Scientific Evidence Indicates that Reducing NOx Emissions is the Most Effective Strategy to Reduce Concentrations of Ammonium Nitrate, a Significant Contributor to PM2.5 Concentrations in California’s San Joaquin Valley

Recently there has been increased interest in regulating ammonia emissions to reduce PM2.5 (“fine” particles with an aerodynamic diameter less than 2.5 micrometers)  concentrations.  However, understanding the quantity of and interactions between ammonia and nitrogen oxide (NOx) is necessary in determining whether controlling ammonia is an effective strategy for reducing PM2.5 in a particular region.  Research from the California Regional Particulate Air Quality Study and other studies has demonstrated the relative abundance of ammonia in comparison to the limited concentrations of the other key precursor, nitric acid formed by NOx emissions.  As a result, NOx acts as the primary limiting precursor for the formation of secondary ammonium nitrate in the San Joaquin Valley (SJV).  Modeling based on data from these studies also found that controlling NOx was the most effective strategy to reduce ammonium nitrate particulate in the SJV and controlling ammonia had little effect on PM2.5 concentrations. 

In summary and as explained in the San Joaquin Valley Air Pollution Control District 2012 PM2.5 Plan, the best scientific information available indicates that controlling NOx emissions is the most effective strategy to reduce secondary ammonium nitrate in the SJV.  While it has been demonstrated that controlling ammonia will not significantly reduce PM2.5 concentrations in the SJV, the District has adopted stringent regulations that have significantly reduced ammonia emissions.

Purpose

The San Joaquin Valley is primarily a rural region with large areas dedicated to agriculture. Recently there has been increased interest in regulating ammonia emissions from agricultural operations and other sources as a means to reduce PM2.5 concentrations. However, understanding the quantity and interactions between ammonia and NOx are necessary in determining whether controlling ammonia emissions is an effective strategy for reducing secondary PM2.5 formation in a particular geographic region.

average of peak day pm2.5 chemical composition

The United States Environmental Protection Agency (U.S. EPA) periodically reviews and establishes health-based air quality standards (often referred to as National Ambient Air Quality Standards, or NAAQS) for ozone, particulate matter (PM), and other pollutants. Although the air quality in California’s San Joaquin Valley has been steadily improving, the region is currently classified as “serious” non-attainment for the 1997 and 2006 federal ambient air quality standards for PM2.5. The periods for which measured PM2.5 concentrations drive nonattainment of these standards occur primarily in the winter months and air quality research in the San Joaquin Valley has identified ammonium nitrate as the predominant contributor to secondary PM2.5 in the region. Ammonium nitrate particulate is formed through chemical reactions between ammonia in the air and NOx emissions produced by mobile and stationary combustion sources. As shown in Figure 1 above, ammonium nitrate is commonly the largest contributor to PM2.5 mass during the winter in the San Joaquin Valley.

What did we do?

modeled ammonium nitrate response to NH3 vs NOxAtmospheric modeling has demonstrated that controlling NOx is the most effective strategy to reduce ammonium nitrate concentrations in the San Joaquin Valley and controlling ammonia has little effect on these concentrations. The California Air Resources Board conducted multiple modeling runs to simulate the formation of PM2.5 in the San Joaquin Valley and compare the effect of reducing various pollutants on PM2.5 concentrations. As seen in Figure 2, U.S. EPA’s Community Multi-scale Air Quality (CMAQ) indicated that reducing NOx by 50% reduced nitrate concentrations by 30% to 50% reductions, while reducing ammonia by 50% resulted in less than 5% reductions in nitrate concentrations. Similarly, the UCD/CIT photochemical transport model indicated that for the conditions on January 4-6, 1996 in the San Joaquin Valley, controlling NOx emissions is far more effective for reducing nitrate concentrations than controlling ammonia.

