This webinar examines the role of the environment in livestock disease risk and surveillance. Presentations will explore the association between manure handling activities and PRRSV outbreaks in wean-to-market swine, as well as the use of environmental sampling to better understand pathogen distribution on HPAIv-infected egg layer farms. Together, these studies highlight how environmental data can inform biosecurity practices, disease monitoring, and future research applications in livestock production systems. This presentation was originally broadcast on February 20, 2026. Continue reading “Pathogens Beyond the Animal: Environmental Drivers of Disease in Livestock Systems”
Mortality Management – From Routine to Catastrophic
This webinar will explore how mortality is part of livestock production, whether in the day-to-day on the farm or after a catastrophic disease or environmental disaster. Handling and disposal of mortality in a safe and efficient manner is critical for continuity of operations. In this webinar, the presenters will present on studies evaluating different techniques of mortality management and the lessons learned from each study This presentation was originally broadcast on October 10, 2025. Continue reading “Mortality Management – From Routine to Catastrophic”
Antibiotic Resistance and Agriculture: What Farmers, Processors, and Consumers Need to Know
Antimicrobial resistance (AMR) is a growing concern for the health and well-being of people around the world, and not just in hospitals, but on farms and in the food chain as well. Responsible antibiotic use in livestock and good manure management are critical to protecting animal health, public health, and the future effectiveness of our most important medicines.
From Waste to Worth; Creating an educational opportunity from a disaster
Purpose
North Dakota was impacted by the 2022 Highly Pathogenic Avian Influenza (HPAI) outbreak. Responders to the HPAI outbreak included the North Dakota Department of Agriculture, North Dakota Department of Environmental Quality, USDA Animal and Plant Health Inspection Service (APHIS), North Dakota State University (NDSU) Veterinary Diagnostic Laboratory, NDSU Extension, county emergency managers and veterinarians. Many responders were new employees and were not involved in response efforts during the 2015 HPAI outbreak, including 62% of county Extension agents. The lack of experience and knowledge resulted in a significant amount of time and effort spent determining the appropriate agencies to contact, defining agency roles, developing educational resources, and creating an awareness of biosecurity and procedures used in active cases. Additionally, limited attention was given to stress management or mental health and well-being during this period of heightened stress for personnel involved in response.
What Did We Do?
NDSU Extension received a 2023 USDA APHIS National Animal Disease Preparedness and Response Program grant to train professionals on how to safely respond to an animal disease outbreak or mass livestock mortalities. Training topics included:
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- An overview of animal diseases
- Continuity of business planning
- Personal protective equipment and decontamination
- Incident command systems, local response roles and impact assessment
- Humane endings
- Carcass disposal site selection and methods
- Stress management and responding to stressed people
- Effective communication in high stress situations
- A response simulation exercise.
The curriculum was developed over a 5-month period and was previewed by 25 attendees during the North Dakota Veterinary Medical Association’s Annual Winter Conference. A total of 11 attendees responded to a survey of which 100% agreed the training increased their confidence in responding to a foreign animal disease (FAD), while 91% indicated the materials presented were appropriate for those responding to an animal disease outbreak at the local level. All topic areas were rated as either moderately useful or very useful. Suggested improvements to the curriculum were made over the next 4 months until the first full training.
The one and a half day training events were held in person at the NDSU Carrington Research Extension Center (CREC) in June and September 2024. The training format included classroom, group work, demonstrations and hands-on activities. Each participant received a kit which contained personal protective equipment. A table-top exercise at the end of the training tied in all topics presented and provided time for groups to share experiences with response efforts.
Participants of the Emergency Response Preparedness for Foreign Animal Diseases and Mass Livestock Mortalities in North Dakota training viewed a non-disease mortality compost site. NDSU photo.
Emergency Response Preparedness for Foreign Animal Diseases and Mass Livestock Mortalities in North Dakota training participants practice donning PPE during hands-on portion of training. NDSU photo.
Participants of the Emergency Response Preparedness for Foreign Animal Diseases and Mass Livestock Mortalities in North Dakota training received Glo-Germ on their gloves as they exited the people movers to doff PPE. They rubbed it on their hands and then up and down their PPE. The Glo-Germ was used as a tool to aid in visual “contamination”. A black light was used after doffing was complete to spot any signs of “contamination”. NDSU photo. The NDSU Extension does not endorse commercial products or companies even though reference may be made to tradenames, trademarks or service names.
What Have We Learned?
In post-event evaluations of training participants, all respondents (57) indicated that the training increased their confidence and ability in responding to an animal disease or mass livestock mortality event. Additionally, 96% of respondents indicated they planned to make changes to be better prepared and better able to respond to animal diseases or mass livestock mortalities because of their participation in the training. Responses also indicated 93% improved their ability to provide support to individuals in high stress situations.
Post-training evaluation respondent comments included:
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- “One of the best trainings I’ve ever attended. Please make sure new ANR [agriculture and natural resources] agents attend this in the future.
- “This was a great training and appreciate all the work put into it! It was good to understand the chain of command and know that many other offices would be working with a producer in a situation involving a FAD.”
- “I appreciated the number of different professions represented at this meeting and their unique perspectives for this type of emergency response.”
- “It was a great learning experience. The information was very useful and will be put to use if an event occurs. We EM’s [emergency managers] don’t normally deal directly with the emotional responses but we are resources for finding avenues for emotional support, which is great to know that there are people to reach out to in the animal industry. Overall, it was great to network with others and have more tools in the toolbox for when the situation occurs. GREAT JOB to everyone involved!!”
Six-month follow-up evaluation data from the first training session indicated that 91% of respondents (12) felt their community is better prepared for and able to respond to an animal disease or mass livestock mortality. Of these respondents, 45% took action to be more prepared for an animal disease or mass livestock mortality. Additionally, the training was successful in building relationships between responders in the state with 55% collaborating with individuals they connected with at the training to better prepare their communities to respond to an animal disease or mass livestock mortality. The six-month follow-up evaluation for the second training session will be administered in March 2025 and these proceedings will be updated with the information.
As part of the six-month evaluation, respondents were asked if they had taken actions to prepare for an animal disease or mass livestock mortality. Comments to date included:
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- “Put together a list of resources, working on a response plan, informed stakeholders on the process and procedures involved.”
- “Monitoring of animal diseases in state and working with local producers and County Extension Agent.”
- “I have been more diligent about collecting names of producers or contacts needed if any outbreak would occur.”
Future Plans
Based on feedback from participants, an online discussion and a one-day table-top training are being planned. A follow-up one-hour online discussion session for all training participants will occur in February 2025. A day-long tabletop training is being planned for September 2025. This training will be for Extension agents and emergency managers. The goal of this training is to continue to increase preparedness and response capacity at the local level through the development of skills and relationships.
