Costs of Slurry Manure Application and Transport

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Manure Value and Economics

Livestock such as dairy and swine often have slurry type manure. The manure is liquid but does not flow easily. It is either stored directly below the animal pens, or scraped or pumped periodically into a holding pen outside of the building.

Loading Slurry Manure

Loading slurry manure is accomplished with a pump powered by a tractor or stationary engine. The slurry can be loaded into tractor-pulled or truck-mounted tankers, or pumped through a hose attached to a tractor that applies it as it is being pumped from the pit. The cost of loading slurry is usually low because the pump can do it quickly and the volume per animal is not usually high.

Slurry Manure Transport

Transportation of slurry by tanker can be expensive because a lot of water is being transported and the same equipment that is hauling the slurry is usually land applying the slurry. When tankers are used, the number of hours spent transporting the slurry is frequently the limiting cost. The land may become unavailable to receive the slurry, due to crop planting times or soil conditions, before all of the slurry can be land applied. Often, the distance transported is limited so that the time constraints can be met.

If the slurry is pumped through a hose to the field, the transport time is negligible. As the slurry is pumped, it is simultaneously injected or surface applied to the land. The important cost becomes the cost of purchasing pipe and hose that is sufficient for this method of land application.

Land Application of Slurry Manure

The cost of land application of slurry varies with the type of equipment used. Tankers can be expensive to own unless they are used for many animals on many acres. There is a definite economy of scale with tankers. Additionally, the tankers usually require fairly large tractors or trucks. If the livestock owner does not have a cropping enterprise that requires the large tractor, ownership of the tractor for manure distribution alone becomes expensive.

Tankers are economical for large-scale operations with slurry manure.

When slurries are applied via hoses (called dragline hoses), a tractor pulled distributor is used to move the hose around the field so that the slurry is evenly distributed. The cost of the equipment can be very expensive, but the amount of time is decreased considerably compared to using tankers because most of the time is spent in applying the slurry. Very little time is spent getting into and out of the field, as is the case when using tankers.

Authors: Ray Massey, University of Missouri and Josh Payne, Oklahoma State University

Costs of Liquid Manure Application and Transport

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What Systems Produce Liquid Manure?

Liquid manures are most common with pork production where the manure is flushed from the building and stored outside in lagoons. Liquid manures are mostly water with some organic matter and nutrients suspended in the water. Most of the organic matter decomposes in the lagoons and is not removed.

Options to Haul and Apply Liquid Manure

While some livestock producers haul liquid manure in tankers, it is usually considered cost prohibitive. The amount of water is so great that the hours spent distributing it and the resulting dollar cost exceeds the value of the manure supplied nutrients when using tankers.

Liquid manure is usually pumped through pipes and hoses to the land that will be accepting the manure. This means that loading costs and transportation costs are relatively low. Once the manure is at the field, it can be applied with a tractor that pulls the dragline hose through the field or via an irrigation system. The irrigation system can be a stationary sprinkler or a single big gun sprinkler that must be moved periodically by the operator.

Liquid manure can be land applied with a dragline hose.

Other options include, a big gun sprinkler or a center pivot irrigation system that move automatically through the field. The center pivot irrigation system is usually too expensive to own just for liquid manure distribution; it is usually part of an irrigation system that also pumps clean water. The stationary and big gun sprinklers are inexpensive and easy to use.

Authors: Ray Massey, University of Missouri and Josh Payne, Oklahoma State University

Nutrient Planning on Small Farms

livestock and poultry environmental learning center logo with cow, pig, and chicken sillhouettes over a map of the U.S. with three circling arrowsThe LPE Learning Center hosted a webcast on Nutrient Planning on Small Farms in June, 2008.

Positive Impacts of Manure

When managed properly, manure can be a valuable resource on a farm. Manure can be a source of nutrients for crop production and improve soil quality. The organic matter present in manure can improve both tilth and water holding capacity of the soil. Livestock and poultry manure is a valuable fertilizer for crop and pasture production. Most farm owners do not realize the value of the manure that is produced on their farms.

