3. Animal Feeding Operations
Animal feeding operations (AFOs) are lots or facilities in which confined animals are fed, raised, and maintained.194 Unlike farms that allow livestock to graze or be integrated into crop production, AFOs are focused on one task: maximizing the production of meat, dairy, or eggs.
EPA classifies AFOs as concentrated animal feeding operations (CAFOs) if they exceed a95
certain size threshold or, in some circumstances, if they discharge waste into surface waters.195
There are roughly 450,000 AFOs196 in the United States, including 20,000 CAFOs.197 CAFOs alone hold the majority of the country’s foodproducing animals.198 While AFOs are credited with lowering consumer costs for animal products, they have considerable externalities. They can harm animal welfare, increase antibiotic resistance due to the routine use of antibiotics,199 emit air and water pollution,200 depress property values,201 hurt small-scale farms and businesses,202 and diminish quality of life in rural communities.203
There are AFO systems for production of all types of meat—beef, pork, and poultry—as well as production of eggs and dairy products. While the details vary, in general, swine and dairy AFOs often rely on liquid manure systems, poultry and egg AFOs produce a dry litter, and cattle feedlots leave the animal waste on the open ground. In liquid systems, workers wash the manure from the animal pens to a storage lagoon, usually uncovered, where it is eventually pumped out and spread onto fields.
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AFO manure management systems produce much more methane than pasture-based livestock operations. When manure is left as a solid (as naturally happens on grazing lands and pasturelands), it typically decomposes aerobically and produces little to no methane.
However, when it is stored or handled in a system that creates an anaerobic environment, such as a lagoon, it releases large amounts of methane.204 Storage in uncovered anaerobic lagoons can result in methane conversion rates over 100 times as high as those in pasture and range.205AFOs produce an enormous amount of waste and emit tremendous amounts of greenhouse gases. Iowa’s 4,000 hog AFOs generated more than 68 billion pounds of manure in 2019, 68 times the amount of human excreta produced by the state’s residents, according to a conservative estimate.206 Meanwhile, Wisconsin’s 8,600 dairy farms are estimated to have generated almost 28 million tons of manure in 2018207—more than 50 times the amount of human excreta produced within the state.208 And since human waste must be treated before being released into the environment, reducing both the threat of pathogens209 and volume of organic material discharged, the relative impact from CAFO waste is even more stark—a CAFO with 250 dairy cows produces more organic waste every day than does a city the size of Albany.210 As a result of their reliance on anaerobic
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storage practices, dairy and hog operations are responsible for almost 90% of methane emissions from manure management.211 When comparing net greenhouse gas emissions from AFO systems, however, it is important to take into account other factors as well, including enteric emissions and the greater length of time that may be needed for animals to reach market weight in pasture-based systems.
This section evaluates four different strategies for reducing emissions from AFOs. The first strategy—transitioning to integrated crop-livestock systems—offers the most significant co-benefits, although its impact on greenhouse gas emissions will vary considerably by animal type and breed, the local environment, and other factors. The second strategy focuses on the benefits of eliminating concentrated liquid manure, which, as discussed above, is the dominant source of emissions from manure management.
The third strategy considers methods for reducing emissions from liquid manure. The final strategy focuses on feed additives and vaccines designed to reduce enteric emissions from ruminants.
Reincorporate animals into croplands. The most effective way to reduce emissions from AFOs would be to replace them with well-managed integrated crop-livestock systems. Traditionally, most farms incorporated animals into cropping systems by allowing them to forage on plant residues after harvest, but early agricultural scientists and extension agents discouraged this practice, perceiving it as archaic and inefficient. As late as 1974, 19% of farms in the United States used a crop-grazing rotation, accounting for 52% of cropland.212 By 2012, only 7% of farms used livestock in their rotations on less than 2% of all cropland.213 As scientists have begun to understand the ecology of agriculture better, however, they have started to encourage it as an environmentally friendly way to intensify agricultural
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production.214 Some even argue that crop-livestock farms are economically and environmentally optimal, creating an efficient nutrient cycle between plants and animals.215
Mixed crop-livestock systems increase inputs of plant litter and manure into soil along with the impacts of living plant roots and livestock, which can increase soil health and carbon sequestration. They can substantially reduce methane emissions from manure management because manure in integrated systems is typically left to decompose aerobically.216 As noted above, however, both animal growth rates and enteric emissions must be taken into account when comparing net emissions from different systems of animal agriculture.
In addition to their climate benefits, properly managed crop-livestock systems naturally control pest and weed populations217 and can improve soil structure, animal health, water quality, and biodiversity.218
Eliminate concentrated liquid manure.