Authors
Presenting & corresponding author
Mary A. Keena, Extension Specialist, North Dakota State University, mary.keena@ndsu.edu
Additional authors
Miranda Meehan, Ph.D., Associate Professor, Livestock Environmental Stewardship Specialist and Disaster Education Coordinator, North Dakota State University; Carolyn Hammer, DVM, Ph.D., Professor, Associate Dean of College of Agriculture, Food Systems and Natural Resources, North Dakota State University; Heidi Pecoraro, DVM, Ph.D., DACVP, Director, Veterinary Diagnostic Laboratory, North Dakota State University; Sean Brotherson, Ph.D., Professor and Family Science Specialist, North Dakota State University; Ethan Andress, DVM, State Veterinarian, ND Department of Agriculture; Jodi Bruns, M. Ed., Leadership and Civic Engagement Specialist, North Dakota State University; Adriana Drusini, Extension Program Coordinator, Farm and Ranch Stress, North Dakota State University; Marty Haroldson, Program Manager, Division of Water Quality, ND Department of Environmental Quality; Angela Johnson, Farm and Ranch Safety Coordinator, North Dakota State University; Margo Kunz, DVM, Assistant State Veterinarian, ND Department of Agriculture; Julianne Racine, Extension Agent, Agriculture and Natural Resources, LaMoure County, North Dakota State University; Karl Rockeman, P.E., Director, Division of Water Quality, ND Department of Environmental Quality; Jan Stankiewicz, MS, MPH cert., Community Health and Nutrition Specialist & Tribal Liaison, North Dakota State University; Rachel Strommen, Environmental Scientist, ND Department of Environmental Quality; and Kent Theurer, Emergency Management Specialist, ND Department of Agriculture.
Additional Information
Twenty-one new Extension publications in either English or Spanish will be created from this project. Completed to-date include:
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- 4 Pasos sencillos para compostar ganado muerto
- Highly Pathogenic Avian Influenza (HPAI)
- African Swine Fever (ASF)
- Peste porcina africana (ASF)
- Ser agricultor o ganadero en tiempos difíciles
- Select Animal Disease Disinfectant Chart
- Cuadro de desinfectantes para enfermedades selectas de animales
- Select Animal Disease Personal Protective Equipment Chart
- Cuadro de equipo de protección personal para enfermedades selectas de animales
- Personal Protective Equipment (PPE) Donning and Doffing Guidelines for On-Site Animal Disease Outbreaks
- Instrucciones para colocarse y retirarse el equipo de protección personal (EPP) en caso de brotes de enfermedades animales
Acknowledgements
The USDA Animal and Plant Health Inspection Service National Animal Disease Preparedness and Response Program funded this project. Project ID: ND01.22.
Special thank you to our support staff members, Myrna Friedt, Linda Schuster, Stephanie Sculthorp-Skrei and Lynne Voglewede as well as the NDSU Agriculture Communications department for all of the time and effort you put into these trainings and materials.
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. 2025. Title of presentation. Waste to Worth. Boise, ID. April 7-11, 2025. URL of this page. Accessed on: today’s date.
Risk Mapping of Potential Groundwater Contamination from Swine Carcass Leachate Using HYDRUS-1D and GIS
Purpose
The on-farm disposal of swine carcasses poses a potential risk to groundwater quality due to the generation of leachate with nitrate compounds (Koh et al., 2019). This study aims to evaluate the vertical movement of nitrate nitrogen from leachate produced during decomposition of swine carcasses in Nebraska soil types by integrating HYDRUS-1D modeling with GIS-based spatial analysis.
What Did We Do?
Leachate from six on-farm mortality disposal units was gathered during a year-long field study. A soil column study was conducted using the leachate from the field study to evaluate contaminant fate and transport through two common Nebraska soil types – a sandy clay loam and a silty clay.
HYDRUS-1D Model Calibration and Simulation. The model was calibrated using laboratory soil column data; no field-scale observations were used for validation. The objective was to parameterize the model based on controlled experimental conditions and use these simulations to inform spatial risk assessments.
Soil Hydraulic and Solute Transport Parameters. The van Genuchten-Mualem model was chosen to define the soil hydraulic properties for the two soil types used in the columns study, sandy clay loam (SCL) and silty clay (SC). Ten simulations were conducted to develop the HYDRUS-1D model, each run for 365 days, using the mean monthly nitrogen (N lb/ac) generated in leachate during the field study, which was converted into NO₃-N units. The model simulated nitrate leaching in a 10-meter soil column profile using boundary conditions that replicated laboratory leachate transport where the upper boundary represents a constant flux boundary to simulate leachate application based on controlled experimental data and lower boundary represents a free drainage condition representing natural percolation.
Model Calibration. Calibration was performed using inverse modeling within HYDRUS-1D, adjusting key parameters to minimize the sum of squared errors (SSQ) between observed and simulated nitrate concentrations in soil columns at 5 cm, 15 cm, and 25 cm. The results may not fully represent field-scale variability since the model was calibrated only using laboratory data. However, the controlled conditions ensured that parameterization was optimized for subsequent spatial risk assessment using GIS. The sandy clay loam soil strongly correlated with observed and simulated values (R²=0.99). The silty clay soil had a slightly lower R² (0.86). Identical RMSEs of 3.15 for both soil types suggest similar levels of overall deviation from observed concentrations.
The model outputs were exported as time-series CSV data and georeferenced to the study area using ArcGIS Pro. Statewide soil texture data were obtained from the USDA-NRCS soil texture class map (Knoben, 2021) and depth were derived from interpolated data using the Kriging method, based on historical water levels from the UNL Groundwater and Geology Portal (CSD, 2025) respectively. Soil type, groundwater depths, and digital elevation models (DEM) were imported into ArcGIS Pro and processed under the NAD 1983 UTM Zone 14N coordinate system to ensure spatial alignment.
Hydraulic parameters for the ten soil textural classes in Nebraska were defined by the ROSETTA model in HYDRUS-1D and used to model nitrate transport and concentration at 2m soil depth at 1,000 randomly defined locations statewide. Nitrate concentration data at 2 m of soil depth was interpolated using the Kriging tool to create a continuous nitrate concentration data layer. Soil type and groundwater depth data were converted into raster format to enhance the spatial analysis, and a vulnerability assessment was performed using a classification system based on soil permeability, groundwater depth, and nitrate concentrations to produce a spatial representation of groundwater contamination vulnerability (Figure 1).


