Environmental Interactions with Agricultural Production: Animal Agriculture and the Environment
Animal production industries have seen substantial changes over the past several decades, the result of domestic/export market forces and technological changes. The number of large operations has increased, and animal and feed production are increasingly separated in terms of both management and geography. Concern that these changes are harming the environment has prompted local, State, and Federal policies and programs to control pollution from animal production facilities.
Trends in Animal Production and Manure Nutrients
Changes in the structure of livestock and poultry production are behind many of the current concerns about animals and the environment. Structural changes have been driven by both innovation and economies of scale. Organizational innovations, such as production contract arrangements, enable growers to access the capital necessary to adopt innovative technologies and garner economies of size in their efforts to increase profits. The significant economic benefits from vertical coordination, particularly for poultry and swine operations, have led to both larger operations and greater geographic concentration of animals.
For example, the number of hog farms fell more than 70 percent between 1992 and 2004 while the hog inventory remained stable. Larger farms account for an increasing share of total output. The average size of U.S. hog farms grew from 945 head in 1992 to 2,589 head in 1998 and to 4,646 head in 2004. The share of hogs produced on farms with more than 2,000 head increased from less than 30 percent to nearly 80 percent. Similar trends occurred in the dairy, poultry, and cattle sectors.
The innovations and economies of size that underlie changes in the livestock and poultry sectors also served to separate animal production from crop production. Large, specialized facilities today focus on producing animals and purchase most of their feed from off the farm. This means there is generally less land on the animal farm on which to spread manure. The amount of land per animal unit declined nearly 40 percent across all animal types between 1982 and 1997, from 3.6 to 2.2 acres per AU (AU defined as 1,000 pounds of live weight).
Environmental Impacts of Animal Production
The major source of environmental degradation from confined animal production is the wastes (manure, urine, bedding material) that are produced. Animal waste can be transmitted through runoff of nutrients, organic matter, and pathogens to surface water; leaching of nitrogen and pathogens to ground water; and volatilization of gases and odors to the atmosphere. Pollutants may originate at production houses/lots where animals are kept; manure storage structures such as tanks, ponds, and lagoons; or land where manure collects or is applied.
The major pollutants include:
- Nutrients—Nitrogen and phosphorus are essential plant nutrients, but can degrade water quality by causing eutrophication.
- Ammonia—A pungent, colorless gas that can be a health hazard to humans and animals at high concentrations, and a precursor for fine particulates (haze) in the atmosphere. It also contributes to soil acidification and water eutrophication.
- Hydrogen sulfide—A colorless gas also hazardous to humans and animals.
- Methane—A nontoxic, odorless greenhouse gas.
- Odor—A nuisance associated with animal production facilities. Odorous gases consist of a host of compounds (over 300) that originate from manure in animal housing, manure storage units, and land application.
- Pathogens—Threats to human health that are often contained in manure. Some of the pathogens that pose a threat to human health include the protozoan parasites Cryptosporidium and Giardia and some bacteria species such as Salmonella, E. coli, and Campylobacter.
Manure Production and Excess Nutrients
Two indicators of potential environmental degradation from animal feeding operations are total nitrogen excreted and excess nitrogen and phosphorus. Total nitrogen is an indicator of the potential for both air and water pollution from the entire operation (production facility, manure storage, and land application). Excess nutrients are manure nutrients produced on the farm in excess of the farm's crop needs. Excess nutrients are susceptible to running or leaching off the field and into water resources unless steps are taken to move the manure off the farm to additional farm land or to other industrial uses such as energy production or commercial fertilizer production.
In 1997, animal feeding operations controlled 73 million acres of cropland and permanent pasture. This land was estimated to have the capacity to assimilate only 40 percent of the nitrogen and 30 percent of the phosphorus in the manure recoverable from animal production facilities and available as a crop fertilizer. Large farms, which constitute 2 percent of the total number of farms, accounted for almost half of the excess onfarm nutrients.
In 1997, 68 counties had manure nitrogen levels that exceeded the assimilative capacity of the entire county's crop and pasture land. Many more counties (152) had surplus manure phosphorus.
In these areas, it may be difficult to find enough land locally to spread manure without posing a risk to water quality. Research suggests that producers may have to haul manure extended distances in order to apply manure to land at agronomic rates.
Manure's Contribution to Environmental Degradation
While a nationwide study has yet to be completed, a number of studies have indicated that animal operations are significant contributors to water quality impairments in several regions. States reported to the Environmental Protection Agency (EPA) in 1996 that animal feeding operations were a contributing source in 10 percent of rivers and streams reported as being impaired. A U.S. Geological Survey (USGS) study of 16 watersheds found that manure was the largest source of nitrogen loadings in 6, primarily in the Southeast and Mid-Atlantic States. USGS modeling of total nitrogen and phosphorus export from watersheds in major water resource regions of the U.S. found that, nationally, the median contribution of nitrogen from animal agricultural sources was 14 percent, compared to 22 percent for commercial fertilizer and 0.8 percent for point sources (sewage treatment plants, factories). For phosphorus, the median contribution from animal agricultural sources was 26 percent, compared to 17 percent for commercial fertilizer and 3 percent for point sources. The USGS' National Water Quality Assessment Program found that the highest concentrations of nitrogen in streams occurred in agricultural basins, and were correlated with nitrogen inputs from fertilizers and manure. An analysis of fecal coliform bacteria in streams found that concentrations were partly a function of the number of both confined and unconfined animals in a watershed.
