Developing Science-Based Estimates of Best Management Practice Effectiveness for the Phase 6 Chesapeake Bay Watershed Model

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Purpose

The Chesapeake Bay Program (CBP) is a regional partnership that leads and directs Chesapeake Bay restoration and protection. The CBP uses a suite of modeling and planning tools to estimate nutrient (nitrogen and phosphorus) and sediment loads contributed to the Bay from its watershed, and guide restoration efforts. Non-point source (NPS) pollutant sources (e.g., agricultural and urban runoff) are largely related to diverse land uses stretching across six states and the District of Columbia. On-the-ground pollutant reductions are achieved by implementing both management and structural best management practices (BMPs) on those diverse land uses. Short and long-term reductions in NPS pollutant loads that result from BMP implementation are estimated using the CBP modeling suite of tools. The CBP recognizes (i.e., represents pollutant reduction credits for) over 150 BMPs across 66 land uses total for all sectors in its Phase 6 suite of modeling tools. The estimated pollutant reduction performance (i.e., effectiveness) of each BMP is parameterized in the CBP modeling suite. Within the CBP, BMP effectiveness is determined by groups of qualified scientific and technical experts (BMP Expert Panels) that review the relevant literature and make an independent determination regarding BMP performance which are reviewed and approved by the CBP partnership before being integrated in to the modeling tools by the CBP modeling team.

BMP Expert Panels are primarily convened under the auspices of the CBP’s Water Quality Goal Implementation Team and tasked to specific sector workgroups for oversight and management. Panels are tasked with addressing a specific BMP, or a suite of related BMPs. Panel members, in coordination with the CBP partnership, are selected based on their scientific expertise, practical experience with the BMP, and expertise in fate and transport of nutrients and sediment. Panels review the relevant literature and through a deliberative process and form recommendations on BMP pollutant production performance, and how the BMP(s) should be accounted for/incorporated into the CBP modeling tools and data reporting systems. Convening BMP Expert Panels is an ongoing focus and priority of the CBP partnership, given the integral role BMP implementation plays in achieving the pollution reduction goals required by the 2010 Chesapeake Bay Total Maximum Daily Load (TMDL).

What Did We Do?

Expert panels follow the process and adhere to expectations outlined in the Chesapeake Bay Program Partnership’s Protocol for the Development, Review, and Approval of Loading and Effectiveness Estimates for Nutrient and Sediment Controls in the Chesapeake Bay Watershed Model (aka the “BMP Protocol”). The expert panel process functions as an independent peer review, similar to that of the National Academy of Sciences.

Each panel reviews and discusses all current published literature and available unpublished literature and data related to the BMP(s), and formulates recommendations using the guidance provided in the BMP Protocol to help weigh the applicability of each data source.  Consensus panel recommendations are recorded in a final report, which is presented to relevant CBP partnership groups, including the CBP partnership’s Agriculture Workgroup for feedback and approval.

Panel recommendations are built into the modeling tools following CBP partnership approval of the panel’s report.

Chesapeake Bay Watershed Map

Basic Diagram of the Chesapeake Bay Program Expert Panel BMP Review Process

What Have We Learned?

The availability of published, peer-reviewed data varies greatly based on the scope of the panel. Some panels have dozens of articles to analyze while others may have a limited number of published studies to supplement gray literature, unpublished data and their best professional judgment. Even panels with a large amount of relevant literature at their disposal identify important gaps and future research needs. Given the wide range of stakeholders in the CBP partnership, regular updates and communication with interested parties as the panel formulates its recommendations is extremely important to improve understanding and acceptance of final panel recommendations.

Future Plans

The Chesapeake Bay Program evaluates BMP effectiveness estimates as new research or new conservation and production practices become available. Thus, expert panels sometimes revisit BMPs that were previously reviewed, but new and innovative BMPs are also considered. The availability of resources and new research limit the frequency of these reviews in conjunction with the priorities of the CBP partnership. Given the CBP partnership’s interest in adaptive management and continually improving its scientific estimates of BMP effectiveness, there will continue to be BMP expert panels for the foreseeable future.

Corresponding author (name, title, affiliation)

Jeremy Hanson, Project Coordinator – Expert Panel BMP Assessment, Virginia Tech

Corresponding author email address

jchanson@vt.edu

Other Authors

Mark Dubin, Agricultural Technical Coordinator, University of Maryland Extension

Brian Benham, Professor and Extension Specialist, Virginia Tech

Each expert panel has at least several other authors and contributors, which is not practical for listing here. Each individual report identifies the panel members and other contributors for that specific panel.

Additional Information

The BMP Review Protocol is available online at http://www.chesapeakebay.net/publications/title/bmp_review_protocol

All final expert panel reports are posted on the Chesapeake Bay Program website under “publications”: http://www.chesapeakebay.net/groups/group/bmp_expert_panels

Acknowledgements

These BMP expert panels would not be possible without the generosity of expert panel members who volunteer their valuable time and perspectives. Staff support, coordination and funding for these panels is provided by the EPA Chesapeake Bay Program, specifically through Cooperative Agreements with Virginia Tech and University of Maryland, with additional contract support from Tetra Tech as needed. The work of these expert panels is strengthened through the participation, review and comments of the CBP partnership.

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. 2017. Title of presentation. Waste to Worth: Spreading Science and Solutions. Cary, NC. April 18-21, 2017. URL of this page. Accessed on: today’s date.

Cultivation of Duckweed on Anaerobically Digested Dairy Manure for Nitrogen and Phosphorus Removal

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Purpose

The purpose of this research included identifying the optimum cultivation conditions of five different strains of duckweed while evaluating the nutrient uptake of nitrogen (N) and phosphorus (P) in anaerobically digested dairy manure to promote biomass production.

What did we do?

The growth of duckweed was assessed on the cultivation parameters of temperature, pH, dissolved oxygen, light intensity, nutrient concentrations, and biomass production. Three strains, namely Landoltia punctata, Lemna gibba and Lemna minuta, were identified as the promising candidates for their high levels of nutrient uptake and biomass production. The temperature and light intensity were maintained in an environmental chamber at 25°C and 10,000 lux, respectively. The nutrient uptake through duckweed cultivation, characterized by the changes of total nitrogen (TN), total Kjeldahl nitrogen (TKN), and total phosphorus (TP), was assessed on the anaerobically digested dairy manure in three dilution ratios i.e., 1:13, 1:18, and 1:27 by volume.

What have we learned?