Swine population inventories (Figure 2) were obtained from the 2022 USDA Census of Agriculture (IARN, 2025), allowing for comparison of county-level swine populations to groundwater contamination vulnerability.
What Have We Learned?
The HYDRUS-1D model successfully modeled nitrate movement in the soil profile, producing time-series data that matched expected trends based on soil properties and environmental conditions. Counties with the greatest groundwater contamination risk are predominantly located in the western and northern regions of the state due to well-drained soils and shallow depths of groundwater. Very few swine operations are located in these moderate- to high- risk zones, but those that are located in these zones should be aware of the potential for groundwater contamination and should utilize mortality disposal methods that minimize leachate production. Four counties in northeast Nebraska contain moderate swine populations and have moderate to high risks for groundwater contamination. Castro and Schmidt (2023) found that carcass disposal via shallow burial with carbon (SBC) yielded much less leachate – and, subsequently, much lower loads of contaminants to the soil environment – than composting of whole or ground swine carcasses, suggesting that SBC may be a more environmentally conscious disposal method in these counties. Counties having low vulnerability to groundwater contamination cover much of the state’s central and eastern portions where the majority of swine production is located. This study provides critical insights into the risks of groundwater contamination from on-farm swine carcass disposal in Nebraska. Guidance for on-farm disposal of mortalities by all livestock producers should focus on selecting disposal methods that minimize leachate production and contaminant transport potential.
Future Plans:
Outreach efforts will focus on promoting mortality disposal BMPs with a primary focus on selecting disposal methods that minimize leachate production. Field research will be expanded to include evaluation of multiple carbon sources used for on-farm carcass disposal to reduce leachate generation. Future research will focus on enhancing the predictive accuracy of the HYDRUS-1D model by incorporating field-scale validation using observed nitrate concentrations from groundwater monitoring wells in high-risk areas. This validation will improve the reliability of the model’s output and support more precise risk assessments.
Authors:
Presenting Author
Gustavo Castro Garcia, Graduate Extension & Research Assistant, Department of Biological Systems Engineering, University of Nebraska-Lincoln
Corresponding Author
Amy Millmier Schmidt, Professor, Department of Biological Systems Engineering and Department of Animal Science, University of Nebraska-Lincoln, aschmidt@unl.edu
Additional Authors
Mara Zelt, Research Technologist, University of Nebraska-Lincoln
Aaron Daigh, Associate Professor, Department of Biological Systems Engineering and Department of Agronomy & Horticulture, University of Nebraska-Lincoln
Benny Mote, Associate Professor, Department of Animal Science, University of Nebraska-Lincoln
Carolina Córdova, Assistant Professor, Department of Agronomy & Horticulture, University of Nebraska-Lincoln
Acknowledgments
This project was supported by the National Pork Board Award #22-073. The authors wish to recognize Jillian Bailey, Logan Hafer, Alexis Samson, Nafisa Lubna, Andrew Ortiz, and Maria Oviedo Ventura, for their technical assistance during the field and column studies that provided input data for this modeling effort.
Additional Information
Castro, G., and Schmidt, A. (2023). Evaluation of swine carcass disposal through composting and shallow burial with carbon (poster presentation). ASABE AIM. Omaha, NE. July 9 – 12, 2003.
CSD. (2025). UNL Ground Water and Geology Portal: CSD Ground Water and Geology Data Portal. University of Nebraska-Lincoln. Retrieved from: CSD Ground Water and Geology Data Portal.
IANR. (2025). Hogs and pigs, operations with inventory, total operations by county. Nebraska Map Room. Data source: Census of Agriculture, 2022. Retrieved from: https://cares.page.link/Xu1J.
Knoben, W. J. M. (2021). Global USDA-NRCS soil texture class map, HydroShare, https://doi.org/10.4211/hs.1361509511e44adfba814f6950c6e742.
Koh, EH., Kaown, D., Kim, HJ., Lee, KK., Kim, H., and Park, S. (2019). Nationwide groundwater monitoring around infectious-disease-caused livestock mortality burials in Korea: superimposed influence of animal leachate on pre-existing anthropogenic pollution. Environ Int 129:376–388.
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. 2025. Title of presentation. Waste to Worth. Boise, ID. April 7-11, 2025. URL of this page. Accessed on: today’s date.
Community Engagement to Mitigate Transmission of Infectious Diseases and Antibiotic Resistance from Backyard Poultry
Purpose
Backyard poultry production is growing globally with 85 million backyard chickens estimated in the U.S. (Mace & Knight, 2024). Whether kept as pets or to provide a local and sustainable food source, flocks can harbor pathogens and antibiotic-resistant bacteria that can be transmitted to humans via the environment, pests, food products, and direct contact. Poultry waste can contaminate soil and water sources, posing risks to nearby humans and other animals. Flocks can attract pests that may carry diseases and disrupt local ecosystems. This project, which will launch in the summer of 2025, aims to improve understanding among backyard poultry farmers of potential health, environmental, community, and food safety risks associated with their systems and motivate the adoption and promotion of behaviors critical to public health and sustainability of local food systems using a peer-to-peer outreach approach.
This project will evaluate an approach to motivating behavioral changes among a cohort of backyard poultry farmers that is predicated on evaluating current flock management practices among participants, improving understanding of health risks associated with current practices, and motivating implementation of recommended practices to mitigate health risks. Beneficiaries of project outcomes include members of households in which chickens are maintained, local community members, consumers of local poultry products, and the broader population that shares environmental resources with these sites and are impacted by human health threats. Our project will uniquely address multiple facets of backyard poultry production that contribute to human health, environmental sustainability, food safety, and community well-being through engagement with existing poultry owners to improve knowledge, promote the adoption of best practices, and facilitate communication networks. Assessments of current production practices among participating local backyard poultry farmers will inform educational needs related to managing these systems for environmental and public health benefits. Facilitated engagement among participants during educational events will promote shared goals, motivate practice adoption, and build confidence among participants in their role as citizen scientists capable of promoting a broader community understanding of the topics addressed.
What Did We Do?
The overall goal of this project is to mitigate potential disease transmission risks to humans from small poultry flocks by delivering data-informed educational programming and assessing subsequent behavioral changes among audience members. After a thorough investigation using previous studies conducted on the impact of community engagement in health education, we have designed our research to identify, deliver, and assess an effective methodology to achieve the following objectives.
Objective 1: Evaluate the knowledge, perceptions, and practices among backyard poultry farmers that may contribute to their risks for acquiring AMR genes/infections from their birds using a Reasoned Action Approach.

