Tag: composting

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Markets for Composted Agricultural Waste

Why Consider Composting Manure?

Enforcement of nutrient management regulation has forced Maryland farms and agricultural facilities to adopt new waste management practices. Few options exist that are financially sustainable. Regulatory agencies witnessed the unexpected consequence of closing small and mid-sized farms who could not afford to institute new waste management technologies. To counter that consequence, Maryland Department of Agriculture offered grants to subsidize the development of innovative technology and business practices. These new systems and business models had to offer both financial and environmental sustainability.

What Did We Do?

The first step in this project (supported by the Maryland Department of Agriculture, 2014) was to identify the biological make up and characteristics of the stable waste both before and after processing. We measured nutrient content and form (N, P, K), porosity, moisture absorption and C: N ratio. By understanding what the material consisted of pre-processing, we were able to determine what effects different controls during processing would have on the end product. As an example, when using stable waste for bedding re-use the material is run through the composting system as quickly as possible. A shorter composting period with auger mixing technology allowed the biological activity to breakdown the manure balls, support the transformation of the waste nutrients and yet protect the integrity of the shavings for second use. Related: Managing Manure on Horse Farms

Next, the local markets were studied:

    • Soil types and needs: compost to add porosity, water retention, nutrients to soil
    • Weather patterns and created needs: compost added for water retention, binding material to diminish run off
    • Population centers for urban market: compost for landscape needs, potting medium
    • Rural character for on farm market: compost for nutrient replacement, bedding re-use
    • Cost of operations on local farms: cost of bedding, cost of disposal, cost of landscape material, cost of synthetic or imported fertilizer
    • Wholesale market needs: compost for distribution centers (Scotts products), soil specialty companies, land reclamation sites, Department of Transportation needs, green house growers

Identifiable, viable market channels to move the processed stable waste were necessary components of a business model.  Uses for the processed waste were identified both on site and off site.

On site uses were identified as:

    • Land application: field enhancement
    • Bedding re-use
    • Landscape use
    • Improved footing arenas
    • Land reclamation
    • Pelletized for heat systems
 Off site uses were identified as:

    • Soil amendment
    • Land reclamation
    • Potting Medium
    • Food Waste Bulking agent
    • Whole sale distribution centers
    • Soil Specialty companies

What Did We Learn?

Data was gathered and studied from equine facilities with existing composting operations to illustrate what the benefits and challenges can be. IOS Ranch on Bainbridge Island Washington is a sustainably designed 7.5 acre property that supports 20-25 stalled horses. The design concentrates the structures, indoor arena, stall, office and supporting buildings, so there could be surrounding pasture turn out and an outdoor arena. The facility was paying high waste disposal fees. Their decision to bring composting technology to the farm was an effort to eliminate disposal fees and diminish their bedding cost through bedding re-use. However, once the system was installed a local landscaper visited the site and saw value in the compost. The material is now sold for $30/yard wholesale and $45/yard retail to local landscapers and gardeners. With the price of shavings for bedding delivered at $7.50/yard the business decision to sell the compost was an obvious one. The property was formerly a gravel pit with large areas of exposed pit run. Once realizing the value of the compost for land application, the owner spread on the exposed areas greatly improving grass performance in the turnout fields. This farm was saving $100-$140/day producing compost because of the reduced disposal fees plus profits from marketing, allowing for a breakeven on investment in 3 years.

manure composting operation on horse farm manure composting operation on horse farm manure composting operation on horse farm

Joint Base Myer Henderson Hall hosted a pilot project for composting of food waste on remote contingency bases. On this base the Army’s Caisson horses are housed in a 50+ stall barn. After the pilot was completed the in vessel composting system will revert to the base for processing the stable waste. The base has the choice of bedding re-use or using the compost for landscape needs on base and/or in the adjacent Arlington National Cemetery. Outside contractors were supplying the base with compost at nearly $400,000 per year. The project could pay for itself in the first year. Thorough lab analysis showed the compost to be consistently of high quality, pathogen free, and weed seed free.

army base horse manure composting photos

Currently two sites in Maryland are being studied; one an equine rescue facility housing 50-80 horses, and the other a dairy with 240 head. The use of composted stable waste as a peat moss replacement will bring value to the equine and dairy farms and to the large, local greenhouse industry. Currently 80% of the peat moss used in Maryland is imported from Canada. The farms selected are large enough that they can produce enough material for bedding re-use (savings of nearly 20% of operating budget) and/or sell the material to wholesale buyers. The composting material from both sites show the favorable attributes of peat moss, porosity and moisture retention. Blending can alter the nutrient levels to what the market needs by using the more nutrient rich dairy waste. The collection of compost and blending can be done on on site or at an off site location in cooperation with other local farms, this may help meet larger volume needs of wholesale buyers.

horse manure composting operation in Maryland horse manure composting operation in Maryland horse manure composting operation in Maryland

Future Plans

The Maryland projects are both two years in duration with continual data gathering and recording. The next step is the location and operation of a collection yard for multiple local farms to send their processed stable waste. Such a yard allows for mixing to meet differing market needs and the creation of large quantities of homogenous product for local greenhouse growers.