The impact of gases and odor from animal feeding operations on human health and the environment has been difficult to determine because data on emissions are generally lacking. Animal waste in the United States has been estimated to contribute about 50 percent of all anthropogenic ammonia emissions, 25 percent of nitrous oxide emissions, and 18 percent of methane emissions.
Emissions to water and to the atmosphere are not independent events, but are linked by biological and chemical processes that produce various compounds. For example, nitrogen excreted from an animal can follow any number of pathways and enter water as nitrate or the atmosphere as ammonia, nitrous oxide, nitric oxide, or as part of a volatile organic compound. Reducing nitrogen movement along one pathway by changing its form will increase nitrogen movement along a different path.
A number of practices are available for reducing gaseous emissions and runoff/leaching from animal feeding operations.
- Diet manipulation—Feed additives and more efficient nutrient utilization in animals can reduce the amount of nitrogen and phosphorus in manure. This helps reduce the odor and ammonia emissions from production houses, and simplifies manure management for protecting water quality at all stages of handling and disposal.
- Chemical additive—Different chemicals can be added to manure during collection in order to bind nutrients, thus reducing odorous compounds and ammonia emissions. By reducing atmospheric emissions, the nitrogen content of manure available for spreading is higher, increasing its value as a fertilizer. But the higher nitrogen content can also increase the cost of applying manure at agronomic rates that protect water quality.
- Air treatment—Trapping air vented from production houses and treating it before discharge to the atmosphere can reduce the release of odorous compounds, ammonia, and other gases.
- Tank and lagoon cover—Covering storage tanks and lagoons can greatly reduce the discharge of ammonia and other gases. Conserving nitrogen in tank and lagoon waste increases the value of the effluent as a fertilizer, but can increase the cost of managing manure to protect water quality.
- Solid-liquid separation— Separating urea from solid fecal matter using sedimentation basins or mechanical methods avoids some of the reactions that cause the formation of ammonia and odor. Separation also reduces the cost of moving waste to land for efficient disposal.
- Manure incorporation/injection—Rapidly incorporating manure into the soil after spreading by plowing or disking—or injecting manure liquids or slurries directly into the soil—reduces odor, ammonia emissions, and the potential for runoff to surface waters. However, incorporation/injection may increase the risk of nitrogen leaching to ground water.
- Comprehensive nutrient management—Nutrient management matches the combined nutrient applications from manure and commercial nutrient sources to crop needs so that as few nutrients as possible are lost to the environment.
An important characteristic of most of these practices is that in reducing one type of emission, they may increase another type of emission. Such interactions can have an important bearing on the design of policies for protecting environmental quality.
Federal, State, and local governments have responded to the environmental problems posed by animal operations through a variety of regulations and conservation programs (see the chapter on Federal Laws Protecting Environmental Quality in this briefing room). The Environmental Protection Agency introduced Clean Water Act regulations in 2003 for controlling runoff of manure nutrients from the largest animal feeding operations. Concentrated animal feeding operations (CAFOs) requiring a pollution discharge permit must develop and implement a nutrient management plan that bases nutrient applications on agronomic rates. This provision requires permitted CAFOs to spread their manure over a much larger land base than they are currently using, and most will need to move their manure off farm. The impact on the livestock and poultry farms' annual net income depends heavily on the willingness of local landowners to use manure as a nutrient source.
USDA is using voluntary approaches (see Policy Instruments for Protecting Environmental Quality in this briefing room) such as education and financial incentives to encourage improved manure handling practices on all AFOs. Sixty percent of Environmental Quality Incentive Program funds are earmarked to environmental concerns on animal operations.
Many States have enacted regulations that address environmental issues associated with animal feeding operations (AFOs), including some not addressed at the Federal level. Some States had manure land application requirements in place prior to EPA's 2003 regulations, with coverage often extended to smaller AFOs. Odor is a persistent local issue, and many States are using setback requirements to separate animal operations from residential areas. Ammonia emissions from large animal feeding operations have prompted California to enact regulations in the San Joaquin Valley to protect heavily populated areas downwind.
For more information, contact: Marc Ribaudo
Updated date: December 5, 2008
- Also, see: Animal Waste and Hazardous Substances: Current Laws and Legislative Issues in the Encyclopedia of Earth.
- Also, see: Thomas F. Ducey, Anthony D. Shriner, Patrick G. Hunt. Nitrification and Denitrification Gene Abundances in Swine Wastewater Anaerobic Lagoons. Journal of Environment Quality, 2011; 40 (2): 610 DOI: 10.2134/jeq2010.0387