In the dilution ratios 1:18 and 1:27 all duckweed strains grew successfully. However, in dilution ratio 1:13 all three duckweed species were inhibited by the high nutrient concentration. The batch system created an aerobic environment within the anaerobically digested dairy manure medium with a dissolved oxygen content of 2-6 mg/L. At the high light intensity of 10,000 (lux) a buffer was needed in order to keep the medium’s pH constant to promote duckweed growth. This research compared the nutrient reduction of the microbial growth within the anaerobically digested dairy manure and a standard solution of 1.6 g/L of Hoagland E-medium to the nutrient reduction from the three strains of duckweed at the dilution ratios of 1:13, 1:18, and 1:27. Experimental results revealed that the average duckweed productivities were 1.50, 1.30 and 0.50 grams per square foot per day for Landoltia punctata, Lemna gibba, and Lemna minuta, respectively. At the dilution ratio of 1:27 the highest significant reductions came from Landoltia punctata at 86.0% for TN, 87.5% for TKN, and a TP of 89.5%. At the dilution ratio of 1:18 Lemna gibba got the next highest at 83.8% for TN, 85.6% for TKN, and a TP of 76.2%. Lemna minuta came in last with the highest nutrient reductions in dilution ratio 1:18 with 83.1% for TN, 84.7% for TKN, and a TP of 76.5%. A light intensity of 10,000 lux, pH of 6.5, a temperature of 25°C and a dilution ratio of 1:27 promoted active duckweed growth on anaerobically digested dairy manure.

Future Plans

We will continue the duckweed cultivation work to optimize manure nutrient uptake and to convert duckweed biomass into bioethanol.

Corresponding author, title, and affiliation

Lide Chen, Assistant Professor/Waste Management Engineer, University of Idaho

Corresponding author email

lchen@uidaho.edu

Other authors

Kevin Kruger (University of Idaho)

Additional information

Kevin Kruger is a graduate student who conducted the duckweed cultivation tests.

Acknowledgements

This work is supported by the USDA NIFA and Idaho Agricultural Experiment Station.

Valorization of Manure Treatment for Poultry and Swine Operators


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Purpose 

Current practices for nutrient removal or recovery of phosphorus focus on chemical precipitation technologies, where the recovered products are low-grade, slow-release, low-value land applied fertilizers. Three significant deficiencies re this process – the cost of recovery is greater than the market value as commercial P fertilizer; the land application of such materials perpetuates the current cycle of pollutant nutrient “leakage” into surface waters; and the approach is not viable to address non-point source pollution or the legacy P present in impaired water bodies. Hence, research was initiated based on commercially available Hybrid Ion Exchange Nanomaterials (HIX-Nano), which remove naturally occurring arsenic from drinking water, and apply it to remove, recover, reconcentrate, reuse and recycle soluble reactive phosphorus from diverse organic waste and wastewaters.

What did we do? 

The infusion of high surface area nano iron oxide into conventional ion exchange resins, HIX-(Fe) Nano makes it possible to remove phosphates from wastewater and this has been proven by Lehigh U., ESSRE Consulting and others. Thus, residual dissolved phosphorus not chemically precipitated is captured and removed to supplement and complement the current P recovery processes or capture all of the dissolved P where nutrient recovery does not occur. The key to nutrient recovery is regeneration of the spent media and the conventional chemistry to achieve this is with a weak alkaline (caustic soda) rinse to desorb captured phosphate. The end product is a phosphate solution with a peak concentration of about 1600 mg/L. However, Na does not add any nutrient value whereas potassium hydroxide or ammonium hydroxide or both will add N and K to desorbed P and allow the custom formulation of N-P-K liquid products for hydroponic growers and greenhouse horticulturists. Moreover, when the source of concentrated N and P is livestock manures, there is a way to impart the micronutrients, Ca, Mg, Fe, etc. into the liquid formulations that will result in an N-P-K Plus product.

What have we learned? 

We know that making liquid fertilizer products from manures will help valorize manure treatment because hydroponic growers will pay a premium for a premixed N-P-K product and such an approach will limit the recycled nutrients “leakage” when direct land application is avoided. We also know that commercial synthetic fertilizer production is energy intensive and that any form of pollutant nutrient recovery/reuse will reduce GHG emissions via avoided fertilizer production.

We have also learned that we can do better in terms of manure valorization, if we take the view that even small amounts of soluble reactive phosphorus serve as a “biocatalyst” for intense and frequent harmful algae blooms in fresh and coastal waters. Hence, why not convert recovered nutrients into non-fertilizer products that are more highly valued in the marketplace. In mind are inorganic chemical catalysts that contain P and happen to be widely used in the Oil & Gas sector and Energy Storage sector, as follows:

1) Fluidized Catalytic Catalysts (FCC) – Phosphate-Zeolites (Oil Refineries)

2) Li-ion Battery Cathode Materials – LiFePO4 (Energy Storage)

Finally, we have also learned of recent advances in HIX-Nano technology, where the oxide of Nano Fe particles are replaced with that of Zirconium (Zr) particles. The HIX-(Zr) Nano resin exhibits enhanced P removal/regeneration potential and concurrent removal/recovery of pollutant nutrient N-Nitrate.

The attributes of the HIX-nanomaterial capabilities in manure treatment manifest in the advancement of 4Rs Nutrient Stewardship for fertilizers including land application of manure – Right type, Right place, Right rate and Right time – into “5Rs” of livestock manure management of the dissolved nutrient losses:  Remove, Recover, Reconcentrate, Reuse and Recycle.

The HIX-Nano can be configured and operated with equal efficiency for wastewater streams with high concentrations of nutrients (direct manure treatment after liquid/solids separation) or dilute runoff concentrations or very dilute legacy concentrations in surface or groundwater sources.  A commercial business model of HIX 5Rs treatment is established as a “hub” and “spoke” system.  The spokes are all of the pollutant nutrient pathways to surface waters shown in Figure 1, adapted from Wind’s version (2007).

 

Thus, the application of HIX-Nano technology serves as a barrier to pollutant nutrient leakage from all sources.  Hence, each farm, wastewater treatment plant, each urban stormwater runoff source within the watershed is a “spoke”.  Spent HIX-Nano is transported to a nearby Regeneration Center (Hub) and “refreshed” media is sent (i.e., recycled) back to the source (Spoke) for continued removal of nutrients.   At the Regeneration Center, the further processing of recovery via regeneration and reconcentration generates custom liquid fertilizer products and the aforementioned inorganic chemical catalysts and materials.  Hence, the Regeneration Center also serves as a Product Distribution Center – an all-purpose Hub.  Moreover, regardless of the location of the Hub within or outside the watershed, the recycling of nutrients in products that are not land applied fertilizer in essence “export” pollutant nutrients out of the watershed irrespective of the location of use.  Add the quantification of recycled nutrients to manufacture specific formulations, the HIX-Nano Hub-Spoke model becomes an additional revenue stream to producers for nutrient trading credits, where these programs exist, and a useful tool to develop trading credit programs where they do not exist.

