Natural Resource Conservation Service (NRCS) Manure Related Conservation Innovation Grants (CIG)

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Abstract

A number of the manure related Conservation Innovation Grants (CIG) have been successful.  Several feed management related projects have been major successes under the CIG program.  Other successful projects have dealt with such technologies as anaerobic digesters; community digesters; environmental credit trading; lagoon management; manure to energy generation; alternative litter sources, storage, and handling; and pathogen, odor, and emissions mitigation, to name just a few. 

The presentation will provide specific numbers of projects and funding per year, and information about actual projects that NRCS considers to have been successful. 

What Is the Purpose of the CIG Grant Program?

Glenn Carpenter came to Natural Resources Conservation Service as a Senior Economist in December of 2001 with the Animal Husbandry and Clean Water Division.  In May, 2004 he became the agency’s National Leader for Animal Husbandry, with that Division.  In 2010 his position was moved to the Ecological Sciences Division.  Much of his work with NRCS has been related to the animal waste issue and the agency’s interaction with EPA over the CAFO Rule. 

Glenn has three degrees in Poultry Science from Michigan State University.  Prior to joining NRCS, Glenn served in Extension Poultry positions at two universities.

The 2002 Farm Bill created a mechanism under the Environmental Quality Incentives Program (EQIP) for a program of Conservation Innovation Grants (CIG).  These grants were “…intended to stimulate innovative approaches to leveraging Federal investment in environmental enhancement and protection, in conjunction with agricultural production…”  The grants were to provide a mechanism for funding projects to aid in technology development and transfer.    The granting program actually began in 2004, and has continued since that time.

What Did We Do?

By statute, the USDA Natural Resources Conservation Service cannot do research.  Because of this, and because the interest of NRCS lies in directly assisting farmers and ranchers in the adoption of technologies that will benefit conservation, projects funded under this program must be in the field demonstration or tool application stages.  Since the initial grant funding cycle in 2004, NRCS has provided funding through EQIP every year.  To date nearly 500 grants have been awarded, with total funding in excess of $180 million. 

A large share of these CIGs has been strongly animal, and/or manure related.  Almost 25 percent of the total number of grants has been animal related, and these grants have received slightly over 26 percent of the total dollars.  About 19 percent of the total grants have been manure related and these have received about 22 percent of the funding.  Those animal related grants that are not manure related largely deal with range and pasture systems.

What Have We Learned?

Several feed management related projects have been major successes under the CIG program.  Other successful projects have dealt with such technologies as anaerobic digesters; community digesters; environmental credit trading; lagoon management; manure-to-energy generation; alternative litter sources, litter storage, and handling; and pathogen, odor, and emissions mitigation from manure, to name just a few. 

The number and variety of funded projects has covered a wide range of geographic areas and technical  innovations.  A multistate feed management project resulted in training programs, a tech note for NRCS, and many fact sheets and other materials that are available on Livestock and Poultry Environmental Learning Center webpage.   Another major grant demonstrated the effectiveness of filter strips and other vegetated treatment areas on mitigating manure runoff from cattle feedlots.  Utilizing high pressure injection of manure, a Pennsylvania project demonstrated a decrease in odor and runoff while also preserving nitrogen.  Several projects have successfully demonstrated the effects of precision feeding of dairy cattle to show the change in manure nutrients.  Projects have demonstrated the effectiveness of different tillage systems and technologies on manure nutrient runoff.  Other projects have dealt with innovative waste-to-energy technologies, or waste to value-added-product creation.   These are just a few of the number and variety of projects funded  through the Conservation Innovation Grants program.

Future Plans

The success of the CIG program since 2004, both in numbers of projects and in innovative technologies and tools applied, demonstrates that the program is important to agriculture in the U.S.  NRCS has shown its support by continually funding the program, and by making additional moneys available for special targeted CIGinitiatives.

Authors

Glenn H. Carpenter, National Leader, Animal Husbandry, USDA Natural Resources Conservation Service glenn.carpenter@wdc.usda.gov

Gregorio Cruz, CIG Program Manager, NRCS, Rosslyn, VA;  William Reck, Environmental Engineer,  NRCS, Greensboro, NC;  Jeffrey Porter, Environmental Engineer, NRCS, Greensboro, NC; Cherie Lafleur, Environmental Engineer, NRCS, Ft Worth, TX; Sally Bredeweg, Environmental Engineer, NRCS, Portland, OR; Harbans Lal, Environmenal Engineer, NRCS, Portland, OR; Greg Zwicke, Environmenatl Engineer, NRCS, Ft Collins, CO

Additional Information

NRCS Conservation Innovation Grant webpage at:  http://www.nrcs.usda.gov/wps/portal/nrcs/main/national/programs/financial/cig/

Acknowledgements

United States Department of Agriculture, Natural Resources Conservation Service, Conservation Innovation Grants Program

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.