Objective 2: Quantify the contribution of backyard poultry manure and bird management practices to the presence and concentration of pathogenic organisms and resistance genes in the environment via sampling and analysis of manure, soils, runoff, and flying insects.
Objective 3: Develop, deliver, and assess impacts of educational programming designed to motivate the adoption of new integrated antimicrobial management approaches in backyard poultry farming to reduce the potential spread of AMR.
Thirty backyard poultry farmers from up to three counties in Nebraska will be recruited through community groups, personal connections, and university extension contacts. Participants will be surveyed and observed to understand their current knowledge, perceptions, and management practices, and identify knowledge gaps related to bird health, biosecurity, and disease transmission risks. The Reasoned Action Approach, a social cognitive model for behavioral analysis will be used to categorize the data, predicting and explaining their behavior towards healthy farming practices. The mixed-methods study will use standard statistical methods and qualitative data for a richer interpretation.
Sampling of environmental matrices and potential insect transmission vectors will be conducted and used to complete a risk factor assessment to understand disease demography.
Through face-to-face and digital sessions, engagement and education sessions will be designed to address knowledge gaps in poultry handling, waste management, personal hygiene, water quality, food safety, and human health risks. It will promote best practices and encourage participation through rewards, project-based learning, on-farm demonstrations, and regular reflection on personal impact. The recruited farmers will be appointed as trainers for other farmers in their locality to continue to promote the learning outcomes from the training. The training sessions will be assessed through a post-training survey using a knowledge-based questionnaire, and all discussions with farmers will be recorded for future evaluation. This data will help determine improvements for future outreach events on infectious disease control in backyard poultry farms, enhancing the training’s impact.
What Have We Learned?
The number of households engaging in “backyard poultry production” is growing regionally, nationally, and globally. Evidence also suggests that chickens are not strictly confined to the outdoors but are becoming indoor “pets,” creating complex human-chicken relationships responsible for zoonotic disease outbreaks and antibiotic resistance risks (Singh et al., 2018; Tobin et al., 2015). According to a 2010 study, the USDA confirmed almost 50% of the population related to backyard poultry production lacks knowledge about human health risks associated with contact with live birds (USDA, 2011). Studies reflect a critical need for decision-making support to ensure healthy birds, applying biosecurity practices that mitigate animal-to-human disease transmission risks and development of antibiotic-resistant bacteria, promoting environmental sustainability, and providing healthy local food sources to communities. While these systems represent only a small part of the U.S. poultry industry, their positive impact on local food systems is widely recognized, as are their potential contributions to zoonotic disease transmission, antibiotic resistance, and local ecosystem disruptions. Public awareness about poultry-associated health risks and adopting best practices for biosecurity and disease prevention is critical to balancing healthy local food production with community well-being.
Future Plans
This project aims to improve the health, prosperity, and sustainability of backyard poultry farmers by focusing on zoonotic disease transmission, pest management, and natural resource protection. It will provide training, technical assistance, and peer support to improve knowledge and adoption of best practices for producing healthy local food sources. This will reduce health risks, decrease healthcare costs, and support market access and profitability among urban farmers. The community-based approach will foster mutually beneficial relationships among producers, communities, and experts, promoting sustainable production practices that prioritize health, community needs, and the environment.
Authors
Presenting author
Nafisa Lubna, Graduate Student, University of Nebraska-Lincoln
Corresponding author
Amy Schmidt, Professor, University of Nebraska-Lincoln, aschmidt@unl.edu
Additional author
Mark E. Burbach, Environmental Social Scientist, University of Nebraska-Lincoln
Additional Information
Mace, J. L., & Knight, A. (2024). From the backyard to our beds: The spectrum of care, attitudes, relationship types, and welfare in non-commercial chicken care. Animals, 14(2), 288.
Peters, G. J., & Crutzen, R. (2021). The core of behavior change: introducing the Acyclic Behavior Change Diagram to report and analyze interventions.
Singh, S., Chakraborty, D., Altaf, S., Taggar, R. K., Kumar, N., & Kumar, D. (2018). Backyard poultry system: A boon to rural livelihood. International Journal of Fauna and Biological Studies, 5(1), 231-236.
Tobin, M. R., Goldshear, J. L., Price, L. B., Graham, J. P., & Leibler, J. H. (2015). A framework to reduce infectious disease risk from urban poultry in the United States. Public Health Reports, 130(4), 380-391.
USDA. (2011). Reference of the health and management of chicken flocks in urban settings in four U.S. cities, 2010. Fort Collins, CO: USDA.
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. 2025. Title of presentation. Waste to Worth. Boise, ID. April 7–11, 2025. URL of this page. Accessed on: today’s date.
Evaluation of the aerosol transmission of the porcine reproductive and respiratory (PRRS) virus from swine production systems
Purpose
Porcine reproductive and respiratory syndrome virus (PRRSV) is a major concern to the U.S. swine industry due to the severe economic loss it can cause. Its symptoms include severe flu-like symptoms, respiratory distress, fever, and premature abortions in pregnant sows. The virus is spread during close contact between pigs or exposure to contaminated urine, semen, feces, and nasal and mammary secretions (1). Control measures have proven exceedingly costly with PRRSV which causes an estimated $1 billion in lost production in the U.S. pork industry per year (3), an 80% increase from a decade earlier (2)(4). With very few, truly effective methods available to control PRRSV after the start of an outbreak, developing methods to mitigate the dispersion of the virus has become a major priority.
Common biosecurity measures for swine operations (e.g., controlled access, personal hygiene, animal management, pest control, and production area cleaning and disinfection) have proved insufficient to stop PRRSV transmission. Producers are, therefore, seeking to understand the potential risks posed by more novel transport methods. Observations of new PRRSV cases emerging during manure handling activities have raised questions about aerosolized manure as a potential transmission vector. This study was conducted to test this possibility in the following stages:
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- Verify the presence of viable virus sample within pit manure, lagoon samples, or dust coming from barns with active PRRSv outbreaks.
- Develop a reliable method for collecting and preserving viable airborne viral samples.
- Assess the aerosol transmission “footprint” of PRRSV originating from positive swine farms to improve understanding of potential farm-to-farm disease transmission risks.
What Did We Do?
Novel air sampling devices were constructed by the project team (Figure 1) to be deployed inside and outside swine production units to accumulate samples of particulates and aerosols. The devices accommodate a commercially available Air Prep filter cartridge (innovaprep.com) to capture particulates pulled across the filter by a fan housed within the sampling unit.


