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The Future of Animal Agriculture in North America - Farm Foundation

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regulated federally by the Comprehensive Environmental<br />

Response, Compensation and Liability Act (CERCLA), the<br />

Emergency Plann<strong>in</strong>g and Community Right-to-Know Act<br />

(EPCRA) and the Occupational Safety and Health<br />

Adm<strong>in</strong>istration (OSHA), a federal agency deal<strong>in</strong>g with worker<br />

safety. While CERCLA and EPCRA have not been applied to<br />

animal agriculture <strong>in</strong> the past, current litigation is challeng<strong>in</strong>g<br />

this view <strong>of</strong> the law (Sierra Club v. Seaboard <strong>Farm</strong>s Inc., State <strong>of</strong><br />

Oklahoma v. Tyson Foods). Air emissions from AFOs have<br />

traditionally been a local issue, but states and the federal<br />

government have become more active <strong>in</strong> this area. EPA has<br />

<strong>in</strong>itiated research through the Air Quality Compliance<br />

Agreement <strong>of</strong> January 21, 2005, which reflects the <strong>in</strong>tent <strong>of</strong><br />

EPA to address air quality concerns with respect to animal<br />

production, with the goal <strong>of</strong> develop<strong>in</strong>g federal emission<br />

standards for livestock and poultry. Specifically, the agreement<br />

focuses on nitrogen oxides (NOx), hydrogen sulfide (H2S),<br />

volatile organic compounds (VOCs), or particulate matter<br />

(PM), which are covered under the Clean Air Act, and which<br />

may or may not be released from CAFOs.<br />

Responsibility for implement<strong>in</strong>g the federal CAFO program has<br />

been assumed by all but about five states. From a national<br />

perspective, the implementation <strong>of</strong> the CAFO program was<br />

perceived to be slow and uneven, prompt<strong>in</strong>g an environmental<br />

group to sue EPA to force implementation <strong>of</strong> the rules and<br />

improve the program. EPA lost the case and, <strong>in</strong> response,<br />

released f<strong>in</strong>al revised CAFO regulations <strong>in</strong> 2003. States were<br />

given two years to br<strong>in</strong>g CAFO-permitt<strong>in</strong>g programs <strong>in</strong>to<br />

conformity. EPA was then sued aga<strong>in</strong> by environmental and<br />

agricultural <strong>in</strong>terests regard<strong>in</strong>g changes <strong>in</strong> the revised CAFO<br />

regulations. This has delayed implementation <strong>of</strong> the regulatory<br />

changes as EPA is develop<strong>in</strong>g new regulations <strong>in</strong> response to the<br />

decision by the Second Circuit Court <strong>of</strong> Appeals <strong>in</strong> Waterkeeper<br />

Alliance et al. v. EPA, (2nd Cir. 2005). A number <strong>of</strong> states also<br />

have policies and regulations for water quality. In the 1990s,<br />

some states’ regulations began surpass<strong>in</strong>g federal regulation <strong>in</strong><br />

str<strong>in</strong>gency. Each state has policies and regulations for water<br />

quality, and most have CAFO-permitt<strong>in</strong>g programs. <strong>The</strong><br />

regulations and policies vary <strong>in</strong> what they address, <strong>in</strong>clud<strong>in</strong>g<br />

nutrient management and application plans, facility designs,<br />

and, <strong>in</strong> some cases, protections for producers from nuisance<br />

suits, exemptions from local authorities, and provision for<br />

mediation <strong>in</strong> conflicts (<strong>Animal</strong> Conf<strong>in</strong>ement Policy National<br />