 

Fate of Barbiturates and Non-steroidal Anti-inflammatory Drugs During Carcass Composting

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Why Are We Concerned About Drug Residues in Animal Mortality Compost?

With disease issues, the decline of the rendering industry, a ban on use of downer cows for food, and rules to halt horse slaughter, environmentally safe and sound practices for disposal of horses and other livestock mortalities are limited. Improper disposal of carcasses containing veterinary drugs has resulted in the death of domestic animals and wildlife. Composting of carcasses has been performed successfully to reduce pathogens, nutrient release, and biosecurity risks. However, there is concern that drugs used in the livestock industry, as feed additives and veterinary therapies do not degrade readily and will persist in compost or leachate, threatening environmental exposure to wildlife, domestic animals and humans.

Two classes of drugs commonly used in the livestock and horse industries include barbiturates for euthanasia and non-steroidal anti-inflammatory drugs (NSAID) for relief of pain and inflammation. Sodium pentobarbital (a barbiturate) and phenylbutazone (an NSAID) concentrations in liver, compost, effluent and leachate were analyzed in two separate horse carcass compost piles in two separate years. Horse liver samples were also buried in 3 feet of loose soil in the first year and drug concentrations were assessed over time.

What did we do?

Year 1- On 9/22/09 a 6 x 6 m piece of 10 mil plastic sheeting was laid on bare soil with a 2% slope, at the edge of Cornell University’s compost site in Ithaca, NY. Water was poured on the plastic to check the direction of flow. A hole was dug at the low end of the pad, under the plastic, large enough to fit a 76 l galvanized garbage can. A stainless steel canner was placed in the garbage can to collect effluent. A hole was cut in the plastic over the canner for collection. A 0.6 m high base (3.7 x 3.7 m) of coarse carbon material (woodchips) was laid on the plastic. A 27 year old Appaloosa mare, weighing approximately 455 kg that had been dosed with 1 gram phenylbutazone at midnight on 9/22/09 and again at 8:00 am was led onto the base and euthanized for severe lameness by a qualified veterinarian with 120 ml Fatal Plus® solution (active ingredient 390 mg/ml Pentobarbital Sodium). After the horse had been euthanized and the veterinarian ensured there were no signs of life, the carcass was maneuvered onto the wood chips with the head on the upward slope of the pad. The liver was removed from the horse and cut into 48 pieces, each weighing approximately 100 grams, and nylon mesh bags were then placed in whiffle balls. A 2 m length of nylon twine was attached to each ball. Twenty-three balls were inserted in the horse’s gut cavity and 22 balls were placed in a 1 m hole in the ground (burial hole) which was dug approximately 1.5 m from the pad. Pieces of the intestine and some blood were also placed in the hole to help mimic the presence of a carcass. The remaining 3 nylon mesh bags with liver were packaged for delivery to Cornell University’s Animal Health Diagnostic Center (AHDC) to determine initial NSAID and barbiturates concentrations. Two Hobo U12 data loggers with 4 temperature probes each were set up to record hourly temperatures. Five of the probes were placed in the compost pile: under the horse’s chest, in the horse’s hind gut, in the horse’s chest cavity, under the horse’s spine and under the horse’s right hind quarter. Two of the probes were placed in the burial hole and one probe was left out to record ambient temperature. The hole was covered with loose soil. The horse was covered with woodchips so that the pile was approximately 1.8 m high. The plastic liner was tightened by rolling it over and under wooden fence posts.

Year 2- In year 1, the collection of “leachate” included precipitation that diluted the leachate. In year 2, to target only the liquids that leached out of the horse and through the pile, two 3 m long troughs with a 1% slope were built out of 15 and 10 cm diameter PVC pipe attached to 5 x 15 cm untreated lumber. The troughs were placed on the pad from the centerline to the edge of the pile end-to-end with slopes going toward the outside of the pile. Leachate drained via gravity into 2-liter polyethylene bottles attached to the troughs. The exposed ends of the troughs were covered with 1 m length of aluminum flashing to keep rainwater out of the collection bottles.