Our project team worked closely with the lead veterinarian at a large swine integrator in Nebraska to access farms within 5 to 7 d of pigs being confirmed PRRSV-positive. Sampling events 1 and 2 focused on evaluating PRRSV presence on indoor surfaces, fresh and stored manure, flies, and maggots. Sampling events 3 through 5 focused on evaluating PRRSV presence in air downwind of PRRSV-positive swine production areas or downwind of land application of manure from PRRSV-positive animals.
Sampling Event 1. A swine breeding operation was identified where animals were currently testing positive for and showing clinical signs of PRRSV infection. At this site, two production areas were selected at random for sampling. Surface swabs were collected from floors, fan louvers, and pen dividers. Fresh fecal samples were collected from sows in the same production areas, and an air sampler was placed on the floor in each room and allowed to operate for two hours before retrieving the filters. For surface samples, sterile swabs were swept over each surface type and then placed into phosphate buffered saline (PBS) elution buffer. Fresh fecal samples were collected using a sterile spatula and placed into clean sample containers. Upon retrieving filters from air samplers, a sterilized knife was used to separate the filter from the plastic casing in which it was mounted, and sterile forceps were used to transfer the filter into a PBS elution tube. All samples were transported on ice to the University of Nebraska-Lincoln (UNL) Schmidt Lab and then submitted to the Iowa State University Veterinary Diagnostic Laboratory for analysis by polymerase chain reaction (PCR).
Sampling Event 2. A swine finisher unit was identified where animals were currently testing positive for and showing clinical signs of PRRSV infection. At this site, two production areas were selected at random for sampling inside the building. Surface swabs were collected from floors, fan louvers, feeders, and pen dividers. An air sampler was placed on the floor in each room and allowed to operate for four hours before retrieving the filters. Additional air samplers were mounted outside the building. For one production area, three samplers were mounted at a height aligning with the center of a minimum ventilation fan and spaced at 5, 12, and 19 feet from the rim of the fan hood. For a second production area, two samplers were mounted at a height aligning with the center of a minimum ventilation fan and spaced at 5 and 13 feet from the rim of the fan hood. These samplers were allowed to run for three hours before filters were retrieved. For surface samples, sterile swabs were swept over each surface type and then placed into PBS elution buffer. Manure samples from two deep pit storage sections of the building were collected using a plastic pole and dipper cup and placed into clean plastic bottles. Maggots observed in one pump out port were collected by hand and placed into PBS elution buffer. Upon retrieving filters from air samplers, a sterilized knife was used to separate the filter from the plastic casing in which it was mounted, and sterile forceps were used to transfer the filter into a PBS elution tube. Flies present around the production buildings were also collected at this site. For one sample, approximately six flies were captured and placed directly into PBS elution buffer. For a second sample, approximately six flies were captured, placed into 70% EtOH for 10 s, and then transferred from the ethanol to PBS elution buffer. All samples were transported on ice to the UNL Schmidt Lab and then submitted to the Iowa State University Veterinary Diagnostic Laboratory for analysis by PCR.
Sampling Event 3. A naturally-ventilated PRRSV-positive swine farm was identified. Air samplers mounted on t-posts were deployed in an array at a height above the ground of roughly 6 ft at varying distances (10 yards to 1 mile) from the buildings after using smoke candles to confirm wind direction and dispersion. Sampling was conducted for approximately 2.5 hours on a day with 40-55°F temperature,10-20 mph winds, and full cloud cover (Figure 2).
Sampling Event 4. At a mechanically-ventilated PRRSV-positive swine farm, sampling was conducted using the same process as for Event 3 for approximately 21.25 hours starting on a day with 85-105°F temperature, 4-10 mph winds, and full sun exposure, then continuing overnight.
Sampling Event 5. Using the previously described process, sampling was conducted for approximately 2.5 hours on a day with 70-95°F temperature, 2-10 mph winds, and partly cloudy conditions downwind of a field where lagoon effluent from PRRSV-positive pigs was being applied via center pivot.

All samples were submitted to the Iowa State Veterinary Diagnostic Lab for RT-qPCR analysis to identify PRRS viral genomic material.
What Have We Learned?
Results of PCR analyses for sampling event 1 (Table 1) revealed that, in barns where swine oral fluid samples were positive for PRRSv, all surface samples collected were also positive or suspected positive for PRRSv. The same was true for all of the surface and air samples collected inside the barn and for the air samples located up to 19 ft minimum from the building ventilation fans during sampling event 2 (Table 2). Maggots taken from the manure pit during sampling event 2, along with sterilized and unsterilized flies, tested positive for PRRSV, as well. Conversely, all manure samples obtained during sampling event 2 tested negative using the methodologies employed. This outcome does not dismiss manure as a possible transmission source; rather, it underscores the need for ongoing research to develop a reliable detection method for PRRS within such a complex matrix.
The team has not yet recovered air samples testing positive for PRRSV from any of the exterior arrays in sampling events 3-5 (Table 3). This could be due to ambient air conditions during the tests which may have caused rapid destruction of the virus or dilution of the virus below detectable concentrations. The rolling terrain surrounding facilities where arrays of samplers were posted downwind of buildings or the land application site may have created turbulent air movement that diluted samples such that concentrations of PRRSV genomic material capture on filters were too low to produce a positive result by PCR.
Table 1. Cycle Threshold (Ct) values for sampling event 1
| Sample Description | Ct (Result) |
| Pen Floor, Room 17 | 37.5 (Suspect) |
| Fan Louver, Room 17 | 30.1 (Positive) |
| Feeder, Room 17 | 31.6 (Positive) |
| Air Filter, Room 17 | 31.2 (Positive) |
| Pen Floor, Room 18 | 31.5 (Positive) |
| Fan Louver, Room 18 | 31.4 (Positive) |
| Feeder, Room 18 | 37.6 (Suspect) |
| Air Filter, Room 18 | 30.5 (Positive) |
| Fecal Sample 1 | ³40 (Negative) |
| Fecal Sample 2 | ³40 (Negative) |
Cycle threshold (Ct) indicates the number of PCR cycles required for the sample fluorescence to reach a predefined threshold for identification (<38 = positive, ~38-40 = suspect, ≥40 = negative). Lower Ct values correspond to higher viral RNA concentration.
