
in practices that are ultimately ineffective.
© 2026 the author(s). Published with license by taylor & francis Group, llC
CONTACT Bonnie l. Keeler keeler@umn.edu
Supplemental data for this article can be accessed online at https://doi.org/10.1080/00224561.2025.2597160.
https://doi.org/10.1080/00224561.2025.2597160
this is an open access article distributed under the terms of the Creative Commons attribution-nonCommercial-noderivatives license (http://creativecommons.org/licenses/by-nc-nd/4.0/),
which permits non-commercial re-use, distribution, and reproduction in any medium, provided the original work is properly cited, and is not altered, transformed, or built upon in
any way. the terms on which this article has been published allow the posting of the accepted Manuscript in a repository by the author(s) or with their consent.
ARTICLE HISTORY
received March 12, 2025
revised June 23, 2025
accepted July 8, 2025
KEYWORDS
best management practices;
compliance; implementation;
nonpoint source; nutrient
pollution; semistructured
interviews
Journal of Soil and Water ConServation
Implementing nonpoint source pollution programs: Insights from
interviews with agency professionals
Bonnie l. Keeler , taylor hohensee, Meghan anderson, and erin Niehoff
Center for Science, technology, and environmental Policy, Humphrey School of Public affairs, university of Minnesota, Minneapolis,
Minnesota, uSa
ABSTRACT
Nutrient pollution from agriculture remains a leading cause of water quality impairments in
the United states despite decades of policy interventions. the authority to implement water
quality policies falls to states, with significant variation in the development and execution of
programs designed to reduce nutrient pollution. Few studies have evaluated how states
implement these programs, limiting insights into how policy actors can improve the design
and delivery of water quality policies. state agency professionals have unique insights into
the implementation of programs designed to address nutrient runoff. here we report on
interviews with agency staff involved in six water quality programs across three Us states. We
asked interviewees to reflect on the implementation of each program and share
recommendations for how policies could be adapted to other states or contexts. Respondents
identified several insights relevant to successful policy implementation. they stressed the
need for strong partnerships between state and local agencies, robust technical tools for
monitoring and compliance, and adaptable strategies that account for regional and operational
differences. agency staff noted that voluntary policies are more politically feasible but less
effective, while mandatory policies can achieve broader compliance when robust enforcement
mechanisms are in place. in addition to implementation challenges, agency staff were asked
to reflect on the equity implications of agricultural policies. Many programs fail to account for
barriers faced by small-scale, minority, and underrepresented farmers, including limited access
to land and resources. this research provides actionable insights for policymakers, emphasizing
the importance of balancing flexibility and resource allocation to create more effective and
sustainable water quality programs.
INTRODUCTION
Despite years of effort, policies to reduce non-
point source pollution have had limited success
in improving water quality (Dubrovsky and
Hamilton 2010; Lintern et al. 2020). More than
half of US stream and river miles and 40% of
lakes are still considered impaired (US EPA
2024b). Agricultural runoff is the largest source
of pollution to rivers and streams and the third
leading source for lakes in the United States (US
EPA 2024a).
States have implemented voluntary and regu-
latory approaches to reduce the impacts of agri-
culture on water quality. These include
encouraging farmers to adopt best management
practices (BMPs) such as cover crops and riparian
buffers (Liu et al. 2017; Schramm et al. 2024;
Shahady 2022) and regulating nutrient manage-
ment by mandating the quantity or timing of
fertilizer application. Efforts to document the
impact of state-level nonpoint source pollution
programs have proven challenging due to the
inability to identify specific sources of water pol-
lution, lag times between policy interventions and
measurable nutrient reduction impact, and the
resources required to monitor water quality out-
comes (Tomczyk et al. 2023). Additional chal-
lenges include insufficient monitoring or
enforcement, low adoption rates, limited resources
to oversee or execute programs, and investments
in practices that are ultimately ineffective.
© 2026 the author(s). Published with license by taylor & francis Group, llC
CONTACT Bonnie l. Keeler keeler@umn.edu
Supplemental data for this article can be accessed online at https://doi.org/10.1080/00224561.2025.2597160.
https://doi.org/10.1080/00224561.2025.2597160
this is an open access article distributed under the terms of the Creative Commons attribution-nonCommercial-noderivatives license (http://creativecommons.org/licenses/by-nc-nd/4.0/),
which permits non-commercial re-use, distribution, and reproduction in any medium, provided the original work is properly cited, and is not altered, transformed, or built upon in
any way. the terms on which this article has been published allow the posting of the accepted Manuscript in a repository by the author(s) or with their consent.