Negative Impacts of Manure

When not managed properly, manure can pollute the environment; mainly as ground or surface water pollution due to the nutrients nitrogen (N), phosphorus (P), and carbon (organic matter). In addition manure can lead to air quality concerns, pathogens in water supplies, odors, dust, and the presence of vermin.

Manure Nutrients

Manure nutrients can be beneficial for the soil and plant growth; however, manure application rates should be based on plant growth needs. Excessive manure application to the soil can result in nutrient leaching and increased losses through runoff. In addition, manure contains soluble salts and minerals such as arsenic, copper, and zinc which in excessive amounts may negatively impact the soil quality.

Manure nutrients, (N, P, and organic matter) can be major pollutants in lakes and estuaries as well as rivers. Nitrogen and phosphorus attached to soil particles may reach waterways through surface runoff or wind deposition. Dissolved N and P may leach through the soil, ultimately reaching water bodies. Organic matter can enter water bodies in the form of manure, vegetative matter, or animal carcasses. Waters rich in minerals, organic matter, and nutrients promote a proliferation of plant life, especially algae. This process is called eutrophication. Algae growth and the decomposition of organic matter in water bodies reduces the dissolved oxygen content of the water, which may lead to the death of aquatic life.

Pathogens and Vermin

In addition to the concerns regarding nutrients, pathogens may be present in manure. Some examples of the pathogens are E. coli, Salmonella, and Cryptosporidium parvum. These pathogens can impair water bodies and potentially pose human health risks when manure or contaminated water comes in contact with food sources. Flies and rodents are other manure related concerns on livestock farms. These problems can be minimized by proper design of animal housing and manure storage, and proper handling procedures when turning or moving manure piles.

Air Quality

Air quality concerns arise from odors, particulate matter, and aerial pathogens. Ammonia released from manure can result in odor and may react with other compounds in the atmosphere producing particulate matter (PM 2.5) which can affect the environment and public health. There are a variety of other compounds released from manure such as hydrogen sulfide, green house gases (methane and nitrous oxide), and some volatile organic compounds that can also cause air quality concerns. Particulate matter that arises from dust and reaction of ammonia with other compounds in the atmosphere are also a concern.

Why Implement Nutrient Management Planning?

The purpose of nutrient management is to implement practices that permit the efficient use of manure for crop production while protecting potential environmental damage that may be caused by nutrients. Nutrient management planning is a site specific exercise; and, if the recommendations are followed, nutrient losses should be minimal. In general, nutrient management considers the nutrients available on a farm, how best to use them, and the potential impacts of the nutrients on the environment. Factors typically considered in nutrient management planning are: goals of the farming operation as well as any constraints; available farm resources (land, equipment, financial resources); potential critical areas on the farm (sensitive water bodies, neighbor concerns, erosion, manure storage); and nutrient balance analysis (shown in the figure below).

 

Recycling

CC2.5 Mike Westendorf

Farm nutrient inputs consist of animals, feed, fertilizer, legume nitrogen, and bedding. Outputs are animals, milk, meat, eggs, manure, and crops. Recycling also occurs on the farm with nutrients moving from feed through livestock, applied to soil, utilized by plants, and back to feed again. The optimal goal (Whole Farm Nutrient Balance) is for the farm to remain in balance between inputs and outputs without losses as runoff or leachate from either the soil or manure. Soil can store some nutrients assuming that the amount of manure applied to the soil is not excessive.

 

Small Farms are Different than Large Farms

The challenges of managing manure nutrients are different on a small farm than on many larger farms although the principles are similar. Small farms have fewer animals and sometimes several animal species on the same farm. They also may have limited acreage and/or lack equipment for spreading manure. The nutrient management planning section provides information on feeding animals and managing their diets; manure production; basic soil science and soil fertility; and nutrient (manure) management. The section details on- and off-farm use within the context of a nutrient management plan.

The following articles are coming soon!