Future Plans 

The potential to simultaneously Remove, Recover, Reconcentrate, Reuse and Recycle pollutant nutrients N and P from manures doubles the work ahead. For the reuse/recycle of fertilizer products confirmation is needed that N-P-K products will be free of impurities and commercially accepted after fertilization testing; similar confirmation path for N (NH4+ and N-NO3)-P-K products. Once established for reuse, HIX-Nano filters can be applied to the flushing discharge of spent fertilizer/nutrient solution for capture of N or P, thus closing the pollutant overload loop and recycling recycled pollutant nutrients.

For the reuse/recycle of treated water deficient in P when removing soluble P only, this needs to be tested for spray application onto soils oversaturated with P to assure compliance with the Nutrient Management Plans for N and P and thus safe reuse and reclamation of this water.

For the catalytic products thorough testing of composition (impurities), stability and performance testing needs to be carried out to gain acceptance as “green” catalysts or solution precursors for “green” catalysts. In either case, reconcentration must be carried out (thermal or mechanical) in a cost-effective way and in a way that carries out manure pathogen total destruction when the source of removed nutrients is from livestock manures .Similar research efforts are needed for battery cathode material manufactured from recycled pollutant P.  Moreover for both catalysts and battery materials, if the final disposition of these materials is landfilling, the application of HIX-Nano on landfill leachate containing P will close the nutrient pollution loop by applying 5Rs treatment principles.

Lastly, to address the Food-Energy-Water nexus challenge the future plans will favor HIX-Nano application on manure digestate after liquid/solids separations.  Nutrient recycling using HIX-Nano will also come into play with biomass to energy technologies such as Anaerboic Digestion and Hydrothermal Liquefaction, where the output is biofuels or biofuels and biochemical.

Corresponding author, title, and affiliation       

Ed Weinberg, PE, President, ESSRE Consulting, Inc.

Corresponding author email    

edweinberg_essre@verizon.net

Additional information               

Ed Weinberg can be reached at (215) 630-0546. Additional key people:

Dr. Mark Snyder, Lehigh U.; Dr. Raul Lobo, U of Delaware.

video: https://www.youtube.com/watch?v=g1LYFVS7wY8

Acknowledgements       

Dr. Arup K. SenGupta, Lehigh U.

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. 2017. Title of presentation. Waste to Worth: Spreading Science and Solutions. Cary, NC. April 18-21, 2017. URL of this page. Accessed on: today’s date.

Panel Discussion: A Look at Extension Programs Working with Commercial Manure Haulers


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Commercial manure haulers are an important link in the nutrient management process. Panelists from different areas of the country will discuss how they work with manure haulers in their state – examples that range from targeted workshops to certification programs and even professional associations. Information on building relationships with this important audience will be shared along with challenges, successes, and future plans.

Panelists

Melony Wilson – Georgia (moderator)

Leslie Johnson – Nebraska

Mary Berg – North Dakota

Doug Hamilton – Oklahoma

Glen Arnold – Ohio

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. 2017. Title of presentation. Waste to Worth: Spreading Science and Solutions. Cary, NC. April 18-21, 2017. URL of this page. Accessed on: today’s date.

 

Poultry Mortality Freezer Units: Better BMP, Better Biosecurity, Better Bottom Line.

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Purpose

Why Tackle Mortality Management?  It’s Ripe for Revolution.

The poultry industry has enjoyed a long run of technological and scientific advancements that have led to improvements in quality and efficiency.  To ensure its hard-won prosperity continues into the future, the industry has rightly shifted its focus to sustainability.  For example, much money and effort has been expended on developing better management methods and alternative uses/destinations for poultry litter.

In contrast, little effort or money has been expended to improve routine mortality management – arguably one of the most critical aspects of every poultry operation.  In many poultry producing areas of the country, mortality management methods have not changed in decades – not since the industry was forced to shift from the longstanding practice of pit burial.  Often that shift was to composting (with mixed results at best).  For several reasons – improved biosecurity being the most important/immediate – it’s time that the industry shift again.

The shift, however, doesn’t require reinventing the wheel, i.e., mortality management can be revolutionized without developing anything revolutionary.  In fact, the mortality management practice of the future owes its existence in part to a technology that was patented exactly 20 years ago by Tyson Foods – large freezer containers designed for storing routine/daily mortality on each individual farm until the containers are later emptied and the material is hauled off the farm for disposal.

Despite having been around for two decades, the practice of using on-farm freezer units has received almost no attention.  Little has been done to promote the practice or to study or improve on the original concept, which is a shame given the increasing focus on two of its biggest advantages – biosecurity and nutrient management.

Dusting off this old BMP for a closer look has been the focus of our work – and with promising results.  The benefits of hitting the reset button on this practice couldn’t be more clear:

  1. Greatly improved biosecurity for the individual grower when compared to traditional composting;
  2. Improved biosecurity for the entire industry as more individual farms switch from composting to freezing, reducing the likelihood of wider outbreaks;
  3. Reduced operational costs for the individual poultry farm as compared to more labor-intensive practices, such as composting;
  4. Greatly reduced environmental impact as compared to other BMPs that require land application as a second step, including composting, bio-digestion and incineration; and
  5. Improved quality of life for the grower, the grower’s family and the grower’s neighbors when compared to other BMPs, such as composting and incineration.

What Did We Do?

We basically took a fresh look at all aspects of this “old” BMP, and shared our findings with various audiences.

That work included:

  1. Direct testing with our own equipment on our own poultry farm regarding
    1. Farm visitation by animals and other disease vectors,
    2. Freezer unit capacity,
    3. Power consumption, and
    4. Operational/maintenance aspects;
  2. Field trials on two pilot project farms over two years regarding
    1. Freezer unit capacity
    2. Quality of life issues for growers and neighbors,
    3. Farm visitation by animals and other disease vectors,
    4. Operational and collection/hauling aspects;
  3. Performing literature reviews and interviews regarding
    1. Farm visitation by animals and other disease vectors
    2. Pathogen/disease transmission,
    3. Biosecurity measures
    4. Nutrient management comparisons
    5. Quality of life issues for growers and neighbors
  4. Ensuring the results of the above topics/tests were communicated to
    1. Growers
    2. Integrators
    3. Legislators
    4. Environmental groups
    5. Funding agencies (state and federal)
    6. Veterinary agencies (state and federal)

What Have We Learned?