Table 2. Cycle Threshold (Ct) values for sampling event 2
| Sample Description | Ct (Result) |
| Exhaust Air, Room 5, 5 ft from fan | 33.1 (Positive) |
| Exhaust Air, Room 5, 12 ft. from fan | 34.1 (Positive) |
| Exhaust Air, Room 5, 19 ft. from fan | 38.1 (Suspect) |
| Indoor Air, Room 5, Rep 1 | 30.9 (Positive) |
| Indoor Air Room 5, Rep 2 | 33.3 (Positive) |
| Exhaust Air, Room 6, 5 ft from fan | 32.6 (Positive) |
| Exhaust Air, Room 6, 13 ft. from fan | 32.4 (Positive) |
| Flies | 37.0 (Suspect) |
| Flies Sterilized in Ethanol | 36.3 (Positive) |
| Maggots | 39.9 (Suspect) |
| Floor, Room 5, Rep 1 | 32.4 (Positive) |
| Floor, Room 5, Rep 2 | 32.3 (Positive) |
| Louvers, Room 5, Rep 1 | 33.1 (Positive) |
| Louvers, Room 5, Rep 2 | 32.1 (Positive) |
| Pens, Room 5, Rep 1 | 37.9 (Positive) |
| Pens, Room 5, Rep 2 | 35.8 (Positive) |
| Feeder, Room 5, Rep 1 | 35.8 (Positive) |
| Feeder, Room 5, Rep 2 | 37.5 (Suspect) |
| Pens, Room 4, Rep 1 | 35.6 (Positive) |
| Pens, Room 4, Rep 2 | 35.3 (Positive) |
| Floor, Room 4, Rep 1 | 31.4 (Positive) |
| Floor, Room 4, Rep 2 | 32.9 (Positive) |
| Louvers, Room 4, Rep 1 | 33.0 (Positive) |
| Louvers, Room 4, Rep 2 | 32.1 (Positive) |
Cycle threshold (Ct) indicates the number of PCR cycles required for the sample fluorescence to reach a predefined threshold for identification (<38 = positive, ~38-40 = suspect, ≥40 = negative). Lower Ct values correspond to higher viral RNA concentration.
Table 3. Cycle Threshold (Ct) values for sampling events 3 through 5
| Sampling Event | Sample Description | Ct (Result) |
| Event 3 | Air Filters (n=2) | ³40 (Negative) |
| Event 4 | Air Filters (n=4) | ³40 (Negative) |
| Fans (n=4) | ³40 (Negative) | |
| Oral Fluids, Room 15 | 34.0 (Positive) | |
| Oral Fluids, Room 16 | 36.1 (Positive) | |
| Oral Fluids, Room 17 | 38.0 (Suspect) | |
| Oral Fluids, Room 18 | 34.7 (Positive | |
| Event 5 | Air Filters (n=4) | ³40 (Negative) |
Cycle threshold (Ct) indicates the number of PCR cycles required for the sample fluorescence to reach a predefined threshold for identification (<38 = positive, ~38-40 = suspect, ≥40 = negative). Lower Ct values correspond to higher viral RNA concentration.
Future Plans
It is essential to identify which ambient weather conditions, if any, are favorable for air dispersion of infective PRRSv and which conditions will significantly limit dispersion. As research continues, the suspected ideal conditions for sampling downwind of mechanically ventilated PRRSv-positive barns or irrigation systems applying lagoon effluent from PRRSv-positive pigs will be 0 to 50°F with low to moderate wind speed and full cloud cover. At least 24 hours of continuous sampling is also expected to produce greater opportunity for positive air samples.
The continued inability to isolate the virus from manure samples is curious, given the universally positive samples we identified from the positive barns. However, the PRRSV is believed to require as few as 10 viral particles to be transmitted. Given the potentially very low concentration of viral material in manure, and the significant PCR inhibitors present in complex organic samples, the team continues to explore new sample preparation and testing methods for this matrix.
Lastly, further investigation into the potential roles of flies and maggots is warranted, particularly with the discovery of sufficient PRRSV genomic material in the gut of surface sterilized flies to yield a positive PRRSV result via RT-qPCR.
Authors
Presenting author
Logan Hafer, Undergraduate Research Assistant, Department of Biological Systems Engineering, University of Nebraska-Lincoln
Corresponding author
Dr. Amy Millmier Schmidt, Professor, Department of Biological Systems Engineering and Department of Animal Science, University of Nebraska-Lincoln, aschmidt@unl.edu
Additional author(s)
Dr. Benny Mote, Associate Professor, Department of Animal Science, University of Nebraska-Lincoln
Dr. Hiep Vu, Associate Professor, Department of Animal Science, University of Nebraska-Lincoln
Additional Information
-
- Porcine Reproductive and Respiratory Syndrome virus (PRRSV). Iowa State University – College of Veterinary Medicine; 2024 [accessed 2024 November 22]. https://vetmed.iastate.edu/vdpam/FSVD/swine/index-diseases/porcine-reproductive.
- Butler, J. E., Lager, K. M., Golde, W., Faaberg, K. S., Sinkora, M., Loving, C., & Zhang, Y. I. 2014. Porcine reproductive and respiratory syndrome (PRRS): an immune dysregulatory pandemic. Immunologic research, 59, 81-108. https://link.springer.com/article/10.1007/s12026-014-8549-5.
- Dee, S., T. Clement, and E. Nelson. 2023. Transmission of porcine reproductive and respiratory syndrome virus in domestic pigs via oral ingestion of feed material. J of the Am Vet Med Assoc, 262(1). https://doi.org/10.2460/javma.23.08.0447
- Osemeke, O.H., T. Donovan, K. Dion, D.J. Holtkamp and D.C.L. Linhares. 2021. Characterization of changes in productivity parameters as breeding herds transitioned through the 2021 PRRSV Breeding Herd Classification System. J Swine Health Prod. 2022;30(3):145-148. https://doi.org/10.54846/jshap/1269
Acknowledgements
Funding for this research was provided by the Nebraska Pork Producers Association under award #22-063 and an Undergraduate Student Research Program award from the UNL Institute of Agriculture and Natural Resources, Agricultural Research Division.
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. 2025. Title of presentation. Waste to Worth. Boise, ID. April 7–11, 2025. URL of this page. Accessed on: today’s date.
Impacts on Soil Properties, E. Coli Prevalence, and Soybean Yield from Surface-Applied Swine Mortality Compost During a Single Growing Season in Eastern Nebraska
Purpose
Livestock producers dealing with animal mortalities may opt for composting as a biosecure on-farm carcass disposal method. The composting process accelerates the decomposition of animal remains, stabilizes nutrients, and, when executed correctly, subjects the carcasses to elevated temperatures capable of eliminating pathogens. Nevertheless, the use of compost derived from animal mortalities may introduce potentially harmful nutrients, heavy metals, pharmaceuticals, or pathogens to cropland when applied as a soil amendment (Sims and Kleinman, 2005).
At the same time, mortality compost represents a potential soil health amendment due to its high carbon content. With carbon being an important building block for organic matter in the soil, the soil will have improved structure and water-holding capacity if carbon content is elevated. There will also be increased microbial activity adding to the soil’s microbial diversity and nutrients present.