Task Force, 1998).<br />

<strong>The</strong> <strong>in</strong>creas<strong>in</strong>g use <strong>of</strong> litigation as means <strong>of</strong> chang<strong>in</strong>g<br />

environmental regulatory frameworks and enforc<strong>in</strong>g<br />

implementation <strong>of</strong> exist<strong>in</strong>g laws has emerged as a new tool <strong>in</strong><br />

ongo<strong>in</strong>g water quality debates (Cushman, 1998). <strong>The</strong>re are<br />

substantial concerns related to the use <strong>of</strong> litigation, <strong>in</strong>clud<strong>in</strong>g<br />

the length <strong>of</strong> time before court decisions are made, cost <strong>of</strong><br />

litigation as a tool and risk that the court process may not<br />

<strong>in</strong>clude stakeholders (Boggess et al., 1997; Batie, 2003).<br />

Environmental Issues<br />

Litigation has also created a check on federal progress, as <strong>in</strong> the<br />

case aga<strong>in</strong>st EPA’s f<strong>in</strong>al 2003 CAFO regulations. However,<br />

litigation has also created an uncerta<strong>in</strong> environment <strong>in</strong> which<br />

bus<strong>in</strong>esses must operate, mak<strong>in</strong>g <strong>in</strong>vestment decisions difficult.<br />

<strong>The</strong> U.S. Clean Air Act amendments <strong>of</strong> 1990 required EPA to<br />

establish National Ambient Air Quality Standards (NAAQS)<br />

for pollutants considered harmful to human health. <strong>The</strong>se<br />

standards are applicable to all <strong>in</strong>dustries. Under the federal<br />

CERCLA and EPCRA, ammonia and particulate matter are<br />

reportable compounds if emissions exceed 100 lbs. per day.<br />

OSHA has established Permissible Exposure Limits (PELs) for<br />

specific compounds <strong>in</strong>side AFOs. EPA is beg<strong>in</strong>n<strong>in</strong>g to exam<strong>in</strong>e<br />

the need to establish federal emission standards for livestock<br />

and poultry, and the courts are hear<strong>in</strong>g arguments concern<strong>in</strong>g<br />

the applicability <strong>of</strong> CERCLA and EPCRA to CAFO<br />

operations. <strong>The</strong>se issues are not resolved.<br />

A few states are develop<strong>in</strong>g air quality regulations. Odor issues<br />

have historically been addressed through local zon<strong>in</strong>g and<br />

setback ord<strong>in</strong>ances direct<strong>in</strong>g facility sit<strong>in</strong>g decisions. Most state<br />

regulatory discussions regard<strong>in</strong>g air emissions from animal<br />

agriculture have focused on odor concerns. Odor is usually<br />

considered a common law nuisance, but there is ongo<strong>in</strong>g<br />

research to determ<strong>in</strong>e potential human health effects.<br />

Current Situation—<br />

Environmental and Related Issues<br />

Water Quality<br />

How animal production and manure <strong>in</strong>teract with the<br />

environment are issues for <strong>in</strong>dustry, government, <strong>in</strong>terest groups<br />

and the public, especially rural residents. Producers and<br />

agribus<strong>in</strong>esses have concern for their future <strong>in</strong> light <strong>of</strong> chang<strong>in</strong>g<br />

regulatory environments. In the United States, events such as a<br />

spill <strong>in</strong> the mid-1990s <strong>of</strong> the contents <strong>of</strong> a 25-million-gallon<br />

lagoon have put animal manure management issues <strong>in</strong>to the<br />

reform spotlight.<br />

Livestock and poultry farms generate manure, bedd<strong>in</strong>g, milk<strong>in</strong>g<br />

house wash water, spilled feed and dead animals that can<br />

impact water quality if not properly managed. Manure, bedd<strong>in</strong>g<br />

and other byproducts from livestock can be recycled as an<br />

energy source (through methane production or burn<strong>in</strong>g),<br />

compost, heat source and most commonly by application to<br />

land as a nutrient for crops.<br />

<strong>Animal</strong> manure and related byproducts conta<strong>in</strong> elements that,<br />

under certa<strong>in</strong> circumstances, might reach surface or ground<br />

water and cause pollution. Surface water contam<strong>in</strong>ation from<br />

manure and other animal production byproducts usually is<br />

due to organic matter, nutrients and fecal bacteria. Sediment<br />

transferred from outdoor livestock operations can also<br />

affect surface water. <strong>The</strong> location <strong>of</strong> an AFO plays a role<br />

<strong>in</strong> how pollutants may reach water and the magnitude <strong>of</strong>

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