The breadth of the work at times limited the depth of any one topic’s exploration, but here is an overview of our findings:

  1. Direct testing with our own equipment on our own poultry farm regarding
    1. Farm visitation by animals and other disease vectors
      1. Farm visitation by scavenger animals, including buzzards/vultures, raccoons, foxes and feral cats, that previously dined in the composting shed daily slowly decreased and then stopped entirely about three weeks after the farm converted to freezer units.
      2. The fly population was dramatically reduced after the farm converted from composting to freezer units.  [Reduction was estimated at 80%-90%.]
    2. Freezer unit capacity
      1. The test units were carefully filled on a daily basis to replicate the size and amount of deadstock generated over the course of a full farm’s grow-out cycle.
      2. The capacity tests were repeated over several flocks to ensure we had accurate numbers for creating a capacity calculator/matrix, which has since been adopted by the USDA’s Natural Resources Conservation Service to determine the correct number of units per farm based on flock size and finish bird weight (or number of grow-out days) in connection with the agency’s cost-share program.
    3. Power consumption
      1. Power consumption was recorded daily over several flocks and under several conditions, e.g., during all four seasons and under cover versus outside and unprotected from the elements.
      2. Energy costs were higher for uncovered units and obviously varied depending on the season, but the average cost to power one unit is only 90 cents a day.  The total cost of power for the average farm (all four units) is only $92 per flock.  (See additional information for supporting documentation and charts.)
    4. Operational/maintenance aspects;
      1. It was determined that the benefits of installing the units under cover (e.g., inside a small shed or retrofitted bin composter) with a winch system to assist with emptying the units greatly outweighed the additional infrastructure costs.
      2. This greatly reduced wear and tear on the freezer component of the system during emptying, eliminated clogging of the removable filter component, as well as provided enhanced access to the unit for periodic cleaning/maintenance by a refrigeration professional.
  2. Field trials on two pilot project farms over two years regarding
    1. Freezer unit capacity
      1. After tracking two years of full farm collection/hauling data, we were able to increase the per unit capacity number in the calculator/matrix from 1,500 lbs. to 1,800 lbs., thereby reducing the number of units required per farm to satisfy that farm’s capacity needs.
    2. Quality of life issues for growers and neighbors
      1. Both farms reported improved quality of life, largely thanks to the elimination or reduction of animals, insects and smells associated with composting.
    3. Farm visitation by animals and other disease vectors
      1. Both farms reported elimination or reduction of the scavenging animals and disease-carrying insects commonly associated with composting.
    4. Operational and collection/hauling aspects
      1. With the benefit of two years of actual use in the field, we entirely re-designed the sheds used for housing the freezer units.
      2. The biggest improvements were created by turning the units so they faced each other rather than all lined up side-by-side facing outward.  (See additional information for supporting documentation and diagrams.)  This change then meant that the grower went inside the shed (and out of the elements) to load the units.  This change also provided direct access to the fork pockets, allowing for quicker emptying and replacement with a forklift.
  3. Performing literature reviews and interviews regarding
    1. Farm visitation by animals and other disease vectors
      1. More research confirming the connection between farm visitation by scavenger animals and the use of composting was recently published by the USDA National Wildlife Research Center:
        1. “Certain wildlife species may become habituated to anthropogenically modified habitats, especially those associated with abundant food resources.  Such behavior, at least in the context of multiple farms, could facilitate the movement of IAV from farm to farm if a mammal were to become infected at one farm and then travel to a second location.  …  As such, the potential intrusion of select peridomestic mammals into poultry facilities should be accounted for in biosecurity plans.”
        2. Root, J. J. et al. When fur and feather occur together: interclass transmission of avian influenza A virus from mammals to birds through common resources. Sci. Rep. 5, 14354; doi:10.1038/ srep14354 (2015) at page 6 (internal citations omitted; emphasis added).
    2. Pathogen/disease transmission,
      1. Animals and insects have long been known to be carriers of dozens of pathogens harmful to poultry – and to people.  Recently, however, the USDA National Wildlife Research Center demonstrated conclusively that mammals are not only carriers – they also can transmit avian influenza virus to birds.
        1. The study’s conclusion is particularly troubling given the number and variety of mammals and other animals that routinely visit composting sheds as demonstrated by our research using a game camera.  These same animals also routinely visit nearby waterways and other poultry farms increasing the likelihood of cross-contamination, as explained in this the video titled Farm Freezer Biosecurity Benefits.
        2. “When wildlife and poultry interact and both can carry and spread a potentially damaging agricultural pathogen, it’s cause for concern,” said research wildlife biologist Dr. Jeff Root, one of several researchers from the National Wildlife Research Center, part of the USDA-APHIS Wildlife Services program, studying the role wild mammals may play in the spread of avian influenza viruses.
    3. Biosecurity measures
      1. Every day the grower collects routine mortality and stores it inside large freezer units. After the broiler flock is caught and processed, but before the next flock is started – i.e. when no live birds are present,  a customized truck and forklift empty the freezer units and hauls away the deadstock.  During this 10- to 20- day window between flocks biosecurity is relaxed and dozens of visitors (feed trucks, litter brokers, mortality collection) are on site in preparation for the next flock.
        1. “Access will change after a production cycle,” according to a biosecurity best practices document (enclosed) from Iowa State University. “Empty buildings are temporarily considered outside of the [protected area and even] the Line of Separation is temporarily removed because there are no birds in the barn.”
    4. Nutrient management comparisons
      1. Research provided by retired extension agent Bud Malone (enclosed) provided us with the opportunity to calculate nitrogen and phosphorous numbers for on-farm mortality, and therefore, the amount of those nutrients that can be diverted from land application through the use of freezer units instead of composting.
      2. The research (contained in an enclosed presentation) also provided a comparison of the cost-effectiveness of various nutrient management BMPs – and a finding that freezing and recycling is about 90% more efficient than the average of all other ag BMPs in reducing phosphorous.
    5. Quality of life issues for growers and neighbors
      1. Local and county governments in several states have been compiling a lot of research on the various approaches for ensuring farmers and their residential neighbors can coexist peacefully.
      2. Many of the complaints have focused on the unwanted scavenger animals, including buzzards/vultures, raccoons, foxes and feral cats, as well as the smells associated with composting.
      3. The concept of utilizing sealed freezer collection units to eliminate the smells and animals associated with composting is being considered by some government agencies as an alternative to instituting deeper and deeper setbacks from property lines, which make farming operations more difficult and costly.