What have we learned?

abundance of NH3 in San Joaquin ValleyAmmonium nitrate particulate is limited by NOx in the San Joaquin Valley

Extensive research conducted through the California Regional Particulate Air Quality Study (CRPAQS) and other studies has demonstrated the relative abundance of ammonia in comparison to the limited concentrations of the other key precursor, nitric acid formed by NOx emissions in the San Joaquin Valley. As a result, NOx (via nitric acid) acts as the primary limiting precursor for the formation of secondary ammonium nitrate. (See Figures 3 and 4)

Future Plans

NOx control reduces ammonium nitrate more efficientlyAs explained in detail in the San Joaquin Valley Air Pollution Control District 2012 PM2.5 Plan, the best scientific information available indicates that controlling NOx emissions is the most effective strategy to reduce secondary ammonium nitrate in the San Joaquin Valley. While ammonia has been demonstrated to not significantly contribute to PM2.5 concentrations in the San Joaquin Valley, the District has developed control strategies, via stringent regulations (Confined Animal Facilities – Rule 4570, Organic Material Composting – Rule 4566, Biosolids, Animal Manure, and Poultry Litter Operations – Rule 4565), that have resulted in significant reductions in ammonia emissions.

Authors

Errol Villegas, Program Manager, San Joaquin Valley Air Pollution Control District errol.villegas@valleyair.org

Ramon Norman, Air Quality Engineer, San Joaquin Valley Air Pollution Control District

Additional information

California Air Resources Board Technical Symposium: Scientific Basis of Air Quality Modeling for the San Joaquin Valley 2012 PM2.5 Plan (April 27, 2012). Fresno, CA

Magliano, K. L. & Kaduwela, A. P. (2012) California Air Resources Board Technical Symposium: Technical Basis of the 2012 San Joaquin Valley PM2.5 Plan Modeling. Fresno, CA.

San Joaquin Valley Unified Air Pollution Control District. 2012 PM2.5 Plan (2012), Chapter 4 – Scientific Foundation and PM2.5 Modeling Results

Chen, J.; Lu, J.; Avise, J. C.; DaMassa, J. A.; Kleeman, M. J. & Kaduwela, A. P. (2014), Seasonal modeling of PM2.5 in Californias San Joaquin Valley, Atmospheric Environment 92, p. 182-190.

Kleeman, Michael J., Qi Ying, Ajith Kaduwela (2005) Control Strategies for the Reduction of Airborne Particulate Nitrate in California’s San Joaquin Valley. Atmospheric Environment, 39 (29), p. 5325 – 5341

The authors are solely responsible for the content of these proceedings. The technical information does not necessarily reflect the official position of the sponsoring agencies or institutions represented by planning committee members, and inclusion and distribution herein does not constitute an endorsement of views expressed by the same. Printed materials included herein are not refereed publications. Citations should appear as follows. EXAMPLE: Authors. 2015. Title of presentation. Waste to Worth: Spreading Science and Solutions. Seattle, WA. March 31-April 3, 2015. URL of this page. Accessed on: today’s date.

Managing Livestock Ammonia: A Volatile, Promiscuous Fugitive In the Atmosphere (Rocky Mountain National Park)

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Abstract

Livestock production is the largest source of atmospheric ammonia, accounting for over 50 % and 40 % of the national and global inventories, respectively. At beef feedlots for example, 40 to 60 percent of the fed nitrogen is lost to the atmosphere as ammonia. Once ammonia enters the atmosphere it can convert to an aerosol and travel long distances from the source. Most of this fugitive nitrogen is eventually deposited back to the ground when scavenged from the air by precipitation. Unfortunately, this unintentional nitrogen transport and fertilization is having a negative ecological impact on pristine ecosystems around the globe. Thus, it is not surprising that livestock ammonia is an area of growing public concern and regulatory debate. Perhaps nowhere is ammonia from livestock under greater scrutiny than along the Front Range of Colorado. Increased levels of atmospheric nitrogen deposition are having a negative impact on the ecology of Rocky Mountain National Park, a crown jewel of the National Park System. While studies suggest many different sources are contributing to nitrogen deposition in the park (e.g., urban, out of state sources), much attention has been directed to the beef feedlots and dairies that populate the plains just east of the mountains. The keynote address will briefly discuss ammonia emissions from livestock at global scales, with commentary on a new United Nations report “Our Nutrient World” that draws considerable attention to manure management and atmospheric ammonia. The remainder of the presentation will focus on Colorado’s regional ammonia issue and what is being done to reduce ammonia loss from feedlots and dairies along the Front Range. New technologies for measuring ammonia and minimizing environmental impacts will be discussed.

