Poultry production is an important and diverse component of American agriculture. Poultry products including eggs, chicken and turkey meat are a healthy part of the diets of most Americans. In 1997, nearly 99,700 farms were producing poultry and poultry products (egg, broiler, and turkey; NASS/USDA). While broiler chicken production is concentrated primarily in the southern and southeastern U.S., turkey production occurs primarily in the Corn Belt and in North Carolina. Egg production is distributed throughout the U.S.
Modern poultry production occurs primarily in enclosed buildings to protect the birds from weather, predators, and the spread of diseases from wild birds. This has allowed farmers to greatly increase production efficiency while significantly reducing the amount of labor required. As with pork production, this has resulted in environmental challenges with production of larger volumes of manure in much smaller areas.
This module will cover the modernization of poultry production over the past 60 years, different phases of production and the production systems in which they occur.
Background of Poultry Production in U.S.
The poultry industry has largely grown from backyard operations which provided supplemental income for the family to a vertically integrated industry. (PDF, 373KB) Poultry consumption in the U.S. has increased from the 1900s, when chicken was eaten only on Sundays to making poultry an every day item today.
Broiler production greatly increased throughout the 1980s and 1990s due to Americans becoming more health conscious and through an unprecedented increase in exports. Part of this increase has also been attributed to the poultry industry supplying products that are further processed and easier for the consumer to prepare. These increases have led to an all time high in poultry production in the U.S. (Table). Currently, most poultry production in the United States is in the Southeastern states.
At one time, there were many distinct breeds of chicken, each having particular traits or characteristics. Through selective breeding, only a few strains of birds dominate the market today. There are many primary breeding companies of poultry, but only a handful are responsible for most of the broiler chicken, laying hen, and turkey production in the world.
Concentration and specialization of the poultry industry have led to the development of allied industries. These industries supply housing, feeding and other equipment, hatchery equipment, processing supplies and equipment, drugs and other health products, feed additives, and several other items.
Products from Poultry
Poultry products (broiler meat in particular) has the highest per capita consumption in the United States. People eat many different poultry products, including eggs, turkey ham, buffalo wings, hot dogs, chicken nuggets, chicken-patties, fried, roasted, glazed, marinated, etc. Not all of poultry products, however, are directly consumed by humans. For example, eggs are also used for the production of therapeutic vaccines and are beginning to be used for production of antibodies and pharmacological proteins. Part of the increase in poultry production in the 1980s and 1990s can be attributed to the development of new, further-processed, value-added products. Similarly, the egg market has changed in scope through the late 1980s such that a greater proportion of eggs that are produced are destined for a liquid egg market. Liquid egg is used in a variety of institutions including hotels, restaurants, hospitals, and if dried, included in numerous other products, such as cake mixes. Today, the U.S. produces 33% of the world's broiler meat, 53.7% of the turkey meat, and 11% of the eggs (USDA-FAS, 2001).
Poultry Production Phases
Breeding FlocksLighting and Housing Types
Lighting plays a very important role in bird growth, development, and maturity. Most commercial poultry specie are photosensitive animals. For example, a constant or decreasing amount of daily light (as occurs during the fall and winter months) will delay sexual maturity in growing birds. An increasing amount of light (as occurs in the spring) will stimulate sexual maturity. Since lighting plays such an important role in the development of sexual maturity, adolescent birds are generally reared in black-out houses. This allows the producer to have complete control over the lighting cycle of the birds by providing artificial light.
Once birds reach the age of sexual maturity, they are moved to the laying
house. Breeder broilers and ducks
are generally be kept in a barn with a slotted floor or with a wire floor
with litter in the middle of the house to act as a mating area. Breeder
turkeys are generally reared in all litter houses. Clean, nesting boxes
are provided so that the birds may lay their eggs without being disturbed
by other birds and so that the eggs may be kept clean and easily collected.