  • Basic soil science and fertility
  • Nutrient management on the farm
  • Crop utilization
  • Nutrient management plans
  • Off-farm utilization
  • Soil and manure testing
  • Record keeping

Additional Resources

Nutrient Management–SIMPLIFIED! by Randall James, Ohio State University Extension

Authors: Jactone Arogo Ogejo, Virginia Polytechnic Institute and State University (Virginia Tech) and Michael Westendorf, Rutgers, The State University of New Jersey

Managing Dietary Phosphorus for Livestock and Poultry

Phytate Phosphorus

Phosphorus is required in the diet of animals, but if overfed or wasted, can contaminate the environment and water supplies. Cereal grains fed to livestock contain phytate-bound phosphorus. Phytate-bound phosphorous is digestible by ruminant animals such as cows, sheep, and goats, but it cannot be digested by single-stomached animals, such as pigs and chickens. Phytate consists of a carbon ring structure with balanced phosphate groups surrounding the ring. Since horses are a hind gut fermenter, they are able to process the phosphorus much like ruminant animals.

Since phytate-bound phosphorous is unavailable to pigs, chickens, and other single stomached animals, phosphorous from other sources is supplemented to meet the needs of the animal. The extra phytate-bound phosphorus will be unavailable and excreted in the manure.

Reducing the proportion of cereal grains in the diet will usually reduce the amount of phosphorus fed. However, for pigs and chickens, and there are few economic alternatives to cereal grains. Plant breeders are working to develop feed grains lower in phytate content and higher in available phosphorus.

Phytase in the Feed

An enzyme called phytase can be included with the diet. Phytase will break down phytate and release digestible phosphorus. Mixing phytase (commercially available) in the diet will reduce the phosphorus required in supplements.

Interactions Between Nutrients

Another factor affecting phosphorus availability is the presence of other nutrients in the diet. Overfeeding calcium can limit the availability of phosphorus. Calcium and other nutrients should be fed in balance so as not to disrupt the availability of phosphorus.

Calcium:Phosphorus Ratio for Horses

Horses are a bit unique; they require calcium and phosphorus to be in a specific ratio in the diet. Young growing horses, as well as lactating mares, should receive a Ca:P ratio of 2:1, while mature horses not reproducing can get by with a 1:1 ratio. Calcium should never be fed at a level lower than phosphorus because phosphorus will tend to interfere with calcium absorption into bone. Horses at maintenance require .17% phosphorus in the diet and .24% Ca. The highest levels of phosphorus are needed in reproducing mares (.34%). Typical horse diets approach 2 to 3 times the required level of phosphorus, which can be detrimental to the environment. This high phosphorus level is partially due to the estimated Ca:P ratio in alfalfa hay being 6:1. Many horse owners try to counteract this by adding more phosphorus to the diets. Many equine supplements already contain more phosphorus than is necessary. There are also phosphorus concerns for ruminant animals such as cows, sheep, goats, and etc.

Ruminants and Phosphorus

Ruminant animals have a phytate enzyme produced naturally within the rumen that breaks down phytate-bound phosphorus and makes it available to the animal. According to the National Research Council, a lactating dairy cow requires between .35 and .40% phosphorus in the diet. Previous dairy feeding practices included as high as .55% or .60% phosphorus in the diet. This would mean an excess of 25 to 30 pounds fed to a cow in a normal lactation. If you multiply this over a dairy herd with 100 cows, then nearly 3,000 pounds extra phosphorous would be fed over the course of a year. Some dairy farmers think that phosphorus is a mineral required for proper reproductive function. While phosphorous is indeed important for normal bodily functions and is important for reproduction just as all nutrients are important for reproduction, there is no special link between phosphorus and reproduction in a cow. Most dairy farmers have already reduced phosphorus in their diets to levels given by the National Research Council.

Managing Dietary Nitrogen for Livestock and Poultry

Diets should be managed to reduce nitrogen (N) losses. Protein is the chief N source in the diet, and N is the nutrient we are most concerned with. If a growing pig requires 22% protein in the diet and is fed 25% protein, then the excess (containing N) is going to be lost. Some N is going to be lost in the feces, and some that is absorbed is going to be lost as urea in the urine. Conversely, if a pig requires 22% protein, and is only fed 18% protein, then that animal’s production will be limited to the 18% level. In this case other nutrients in the diet will be in excess and cannot be utilized efficiently. Nitrogen feeding strategies are different for all livestock species.