ARTICLE HISTORY
received March 12, 2025
revised June 23, 2025
accepted July 8, 2025
KEYWORDS
best management practices;
compliance; implementation;
nonpoint source; nutrient
pollution; semistructured
interviews
2 B. l. KeeleR et al.
Existing policy implementation research on
agricultural water quality has focused on the per-
spectives of farmers and producers. Scholars have
used focus groups (Irvine et al. 2024), surveys
(Denny, Marquart-Pyatt, and Houser 2019), inter-
views (Reimer, Denny, and Stuart 2018), mixed
methods (O’Connell and Osmond 2022; Osmond
et al. 2015), and meta-analyses (Baumgart-Getz,
Prokopy, and Floress 2012) to assess farmer per-
spectives on program adoption and participation.
Research has assessed farmer perspectives on cli-
mate change (Arbuckle et al. 2014), adoption of
climate change adaptation practices (Soubry,
Sherren, and Thornton 2020), and motivations
to reduce nutrient inputs (Young et al. 2022).
Insights from this work have identified the
importance of trusted sources in enhancing par-
ticipation in conservation programs and motivat-
ing farmer behavior and adoption of BMPs.
Relatively less attention has been devoted to
the perspectives of agency staff and the practi-
tioners who implement water quality policies.
Policy scholars use the terms “street-level bureau-
crats” or “policy entrepreneurs” to describe actors
who interact with the public and have consider-
able autonomy in decisions that affect policy and
program implementation (Lipsky 1980). Policy
implementation research in this area explores
questions related to the impact and influence of
street-level bureaucrats in determining policy out-
comes (Sætren 2024). In the context of state
nutrient reduction policies, these actors include
agency staff who oversee the implementation of
state and federal nutrient management programs,
as well as local soil and water conservation dis-
trict (SWCD, or its equivalent) professionals. In
contrast to farmers and producers who are often
the target of nutrient reduction programs,
street-level bureaucrats offer unique perspectives
on the details of policy design, implementation,
and enforcement.
Previous research found that street-level
bureaucrats impact policy outcomes through their
discretionary power and allocation of resources.
Wardropper (2018) surveyed SWCD staff in the
Upper Mississippi River basin, finding variation
in how staff integrated environmental perfor-
mance information in watershed planning. Reimer
and Prokopy (2014) interviewed USDA Natural
Resources Conservation Service (NRCS) staff
involved in the implementation of the USDA’s
Environmental Quality Incentives Program
(EQIP), identifying ways that agency staff adapted
federal programs to accommodate local contexts.
In a study of Missouri agroforestry programs,
Kronenberg et al. (2023) found that uptake of
recommended practices was hindered by a lack
of in-depth knowledge by conservation officials
overseeing program implementation. These exam-
ples demonstrate the potential influence of agency
staff on program effectiveness.
Much of the existing research on water policy
has focused on the empirical evaluation of policy
design and associated outcomes, often supported
by coupled hydrologic and economic modeling
(Keiser and Shapiro 2019). Research of this type
has contributed greatly to our understanding of
the return on investment in water quality pro-
grams and informed evaluation of alternative
designs including market-based versus regulatory
approaches (Olmstead and Stavins 2009). However,
quantitative analyses of policy outcomes can over-
look key institutional and political factors that
are key to policy implementation (Sevä and Jagers
2013; Sætren 2024). Street-level bureaucrats are
the primary implementers of environmental pol-
icy and therefore offer unique insights related to
the monitoring, evaluation, and enforcement of
water programs (Holstead, Funder, and
Upton 2021).