Adolescent broilers (especially), turkeys, and ducks, when given the opportunity, will eat until they become obese. Therefore, restricted feeding is necessary if the birds are going to be used as breeder stock. Otherwise, the obesity severely limits the numbers of eggs laid and the fertility of those eggs. For this reason, restricted feeding is necessary. There are two main types of restrictive feeding programs. The first of these is every day feeding of a limited amount, or lower nutrient content diet. The amount fed will ensure adequate growth but not result in obesity. Another type of restrictive feeding is an every other day feeding program. where birds are fed a specific quantity of feed every other day. Since male broiler chickens grow faster, they often are reared separately from the females until they are moved into the breeder house. Specific ratios of male-to-females are kept in the breeder house (typically, broilers-1 male :15 females, turkeys and ducks-1:8 to 10) to ensure fertility of hatching eggs.
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Laying HensThe modern laying hen is a biological marvel. She begins laying eggs at approximately 18 weeks of age and by the end of her first year, she may have produced upwards of 200 eggs - nearly 25 pounds. The hen reaches peak egg production (95 + %) within 4 to 6 weeks after she begins to lay eggs. In order to produce such a hen, it is critical that the hen be carefully managed during her first 17 weeks of life.
At the beginning of a pullet's life in the hatchery, she is vaccinated to prevent future diseases. On the farm, pullets will be grown in cages until they are moved into the laying house at 16 to 17 weeks of age. Pullet chicks will typically be beak trimmed during their first three weeks of life in the pullet house to minimize cannibalism.
Lighting programs are very similar to what was described for breeding flocks.
Molting is the process of the bird shedding and re-growing feathers. Molting occurs naturally in the wild, as seasonal daylight shortens and females stop laying eggs. Laying hens are generally molted once or twice during their productive lives. Molting usually does not affect egg size, but allows for an improved egg laying rate, improved shell quality, and increased albumin height. It also allows a producer to keep the birds longer than they might otherwise be kept. To induce molt, a producer may use a period of fasting and a reduced amount of daylight, giving the birds water and allowing them to lose a proportion of their body weight. Daylight length will then be increased, and the hens begin laying eggs again.
In-line vs. Off-line production
In-line production - Hen houses are placed side-by-side and linked by a conveyor belt. The conveyor belt leads to a centralized processing building, where the eggs from all houses are sorted, graded, either packed or broken and further processed, and refrigerated prior to shipping.
Off-line production - This is similar to the
in-line production, but the eggs that are collected on a conveyor belt
and sent to a main building are packed and refrigerated prior to shipping
to another facility to be processed.
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Broilers, Turkeys, Ducks (meat-bird production)Broilers
Broilers are relatively easy to raise. To begin with, the whole house is heated and brooder rings are placed around each brooder (heating) unit. These rings create a "microclimate" relative to the rest of the room to prevent drafts and keep the birds near each other and near the feed and water. The nipple or cup waterers in each pen must be fully functional and supplemental jug waterers in the brooder rings must be kept filled. When the birds arrive, they are placed into the rings and introduced to the waterers and feed. Feed is placed in the feeders and on paper placed on the floor of the pen to encourage young birds to eat. Generally, broilers are brooded in a portion of the house until a certain age before being given access to the entire barn. These facilities, or "houses" generally have litter floors. Depending on the geographical location of the house, natural ventilation will be either provided by opening curtain-sided walls or large insulated door panels on the sides of the house.
Some farms separate male and female birds, a practice called separate-sex feeding. Separate-sex feeding accomplishes a number of goals. When birds are separated and fed according to gender (versus rearing males and females together), there will be more uniformity among males and among females in the flock. Separation of the birds also allows producers to feed diets that more closely meet the nutritional needs of the male and female birds.
In previous decades, turkeys have been mainly considered a holiday product. However, with advances of further-processing as well as an increasingly health-conscious population in the U.S., the turkey has become a popular year-round meat. Raising turkeys takes more time than raising broilers, as turkeys take longer to mature. Generally, a turkey is sent to market anywhere between 15 and 25 weeks of age. At 20 weeks of age, a male turkey should weigh about 35-40 pounds.