Future Plans

We see more work on three fronts:

  • First, we’ll continue to do monitoring and testing locally so that we may add another year or two of data to the time frames utilized initially.
  • Second, we are actively working to develop new more profitable uses for the deadstock (alternatives to rendering) that could one day further reduce the cost of mortality management for the grower.
  • Lastly, as two of the biggest advantages of this practice – biosecurity and nutrient management – garner more attention nationwide, our hope would be to see more thorough university-level research into each of the otherwise disparate topics that we were forced to cobble together to develop a broad, initial understanding of this BMP.

Corresponding author (name, title, affiliation)

Victor Clark, Co-Founder & Vice President, Legal and Government Affairs, Farm Freezers LLC and Greener Solutions LLC

Corresponding author email address

victor@farmfreezers.com

Other Authors

Terry Baker, Co-Founder & President, Farm Freezers LLC and Greener Solutions LLC

Additional Information

https://rendermagazine.com/wp-content/uploads/2019/07/Render_Oct16.pdf

Farm Freezer Biosecurity Benefits

One Night in a Composting Shed

www.farmfreezers.com

Transmission Pathways

Avian flu conditions still evolving (editorial)

USDA NRCS Conservation fact sheet Poultry Freezers

Nature.com When fur and feather occur together: interclass transmission of avian influenza A virus from mammals to birds through common resources

How Does It Work? (on-farm freezing)

Influenza infections in wild raccoons (CDC)

Collection Shed Unit specifications

Collection Unit specifications

Freezing vs Composting for Biosecurity (Render magazine)

Manure and spent litter management: HPAI biosecurity (Iowa State University)

Acknowledgements

Bud Malone, retired University of Delaware Extension poultry specialist and owner of Malone Poultry Consulting

Bill Brown, University of Delaware Extension poultry specialist, poultry grower and Delmarva Poultry Industry board member

Delaware Department of Agriculture

Delaware Nutrient Management Commission

Delaware Office of the Natural Resources Conservation Service

Maryland Office of the Natural Resources Conservation Service

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. 2017. Title of presentation. Waste to Worth: Spreading Science and Solutions. Cary, NC. April 18-21, 2017. URL of this page. Accessed on: today’s date.

EPA’s Nutrient Recycling Challenge


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Purpose 

Come to this session to learn about the Nutrient Recycling Challenge and meet some of the involved partners and experts, as well as some innovators who are competing to develop nutrient recovery technologies that meet the needs of pork and dairy farmers. This session will begin with an overview of the challenge. Next, innovators will provide snapshot presentations about the technology ideas they are working on, followed by live feedback/Q&A sessions on each technology where we can harness the buzzing brainpower at Waste to Worth. Finally, we will move into a “workshop” designed to support innovators participating in the Nutrient Recycling Challenge as they refine their designs before they build prototypes.

What did we do?

Background on the Nutrient Recycling Challenge

At Waste to Worth 2015, the U.S. Environmental Protection Agency (EPA) hosted a brainstorm session about developing technologies that livestock farmers want to help manage manure nutrients. That session sowed the seeds for the Nutrient Recycling Challenge—a global competition to find affordable and effective nutrient recovery technologies that create valuable products farmers can use, transport, or sell to where nutrients are in demand. Pork and dairy producers, USDA, and environmental and scientific experts saw the tremendous opportunity to generate environmental and economic benefits, and partnered with EPA to launch the challenge in November 2015 (www.nutrientrecyclingchallenge.org).

What have we learned? 

There is a tremendous opportunity to generate environmental and economic benefits from manure by-products, but further innovation is needed to develop more effective and affordable technologies that can extract nutrients and create products that farmers can use, transport, or sell more easily to where nutrients are in demand.

In the Nutrient Recycling Challenge, innovators have proposed a range of technology systems to recover nitrogen and phosphorus from dairy and swine manure, including physical, chemical, biological, and thermal treatment systems. Some such systems may also be compatible with manure-to-energy technologies, such as anaerobic digesters. Farms of all sizes are interested in nutrient recovery, and there is demand for diverse types of technologies due to a diversity in end users. To improve the adoptability of nutrient recovery systems, it is critical that innovators are mindful of the affordability of technologies, and work to lower capital and operations and maintenance costs, and improve the potential for returns on investment. A key factor for offsetting the costs of a technology and improving its marketability will be in its ability to generate valuable nutrient-containing products that are competitive in the market.

Future Plans 

The challenge has four phases, in which innovators are turning concepts into designs, and eventually to pilot these working technologies on livestock farms. Thirty-four innovator teams whose concepts were selected from Phase I are refining technology designs in Phase II.  Design prototypes will be built in Phase III. This workshop is designed to help innovators maximize their potential for developing nutrient recovery technologies that meet farmer needs.

Corresponding author, title, and affiliation 

Joseph Ziobro, Physical Scientist, U.S. Environmental Protection Agency; Hema Subramanian, Environmental Protection Specialist, U.S. Environmental Protection Agency

Corresponding author email 

ziobro.joseph@epa.gov; subramanian.hema@epa.gov

Session Agenda

  1. Overview of the Nutrient Recycling Challenge, Hema Subramanian and Joseph Ziobro of EPA
  2. Nutrient Recycling Challenge Partner Introductions, Nutrient Recycling Challenge Partners (including National Milk Producers Federation, Newtrient, Smithfield Foods, U.S. Department of Agriculture Agricultural Research Service and Natural Resources Conservation Service, U.S. Department of Energy, and Water Environment & Reuse Foundation)
  3. Showcase of Innovators’ Technology Ideas
    • Decanter Centrifuge and Struvite Recovery for Manure Nutrient Management, Hiroko Yoshida
    • Manure Solids Separation BioFertilizer Produccion Drinking Water Efluente, Aicardo Roa Espinosa
    • Nutrient Recovery from Anaerobic Digestates, Rakesh Govind
    • Organic Waste Digestion and Nutrient Recycling, Steven Dvorak
    • Manure Treatment with the Black Solder Fly, Simon Gregg
  4. Nutrient Recycling Challenge Workshop for Innovators
    • Developing technologies: From concept to pilot (to full-scale), Matias Vanotti
    • Waste Systems Overview for Dairy and Swine and Innovative Technologies: What Steps Should be Taken (Lessons Learned), Jeff Porter

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. 2017. Title of presentation. Waste to Worth: Spreading Science and Solutions. Cary, NC. April 18-21, 2017. URL of this page. Accessed on: today’s date.