This study aimed to confirm these findings and to determine the balance of positive and negative impacts of mortality compost application in Eastern Nebraska by exploring key biological and chemical risk factors in soil receiving swine mortality compost over the course of one growing season.
What Did We Do?
This experiment was conducted at the University of Nebraska Rogers Memorial Farm, located 11 miles east of Lincoln, Nebraska. The study site was comprised of silty clay loam soil that had been cropped using a long-term no-till management system with controlled wheel traffic. Background soil and compost chemical results are portrayed in Table 1. Corn was grown during the previous season, and soybeans were grown during the period of this study. Eight plots (15’ x 15’) were established and randomly assigned to either a 20-ton/ac application of swine mortality compost or no application (control). The compost, made with swine mortalies and a bulking agent of wood chips, was applied to the surface one week after planting.
In-season sampling. Two weeks following treatment application, and every two weeks during the growing season thereafter, soil from each plot was collected from the top 0-4” of the soil profile by random core sampling using a 2 in diameter hand probe. A roughly 200 g composite sample of soil from each plot was used for subsequent analysis. Soil temperature was also recorded for each plot on sampling days at two random locations to depths of 2” and 4” at each location using a hand temperature probe.
Soil samples were assessed in the UNL Schmidt Laboratory in the Department of Biological Systems Engineering for moisture content by drying soil for 48 hours at 221°F, and for the mean weight diameter of wet-stable aggregates by wet-sieving for 10 min at a rate of 30 vertical oscillations per minute. Several biological properties of the soil were also examined, including E.coli prevalence, determined by the proportion of positive samples following enrichment of eight 1-g subsamples of soil in LB broth (Miller) for 8 h at 98.6°F followed by culturing on ChromAgar E.coli selective media for 24 h at 98.6°F. Microbial respiration was measured for two 20-g samples of air-dried soil per plot placed into a 33.8 fl oz glass jar containing a 0.5 fl oz vial of 0.5 M potassium hydroxide (KOH). The soil was re-wet with 0.24 fl oz of deionized water before jars were sealed and incubated at 77°F for 4 days, and the mass of CO2 released during the incubation was determined using the difference in electrical conductivity in the trap material. Finally, metabolic functional diversity was observed for the soil microbial populations by determining the oxidation rates of 31 different carbon substrates using Biolog® EcoPlates following a 48-hour incubation at 77°F of a 10-4 dilution of a 3 g soil sample. Soil microbes in the EcoPlate wells cause oxidation of the carbon species in the plates and results in a color change, which is measured by a microplate reader at 590 and 750 optical density (OD) units. The overall average color intensity, a measure of general population size and activity, as well as the proportional activity by metabolic type (amino acids, carbohydrates, carboxylic acids, polymers, and amines/amines), were considered as ecological soil health indicators in this study.
Harvest and post-harvest sampling. Grain yields were determined by hand harvesting a row length equal to 1/1000 ac from each plot. Soybeans were dried and weighed, and yield values were then converted to bu/ac using a standard 15% moisture content for the soybeans.
Following harvest, soil from each plot was retrieved according to the previously detailed methodology and sent to a commercial laboratory to determine end-of-season values for pH, sum of cations, soluble salts, calcium, organic matter (%), nitrate-N, phosphate (P2O5), potassium (K2O), sulfate, sodium, magnesium, zinc, iron, copper, manganese and heavy metals (arsenic, lead, and chromium) in the top 0-4” of the soil profile. Bulk density was also determined for two locations per plot at depths of 0-2″ and 2-4″.
Table 1. Initial chemical characteristics of compost and soil
| Chemical | Compost | Soil |
| pH | 7.1 | 6.6 |
| Soluble salts (mmho/cm) | 11.4 | 0.13 |
| Zinc, ppm | 57.6 | 1.12 |
| Iron, ppm | 1477 | 44.8 |
| Copper, ppm | 13.4 | 0.73 |
| Manganese, ppm | 100.6 | 9.2 |
| Arsenic, ppm | 1.807 | 5.971 |
| Lead, ppm | 2.09 | 14.46 |
| Chromium, ppm | 7.48 | 35.85 |
What Have We Learned?
The application of the compost treatment significantly increased the prevalence of E. coli in the soil samples, but only early (4 weeks) in the growing season (Figure 1). This is likely influenced by the compost’s organic matter and microbial diversity, which serve as a carbon source and support microbial population growth. However, as the season progressed, the difference in the prevalence of E.coli in soil that had or had not received compost application narrowed, potentially due to other factors impacting microbial survivability (such as temperature or moisture content) becoming dominant factors. Regression analysis comparing E.coli prevalence to soil moisture and temperature did not show a strong relationship (R-squared values of 0.48 and 0.18, respectively), which indicates that the microbial population is being impacted by other, more complex factors not included in this analysis.
No other soil biology, chemistry, or physical properties that we tested proved to be significantly impacted (a ≥ 0.05) by the application of mortality compost to the soil, nor was the soybean grain yield. This indicates that while the soil health impacts of this single-season compost application were negligible, there is also little risk to water quality associated with the application of 20 ton/ac swine mortality compost in crop production areas that are well-managed with soil conservation best practices.

Symbols next to values in week 4 denote a significant difference in the proportion of E.coli-positive samples. Error bars represent SEM (n=4).
Future Plans
The results suggest that there is little risk of prolonged elevated E. coli prevalence in soil when using swine mortality compost in row crop production areas. However, precipitation producing runoff may pose a risk to nearby surface water bodies if experienced within six weeks of compost application. Future research would be required to fully understand the risk of this occurring, but previous research conducted at the same farm determined that a 12.2 m (40 ft) setback of bare soil was sufficient to prevent most chemical and biological pollutants from leaving a field via runoff after receiving surface application of manure (Gilley et al., 2017). This is an encouraging and valuable guideline for producers who are generating compost as part of their operation and must find suitable sites for application.
The negligible soil health improvements from mortality compost application during this single-season study could dissuade crop producers from seeking out this material if it were available in their vicinity. However, where organic matter is needed to improve soil health over time, this product should not be discounted as a valuable soil carbon amendment. While we did not observe any positive soil health impacts from a single 20 ton/ac application of compost in this study, other studies have seen single season effects. Several other studies found significant impacts of applying a single season of organic amendment on soil microbial biomass (Lazcano, et al., 2012; Leytem, et al., 2024; Crecchio, et al., 2001) and on C:N ratio, which were not tested in this study. Thus, future research could explore alternative rates of application, frequency of sampling, or testing methodologies.