Poults are usually gender-sorted at the hatchery and the males (toms) and females (hens) are reared separately. They may also toe-trimmed, and beak-trimmed at the hatchery to prevent the birds from injuring each other.
Over their life cycle, turkeys may live in 2 or 3 different barns. The brooder barn, is used for the first 6 to 8 weeks of life. After that, the turkeys may be moved to an intermediate barn. Lastly, they are moved into a grow-out facility. By having multiple barns for different ages, a farm is able to rear a greater number of birds in a shorter amount of time.
While broilers and turkeys may seem like fast-growing birds, the duck is the most rapidly growing animal of all poultry species. A typical duck will weigh 7 pounds in only 6 or 7 weeks!
Ducks can be raised in a number of different types of houses. Some are raised on all-litter floors while others have slats or wire for the flooring. Some houses contain a litter floor with a ramp leading up to raised-wire or expanded plastic flooring over a shallow pit. Since ducks like to play with the watering system (typically a nipple-waterer system), it is located over the raised flooring. Generally, ducks go through two or three stages of housing. Each stage would house anywhere from 13 to 20 groups of ducks per year.
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Prior to WWII, the majority of poultry were reared in backyard flocks on dirt-floored pens, in small sheds with natural or make-shift ventilation.
Between 1940 and 1960, advancements in nutrition and genetics allowed the broiler market to shift from being able to produce a 3-3.5 pound bird at 16 weeks to one that only took 8 weeks. Due to advances in production efficiency and refrigerated trucking, markets expanded to a much larger geography while the price of poultry per pound dropped dramatically from approximately 65 cents in 1940 to 29 cents in 1960. Due largely to changes in price versus other meat options, demand for broilers increased dramatically. Production systems during this time also underwent dramatic changes from the seasonal, small backyard sheds to large year-round naturally ventilated buildings and during some seasons, large outdoor pens.
Today, turkey and broiler flocks are reared in enclosed buildings with updated equipment. For instance, birds are now reared in confinement with on-demand feeder lines, on-demand cup or nipple waterers, or on-demand bell-type waterers. These developments overcame most problems with weather, predators, potential pollution from lot runoff, and allowed the use of more intensive production schedules. Today, almost all turkeys and broilers are reared on litter floors. Ducks, turkeys, and occasionally broilers are reared in multi-stage facilities with facilities for brooding birds, and in larger facilities (either a separate room or separate building) that they will be moved into at an older age.
Young pullets, laying hens, and broiler breeders are reared in either wire-cages or slotted-floor systems. If a slotted flooring system is used, there may or may not be a central area containing litter. Duck facilities encompass a number of different production types and may or may not have multistage facilities. Systems in use include all-litter houses, raised-wire flooring over a shallow pit (which would be located below a nipple water line) and houses with raised-wire floors.
Disadvantages associated with large enclosed, production facilities are that different ages of birds with different degrees of disease resistance are housed in close proximity which can facilitate disease spread if adequate cleaning and disinfecting are not feasible in some situations, and higher levels of medication may be required to control disease. The primary rule of thumb for workers on a farm with multiple ages of birds is to always travel from the youngest birds on the farm to the oldest, and not vice-versa. Biosecurity plans between farms, and between multiple production buildings on the same farm can help reduce the incidence and spread of disease from one flock to the next.
Common Manure Handling Systems
Poultry manure is handled as a solid litter, either deposited directly by animals on pastureland, or collected in bedding placed on solid shelter floors to absorb the urine. Some turkeys, broilers, and ducks are raised on concrete or earthen floors. After every flock, the litter is either:
Cake manure is sometimes removed with a tractor-drawn decaker/cruster which removes the top layer of manure, breaks it apart, and separates the larger manure particles from the finer litter particles (which are placed back into the house). Poultry litter is normally surface applied, but in some cases may be incorporated into the soil with a farm tillage operation shortly after spreading.
For further information on proper sampling of poultry litter.