Spotlight on Manure Management in North Carolina and the Atlantic Coastal Plains


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Purpose 

To provide information about commonly-found manure management systems and approaches in North Carolina and the Coastal Plains, and discuss opportunities for technological innovation in the areas of manure management and nutrient recovery/utilization. Hear from a diverse panel of researchers, animal agriculture producers, and agency representatives who will provide background on the environmental conditions of the region and discuss specific technical considerations for innovative research and development. Learn about what has and hasn’t worked in past attempts to recover nutrients at animal agriculture farms in the area, and about the exciting possibilities for innovation in the U.S. Environmental Protection Agency’s (EPA’s) Nutrient Recycling Challenge (www.nutrientrecyclingchallenge.org).

What did we do? 

N/A

What have we learned? 

N/A

Future Plans 

N/A

Corresponding author, title, and affiliation 

Joseph Ziobro, Physical Scientist, U.S. Environmental Protection Agency; Hema Subramanian, Environmental Protection Specialist, U.S. Environmental Protection Agency

Corresponding author email 

ziobro.joseph@epa.gov; subramanian.hema@epa.gov

Other authors

Dr. John Classen, Associate Professor and Director of Graduate Programs, College of Biological and Agricultural Engineering at North Carolina State University

Dr. Kelly Zering, Professor of Agricultural and Resource Economics, North Carolina State University

Additional information

Session Agenda

  1. Background, history, and technical information about manure management in North Carolina and the Coastal Plains

Presenter: Dr. John Classen, Associate Professor and Director of Graduate Programs, College of Biological and Agricultural Engineering at North Carolina State University

  1. Lessons Learned from the Smithfield Agreement

Presenter: Dr. Kelly Zering, Professor of Agricultural and Resource Economics, North Carolina State University

  1. Panel: Challenges and Opportunities around Manure Management Systems

Moderator: Hema Subramanian

Panel to include the above speakers plus representatives from the local animal agriculture industry, North Carolina Department of Agriculture and Consumer Services, North Carolina Department of Environmental Quality, and U.S. Environmental Protection Agency. 

Nutrient Cycling in Horse Pastures


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Purpose 

This presentation will review the existing multi-species literature on nutrient cycling and how it is affected by the horse’s diet and rotational grazing.

Grazed pastures, particularly rotationally grazed pastures, recycle nutrients faster than ungrazed pastures. Nutrients on pasture land enter through animal waste, and waste feed or fertilizer; they leave through removal of forage, leaching/runoff, or animal product/waste removal. Taking away the animal component removes about half of the inputs needed to recycle the nutrients. Dietary nitrogen (N), phosphorus (P) and potassium (K) are required for basic maintenance of horses; however, not all of what is consumed is used by the animal, therefore the dietary concentrations of these nutrients will impact the nutrient cycling. Digestibility of N, P and K in horses is approximately 80, 25 and 75 %, respectively. What does not get digested will end up excreted back into the soil.

What did we do? 

For example, in one study eight Standardbred mares were divided into two groups and received diets of grass hay and grain. The high P (HP) group received 142 g/d of NaH2PO4, formulated to provide 4.5-times the dietary P requirement, or 65 g phosphorus/d. The low P (LP) group received 28 g of phosphorus/d in the basal diet. Data showed that horses receiving the HP diet excreted higher P and water extractable P in the manure than those fed the LP diet (Table 1; Westendorf and Williams, 2015). The same goes for N, where one study used a treatment group that was supplemented with 700 g/d of soybean meal top dressed on 500 g of sweet feed per day (TRT; 1042 g protein/d DM total), while the control group received the sweet feed meals without the soybean meal (CON; 703 g protein/d total). Both groups were also fed 8 kg/d of a grass hay mix (562 g protein /d DM), water and salt ad libitum. Horses fed the TRT diet excreted more N and NH3 than horses fed the CON diet (Figure 1; Williams et al., 2011).

Nutrient Cycling in horse pastures: Tables and Figures

What have we learned? 

More intensive grazing also creates an increased rate of nutrient cycling due to the added animal inputs on the land. Even though no horse related studies have been performed on this topic studies in cattle have found that plant-available N levels doubled when cattle were rotationally grazed with five grazings per season instead of three (Baron et al., 2002). Kenny (2016) looked at horses grazed under either a continuous or rotational grazing system (see Pictures 1 and 2, Left to Right, respectively) and found no differences in system after one year of grazing, however, the author concludes that more time on the system could have generated differences.

Other factors that affect the rate of nutrient cycling include amount of legumes in the pasture, distribution of manure on pastures (i.e. relation to water, shelters and fencing), and use or rates of fertilizer.

 

Horse in pastureRotational grazing horse

Future Plans    

More equine specific studies need to be performed looking at how grazing systems and equine diets affect nutrient cycling and how horse farm owners can utilize this to best manage their farm for optimal nutrient utilization.

Corresponding author, title, and affiliation        

Carey A. Williams, Equine Extension Specialist, Rutgers, the State University of New Jersey, Department of Animal Science

Corresponding author email    

carey.williams@rutgers.edu

Additional information 

References:

Baron, V. S., E. Mapfumo, A. C. Dick, M. A. Naeth, E. K. Okine, and D. S. Chanasyk. 2002. Grazing intensity impacts on pasture carbon and nitrogen flow. J. Range Manage. 55:525-541.

Kenny, L. B. 2016. The Effects of Rotational and Continuous Grazing on Horses, Pasture Condition, and Soil Properties. Master thesis, Rutgers, the State University of New Jersey, New Brunswick, NJ.

Westendorf, M. L., and C. A. Williams. 2015. Effects of excess dietary phosphorus on fecal phosphorus excretion and water extractable phosphorus in horses. J. Equine Vet. Sci. 35:495-498. doi:10.1016/j.jevs.2015.01.020

Williams, C. A., C. Urban, and M. L. Westendorf. 2011. Dietary protein affects nitrogen and ammonia excretion in horses. J. Equine Vet. Sci. 31:305-306.

 

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. 2017. Title of presentation. Waste to Worth: Spreading Science and Solutions. Cary, NC. April 18-21, 2017. URL of this page. Accessed on: today’s date.

Pennsylvania Horse Farm’s Whole Farm Balance Inputs of Nitrogen and Phosphorus

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Purpose

In Pennsylvania there has been an increased emphasis on farm and nutrient management practices on equine operations due to expansion of environmental regulations. Of the 31,000 operations which house horses in Pennsylvania, 23,250 are non-commercial operations and over 75 percent are on limited acreage, requiring intensive management. Managers of equine operations frequently do not have agricultural backgrounds and need assistance with farm management plans. Proper management of equine operations requires a series of complementing Best Management Practices (BMPs) that implement strategies to preserve pasture vegetative cover, to balance nutrient production with nutrient utilization, to properly manage excess manure nutrients, and to manage equine operations for minimal release of sediment.