Qualitative research also provides an opportu-
nity to investigate the equity implications of envi-
ronmental and agricultural policies (Layman and
Civita 2022). Guidance from the Biden adminis-
tration required federal agencies to consider the
equity and distributional impacts of federal pro-
grams (Federal Register 2023). In recent years,
state water quality funds have also added require-
ments to consider how investments “celebrate
cultural diversity or reach diverse communities,
including reaching low- and moderate-income
households” (Minnesota Legislature 2024). These
efforts are often motivated by a recognition that
discriminatory practices have led to differential
outcomes in access to land or exposure to envi-
ronmental harms. For example, scholars have
highlighted how USDA policies negatively
impacted access to land and farm programs by
Existing policy implementation research on
agricultural water quality has focused on the per-
spectives of farmers and producers. Scholars have
used focus groups (Irvine et al. 2024), surveys
(Denny, Marquart-Pyatt, and Houser 2019), inter-
views (Reimer, Denny, and Stuart 2018), mixed
methods (O’Connell and Osmond 2022; Osmond
et al. 2015), and meta-analyses (Baumgart-Getz,
Prokopy, and Floress 2012) to assess farmer per-
spectives on program adoption and participation.
Research has assessed farmer perspectives on cli-
mate change (Arbuckle et al. 2014), adoption of
climate change adaptation practices (Soubry,
Sherren, and Thornton 2020), and motivations
to reduce nutrient inputs (Young et al. 2022).
Insights from this work have identified the
importance of trusted sources in enhancing par-
ticipation in conservation programs and motivat-
ing farmer behavior and adoption of BMPs.
Relatively less attention has been devoted to
the perspectives of agency staff and the practi-
tioners who implement water quality policies.
Policy scholars use the terms “street-level bureau-
crats” or “policy entrepreneurs” to describe actors
who interact with the public and have consider-
able autonomy in decisions that affect policy and
program implementation (Lipsky 1980). Policy
implementation research in this area explores
questions related to the impact and influence of
street-level bureaucrats in determining policy out-
comes (Sætren 2024). In the context of state
nutrient reduction policies, these actors include
agency staff who oversee the implementation of
state and federal nutrient management programs,
as well as local soil and water conservation dis-
trict (SWCD, or its equivalent) professionals. In
contrast to farmers and producers who are often
the target of nutrient reduction programs,
street-level bureaucrats offer unique perspectives
on the details of policy design, implementation,
and enforcement.
Previous research found that street-level
bureaucrats impact policy outcomes through their
discretionary power and allocation of resources.
Wardropper (2018) surveyed SWCD staff in the
Upper Mississippi River basin, finding variation
in how staff integrated environmental perfor-
mance information in watershed planning. Reimer
and Prokopy (2014) interviewed USDA Natural
Resources Conservation Service (NRCS) staff
involved in the implementation of the USDA’s
Environmental Quality Incentives Program
(EQIP), identifying ways that agency staff adapted
federal programs to accommodate local contexts.
In a study of Missouri agroforestry programs,
Kronenberg et al. (2023) found that uptake of
recommended practices was hindered by a lack
of in-depth knowledge by conservation officials
overseeing program implementation. These exam-
ples demonstrate the potential influence of agency
staff on program effectiveness.
Much of the existing research on water policy
has focused on the empirical evaluation of policy
design and associated outcomes, often supported
by coupled hydrologic and economic modeling
(Keiser and Shapiro 2019). Research of this type
has contributed greatly to our understanding of
the return on investment in water quality pro-
grams and informed evaluation of alternative
designs including market-based versus regulatory
approaches (Olmstead and Stavins 2009). However,
quantitative analyses of policy outcomes can over-
look key institutional and political factors that
are key to policy implementation (Sevä and Jagers
2013; Sætren 2024). Street-level bureaucrats are
the primary implementers of environmental pol-
icy and therefore offer unique insights related to
the monitoring, evaluation, and enforcement of
water programs (Holstead, Funder, and
Upton 2021).
Qualitative research also provides an opportu-
nity to investigate the equity implications of envi-
ronmental and agricultural policies (Layman and
Civita 2022). Guidance from the Biden adminis-
tration required federal agencies to consider the
equity and distributional impacts of federal pro-
grams (Federal Register 2023). In recent years,
state water quality funds have also added require-
ments to consider how investments “celebrate
cultural diversity or reach diverse communities,
including reaching low- and moderate-income
households” (Minnesota Legislature 2024). These
efforts are often motivated by a recognition that
discriminatory practices have led to differential
outcomes in access to land or exposure to envi-
ronmental harms. For example, scholars have
highlighted how USDA policies negatively
impacted access to land and farm programs by