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Layer Manure - Dry
Manure from pullets and laying hens is relatively dry as it falls through layer cages (Figure, above left) into a concrete storage area. Manure composition in these facilities can range in dry matter between 20 and 60 percent. The storage pit provides for long-term storage of the manure. Manure is then typically surface applied (Figure, above right). Composting is another option for solid manure management.
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Layer Manure - Semi-Solid/Liquid
Some laying hen facilities contain shallow pits with scrapers or belts, or shallow flush pits. This manure typically can not be stacked and requires some type of containment storage. Liquid manure that is mostly water (< 12% solids) must be kept in a watertight storage. Liquid manure can be handled with tank trucks/wagons, injection-type spreaders, or irrigation equipment. Semi-solid manure (12 to 20 percent solids), on the other hand, does not flow readily but still requires containment with walls. This type of manure can be handled easily with bucket loaders and open broadcast spreaders. Most Midwestern states require manure storages for larger operations to be large enough to hold six month’s accumulation. This avoids the need to apply manure during the crop growing season and when weather conditions are unsuitable – such as on frozen or snow-covered ground or when the soil is wet enough that heavy application vehicles could compact and damage the soil.
In larger operations, liquid manure may be pumped to nearby application sites and irrigated onto cropland. Spray irrigating liquid manure is a very efficient method of land application, in terms of speed and labor, but odor emissions can be significant; therefore, it is seldom possible to use this method in heavily populated areas.
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Lagoons - Duck
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Lagoons - Egg Wash Water
Since eggs from laying hen houses contain traces of manure on the shell, most states require that the water used to wash the eggs be collected and processed accordingly. Many laying hen operations collect this dilute wash-water in lagoon systems and apply the nutrients to croplands via irrigation systems (typically spray irrigation). Some producers treat this low-nutrient, wastewater using constructed wetlands or other systems prior to land application.
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Potential Environmental Impacts of Animal Feeding Operations
(Adapted in part from Livestock and Poultry Environmental Stewardship Curriculum, MidWest Plan Service; and Proposed US EPA Confined Feeding Rule.)
USEPA's 1998 National Water Quality Inventory indicates that agricultural operations, including animal feeding operations (AFOs), are a significant source of water pollution in the U.S. States estimate that agriculture contributes in part to the impairment of at least 170,750 river miles, 2,417,801 lake acres, and 1,827 estuary square miles (Table 1). Agriculture was reported to be the most common pollutant of rivers and streams.
However, one should not overlook the many positive environmental benefits of agriculture. For example, agricultural practices that conserve soil and increase productivity while improving soil quality also increase the amount of carbon-rich organic matter in soils, thereby providing a global depository for carbon dioxide drawn from the atmosphere by growing plants. The same farming practices that promote soil conservation also decrease the amount of carbon dioxide accumulating in the atmosphere and threatening global warming.
Other benefits compared to urban or industrial land use include greatly reduced storm runoff, groundwater recharge and water purification as infiltrating surface water filters through plant residue, roots and several feet of soil to reach groundwater.
In many watersheds, animal manures represent a significant portion of the total fertilizer nutrients added. In a few counties, with heavy concentrations of livestock and poultry, nutrients from confined animals exceed the uptake potential of non-legume harvested cropland and hayland. USDA estimates that recoverable manure nitrogen exceeds crop system needs in 266 of 3,141 counties in the U.S. (8%) and that recoverable manure phosphorus exceeds crop system needs in 485 counties (15%). It should be pointed out that while legumes are able to produce their own nitrogen, they will use applied nitrogen instead if it is available. The USDA analysis does not consider actual manure management practices used or transport of applied nutrients outside the county; however, it is a useful indicator of excess nutrients on a broad scale. Whole-farm nutrient balance is a very useful tool to identify potential areas of excess.
Air emissions from Animal Feeding Operations (AFO) can be odorous. Furthermore, volatilized ammonia can be redeposited on the earth and contribute to eutrophication of surface waters.