This environmental program was developed to identify needed BMPs for the equine industry and help farm mangers understand, select, and implement sustainable farm management practices. The program consisted of three components: Documentation of existing practices and conditions on equine operations, educational outreach to increase knowledge and skills, and on-farm implementation of BMPs. These three projects covering 2009-2015, measured sediment and nutrient losses, for high density horse operations; and recorded environmentally sound farm management practices.

What did we do?

Swinker in pastureProject 1- documented conservation and farm management practices on 23 equine operations, quantitatively evaluated pasture desirable plants and canopy cover, sampled feed, hay and soil, and conducted nutrient management audits. Pasture data, collected using line point transect methodology, included calculation of percent canopy cover, basal stems and desirable forage. The 23 surveyed operations were used to develop a baseline for total nutrient balances and levels for the Pennsylvania horse industry.

Project 2- looked at nitrogen and phosphorus inputs on 14 farms to determine the risk of horse farms for non-point source pollution. Over a 12 months period, amounts of imported fertilizer, hay, concentrate feed, and bedding were obtained from farm managers. Samples of hay, concentrate feed, and bedding were taken from each farm and analyzed for N and P. Whole farm nutrient balance was calculated as a percent by the equation ((imported nutrients- exported nutrients) /imported nutrients) X 100. Nitrogen and P whole farm balances were recorded as a percentage basis for the total farm and on a kilogram basis for per animal unit and per hectare values. PROC SURVEYMEANS was used to determine descriptive statistics on the sample and whole farm balance values.

Project 3- involved 95 farm operations (1,086.90 ac.) in a project designed to implement practices to increase canopy cover and desirable forages in pastures and reduce nutrient and sediment loss. The team provided individual assistance to help owners locate resources, technical assistance and funding. All farm managers (n=95) farms were visited documenting conservation/management practices, BMPs already in place and identification of areas of concern/improvement needs. The team finalized field farm survey instruments, quantitatively documented pasture plants/canopy cover, sampled feed/hay/soil, and conducted nutrient management audits. Pasture data was collected using line point intercept and Equine Pasture Evaluation Disc methodology. All plant species were documented with pasture condition scores generated using pasture condition score sheets.

Out of the 95 farms visited, a total of 43 farm (744.55 ac. collectively), pastures were targeted for improvement, soil tested and prepared for methods to improve the pasture grass stands. Farms selected to reseed pastures were provided with a seed mix that was custom blended for their farm based on soil conditions, farm management, pasture needs and level of use.

Twenty-seven of the farms conducted reseeding using a no-till drill, 8 farms utilized conventional plowing and 8 farms utilized broadcasting and/or frost seeding. The remaining 48 farms did not need to reseed and instead received recommendations on methods to improve and manage existing forage quality through improving or utilizing BMPs. Four farms did not continue involvement in the program after the initial farm visit by the team.Picture of two horse in a pasture

What have we learned?

Project 1- The surveyed farms have helped to validate and evaluate existing tools on horse operations. The “pasture sediment loss” tools used (at that time) in this project (PA RUSLE2, Pasture Condition Score, Nutrient Balancing, Pasture Nutrient Balancing sheets and PA Phosphorous-Index) helped to analyze the cost-effectiveness and sustainability of the nutrient reduction strategies. The survey results have shown that these selected tools need to be adjusted in order to properly measure sediment and soil loses on horse farms.

Smaller farm operators reported a major hurdle to managing pastures is lack of knowledge and lack of equipment. In addition, 33% of farm managers reported they wanted to utilize the suggested practices, but required financial assistance or more technical information.

Results of the information gathered by the Equine Environmental Stewardship (EES) team projects has been used and examined by state agencies, assisting in development of in-service training for their personnel, used in revising potential regulations and assistance concerning horse farm operations.

Study 2- The majority of the horses on the farms were non-breeding horses, which the only managed output was manure. Four of the farms did not export any manure, 3 exported a small portion of their collected manure and 6 exported all their collected manure. Whole farm balance inputs averaged 53 kg N per 1000 lbs of animal (AU) and 13 kg P/AU. Whole farm balances ranged from 100% retention of imported nutrients where no products were exported to a negative balance where all collected manure was exported. Average N and P whole farm balances were 73% and 51% retention of inputs, respectively. With limited export of nutrients from horse farms as foals or manure, more manure must be exported and/or nutrient imports must be decreased to approach nutrient balance and decrease the risk of nutrient pollution.

Project 3- Out of the 95 farms visited, a total of 43 farms (representing 744.5 acres) were reseeded. Twenty farms needed to utilize the no-till drill purchased through the project grant. Pastures chosen for reseeding had low forage yields and canopy covers less than 50%. After reseeding the pastures, yields increased to 1.0 to 2.0 tons per acre resulting in an economic gain that averaged $450 to $600 per acre.

In conclusion: The Team noted that farm owners are committed to adopting practices that maintain healthy horses, healthy farms, and a healthy environment. Each of the farms listed worked with the Equine Team to select and implement one or more Best Management Practices (BMPs) on their farm. BMP’s were chosen to increase pasture canopy cover and improve pasture quality, proper composting and or disposal of manure, and ration formulation. Practicing rotational grazing, utilizing sacrifice areas, soil testing and applying lime and fertilizers are BMPs farmers were encouraged to adopt.

Future Plans

The survey results are being used in the development of the curriculum for Environmental Stewardship short courses, to help agency personnel understand the equine industry and to help farm owners develop the knowledge and skills necessary to adopt environmentally sound farm management practices.

Corresponding author, title, and affiliation

Ann Swinker, Extension Horse Specialist, Pennsylvania State University

Corresponding author email

aswinker@gmail.com

Additional information

Ann Swinker

Penn State University

324 Henning Building

Department of Animal Science

University Park, PA 16802

814-865-7810

FAX: 814-865-7442

E-mail: aswinker@psu.edu

Bott, R., Greene, E., Trottier, N., Willliams, C., Westendorf, M., Swinker N., Mastellar, S., Martinson, K., Environmental implications of nitrogen output on horse operations: A review, Journal of Equine Veterinary Science 08/2015; DOI:10.1016/j.jevs.2015.

Swinker, A., D. Foulk, H. McKernan , Environmentally Friendly Farm Program Recognizes Pennsylvania Farms that Adopt Sound Management Practices Protecting Water Quality and the Environment, Waste to Worth, Seattle WA, March 31 – April 3, 2015.

USDA, CIG Grant Final Report: Pennsylvania Small Farm Environmental Stewardship Program: Implementing Conservation Practices on Small Farms and Using Environmental, Agreement Number: 69-3A75-11-180. 56 pages.