Dietary Nitrogen Management for Ruminants

Ruminants (cow, sheep, goat, etc.) have a requirement for proteins that are quickly degraded in the rumen, called degradable intake protein (DIP). They also require proteins less quickly degraded or undegradable in the rumen, undegradble intake protein (UIP). If too much UIP protein is fed, then some of that excess will probably be excreted in the feces. On the other hand, if too much degradable protein is fed, there will be too much absorption of nitrogen into the blood supply and it will be lost in the urine as urea. Most research has shown that lactating dairy cows require about 32% to 38% undegradable protein in the diet, with the remainder being made up as degradable protein.

To learn more about protein for cattle see the following Livestock and Poultry Environmental Stewardship (LPES) Curriculum lesson sections:

Dietary Nitrogen Management for Non-ruminants

With non-ruminant animals, like chickens, horses, and pigs, individual amino acids are the basis of diet protein formulation. (Protein is composed of individual nitrogen-containing amino acids). A ruminant has a microbial population that produces essential amino acids in the rumen, so there is less focus on amino acids for them. In the case of pigs, horses, and chickens each individual amino acid is important. Lysine is usually the first limiting amino acid when feeding pigs and horses, and methionine is usually first limiting with chickens. Commonly used feeds are limiting in these amino acids and must be supplemented through balancing with other ingredients or by adding commercially-available crystalline amino acids to the diet.

To learn more about protein for non-ruminants, see the following Livestock and Poultry Environmental Stewardship (LPES) Curriculum lesson sections:

Vegetative Treatment Systems Articles

Passive Composting of Manure

Passive Composting

Passive composting is probably the most common method used today because it involves simply stacking feedstocks and leaving them to compost over a long period of time. Very little, if any activity is performed on the pile once it has been constructed. Initial composting parameters can be controlled but are not usually maintained during the entire process. This process relies on mother nature to draw cool air and oxygen into the pile as the warm air is released. This process is commonly referred to as the chimney effect.

“Chimney effect” within an active composting pile

 

Passive/static yard waste composting

 

In Vessel Composting of Manure

In-Vessel Composting

In-vessel composting refers to any type of composting that takes place inside a structure, container or vessel. Each type of system relies upon mechanical aeration and turning to enhance and decrease the duration of the composting process. The goal of in-vessel composting systems is to combine various composting techniques into one controlled environment, which utilizes the strength and minimizes the weakness inherent to other forms of composting.

Farmers Automatic composting system – mechanically aerated in-vessel. CC 2.5 Jason Governo

 

In-vessel composting system used for poultry manure. CC 2.5 Jason Governo.

 

Composting Manure in Windrows

Windrow composting

Windrow composting is similar to passive composting although the piles of materials are turned or aerated by mechanical equipment to maintain optimum conditions. Materials are placed in long rows where the actual size and shape of the windrow are dependent upon the feedstocks and type of turning equipment. Dimensions of the windrow normally range from three feet to twelve feet high and anywhere between eight to twenty feet wide. Mechanical turning is usually done with a front-end loader or a machine specifically designed for turning windrows

Windrow composting using a front end mounted two pass turner

 

Educational and Commercial Resources for Manure Composting

Educational Resources

Commercial Resources

Consulting Resources

  • Coker Composting & Consulting, Roanoke VA, provides professional support to the composting industry with experience in planning, designing, building and running compost facilities
  • Tetra Tech provides responsible resource management and sustainable infrastructure services, offering innovative and cost effective solutions to complex problems
  • Midwest Biosystems offers consulting services to fit the need of any proposed or existing composting operation
  • Gershman, Brickner & Bratton, Inc. is a national management consulting firm that helps public and private sector organizations find solutions to solid waste management challenges

Author: Jason Governo, University of Georgia