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Industry advocates claim that biogas reduces greenhouse gas emissions, but these assertions rely on unfounded assumptions and overly optimistic projections, while ignoring methane leakage and more effective forms of manure management. Digesters reduce methane emissions when compared to unregulated liquid manure management systems, but liquid manure management systems have the highest per-head methane emission rates among all methods of manure management.220 Instead of comparing biogas to the most carbon-intensive system—and ignoring other methods, as anaerobic digestion proponents often do—we should compare it to other systems currently in use. When we do this, we find that is not only the most expensive method for reducing manure emissions, but it is also among the least effective.
Dairy and swine industrial facilities produce 90% of manure management emissions because they typically rely on liquid management systems, where manure is washed from animal pens to storage lagoons. This produces emissions rates as much as 90 times higher than those found in grazing-based and other dry manure systems.221 Anaerobic digestion can reduce the scale of these emissions, but digesters still release a considerable amount of methane. Large-scale, well-managed digesters can achieve leakage rates around 3% in optimal conditions222—much less than some studies have found223—but still enough to make digestion an inferior method of reducing emissions.224 In addition, the natural gas supply chain has a leakage rate of 2.3%,225 if not higher,226 adding to the amount of methane emitted by digesters.
While anaerobic digestion may reduce emissions relative to conventional liquid manure management, it is less beneficial to the climate than dry management and pastured-based alternatives—and, in contrast to those alternatives—it reinforces highly polluting practices. As discussed infra in Chapter VI.D, liquid manure systems also decrease soil, air, and water quality in rural
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communities, while lowering property values, regardless of whether anaerobic digestion is used.
Improve spreading of concentrated liquid manure. The Clean Water Act requires that the manure be spread at “agronomic rates”—that is in quantities that the plants need and can use.227 However, that provision is often ignored, with the result that manure can pollute nearby waters and release greenhouse gases.228 There is some evidence that specific practices relating to manure spreading can also affect emissions and soil carbon sequestration levels. Spreading on frozen or saturated soils, for example, tends to lead to water pollution and higher nitrous oxide emissions because the manure is more likely to enter waterways instead of being incorporated into the soil.229
Develop methane inhibitors and vaccines. A number of feed additives have been demonstrated to decrease methane emissions from livestock in shortterm experiments.230 When studied over the long term, however, these effects disappear or decrease significantly as the microflora in livestock’s rumen adapt to the new diet.231 Nonetheless, scientists are studying novel approaches that they hope will remain effective throughout a ruminant’s life-span. One study documented a 30% decrease in enteric methane emissions over 12 weeks with the addition of 3-nitrooxypropanol, a chemical compound that blocks an enzyme critical to methane formation.232 Another promising study found that red seawood supplementation reduced enteric emissions from cattle by 80% over 5 months.233
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Other researchers have developed vaccines designed to reduce methane emissions.
A New Zealand team is researching the viability of a vaccine that would target methanogenic archaea, reducing their prevalence in the rumen.234 Industry officials estimate that the vaccine could reduce enteric emissions by 25%-30%;235 however, as with methane inhibitors, the vaccine has yet to be proven safe, effective, or financially feasible.Finally, research indicates that eliminating antibiotic use in livestock may reduce the prevalence of methane-producing archaea. As a result, eliminating the nontherapeutic use of antibiotics in animals could have an effect on emissions similar to that of methane inhibitors and vaccines. Animals in confined production facilities routinely receive antibiotics to increase their growth rates and to prevent disease.236 This alters the microbiota of confined animals, affecting their health and physiology,237 and may increase the amount of methane-producing microflora. For example, a 2016 study showed that tetracycline, a common antibiotic used in livestock production, nearly doubled methane emissions from cow dung.238 Future research will be necessary to test additional classes of antibiotics and confirm that the effect will hold for enteric emissions.239 Nonetheless, these initial results are promising.
Eliminating nontherapeutic antibiotic use in livestock would reduce the development of new resistance genes and the transmission of antibiotic resistance from animals to humans.240 While new chemical inhibitors and vaccines may prove to be an effective and important pathway for reducing
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greenhouse gas emissions, they are unlikely to have significant social or environmental co-benefits. As with any feed additive or animal drug, their effects on animal welfare and human food safety should be rigorously assessed prior to marketing.
More on the topic 3. Animal Feeding Operations:
- The Risks Associated With the Development of SME Operations via E-Commerce
- FDA Regulatory Regimes in Facilitating the Approval of Animal Drugs
- THE COW AND THE PLOW: ANIMAL SUFFERING HUMAN GUILT AND THE CRIME OF CRUELTY
- To implement sound policy and pursue effective legal strategies, decisionmakers and advocates must become familiar with the climate-friendly agricultural practices that constitute carbon farming.1
- The Response of the FDA to Antibiotic Resistance Due to Overuse in Food Animals
- 2. Liability for damage done by animals
- The edictum de feris in South African law
- ABSTRACT
- 4. Farm Finance and Support
- Index
- D. Biogas Subsidies
- 1. Indebitum solutum
- 7. Lending Programs
- Loss caused by animals
- CONCLUSION