On 8/10/10 the leachate collection troughs were laid on bare soil with a 2% slope at the edge of Cornell University’s compost site in Ithaca, NY. A 0.6 m high base (3.7 x 3.7 m) of coarse carbon material (woodchips) was laid on top of the troughs. A 22 year old horse weighing approximately 590 kg, that had been dosed with 1 gram phenylbutazone at midnight on 08/10/10 and again at 7:30 am, was led onto the base and euthanized by a qualified veterinarian with 300 mg xylazine as a sedative, then with 120 ml Fatal Plus® solution (active ingredient 390 mg/ml Pentobarbital Sodium). After the horse had been euthanized and the veterinarian ensured there were no signs of life, the carcass was maneuvered on the wood chips with the head on the upward slope of the pad. The veterinarian took 4 tubes of blood from a vein in the nose and a vein in the front leg of the horse in heparinized Vacutainer® tubes for initial concentrations of pentobarbital and phenylbutazone. Twenty-six whiffle balls that had been pre-filled with wood chips (the base material of the compost pile) were placed such that they would be under the horse and liquids coming from the horse would be absorbed by the chips inside the balls, as well as in the surrounding base material, while the excess would drain down the leachate collection troughs and be captured in the 2 liter bottles at the end of the troughs (Figure 1). One Hobo U12 data logger with 4 temperature probes was set up to record hourly temperatures. The probes were placed under the horse’s neck and rump, on top of the horse’s abdomen, and one was left out to record ambient temperature. The horse was covered with woodchips so that the pile was approximately 1.8 m high. Additional woodchips were added to the pile on August 13 and the pile was covered with a breathable polyester compost cover to collect only what was leaching from the animal.

Figure 1 Cross-section of horse compost pile showing placement of leachate collection troughs and woodchip-filled whiffle balls.

On 8/10/10 a 0.6 m high base (3.5 x 3.5 m) of coarse carbon material was laid near the horse compost pile. A 455 kg 3 year, 7 month old, 2nd lactation Holstein cow was euthanized, due to a lung abscess, in the same manner as the horse (300 mg xylazine, followed by 120 ml Fatal Plus®). Four tubes of blood were withdrawn from her milk vein as described for the horse. One Hobo U12 data logger with 4 temperature probes was set up to record hourly temperatures. The probes were placed under the cow’s udder and rear leg, on top of the cow’s back, and one was left out to record ambient temperature. The cow was then covered with woodchips so that the pile was approximately 1.8 m high. Additional woodchips were added to the pile the following day before the pile was covered with a compost cover.

What did we learn?

In year one, phenylbutazone concentrations in the liver of the horse were undetectable (< 10 ppb) by 20 days of composting or burial in loose soil and were undetectable in effluent from the pile at the time of first sampling on day 6. Pentobarbital concentrations were undetectable (< 10 ppb) in liver samples retrieved from both the compost pile and loose soil by day 83. Rate of decay was faster in the soil, exponentially decreasing by 18% per day, with a half-life of 3 days, than in the compost pile where there was a 2% decrease per day and a half-life of 31 days, but occurred at the same rate of 1% and a half-life between 55 and 67 mesophilic degree days when calculated on the number of mesophilic degree days to which it was exposed. This suggests that breakdown of pentobarbital is not initiated by the heat of composting, but by the biological degradation that occurs in both soil and compost at mesophilic temperatures. Pentobarbital in the effluent decreased by 20% per day with a half-life of 3.1 days but was still detectable (0.1 ppm) at 223 days of composting.

In year 2, phenylbutazone was not detected in any of the samples analyzed (compost and leachate) other than blood taken from the jugular vein of the horse immediately after euthanasia. Pentobarbital concentrations in the compost were still detectable after 224 days of composting, but had decreased from 79.2 (initial) to 5.8 ppm. Pentobarbital in leachate was 2.2 ppm at day 56 of composting, after which no additional fluids leached into the leachate collection containers.  Rate of decay in the leachate was 35.2% per day with a half-life of 1.6 days. When managed properly, composting will deter domestic and wild animals from scavenging on treated carcasses while they contain the highest drug concentrations providing an effective means of disposal of euthanized and/or NSAID treated livestock. The resulting compost contains either no or very low concentrations of both NSAIDs and barbiturates rendering it safe for use in agriculture.