Swinker, A. M., Northeast Regional USDA CRIS Report, September 2013, USDA Regional Project, NE-1041 – Environmental Impacts of Equine Operations, https://projects.sare.org/sare_project/lne10-303/

PSU DAS web site; http://www.das.psu.edu/research-extension/equine/adult-education Environmental stewardship Project and Equine Science Newsletter websites

Acknowledgements

USDA Natural Resource Conservation Service Conservation Innovation Grant and SARE Grant for funding this project. USDA Regional Project, NE-1041, All the hard work of the PSU Extension Equine Team

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. 2017. Title of presentation. Waste to Worth: Spreading Science and Solutions. Cary, NC. April 18-21, 2017. URL of this page. Accessed on: today’s date.

Closing Abandoned Livestock Lagoons Effectively to Utilize Nutrients and Avoid Environmental Problems

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Purpose

In Nebraska alone, nearly 400 earthen manure storage structures are in operation; approximately four dozen requests to cease operation of permitted lagoons were received by the Nebraska Department of Environmental Quality in the prior decade with many more non-permitted storage structures being in need of proper closure. Abandoned livestock lagoons, earthen manure storage basins, and other manure storages (e.g. concrete pits) need to be decommissioned in a manner that controls potential environmental risk and makes economical use of accumulated nutrients. Currently, limited guidance is available to support lagoon closure planning and implementation and few professionals who support livestock producers have experience planning or participating in the manure storage closure process. The main focus of this project was to produce two videos that document the processes for planning and executing a lagoon closure.

What did we do?

The University of Nebraska Haskell Ag Laboratory, located near Concord, NE, had an anaerobic lagoon that was operated for over 20 years, but has not received swine manure additions since 2009 when the swine unit was depopulated. The decommissioning of this storage structure was proposed in 2014 and provided our team an opportunity to plan, implement and document the procedures necessary to properly close this structure. When we went to find material on how to accomplish this properly, we did not find suitable material. Two grants were secured in 2016 from the U.S. Pork Center of Excellence (USPCE) to fund our team efforts to document the closure process – from planning to completion – with two separate videos. The first video is focused on the planning activities necessary to prepare for removal and utilization of stored liquid and sludge. The second is focused on the liquid and sludge removal and utilization activities, decommissioning of conveyance structures, and deconstruction of the lagoon berm to return the site to a natural grade.

Activities conducted to execute the lagoon closure have included:

1) Mapping of sludge levels with sonar and analyzing sludge samples to estimate volume and nutrient content of sludge, which enabled development of a land application plan for utilizing the products

Figure 1. Sonar sludge mapping

Figure 1. Sonar sludge mapping.

2) De-watering the lagoon (effluent used for sprinkler irrigation and flood irrigation)

3) Hosting a demonstration event during which participants:

a. observed sludge removal and land application processes,

b. participated in a manure spreader calibration,

c. inspected the soil beneath the lagoon liner,

d. viewed the abandoned production buildings and heard about options for eliminating conveyance of liquid from the building to the lagoon,

e. explored alternative sludge removal methods, and

f. participated in a classroom session where presenters shared details of the closure planning process, cost-share opportunities for closure of manure storage structures, and expectations for re-grading and re-seeding the site following removal of sludge.

Figure 2. Participants learned about planning land application of the sludge

Figure 2. Participants learned about planning land application of the sludge.

Figure 3. Land application of the sludge and calibration of the manure spreader

Figure 3. Land application of the sludge and calibration of the manure spreader.

4) Removing the sludge and applying it to cropland following the demonstration event.

Documentation of all planning, demonstration, and closure execution activities have been captured via extensive video footage, still photos, and participant interviews. Production of the videos is in process with completion and release of videos anticipated in summer 2017.

What have we learned?

Although every manure storage closure process is expected to present its own unique challenges and opportunities for learning, the process documented during this project has provided a number of insights:

1) While this process involved pumping liquid from the lagoon prior to attempting sludge removal in order to observe the sludge layer and document the volume present, a more appropriate, and likely more effective, process is to agitate the storage prior to and during pumping activities to enable handling all of the material as a slurry;

2) Dewatered sludge volume (nearly 200,000 gallons) and nutrient content (44.2 lbs. TKN, 37.5 lbs. organic N, 89.3 lbs. P2O5 and 7.6 lbs. K2O per 1,000 gallons) for this system yielded enough nutrients to apply to 80-100 acres, based on a phosphorus removal rate. It is unknown what the release of the organic N component of the sludge will be, but using just the phosphorus content, application of 1000 gallons per acre would provide enough phosphorus for what would be removed from 220 bushels of corn, which is worth approximately $35 with winter 2017 prices.;

3) Given the high phosphorus content in the sludge and that the nearby fields at the Haskell Ag Lab were not in need of phosphorus, an appropriate application rate for the sludge was determined as 8-10 tons/acre;

4) Soil beneath the lagoon liner yielded a phosphorus concentration of 556 ppm, likely a result of an inadequate liner in the lagoon as originally constructed in the 1960s; and

5) Installation of a bentonite clay liner during renovation of the structure in 1992 appeared to be effective as the liner was fully intact when observed during closure activities.

Pre-post surveys completed by 33 attendees of the demonstration event revealed that attendees improved their confidence in performing six key tasks identified by the team as being impactful. Results are summarized in Figure 4.

Figure 4. Impacts of the lagoon closure demonstration event

Figure 4. Impacts of the lagoon closure demonstration event.

Future Plans

We plan to continue the decommissioning process by:

1) Completing sludge removal and application to cropland;

2) Deconstructing the berms, leaving the liner intact, and returning the area to natural grade;

3) Seeding the area to establish ground cover and mitigate runoff and erosion; and

4) Plugging the inlet pipes in manure pits within the animal housing in lieu of removing buried conveyance pipes.

The two videos are in production and will be made available through the Pork Information Gateway (www.porkgateway.org) during summer 2017.

Corresponding author, title, and affiliation

Leslie Johnson, Research Technologist, University of Nebraska – Lincoln

Corresponding author email

ljohnson13@unl.edu

Other authors

Charles Shapiro and Amy Schmidt, University of Nebraska – Lincoln

Additional information

https://water.unl.edu/article/animal-manure-management/lagoon-closure-and-your-environmental-responsibility

Acknowledgements

The authors would like to recognize the U.S. Pork Center of Excellence (USPCE) for funding the development of the videos documenting this process and enabling us to complete this project. We would also like to acknowledge that without the support of the industry, who provided equipment and advice, we would not have been able to get this project off the ground. Also a special thanks to the Agricultural Research Division for their support.