Animal manures are a valuable fertilizer and soil conditioner, if applied under proper conditions at crop nutrient requirements. Potential sources of manure pollution include open feedlots, pastures, treatment lagoons, manure stockpiles or storage, and land application fields. Oxygen-demanding substances, ammonia, nutrients (particularly nitrogen and phosphorus), solids, pathogens, and odorous compounds are the pollutants most commonly associated with manure. Manure is also a potential source of salts and trace metals, and to a lesser extent, antibiotics, pesticides and hormones. This problem has been magnified as poultry and livestock production has become more concentrated. AFO pollutants can impact surface water, groundwater, air, and soil. In surface water, manure's oxygen demand and ammonia content can result in fish kills and reduced biodiversity. Solids can increase turbidity and smother benthic organisms. Nitrogen and phosphorus can contribute to eutrophication and associated algae blooms which can produce negative aesthetic impacts and increase drinking water treatment costs. Turbidity from the blooms can reduce penetration of sunlight in the water column and thereby limit growth of seagrass beds and other submerged aquatic vegetation, which serve as critical habitat for fish, crabs, and other aquatic organisms. Decay of the algae (as well as night-time algal respiration) can lead to depressed oxygen levels, which can result in fish kills and reduced biodiversity. Eutrophication is also a factor in blooms of toxic algae and other toxic estuarine microorganisms, such as Pfiesteria piscicida. These organisms can impact human health as well as animal health. Human and animal health can also be impacted by pathogens and nitrogen in animal manure. Nitrogen is easily transformed into the nitrate form and if transported to drinking water sources can result in potentially fatal health risks to infants. Trace elements in manure may also present human and ecological risks. Salts can contribute to salinization and disruption of the ecosystem. Antibiotics, pesticides, and hormones may have low-level, long-term ecosystem effects.
In groundwater, pathogens and nitrates from manure can impact human health via drinking water. Nitrate contamination is more prevalent in ground waters than surface waters. According to the U.S. EPA, nitrate is the most widespread agricultural contaminant in drinking water wells, and nearly 2% of our population (1.5 million people) is exposed to elevated nitrate levels from drinking water wells.
Table 2 lists the leading pollutants impairing surface water quality in the U.S. Agricultural production is a potential source of most of these.
List of Contaminants in Animal Manure:
Comprehensive Nutrient Management Planning
When discharged to surface water, biodegradable material is decomposed by aquatic bacteria and other microorganisms. During this process, dissolved oxygen is consumed, reducing the amount available for aquatic animals. Severe depressions in dissolved oxygen levels can result in fish kills. There are numerous examples nationwide of fish kills resulting from manure discharges and runoff from various types of AFOs.
Manure may be deposited directly into surface waters by grazing animals. Manually-collected manure may also be introduced into surface waters. This is typically via storage structure failure, overflow, operator error, etc.
Manure can also enter surface waters via runoff if it is over-applied or misapplied to land. For example, manure application to saturated or frozen soils may result in a discharge to surface waters. Factors that promote runoff to surface waters are steep land slope, high rainfall, low soil porosity, and proximity to surface waters. Incorporation of the manure into the soil decreases runoff.
Nitrogen (N) is an essential nutrient required by all living organisms. It is ubiquitous in the environment, accounting for 78 percent of the atmosphere as elemental nitrogen (N2). This form of nitrogen is inert and does not impact environmental quality since it is not bioavailable to most organisms and therefore has no fertilizer value. Nitrogen can form other compounds, however, which are bioavailable, mobile, and potentially harmful to the environment. The nitrogen cycle shows the various forms of nitrogen and the processes by which they are transformed and lost to the environment.
Nitrogen in manure is primarily in the form of organic nitrogen and ammonia nitrogen compounds. In its organic form, nitrogen is unavailable to plants. However, organic nitrogen can be transformed into ammonium (NH4+) and nitrate (NO3-) forms, via microbial processes which are bioavailable and have fertilizer value. These forms can also produce negative environmental impacts when they are transported in the environment.