Barbiturate poisoning in domestic and wild animals has occurred from ingestion of tissue from animals euthanized with pentobarbital. Many of the reported cases have occurred from direct feeding on improperly disposed livestock in which little or no degradation or biotransformation of pentobarbital has occurred.  During the time period in which carcasses would be desirable to domestic and wild animals as a food source, composting creates sufficient heat to deter them from digging in to the pile. In addition, when covered properly, the smell of decomposition is minimized, also reducing attraction. The diverse community of microorganisms in the compost pile aids in the degradation and biotransformation of pentobarbital, especially after the thermophilic phase of composting is over. Properly implemented composting, as a means of disposal of euthanized or NSAID treated livestock, will deter domestic and wild animals from scavenging for carcasses when they contain the highest drug concentrations. The resulting compost contains either no or very low concentrations of either NSAIDs or barbiturates, rendering the compost safe for use in agriculture.

Future Plans

Education and implementation work continues in this area nationally and internationally. A 5th International Symposium on Depopulation and Disposal of Livestock is in the planning stages. A study on the Fate of anthelmintics (drugs that expel parasitic worms from the body) in livestock manure has just been completed.

Authors

Jean Bonhotal,  Mary Schwarz,  Cornell University, Cornell Waste Management Institute, Ithaca, NY

Karyn Bischoff, Joseph G Ebel, Jr. Cornell University, College of Veterinary Medicine, Ithaca, NY

Additional Information

Visit Cornell Waste Management Institute Web site: http://cwmi.css.cornell.edu/mortality.htm

Trends in Animal & Veterinary Sciences Journal article http://cwmi.css.cornell.edu/fate.pdf

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.

Can I Use Rendering As an Option For Managing Animal Mortalities?

There are many options available for disposing of livestock and poultry carcasses. Rendering is an option in areas where the service is offered, but has some limitations on the type of animals they will pick up.

Check out the other video FAQs on carcass management.

Author: Joshua Payne, Oklahoma State University

Reviewers: Shafiqur Rahman, North Dakota State University and Jean Bonhotal, Cornell University

 

What Should I Do With Compost That Includes Animal Mortalities?

Compost containing animal carcasses should probably be utilized on crops that are not meant for human consumption for a couple of different reasons.

Disposal of the end product with regard to roadkill compost…we use it on the roadsides and plant vegetation on the roadsides.

With [farm] mortality compost, we want to be careful about where we are putting cows and chickens because we are using it back on the farm. So we may want to remove the large bones [and reuse them as part of the base for the next mortality compost pile]. We do not want to puncture any tires. But the bones do get pitted and will start breaking apart after a couple of cycles of the composting process. We do not want to use this on food crops. We may prefer to use this on field crops where the soil is tilled. We can apply the compost and then till it in. Definitely use it on crops that are harvested above the ground…corn and things like that. Do not use [mortality compost] on root vegetable or on things where we risk contamination if there is a problem.

Mortality compost can also be used in forested areas.

Author: Jean Bonhotal, Cornell University

Why Is It Important To Manage Animal Mortalities Properly?

Improperly disposed livestock or poultry carcasses represent a threat to water and air quality.

Proper management of on-farm animal mortalities is vital to every farming operation. Improper disposal of dead animal carcasses can negatively impact surface water and groundwater from carcass leachate. If the animal died of an infectious disease, pathogenic bacteria and viruses may be present within the carcass. These pathogens can be spread by insects, rodents, preda­tors, and subsurface or above ground water movement, as well as through direct contact with other livestock or poultry leading to increased disease transmission risks. Furthermore, many states have rules regulating the proper disposal of livestock and poultry mortalities. Therefore, the purpose of proper mortality disposal is to prevent the spread of infectious, contagious and communicable diseases and to protect air, water and soil quality. Note that regulated AFOs must abide by their animal mortality disposal plan outlined in their nutrient management plan.

Check out the other video FAQs on carcass management

Author: Joshua Payne, Oklahoma State University

Reviewers: Shafiqur Rahman, North Dakota State University and Jean Bonhotal, Cornell University

What Are Common Animal Mortality Disposal Options

Managing dead animals is not pleasant, but is a necessary task for most livestock and poultry farms. This video discusses several options for disposing of carcasses in an environmentally responsible manner.

In most states, commonly approved disposal options include: burial, landfills, incineration, rendering and composting.

Burial

Perhaps the most common method of disposal is burial. Most states have regulatory burial guidelines outlining site location, distance from waterways, depth to groundwater, etc. When proper guidelines are followed, burial is a safe option. However, poor site selection, such as sandy soils or areas with high water tables, may pose a threat to groundwater. Furthermore, burial does not convert the carcass into a valuable by-product. Variable equipment and labor costs will influence the economic viability of this disposal option.