About the Author

Jay Ham joined the Department of Soil and Crop Sciences at CSU in 2008 with an appointment that includes research, teaching, and extension responsibilities. Prior to joining the faculty at CSU, he led a program in Micrometeorology and Environmental Physics for 18 years at Kansas State University. Dr. Ham’s research includes: (1) evaluation of air and water quality issues at animal feeding operations; (2) instrumentation development for environmental, soil, and crop research; (3) micrometeorological studies of water, carbon, and contaminant transport between the surface and atmosphere; and (4) air quality impacts of oil and gas development. His teaching responsibilities include courses in micrometeorology and research proposal development.

Dr. Ham acts as lead investigator for several federally-funded research projects ($1.75 million) that focus on ammonia emissions from feedlots and dairies. This work includes the develop of management practices to reduce emissions from livestock operations and track atmospheric transport of ammonia along the Front Range – including nitrogen deposition in Rocky Mountain National Park. Jay and his team were recently awarded a new grant as part of the National Robotics Initiative (NSF and USDA) to develop air quality robotics for use at feedlots and diaries. Other research interests include the air quality impacts of hydraulic fracturing used in oil and gas exploration.

He can be contacted at:
Jay Ham, Dept. of Soil and Crop Sciences, Colorado State University
970-491-4112
jay.ham@colostate.edu

Estimating Ammonia Emissions from Livestock Operations Using Low-Cost, Time-Averaged Concentration Measurements

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Abstract

Recent regulations on ammonia (NH3) and other gaseous emissions by the EPA requires managers of animal feeding operations (AFOs) to report their annual emissions of greenhouse gases (GHGs), with the possibility of federal funding in the near future to be allocated for enforcement of GHG reporting as well as to levy large fines against AFOs that exceed the regulation limitations for GHG emissions. The current method of estimating NH3 emissions for AFOs is a “back of the envelope” type calculation based upon population and type of animal within an individual AFO.

Emissions of NH3 can vary drastically depending on climate, soil type, location, and other factors. This causes a need for accurate, nearly continuous, on-site measurements of NH3, which can be difficult to disseminate to and implement in an economically beneficial way by individual AFO facilities required to report NH3. Here we outline a robotic system developed for the measurement of NH3 that is cost-efficient to employ and easy to maintain while providing accurate year-round data on NH3 emissions. The system utilizes diffusive/passive samplers (e.g., Radiello, Sigma-Aldrich distributor) that are exposed to the environment under user-defined weather conditions which will yield observations of NH3 concentrations for a period representing several weeks. Measurement data from the robotic systems can be easily converted to accurate emissions estimates by using an inverse model (e.g., using a simple software package).

Data from the passive samplers will be shown for multiple sites and years of data acquired during extensive field testing of the robotic samplers at dairy and cattle feedlot operations in northeastern Colorado from 2011-2012. Emissions obtained using a simple inverse model on the data will be shown as well.

Authors

Kira Shonkwiler, Colorado State University, Dept of Atmospheric Science kshonk@atmos.colostate.edu

Dr. Jay Ham, Colorado State University, Dept of Soil and Crop Sciences, Christina Williams, Colorado State University, Dept of Soil and Crop Sciences

The authors are solely responsible for the content of these proceedings. The technical information does not necessarily reflect the official position of the sponsoring agencies or institutions represented by planning committee members, and inclusion and distribution herein does not constitute an endorsement of views expressed by the same. Printed materials included herein are not refereed publications. Citations should appear as follows. EXAMPLE: Authors. 2013. Title of presentation. Waste to Worth: Spreading Science and Solutions. Denver, CO. April 1-5, 2013. URL of this page. Accessed on: today’s date.

Affecting Change Through Collaboration: An Industry-Driven Approach

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The efforts related to Colorado’s Rocky Mountain National Park are voluntary, yet there are nitrogen reduction targets, or milestones, established over five year increments out to the year 2032. If a milestone is not met, mandatory controls could follow. How can the proactive emissions reduction efforts being taken by livestock and crop producers today be recognized or credited should mandatory controls be required at some future date? For example, could an agriculture certainty framework (used more for water quality protection/nutrient runoff) be used to validate actions being taken today for air quality purposes? How might an ag certainty program work and what partners should be at the table? Are there other approaches that states are using or researching that Colorado should consider?

During the session, presenters will speak to:

  • a meteorological Early Warning System that is being developed in Colorado to alert livestock producers in advance of an upslope weather event. What methods of messaging the alerts would be most successful, and what other applications (or sectors) might a meteorological Early Warning System be used for?
  • why it is important for producers (crop and livestock) to adopt BMPs and voluntary controls to address the problem of Nitrogen Deposition in Rocky Mountain National Park and what has been done so far in this regard.
  • agriculture, and specifically livestock agriculture’s, engagement in doing our part to sustain and improve the environment in which we operate.

Even though it is too early to make any conclusions as to the success of the proactive approach (i.e., voluntary measures versus regulatory controls) or to the extent that current state air quality plans or best management practices are having on nitrogen deposition in the park, the presentation is intended to share some of the challenges and achievements, to date, of this particular stakeholder-driven approach.

Presenters

Phyllis Woodford is the program manager of the Environmental Agriculture Program at the Colorado Department of Public Health & Environment. Phyllis has worked for the department 18 years and during this time has worked to educate the department on agriculture’s unique issues related to environmental concerns and the need for science-based solutions. She has a master’s degree in Environmental Policy & Management from the University of Denver and a BS in Criminal Justice from Kent State University. Prior to working for the State of Colorado, Phyllis served as a legislative assistant to an Ohio congressman in Washington, D.C.

Phyllis I. Woodford
Division of Environmental Health and Sustainability
Colorado Department of Public Health and Environment
4300 Cherry Creek Drive South
Denver, CO 80246-1530

Phone: 303-692-2978
Fax: 303-782-4969
E-mail: phyllis.woodford@state.co.us


Bill Hammerich has served as the Chief Executive Officer of the Colorado Livestock Association (CLA) for the past ten years. He grew up on a cattle and farming operation in Western Colorado and after graduating from high school he attended Colorado State University where he graduated with a degree in Agricultural Economics. Following graduation he began his working career with Monfort of Colorado, then Farr Feeders and was with the Sparks Companies before joining CLA in 2002.

His time spent in the cattle feeding industry provided him not only with an understanding of how to feed cattle but also the importance of protecting and sustaining the environment in which one operates. Such a background has served Bill and the CLA staff well as they represent a diversified CLA membership in addressing those environmental issues with which the livestock industry has to deal. Bill and his wife Sabrina live in Fort Morgan, Colorado and have two grown children, Justin and Jessica.


Jon Slutsky and his wife, Susan Moore, are first generation dairy farmers and have owned and operated La Luna Dairy in Northern Colorado since 1981.  Currently they milk 1300-1400 cows at their farm near Wellington. They have one adult daughter.  Jon is a native of New York; however he grew up and attended school in Southern California. He graduated from the University of California-Riverside with a bachelor’s degree in biology in 1972.  As general manager of the dairy, Jon oversees the management of the farm including 2600 cows and calves and 26 employees.

In order to add to the dairy data base and body of knowledge and assist in making good BMPs available to the industry, the farm has a policy of giving access as frequently as possible to animal and environmental researchers in the university community. The dairy tries to be a strong member of the local business and agricultural communities. Jon represents the dairy and the industry locally as a board member of the Wellington Area Chamber of Commerce, the Larimer County Agricultural Advisory Board, and the Colorado Livestock Association.  He also serves on several other committees as time permits.

Jon was a member of the  Colorado Air Quality Control Commission from 2007 to 2012 and is currently a member of the Colorado Water Quality Control Commission.


The authors are solely responsible for the content of these proceedings. The technical information does not necessarily reflect the official position of the sponsoring agencies or institutions represented by planning committee members, and inclusion and distribution herein does not constitute an endorsement of views expressed by the same. Printed materials included herein are not refereed publications. Citations should appear as follows. EXAMPLE: Authors. 2013. Title of presentation. Waste to Worth: Spreading Science and Solutions. Denver, CO. April 1-5, 2013. URL of this page. Accessed on: today’s date.

Presentation Slides

Mitigating Dust (Particulate Matter) Emissions from Animal Agriculture

Air emissions from animal animal feedlots are sources of many different emissions including particulate matter (dust).

The materials on this page were developed to assist educators and professors who wish to include dust and particulate emissions and their control as a topic in their classrooms or educational programs.

Fact Sheet

Sharon L. P. Sakirkin, Texas AgriLife Research; Ronaldo Maghirang, Kansas State University; Steve Amosson, Texas AgriLife Extension Service; Brent W. Auvermann, Texas AgriLife Extension Service and Texas AgriLife Research

Alternate download: Includes Dust Emissions Part 1 (Introduction) and Part 2 (Abatement) in a single document (12 pages; PDF format)

Video

Controlling Particulate Matter (PM) Emissions

Ronaldo Maghirang, Kansas State University (8 minutes)

Presentation Slides (Combined with an introductory PM presentation)

If you need to download a copy of a segment, submit a request.

Acknowledgements

These materials were developed by the Air Quality Education in Animal Agriculture (AQEAA) project with with financial support from the National Research Initiative Competitive Grant 2007-55112-17856 from the USDA National Institute of Food and Agriculture.

For questions about the materials on this page contact Dr. Kevin Janni, University of Minnesota (kjanni@umn.edu). For questions about the AQEAA project, contact Dr. Rick Stowell, Unviersity of Nebraska (rstowell2@unl.edu).

If you have presentations, photos, video, publications, or other instructional materials that could be added to the curricula on this page, please contact Dr. Janni or Jill Heemstra (jheemstra@unl.edu).

Ammonia Emissions from Animal Agriculture: An Introduction

Air emissions from animal agriculture operations consist of many different gases as well as suspended particulates (dust or microbes). One of these gases, ammonia, is gaining greater attention for its role in odor, but also as a precursor of fine particulate matter (PM 2.5). PM 2.5 has implications in haze and visibility as well as human health. The materials on this page were developed to assist educators and professors who include an introduction to include ammonia emissions as a topic in their classrooms or programs.

 Fact Sheets

Alternate download: Ammonia from Cattle Operations part 1 (Introduction) and part 2 (abatement) combined in a single document (17 pages; PDF format)

Videos

Ammonia Deposition Alpine Ecosystems


A look at the growing concern about the impacts of ammonia deposition in Rocky Mountain National Park.

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Ammonia Emissions

Rick Todd, USDA ARS (10 minutes)

Presentation Slides

Acknowledgements

These materials were developed by the Air Quality Education in Animal Agriculture (AQEAA) project with with financial support from the National Research Initiative Competitive Grant 2007-55112-17856 from the USDA National Institute of Food and Agriculture.

For questions about the materials on this page contact Dr. Ron Sheffield, Louisiana State University Ag Center. For questions about the AQEAA project, contact Dr. Rick Stowell, University of Nebraska (rstowell2@unl.edu).

If you need to download a copy of a segment, submit a request.