"Ammonia-nitrogen" includes the ionized form (ammonium, NH4+) and the un-ionized form (ammonia, NH3). Ammonium is produced when microorganisms break down organic nitrogen products such as urea and proteins in manure. This decomposition occurs in both aerobic and anaerobic environments. In solution, ammonium is in chemical equilibrium with ammonia.
Ammonia exerts a direct biochemical oxygen demand (BOD) on the receiving water since dissolved oxygen is consumed as ammonia is oxidized. Moderate depressions of dissolved oxygen are associated with reduced species diversity, while more severe depressions can produce fish kills.
Additionally, ammonia can lead to eutrophication, or nutrient over-enrichment, of surface waters. While nutrients are necessary for a healthy ecosystem, the overabundance of nutrients (particularly nitrogen and phosphorus) can lead to nuisance algae blooms.
Pfiesteria often lives as a nontoxic predatory animal, becoming toxic in response to fish excretions or secretions (NCSU, 1998). While nutrient-enriched conditions are not required for toxic outbreaks to occur, excessive nutrient loadings can help create an environment rich in microbial prey and organic matter that Pfiesteria uses as a food supply. By increasing the concentration of Pfiesteria, nutrient loads increase the likelihood of a toxic outbreak (Citizens Pfiesteria Action Commission, 1997).
The degree of ammonia volatilization is dependent on the manure management system. For example, losses are greater when manure remains on the land surface rather than being incorporated into the soil, and are particularly high when the manure is spray irrigated onto land. Environmental conditions also affect the extent of volatilization. For example, losses are greater at higher pH levels, warmer temperatures and drier conditions, and in soils with low cation exchange capacity, such as sands. Losses are decreased by the presence of growing plants. (Follett, 1995)
Nitrifying bacteria can oxidize ammonium to nitrite (NO2-) and then to nitrate (NO3-). Nitrite is toxic to most fish and other aquatic species, but it typically does not accumulate in the environment because it is rapidly transformed to nitrate in an aerobic environment. Alternatively, nitrite (and nitrate) can undergo bacterial denitrification in an anoxic environment. In denitrification, nitrate is converted to nitrite, and then further converted to gaseous forms of nitrogen - elemental nitrogen (N2), nitrous oxide (N2O), nitric oxide (NO), and/or other nitrogen oxide (NOx) compounds. Nitrification occurs readily in the aerobic environments of receiving streams and dry soils while denitrification can be significant in anoxic bottom waters and saturated soils.
Nitrate is a useful form of nitrogen because it is biologically available to plants and is therefore a valuable fertilizer. However, excessive levels of nitrate in drinking water can produce negative health impacts on infant humans and animals. Nitrate poisoning affects infants by reducing the oxygen-carrying capacity of the blood. The resulting oxygen starvation can be fatal. Nitrate poisoning, or methemoglobinemia, is commonly referred to as "blue baby syndrome" because the lack of oxygen can cause the skin to appear bluish in color. To protect human health, EPA has set a drinking water Maximum Contaminant Level (MCL) of 10 mg/l for nitrate-nitrogen. Once a water source is contaminated, the costs of protecting consumers from nitrate exposure can be significant. Nitrate is not removed by conventional drinking water treatment processes; its removal requires additional, relatively expensive treatment units.
Nitrogen in livestock manure is almost always in the organic, ammonia or ammonium form but may become oxidized to nitrate after being diluted. It can reach surface waters via direct discharge of animal wastes. Lagoon leachate and land-applied manure can also contribute nitrogen to surface and ground waters. Nitrate is water soluble and moves freely through most soils. Nitrate contributions to surface water from agriculture are primarily from groundwater connections and other subsurface flows rather than overland runoff (Follett, 1995).
Animal wastes contain both organic and inorganic forms of phosphorus (P). As with nitrogen, the organic form must mineralize to the inorganic form to become available to plants. This occurs as the manure ages and the organic P hydrolyzes to inorganic forms. The phosphorus cycle is much simpler than the nitrogen cycle because phosphorus lacks an atmospheric connection and is less subject to biological transformation.