Landfills

Disposing of carcasses at a licensed landfill that accepts animal mortalities is another form of burial. Landfills may require notification before delivery and/or documentation from a licensed veterinarian stating the cause of death. Landfill tipping fees should be assessed and may range from $20 to $30/ton. Other considerations are transportation costs and breeches of biosecurity by moving carcasses off- farm. Similar to burial, a valuable by-product is not produced.

Incineration

Incineration is a safe and effective means of carcass disposal, especially from the standpoint of biosecurity. The carcass is completely consumed by fire and heat within a self-contained incinerator utilizing air quality and emissions controls. Some states may require air quality permits. Incineration is mainly designed for smaller carcasses and fuel costs should be considered. Due to odor and emission concerns, open air incineration (burning) is not recommended and banned in some states. Furthermore, obtaining complete consumption of the carcass in a timely manner is often difficult to achieve. Burning should only be used in emergencies for controlling infectious or contagious diseases with permission from a regulatory body.

Rendering

Another recommended carcass disposal method is rendering. This is a heat driven process that cooks the product while killing pathogens and converting it into a value-added product such as an animal feedstuff. These feedstuffs, such as meat and bone meal, are generally used as pet food ingredients. Although rendering is a very effective method, currently, there are few render­ing services available. The transportation expense of collecting small volumes creates a financial obstacle for most rendering companies. Some rendering facilities require the producer to transport carcasses to the plant and pay a fee. Biosecurity and disease transmission risks should be considered when allowing vehicles on the farm and when transporting carcasses off-farm.

Composting

Composting dead animal mortalities is an inexpen­sive, biosecure and environmentally sound approach to addressing the issue of carcass disposal. By definition, composting is a controlled biological decomposition pro­cess that converts organic matter into a stable, humus-like product. The carcass (nitrogen source) is buried in a bulking agent (carbon source), such as wood shavings, allowing for the proper carbon to nitrogen ratio (C:N) required by microorganisms to successfully decompose the carcass while absorbing excess moisture and filtering odor. The high temperatures achieved through proper composting will destroy most pathogens. Microorganisms will degrade the carcass leaving only a few small bone fragments, which are brittle and break easily. This valuable by-product can then be land-applied as a fertilizer source, adding nutrients and organic matter to the soil or recycled for new compost piles. As with burial, site selection is important. The site should be located in an area that does not pose a risk to surface or groundwater contamination.

Alternative methods:

Alternative methods are not specifically defined. They may include homogenization, digestion or chemical processes and technologies to recover products from mortalities.

 

Check out the other video FAQs on carcass management

Author: Joshua Payne, Oklahoma State University

Reviewers: Shafiqur Rahman, North Dakota State University and Jean Bonhotal, Cornell University

How Can I Manage Multiple Animal Mortalities?

Sometimes, a disease outbreak or natural disaster results in many livestock or poultry carcasses that must be managed. Disposal of these requires additional planning to ensure this is done in an environmentally responsible manner.

During catastrophic events when multiple livestock losses occur, a producer’s routine mortality disposal plan may be inadequate. In these instances, multiple disposal options may need to be considered. Burial, rendering, landfills, composting and incineration or a combination thereof are recommended options. All catastrophic events should be reported to the appropriate state agency. If a catastrophic mortality event is the result of disease outbreak, bio-security considerations may dictate the method of transportation and disposal.

Check out the other video FAQs on carcass management

Author: Joshua Payne, Oklahoma State University

Reviewers: Shafiqur Rahman, North Dakota State University and Jean Bonhotal, Cornell University

Why Do Animal Carcasses Need Proper Disposal (and Should Not Be Abandoned)?

Abandoning animal carcasses and allowing scavengers to dispose of them is risky.

Though dragging off a carcass to the boneyard has been a historical practice, abandonment is NOT recommended and is likely ILLEGAL in most states. Examples include: carcasses abandoned on the surface, in open pits, ditches, water features and sinkholes or in wells. Abandonment promotes extreme biological and disease hazard, threats to water quality, odors, flies, scavengers, rodents and visual pollution.

Check out the other video FAQs on carcass management

Author: Joshua Payne, Oklahoma State University

Reviewers: Shafiqur Rahman, North Dakota State University and Jean Bonhotal, Cornell University

Livestock and Poultry Mortality Management Frequently Asked Questions (FAQs)

Scroll through the slideshows below to see many of the frequently asked questions (FAQs) about managing animal carcasses. After each question you can play a short (1-2 minute) video or scroll to the next question. Also see the page “Managing Livestock and Poultry Mortalities“. This series of short (<2 minutes each) videos is also gathered into playlist on YouTube.