Authors

Mollie Bogardus, owner, Aveterra and representative of Green Mountain Technologies, Inc. mollie@compostingtechnology.com

Additional Information

http://news.maryland.gov/mda/press-release/2014/08/15/mda-awards-1-million-for-innovative-manure-management-technologies-demonstration-projects-in-howard-frederick-and-worcester-counties-recognized/

Acknowledgements

Dr. Pat Millner, USDA Beltsville, Research Microbiologist is lead researcher and mentor on these projects in Maryland.

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

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On-Farm Field Days as a Tool to Demonstrate Agricultural Waste Management Practices and Educate Producers

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Abstract

Teaching Best Management Practices (BMP) or introducing new agricultural waste management practices to livestock producers and farmers is a challenge. This poster describes a series of on-farm field days designed to deliver information and demonstrate on-site several waste management techniques, most of them well established in other parts of the country but sparsely used in Idaho. During these field days, Extension personnel presented each technique and offered written information on how to apply them. But without a doubt, presentations by the livestock producers and farmers who are already applying the techniques and hosted each field day at their farms was the main tool to spark interest and conversations with attendees.

Four field days were delivered in 2012 with more programmed for 2013. Demonstrated techniques reduce ammonia and odor emissions, increase nitrogen retention from manure, reduce run-off risks, and reduce emissions of greenhouse gases. Topics addressed on each field day were, a: Dairy manure collection and composting, 20 attendees. b: Dairy manure land application ten attendees. c: Grape vine prunings and dairy manure composting, 50 attendees. d: Mortality and offal on-farm composting, 40 attendees. In all cases farm owners and their managers presented and were available to answer attendees’ questions, sharing their experience, and opinions regarding the demonstrated practices. Many attendees expressed their interest and willingness to adopt some of the demonstrated practices. On-farm field days are an excellent tool to increase understanding and adoption of BMP and new technologies. Hearing experiences first hand from producers applying the techniques and being able to see them in action are excellent outreach tools. On-farm field days also fit the fast pace, busy schedule of modern producers who can later visit with Extension and other personnel if they need more details, information, and help on how to adopt the techniques they are interested in.

Why Hold Field Days on Ag Waste Management?

The dairy industry is the number one revenue commodity in Idaho. At the same time Idaho is ranked third in milk production in the nation. Idaho has more than 580,000 dairy cows distributed in 550 dairy operations (Idaho State Department of Agriculture 1/2013). The Magic Valley area in south-central Idaho hosts 54% of those dairies and 73% of all dairy cows in the state (Idaho Dairymen’s Association internal report, 2012).  Odors from dairies and other animal feeding operations are a major issue in Idaho and across the country.  In addition, the loss of ammonia from manures reduces the nutrient value of the manure and generates local and regional pollution. Dairy farmers of all sizes need more options on how to treat and dispose of the manure generated by their operations. Odor reductions, capture of nitrogen in dairy manure, reduction of greenhouse gases emissions, off-farm nutrients export, water quality protection, and reduction of their dairy operation’s environmental impact are some of the big challenges facing the dairy industry in Idaho and around the country. There are many Best Management Practices (BMP) that are proven to work on providing results related to the challenges mentioned before. Some of these practices are widely adopted in certain parts of the country or in other countries, with a lack of adoption by dairy producers and farmers in other parts of the country. This poster shows a series of Extension and research efforts designed to introduce and locally test proven BMP to dairy producers and crop farmers in southern Idaho in an effort to increase their adoption and incorporate those BMP as regular practices in Idaho agriculture. The four projects described were delivered in 2012 and some will continue in 2013.

What Did We Do?