___

Photo (right): Ammonia is a precursor to fine particulate matter (also known as PM 2.5) which can lead to hazy conditions. These conditions are becoming a more common occurrence for visitors to Rocky Mountain National Park.

Mitigating Ammonia Emissions from Animal Agriculture

Air emissions from animal agriculture operations consist of many different gases as well as suspended particulates (dust or microbes). One of these gases, ammonia, is gaining greater attention for its role in odor, but also as a precursor of fine particulate matter (PM 2.5). PM 2.5 has implications in haze and visibility as well as human health.

The materials on this page were developed to be used by educators and professors who include this topic in their classrooms or educational programs.

Fact Sheet

Sharon L. P. Sakirkin, Texas AgriLife Research; N. Andy Cole and Richard W. Todd, USDA-Agricultural Research Service; Brent W. Auvermann, Texas AgriLife Extension Service, Texas AgriLife Research

Alternate download: Ammonia from Cattle Operations part 1 (Introduction) and part 2 (abatement) combined in a single document (17 pages; PDF format)

Videos

Reducing Ammonia Emissions from Cattle Feedyards (5 min)

Andy Cole, USDA ARS

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Mitigation of Nitrogen Excretion Through Dietary Manipulations

Mark Hanigan, Virginia Tech (14 minutes)

Note: the pixelation present at the start cleans up at the 2:00 minute mark

Presentation Slides

Archived Webinar

This webinar contains four individual video segments (ranging from 10 to 27 minutes) that discuss current and future mitigation options for reducing ammonia emissions from poultry litter. Presenters are: Eileen Wheeler, Pennsylvania State University; Hongwei Xin, Iowa State University; and Robert Burns, University of Tennessee. The archive also includes handouts and links to additional information. If you have difficulties please see our webcast troubleshooting page. If you need to download a copy of a segment, submit a request.

Acknowledgements

These materials were developed by the Air Quality Education in Animal Agriculture (AQEAA) project with with financial support from the National Research Initiative Competitive Grant 2007-55112-17856 from the USDA National Institute of Food and Agriculture.

For questions about the materials on this page contact Dr. Kevin Janni, University of Minnesota (kjanni@umn.edu). For questions about the AQEAA project, contact Dr. Rick Stowell, Unviersity of Nebraska (rstowell2@unl.edu).

If you have presentations, photos, video, publications, or other instructional materials that could be added to the curricula on this page, please contact Dr. Janni or Jill Heemstra (jheemstra@unl.edu).

Dust (Particulate Matter) Emissions From Animal Agriculture: An Introduction

Air emissions from animal animal feedlots are sources of many different emissions including particulate matter (dust).

The materials on this page were developed to assist educators and professors who wish to include dust and particulate emissions and their control as a topic in their classrooms or educational programs.

Fact Sheet

Sharon L. P. Sakirkin, Texas AgriLife Research; Ronaldo Maghirang, Kansas State University; Steve Amosson, Texas AgriLife Extension Service; Brent W. Auvermann, Texas AgriLife Extension Service and Texas AgriLife Research

Alternate download: Includes Dust Emissions Part 1 (Introduction) and Part 2 (Abatement) in a single document (12 pages; PDF format)

Video

Quantifying Particulate Matter (PM) Emissions

Russell McGee, Texas AgriLife Research (7 minutes)

Presentation Slides (Combined with a presentation on dust control)

If you need to download a copy of a segment, submit a request.

Acknowledgements

These materials were developed by the Air Quality Education in Animal Agriculture (AQEAA) project with with financial support from the National Research Initiative Competitive Grant 2007-55112-17856 from the USDA National Institute of Food and Agriculture.

For questions about the materials on this page contact Dr. Kevin Janni, University of Minnesota (kjanni@umn.edu). For questions about the AQEAA project, contact Dr. Rick Stowell, Unviersity of Nebraska (rstowell2@unl.edu).

If you have presentations, photos, video, publications, or other instructional materials that could be added to the curricula on this page, please contact Dr. Janni or Jill Heemstra (jheemstra@unl.edu).