Options to Dispose of Livestock and Poultry Carcasses

Options for Managing Animal Mortalities

No farmer or ranch likes to lose an animal, but the need to dispose of livestock or poultry carcasses is an inescapable part of farming.

Storified by LPE Learning Center · Thu, Oct 04 2012 09:09:17

Why Is It Important to Manage Animal Mortalities Properly?
FAQ(v): Why is proper livestock disposal important?lpelc
What Are the Options for Animal Mortality Management?
FAQ(v): What are some common animal mortality disposal methods?lpelc
Animal Mortality Composting
FAQ(v): What is animal mortality composting?lpelc
Burial of Dead Animals
FAQ(v): Is Burial an Option for Managing Animal Mortalities?lpelc
Rendering Animal Mortalities
FAQ(v): Can I use rendering as an option for livestock mortalities?lpelc
Incineration For Managing Animal Mortalities
FAQ(v): Can I use incineration as an option for livestock mortalities?lpelc
Land Fills As An Option for Animal Carcasses
FAQ(v): Can I use landfills as an option for livestock mortalities?lpelc

Composting Animal Mortalities

Composting Animal Mortalities

One option for managing livestock or poultry carcasses is composting. What are some of the most frequently asked questions when people first consider composting dead animals?

Storified by LPE Learning Center · Thu, Oct 04 2012 09:31:49

What Is Animal Mortality Composting?
FAQ(v): What is animal mortality composting?lpelc
Why Should I Consider Composting Animal Mortalities?
FAQ(v): Why should I consider composting livestock mortalities?lpelc
How Long Does Animal Mortality Composting Take?
FAQ(v): Approximately how long does livestock or poultry mortality composting take?lpelc
Economics of Composting Livestock Mortalities
FAQ(v): How much does livestock mortality composting cost?lpelc
What Are the Materials Needed for Composting Livestock or Poultry Mortalities (C:N Ratio, Moisture, etc.)?
FAQ(v): What are the necessary materials for composting livestock mortalities?lpelc
What Carbon Source Should I Use For Composting Livestock Mortalities?
FAQ(v): What carbon source can I use to compost animal mortalities?lpelc
When Should You Turn a Compost Pile Containing Animal Mortalities?
FAQ(v): How do you know when to turn the livestock mortality compost pile?lpelc
Will Odors Be a Problem When I Compost Animal Carcasses?
FAQ(v): Is odor a concern when composting livestock mortalities?lpelc
Will Scavengers Be a Problem When I compost Animal Carcasses?
FAQ(v): Are scavenger animals a concern when composting livestock or poultry mortalities?lpelc
Can I Compost Dead Animals In the Winter?
FAQ(v): Can you compost livestock or poultry mortalities in the winter?lpelc
Do the Bones Break Down When Composting Carcasses?
FAQ(v): Do the bones break down? If not, what should I do with them?lpelc

Catastrophic Mortality Management

Catastrophic Mortality Management

Sometimes fires, natural disasters, disease, or other problems unfortunately result in the loss of large numbers of livestock. If you do not plan ahead, you could be overwhelmed if this situation occurs for you.

Storified by LPE Learning Center · Thu, Oct 04 2012 10:42:04

What Happens If I Have Multiple Animal Mortalities?
FAQ(v): What if I have multiple livestock mortalities?lpelc
Composting Catastrophic Poultry Mortalities Using the Mix and Pile Method
Composting Catastrophic Poultry Mortalities In-House Using the Mix and Pile Methodlpelc
Composting Catastrophic Poultry Mortalities in Outdoor Windrows
Composting Catastrophic Poultry Mortalities in Outdoor Windrows.mp4lpelc

Related Information

  • eXtension: Managing Livestock and Poultry Mortalities
  • June, 2009 webcast presentation on Managing Livestock Mortalities Discusses regulations and an overview of several methods with an emphasis on composting.
  • LPES Curriculum Mortality Review
  • Question #27119, What is animal carcass composting? link
  • Question #27787, How critical are carbon to nitrogen ratios (C:N) in large carcass mortality composting? link
  • Question #27171, Should we be concerned about E. coli O157:H7 in manure compost? link
  • Question #27172, By what factor does composting manure reduce the pathogens present? link

Author: Joshua Payne, Oklahoma State University

Reviewers: Shafiqur Rahman, North Dakota State University and Jean Bonhotal, Cornell University