To demonstrate and test BMP we chose to develop on-farm research projects to collect data and couple these projects with on-farm field days to demonstrate the applicability of the BMP in a real-world setting. Extension personnel developed the research and on-farm field days and did several presentations at each location. But without a doubt the stars during those field days were the dairy producers and farmers who hosted the research and demonstration events and who are already using or starting to use the techniques showcased. These pioneer producers are not only leading the way in using relatively new BMP in southern Idaho, they also share their experiences with other producers and with the academia so everybody around can learn from them. Topics addressed in each field day were, a: Dairy manure collection and composting, 20 attendees. b: Dairy manure land application, 10 attendees. c: Grapevine prunings and dairy manure composting, 50 attendees. d: Mortality and offal on-farm composting, 40 attendees.

On-farm manure collection and composting field day.

Some highlights from each project are: a. The dairy manure collection and composting field day demonstrated the operation and use of a vacuum manure collection system and a compost turner. Dairy managers and machinery operators shared their experiences, benefits and challenges related to the use of these two technologies. During the field day attendees also visited the whole manure management system of the dairy and were able to observe diverse manure management techniques. As a result of this project Extension personnel determined the necessity of generating educational programs for compost and manure management operators for dairy employees. A composting school in Spanish and English proposal was presented and a grant was obtained to develop and deliver them in 2013.

b. The dairy manure land application field day featured the demonstration of a floating manure storage pond mixer and pump, and a drag hose manure injection system. We also showed an injection tank that wasn’t operated during the demonstration. The floating pond mixer serves as lagoon mixer and pump. It mixes and pumps the manure through the drag hose system to the subsurface injector. This system dramatically reduces the time required to land apply liquid and slurried manures. It also significantly reduces ammonia and odor emissions to near background levels, as well as avoids runoff after applications. This project included research of emissions on the manure injection sites (see Chen L., et al. in this conference proceedings).

Demonstrating dairy manure subsurface injection using a drag hose system.

c. The grapevine prunings and dairy manure composting project involves research on the implications of increasing the carbon content of dairy manures using grapevine prunings and other carbon sources to retain more nitrogen in the compost, and how it varies among three diferent composting techniques. This project includes two field days, one during the project (2012), and another one at the end of it in 2013. The demonstration includes how to compost using mechanically turned windrows (common in Idaho), passive aerated, and forced aerated windrows (both very rarely used in Idaho). Another novelty in this project is that it aims to bring together dairy producers and fruit & crop producers, or landscaping insustry so they can combine their waste streams to produce a better compost and to reduce the environmental impact of each operation. Several producers of the diverse audience who attended showed interest in adopting some of the composting techniques presented during the field day.

On-farm composting methods featuring grape vine prunings and dairy manure compost

d. The mortality and offal on-farm composting project was located at a diversified sheep farm that includes sheep and goat dairy and cheese plant, meat lambs, and chickens. A forced aerated composting box was used to compost lamb offal, hives, lamb and chicken mortalities, and whey from the cheese plant. A very diversified audience attended the field day and the composting system generated a lot of interest. The farm owner was so pleased with the system that she created a second composter with materials she had on-hand to increase her composting capabilities and compost all year round. The producer stopped disposing of lamb offal, hives, and mortalities at the local landfill.

What Have We Learned?

On-farm field days are a great tool to demonstrate and encourage the application of otherwise seldom applied techniques. They also can serve a dual purpose of demonstration and research, allowing for quality data collection if designed properly. Farmers’ collaboration and full participation during all phases of the project is paramount and pays off by having a very enthusiastic and collaborative partner. Identiying progressive and pioneer producers that are already applying new BMP or are willing to take the risk is very important to develop this kind of on-farm experience. In general these individuals are also willing to share their knowledge, experience, and results with others to increase the adoption of such techiques. Having a producer hosting and presenting during the field day, at their facilities (as opposed to a dedicated research facility) generates great enthusiasm from other producers and helps to “break the ice” and bring everybody to a friendly conversation and exchange of ideas if properly facilitated.

Future Plans

On both projects, a. manure collection and composting and b. manure injection we will generate a series of videos to demonstrate the proper application of BMP, and educational printed material will also be published. Project c. grape prunings and manure composting is still going on and we will finish collecting data by mid 2013. A second field day will be offered and videos and printed educational material will be developed. Project d. will see an expansion with a mortality composter for dairy calves being installed at a dairy, and with a field day following after the first compost batch is ready. Additional programs are in the works; these programs incorporate the on-farm demonstration and research dual purpose and have high participation from the involved producers.

Authors

Mario E. de Haro-Marti, Extension Educator, Gooding County Extension Office, University of Idaho Extension.  mdeharo@uidaho.edu

Lide Chen, Waste Management Engineer

Howard Neibling, Extension Irrigation and Water Management Specialist

Mireille Chahine, Extension Dairy Specialist

Wilson Gray, District Extension Economist

Tony McCammon, Extension Educator

Ariel Agenbroad, Extension Educator

Sai Krishna Reddy Yadanaparthi, Graduate student

James Eells, Research Assistant. University of Idaho Extension.

Acknowledgements

Projects a. and b. were supported by a USDA-NRCS Conservation and Innovation Grant (CIG). Project c. was supported by a USDA-NRCS Idaho CIG. Project d. was supported by a University of Idaho USDA-SARE mini grant. We also want to thank Jennifer Miller at the Northwest Center for Alternatives to Pesticides for her help and support with projects c. and d. Finally, we want to thank all producers involved in these projects for their support and openess to work with us, and for their innovative spirit.

 

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

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Effect of Manure Handling and Incorporation on Steroid Movement In Agricultural Fields Fertilized With Beef Cattle Manure

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Why Study Manure Land Application and Steroids?

Manure generated from concentrated animal feeding operations may serve as a source of steroids in surface water and adversely impact the development of aquatic ecosystems. The objectives of this research were to determine the amount of steroids and metabolites in manure from beef cattle production pens, and runoff from crop production fields.

What Did We Do?

Heifers were treated with zeranol, trenbolone acetate, and 17b-estradiol implants and fed melengestrol acetate, while a second group was not treated with growth promoters. Manure was sampled in the pens during feeding, run-off was collected during rainfall events, after feeding manure was collected, and either composted or stockpiled overwinter. In the  following summer both composted and stockpiled manure was spread on a field, with plots subjected three tillage practices. Following application, two rainfall simulation events were conducted: one day (1 DAT) and one month later (30 DAT) to determine the effects of rainfall timing, manure handling (treated compost, untreated compost, treated stockpile and untreated stockpile) and tillage (no-till, moldboard plow+disk and disk) on the runoff losses of steroids.

What Have We Learned?

Simulated rainfall apparatus.

Results from the manure composting showed reduction in steroid concentrations over stockpiling for some compounds in manure samples such as 4-androstenedione, a-zearalenol, and progesterone, though not for all steroids. Very low concentrations of steroids were found in most runoff samples, approaching or below detection limits. Considering only detection frequency, fewer runoff samples showed traces of steroids on the 1 DAT in comparison to the 30 DAT simulations.  The amount of  rainfall  before runoff was initiated was affected by tillage, and was different for the 1 DAT and 30 DAT events. A second year’s study with a smaller set of treatments, and use of a surrogate estrogen applied at known mass showed that disking significantly reduced runoff losses of the steroids. Runoff risk is affected by the storm event needed to initiate runoff, and also the time since manure application.

Soil during rain simulation and tube to take runoff to collection point.

Future Plans

From both the steroid runoff and general manure applications risk perspectives, how the soil receives rainfall changes during the first month after tillage. Therefore, this process needs to be investigated more closely and models predicting runoff have to take these changes into account.

Authors

Charles A. Shapiro, Professor, Department of Agronomy and Horticulture, University of Nebraska-Lincoln, Haskell Agricultural Laboratory, Concord, NE cshapiro@unl.edu

Sigor Biswas, Research Assistant, William L. Kranz, Associate Professor, David P. Shelton, Professor, Simon J. van Donk, Assistant Professor, Biological Systems Engineering; Daniel D. Snow, Associate Professor, Schol of Natural Resources; Shannon L. Bartelt-Hunt, Assistant Professor, Tian C. Zhang, Professor, Civil Engineering; Terry L. Mader, Professor, Animal Science, University of Nebraska-Lincoln; David D. Tarkalson, Soil Scientist, USDA-ARS, Kimberly-ID. 

Additional Information

Bartelt-Hunt, S., D. Snow, W. Kranz, T. Mader, C. Shapiro, S. van Donk, D. Shelton, D. Tarkelson, and T.C. Zhang. 2012. Effect of growth promotants on the occurrence of steroid hormones on feedlot soils and in runoff from beef cattle feeding operations. Environ. Sci. Technol. 46(3): 1352-1360.

Biswas, S., C. A. Shapiro, W. L. Kranz, T. L. Mader, D. P. Shelton, D.D. Snow, S. L. Bartell-Hunt, D. D. Tarkalson, S. J. van Donk, T. C. Zhang, S. Enslay. Current knowledge on the environmental fate, potential impact and management of growth promoting steroids used in the US beef cattle industry. J. of Soil and Water Cons. (In press, July 2013 issue).

Acknowledgements

This research was funded by US-EPA Science to Achieve Results (STAR) grant R833423.

 

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

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Quantification of Sodium Pentobarbital Residues from Equine Mortality Compost Piles

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*Abstract

Preliminary research has shown that sodium pentobarbital, a euthanasia drug, can persist up to 180 days in equine mortality compost piles. This experiment attempts to expand upon past research by quantifying pentobarbital residues in equine mortality compost piles over a longer duration using innovative sampling schemes. Six, 3.7 m2 plots were used to construct separate compost bins with 3 bins serving as control. Each bin was constructed with 1.2 m high horse panels. Soil samples were collected in each bin area. The carbonaceous material consisted of wood chips that were added at a depth of 0.46 m creating the base. Twenty-four whiffle balls, pre-filled with wood chips were placed on the center of each pad.  Nylon twine was tied to each ball for retrieval.

A licensed veterinarian provided six horse carcasses for use in the experiment.  These horses had required euthanasia for health reasons. All horses were weighed and then sedated with an intravenous injection of 8 ml of xylazine.  After sedation the three horses in the treatment group were euthanized by intravenous injection of 60 ml of sodium pentobarbital. The three control group horses were anesthetized by intravenous injection of 15 ml of ketamine hydrochloride and then humanely euthanized by precise gunshot to the temporal lobe. Following euthanasia, each carcass was placed on the center of the woodchip pad and surrounded with 0.6 m of additional wood chips. Serum and liver samples were immediately obtained while whiffle ball, soil and compost samples were obtained over time. Each sample was analyzed for pentobarbital residues. Compost pile and ambient temperatures were also recorded. Data illustrates pentobarbital persistence up to 367 days in compost piles with no clear trend of concentration reduction.

Why Be Concerned with Equine Mortality Management?

Equine mortality is an issue encountered by every horse owner. Mortality may be associated with disease, injury, age or a catastrophic event. For horses suffering from an incurable illness or injury, euthanasia is often the most humane option. The American Veterinary Medical Association (AVMA) approved methods for horse euthanasia include barbiturate overdose and captive bolt or gunshot to the temporal lobe (AVMA, 2007). Following mortality, the carcass must be properly disposed of according to local regulations. For many horse owners, carcass disposal options are limited and can be costly.  Improper disposal of animal carcasses can present potential environmental, animal and public health risks.

Recent interest has focused on the common euthanasia barbiturate, sodium pentobarbital, and its persistence in the animal carcass following euthanasia. In 2003 the FDA added environmental warning labels to euthanasia products containing pentobarbital in regards to proper carcass disposal (FDA, 2003). Barbiturates accumulate within the carcass and can cause sedation or death of animals that may consume the body (AVMA, 2007).

Questions exist regarding the potential environmental risk of improperly disposed animal carcasses following euthanasia with pentobarbital. It has been suggested that proper composting of animal carcasses euthanized with pentobarbital may degrade drug residues to negligible concentrations. However, preliminary research has shown that pentobarbital can persist up to 180 days in equine mortality compost piles (Cottle et.al, 2010). The researchers identified a need for controlled experiments investigating the persistence of sodium pentobarbital in animal carcasses during composting. The objectives of this experiment were to expand upon previous research by quantifying pentobarbital residues in equine mortality compost piles over a longer duration using innovative sampling schemes and to determine the efficacy of wood chips as a carbonaceous material for degrading equine carcasses.

Compost bin with pad.

What Did We Do?

Six, 3.7 m2 plots were used to construct separate compost bins. Each compost bin was constructed with 6.1 m x 1.2 m metal horse panels supported by 3 steel t-posts. The bulking agent for construction of compost piles consisted of hardwood chips that were wetted to approximately 50% moisture content. Bulking agent was added at a depth of 0.46 m creating the pad. Twenty-four whiffle balls pre-filled with wood chips were centrally placed on each pad.  Nylon hay twine was tied to each whiffle ball for retrieval during required sampling times.

A licensed veterinarian provided six horse carcasses for use in the experiment.  These horses had required euthanasia for health reasons. All horses were weighed and then sedated with an intravenous injection of 8 ml of xylazine.  After sedation the three horses in the treatment group were euthanized by intravenous injection of 60 ml of sodium pentobarbital (Beuthanasia-D, Schering-Plough Animal Health).  The three control group horses were anesthetized by intravenous injection of 15 ml of ketamine hydrochloride and then humanely euthanized by precise gunshot to the temporal lobe.