Phosphorus is of concern in surface waters because it can lead to eutrophication. Phosphorus is also a concern because phosphate levels greater than 1.0 mg/l may interfere with coagulation in drinking water treatment plants (Bartenhagen et al., 1994). A number of research studies are currently underway to decrease the amount of P in livestock manure, primarily through enzymes and animal ration modifications that make phosphorous in the feed more available (and usable) by the animal. This means that less phosphorus must be fed to ensure an adequate amount for the animal and, as a result, less phosphorous is excreted in the manure.
Phosphorus predominantly reaches surface waters via direct discharge and runoff from land application of fertilizers and animal manure. Once in receiving waters, the phosphorus can become available to aquatic plants. Land-applied phosphorus is much less mobile than nitrogen since the mineralized form (inorganic Phosphate) is easily adsorbed to soil particles. For this reason, most agricultural phosphorus control measures have focused on soil erosion control to limit transport of particulate phosphorus. However, soils do not have infinite phosphate adsorption capacity and with long-term over-application, inorganic phosphates can eventually enter waterways even if soil erosion is controlled.
Both manure and animal carcasses contain pathogens (disease-causing organisms) which can impact human health, other livestock, aquatic life, and wildlife when introduced into the environment. Several pathogenic organisms found in manure can infect humans.
The treatment of public water supplies reduces the risk of infection via drinking water. However, protecting source water is the best way to ensure safe drinking water. Cryptosporidium parvum, a protozoan that can produce gastrointestinal illness, is a concern, since it is resistant to conventional treatment. Healthy people typically recover relatively quickly from such illnesses. However, they can be fatal in people with weakened immune systems such as the elderly and small children.
Runoff from fields where manure has been applied can be a source of pathogen contamination, particularly if a rainfall event occurs soon after application. The natural filtering and adsorption action of soils typically strands microorganisms in land-applied manure near the soil surface (Crane et al., 1980). This protects underlying groundwater, but increases the likelihood of runoff losses to surface waters. Depending on soil type and operating conditions, however, subsurface flows can be a mechanism for pathogen transport.
Soil type, manure application rate, and soil pH are dominating factors in bacteria survival (Dazzo et al., 1973; Ellis and McCalla, 1976; Morrison and Martin, 1977; Van Donsel et al., 1967). Experiments on land-applied poultry manure have indicated that the population of fecal organisms decreases rapidly as the manure is heated, dried, or exposed to sunlight on the soil surface (Crane et al., 1980).
Antibiotics, Pesticides, and Hormones
Antibiotics, pesticides, and hormones are organic compounds which are used in animal feeding operations and may pose risks if they enter the environment. For example, chronic toxicity may result from low-level discharges of antibiotics and pesticides. Estrogen hormones have been implicated in the reduction in sperm counts among Western men (Sharpe and Skakkebaek, 1993) and reproductive disorders in a variety of wildlife (Colburn et al., 1993). Other sources of antibiotics and hormones include municipal wastewaters, septic tank leachate, and runoff from land-applied sewage sludge. Sources of pesticides include crop runoff and urban runoff.
Little information is available regarding the concentrations of these compounds in animal wastes, or their fate/transport behavior and bioavailability in waste-amended soils. These compounds may reach surface waters via runoff from land-application sites.
Airborne Emissions from Animal Production Systems
With the trend toward larger, more concentrated production operations, odors and other airborne emissions are rapidly becoming an important issue for agricultural producers.
Whether there is a direct impact of airborne emissions from animal operations on human health is still being debated. There are anecdotal reports about health problems and quality-of-life factors for those living near animal facilities have been documented.
Source of Airborne Emissions
Odor emissions from animal production systems originate from three primary sources: manure storage facilities, animal housing, and land application of manure.