Another possible explanation for the lack of significant soil health impacts was that the field used in this study has been under long-term conservation (20+ years of no-till) practices. As a result, we suspect that the soil health improvement gap (e.g., the difference between soil health status and potential soil health status under ideal management) may be quite minimal. Soil sampled from our plots prior to treatment application revealed an average organic matter (OM) concentration of 3.8%, which exceeds the average 2 to 3% OM concentration for this soil type (Magdoff et al, 2021). However, other soil health factors such as bulk density, microbial population richness, and organic nutrient availability were in line with reports for similar soil types (Oregon State University Extension Service., 2019; Chau et al., 2011; University of Florida., 2015). This likely indicates that future applications of this sort should avoid fields with elevated soil organic matter, as they will not greatly benefit from the addition of organic amendments where soil carbon is already sufficient to the needs of the soil ecosystem.
Authors
Presenting author
Jillian Bailey; Undergraduate Researcher; Department of Biological Systems Engineering; University of Nebraska-Lincoln
Corresponding author
Amy Schmidt, Professor, Department of Biological Systems Engineering, University of Nebraska-Lincoln, aschmidt@unl.edu
Additional author
Mara Zelt, Research Technologist, Department of Biological Systems Engineering, University of Nebraska-Lincoln
Additional Information
Castro, G., Schmidt, A. (2023). Evaluation of Swine Cadaver Disposal through Composting and Shallow Burial with Carbon (poster presentation). ASABE AIM. Omaha, NE. https://publuu.com/flip-book/818714/1802503
Crecchio, C., Curci, M., Mininni, R., Ricciuti, P., & Ruggiero, P. (2001). Short-term effects of municipal solid waste compost amendments on soil carbon and nitrogen content, some enzyme activities and genetic diversity. Biology and Fertility of Soils, 34(5), 311–318. https://doi.org/10.1007/s003740100413
Gilley, J. E., Bartelt-Hunt, S. L., Eskridge, K. M., Li, X., Schmidt, A. M., & Snow, D. D. (2017). Setback distance requirements for removal of swine slurry constituents in runoff. Transactions of the ASABE, 60(6), 1885–1894. https://doi.org/10.13031/trans.12310
Lazcano, C., Gómez-Brandón, M., Revilla, P., & Domínguez, J. (2012). Short-term effects of organic and inorganic fertilizers on soil microbial community structure and function. Biology and Fertility of Soils, 49(6), 723–733. https://doi.org/10.1007/s00374-012-0761-7
Leytem, A.B., Dungan, R.S., Spiehs, M.J., Miller, D.N. (2024). Safe and sustainable use of bio-based fertilizers in agricultural production systems. In: Amon, B., editor. Developing Circular Agriculture Production Systems. 1st edition. Cambridge, UK: Burleigh Dodds Science Publishing. p. 179-214. https://doi.org/10.19103/AS.2023.0120.16
Magdoff, F., Es, Harold van. (2021) (2024, July 18). CH 3. Amount of organic matter in soils – SARE. USDA Sustainable Agriculture Research and Extension. https://www.sare.org/publications/building-soils-for-better-crops/amount-of-organic-matter-in-soils/
Oregon State University Extension Service, Horneck, D. A., Sullivan, D. M., Owen, J., & Hart, J. M. (2019). Soil Test Interpretation Guide. In EC 1478. https://extension.oregonstate.edu/sites/default/files/catalog/auto/EC1478.pdf
Sims, J. T., & Kleinman, P. J. A. (2005). Managing Agricultural Phosphorus for Environmental Protection. In J. T. Sims, & A. N. Sharpley (Eds.) Phosphorus: Agriculture and the Environment (Vol. 46, pp. 1021-1068). American Society of Agronomy. https://doi.org/10.2134/agronmonogr46.c31
University of Florida. (2015). Urban Design – Landscape plants – Edward F. Gilman – UF/IFAS. (n.d.-b). https://hort.ifas.ufl.edu/woody/critical-value.shtml
Acknowledgements
Funding for this study was provided by the Agricultural Research Division (ARD) of the University of Nebraska-Lincoln through an Undergraduate Student Research Program grant award. Much gratitude is extended to collaborating members of Rogers Memorial Farm, Stuart Hoff and Paul Jasa, and to the members of the Schmidt Lab – Alexis Samson, Logan Hafer, Maddie Kopplin, and Carol Calderon – for their assistance with sample collection and analysis.
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. 2025. Title of presentation. Waste to Worth. Boise, ID. April 7–11, 2025. URL of this page. Accessed on: today’s date.
Call for Abstracts for Waste-to-Worth 2025
You are invited to participate!
The Waste to Worth Conference will be April 7-11, 2025 at the Grove Hotel in Boise, Idaho.
Waste to Worth 2025 welcomes oral, poster, panel, and workshop presentation proposals focused on applied solutions related to animal manure management and protecting the environment.
-
- Submissions should align with one or more of the general areas of emphasis (see below).
- Graduate students are encouraged to submit and participate in a poster presentation competition.
To submit an abstract, go to https://tinyurl.com/W2W2025
For more information, go to: https://wastetoworth.org or the W2W Call for Abstracts flyer.
Deadline is October 30, 2024
Areas of Emphasis
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- Circular Bioeconomy
- Biosecurity
- Feed & Nutrient Management
- Manure, Soil Health & Sustainability
- Emerging Contaminants
- Manure Storage, Treatment, Handling & Application Systems
- Robotics & Artificial Intelligence in Animal Production Systems
- Value-Added Products from Agricultural Production Systems
- Climate Impacts & Adaptation/Mitigation Measures
- Air Quality, Emissions & Fate
- Educational Programming & Delivery
- Environmental Planning & Regulations in Animal Agriculture
- Case Studies/On-Farm Experience
- Mortality Management
- Sustainable Animal Systems
- New & Innovative Technology
- Water Quality
Who attends?
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- Extension agents & specialists
- Progressive farmers & producers
- NRCS staff
- Consultants & technical experts
- Regulatory & policy advisors
- Scientists
- Technology providers
Improving disease identification, treatment, & antibiotic stewardship in livestock production
This webinar will focus on assisting livestock farmers and veterinarians to better identify, diagnose, and treat sick animals with the goal of improving farm efficiency and antibiotic stewardship. This webinar is brought to you by the iAMResponsibleTM Project, a nationwide team of researchers and extension experts working to develop and deliver effective outreach on antimicrobial resistance for diverse audiences. This presentation was originally broadcast on August 18, 2023. Continue reading “Improving disease identification, treatment, & antibiotic stewardship in livestock production”