Compost bin after carcass placement.

Following euthanasia, each carcass was placed on the center of the woodchip pad and surrounded with 0.6 m of additional wood chips. Serum and liver samples were immediately obtained while whiffle ball, soil and compost samples were obtained over time. Each sample was analyzed for sodium pentobarbital residues. Compost pile and ambient temperatures were also recorded throughout the duration of the study.

What Have We Learned?

The findings from this experiment indicate that wood chips were effective at decomposing equine mortalities within 129 days of composting. Nearly all of the soft tissue was completely degraded with only large bones present. Compost temperatures met EPA class B biosolid standards for pathogen reduction. At day 367, sodium pentobarbital still persisted in the treatment group with no clear trend of concentration reduction from day 7 to day 367. Enveloping the carcass with carbonaceous material and constructing a barrier reduces the risk of secondary toxicosis from scavenging animals. Moreover, carcass degradation by composting followed by homogenous compost mixing allows for dilution of any remaining sodium pentobarbital residues.

Future Plans

Future research could focus on alternative livestock mortality management options and their impact on sodium pentobarbital residues.

Authors

Josh Payne. Ph.D. Area Animal Waste Management Specialist. Oklahoma State University.   joshua.payne@okstate.edu

Rodney Farris. Ph.D. Senior Research Station Superintendent. Oklahoma State University.

Gene Parker. D.V.M. Area Food/Animal Quality and Health Specialist. Oklahoma State University.

Jean Bonhotal. Director. Cornell Waste Management Institute.

Mary Schwarz. Extension Support Specialist. Cornell Waste Management Institute.

Additional Information

Managing Livestock Mortalities Link

Horse Mortality: Carcass Disposal Alternatives Link

Acknowledgements

Appreciation is extended to Ted Newell, Tommy Tucker, Robert Havener and Bobby Adams for their assistance with field work as well as Cheryl Ford for her assistance with data entry.

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

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Overview: Manure Management Equipment for Small Farms

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Why Be Concerned With Manure Management for Small Farms?

Increased local or regional food marketing opportunities have allowed commercial success in livestock and poultry operations with relatively small herds and flocks.  The Census of Agriculture recently reports an increase in the number of small farms, as a proportion of all farms, across much of the U.S.  Small animal feeding operations, less than 300 animal units, are a productive component of the animal ag sector.  Finally, there continues to an interest in the development of hobby farm and equine related properties.  All of these scenarios result in the necessity to manage manure resources, often on small acres, and often in close proximity to a neighbor.  Knowledge about, access to, and acquisition of, appropriate manure handling equipment is a requirement to proper manure and nutrient management on all of these types of commercial or hobby farms and ranches.

What Did We Do?

This overview seeks to provide examples of power equipment and manure handling tools appropriate to smaller operations.  An emphasis is placed on solid manure handling, small acreage land application, and light duty compost production equipment.  Examples of equipment choices and options are based on Internet and literature reviews, as well as personal field experiences.

What Have We Learned?

A balance between size/power, cost, and versatility must be considered when purchasing or leasing equipment for small livestock and poultry operations.  Smaller operations often deal only in solid manure. This can simplify equipment choices to small tractors and skidsteer loaders, which can perform a variety of manure management and compost related tasks.  Tractor size will limit traditional manure spreader options.  However, several manufacturers are now offering light weight, ground drive spreaders, towable by small tractors or even ATVs.  

Authors

Thomas M. Bass, Livestock Environment Associate Specialist,  Montana State University tmbass@montana.edu

Acknowledgements

Mike Westendorf, Rutgers University and Jean Bonhotal, Cornell University

 

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

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Equipment and facilities for managing manure on small farms

The number of small farms is increasing in much of the country, ensuring up to date information is available is important to protect water and environmental quality. This webinar focuses on some of the farm and manure management needs of smaller farms. This presentation was originally broadcast on April 20, 2018. More… Continue reading “Equipment and facilities for managing manure on small farms”

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Avian Influenza Mortality Management Options, Composting Procedures and Lessons Learned

This presentation outlines mortality management options during an animal disease outbreak and highlight the composting methodology implemented on poultry operations during the HPAI outbreak, as well as the successes, challenges and lessons learned. This presentation was originally broadcast on February 17, 2017. More… Continue reading “Avian Influenza Mortality Management Options, Composting Procedures and Lessons Learned”

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