In an odor study in a United Kingdom county (Hardwick 1985), 50% of all odor complaints were traced back to land application of manure, about 20% were from manure storage facilities, and another 25% were from animal production buildings. Other sources include feed production, processing centers, and silage storage. With the increased use of manure injection for land application, and longer manure storage times, there may be a higher percentage of complaints in the future associated with manure storage facilities and animal buildings and less from land application.
Animal wastes include manure (feces and urine), spilled feed and water, bedding materials (i.e., straw, sunflower hulls, wood shaving), wash water, and other wastes. This highly organic mixture includes carbohydrates, fats, proteins, and other nutrients that are readily degradable by microorganisms under a wide variety of suitable environments. Moisture content and temperature also affect the rate of microbial decomposition.
A large number of volatile compounds have been identified as byproducts of animal waste decomposition. O'Neill and Phillips (1992) compiled a list of 168 different gas compounds identified in swine and poultry wastes. Some of the gases (ammonia, methane, and carbon dioxide) also have implications for global warming and acid rain issues. It has been estimated that one third of the methane produced each year comes from industrial sources, one third from natural sources, and one third from agriculture (primarily animals and manure storage units). Although animals produce more carbon dioxide than methane, methane has as much as 15 times more impact on the greenhouse effect than carbon dioxide.
Dust, pathogens, and flies are from animal operations also airborne emission concerns. Dust, a combination of manure solids, dander, feathers, hair, and feed, is very difficult to eliminate from animal production units. It is typically more of a problem in buildings that have solid floors and use bedding as opposed to slotted floors and liquid manure. Concentrations inside animal buildings and near outdoor feedlots have been measured in a few studies; however, dust emission rates from animal production are mostly unknown.
Pathogens are another airborne emission concern. Although pathogens are present in buildings and manure storage units, they typically do not survive aerosolization well, but some may be transported by dust particles.
Flies are an additional concern from certain types of poultry and livestock operations. The housefly completes a cycle from egg to adult in 6 to 7 days when temperatures are 80 to 90°F. Females can produce 600 to 800 eggs, larvae can survive burial at depths up to 4 feet, and adults can fly up to 20 miles. Large populations of flies can be produced relatively quickly if the correct environment is provided. Flies tend to proliferate in moist animal production areas with low animal traffic.
Emission Movement or Dispersion
The movement or dispersion of airborne emissions from animal production facilities is difficult to predict and is affected by many factors including topography, prevailing winds, and building orientation. Prevailing winds must be considered to minimize odor transport to close or sensitive neighbors. A number of dispersion models have been developed to Airborne Emission Regulations.
Most states and local units of government deal with agricultural air quality issues through zoning or land use ordinances. Setback distances may be required for a given size operation or for land application of manure. A few states (for example, Minnesota) have an ambient gas concentration (H2S for Minnesota) standard at the property line. Gas and odor standards are difficult to enforce since on-site measurements of gases and especially odor are hard to do with any high degree of accuracy. Producers should be aware of odor- or dust-related emissions regulations applicable to their livestock operation.
Source: Lesson 40 of the LPES: Adapted from Livestock and Poultry Environmental Stewardship curriculum, lesson authored by Larry Jacobson, University of Minnesota; Jeff Lorimor, Iowa State University; Jose Bicudo, University of Kentucky; and David Schmidt, University of Minnesota, courtesy of MidWest Plan Service, Iowa State University, Ames, Iowa 50011-3080, Copyright (c) 2001.
Environmental Impacts of Animal Feeding Operations Study Questions
Identify the definition that best fits the following terms:
Comprehensive Nutrient Management Planning
Recently, the concept of Comprehensive Nutrient Management Planning (CNMP) was introduced by the U.S. Environmental Protection Agency (EPA) and U.S. Department of Agriculture’s (USDA’s) Natural Resources Conservation Service (NRCS). It is anticipated that the CNMP will serve as a cornerstone of environmental plans assembled by animal feeding operations to address federal and state regulations. EPA and NRCS guidelines for CNMP are given in Table 1.
Poultry Production Study Questions
Identify the definition that best fits the following terms: