South Carolina              
Administrative Law Court
Edgar A. Brown building 1205 Pendleton St., Suite 224 Columbia, SC 29201 Voice: (803) 734-0550

SC Administrative Law Court Decisions

CAPTION:
Coneross Concerned Citizens, et al vs. SCDHEC, et al

AGENCY:
South Carolina Department of Health and Environmental Control

PARTIES:
Petitioners:
Coneross Concerned Citizens, Oliver and Frances Medlin, Grant Crowe, James and Guynell Holliday, Jerry and Tanya Mize, Steve and Helen Smith and Milton and Elaine Medlin

Respondents:
South Carolina Department of Health and Environmental Control and Brian Tippett
 
DOCKET NUMBER:
05-ALJ-07-0462-CC

APPEARANCES:
For Petitioners: Robert Guild, Esquire

For Respondent DHEC: Julie F. McIntyre, Esquire

For Respondent C. Brian Tippett: Ronald E. Cardwell, Esquire, Pamela A. Baker, Esquire
 

ORDERS:

FINAL ORDER AND DECISION

STATEMENT OF THE CASE

This matter comes before the Administrative Law Court (Court or ALC) pursuant to the request of the Petitioners (Coneross Citizens) for a contested case hearing. After the South Carolina Department of Health and Environmental Control (DHEC or Department) issued State Agricultural Permit No. 18,991-AG to Brian Tippett (Tippett) for construction and operation of a poultry farm with four (4) broiler houses, the Coneross Citizens challenged the issuance of the Permit. After proper notice, a hearing was held on June 27 and 28, 2006, at the Administrative Law Court.

FINDINGS OF FACT

Having observed the witnesses and exhibits presented at the hearing and taking into consideration the burden of persuasion and the credibility of the witnesses, I make the following findings of fact by a preponderance of evidence:

General Findings

1. On April 6, 2005, Respondent C. Brian Tippett, the owner/operator of the proposed poultry farm, filed an application and an Animal Facility Management Plan for the construction of four (4) poultry broiler houses to accommodate 30,000 broilers per house, with six flocks per year.[1] Mr. Tippett graduated from Clemson University with a Bachelors of Science in Poultry Business. He is quite experienced in the process of receiving, growing out and selling the poultry, as well as the various systems his poultry barns would utilize to minimize odor, air and water pollution.

The proposed facility is located in Oconee County on Irene Drive, four (4) miles north of the Community of Westminster, South Carolina. Before filing the application, Mr. Tippett notified all property owners, including the Coneross Baptist Church, within 1,320 feet of the proposed poultry farm with a Notice of Intent to Construct Form by certified mail or hand delivery. DHEC subsequently held a public hearing in response to the comments from the Coneross community opposing the proposed poultry farm. In addition to other issues, the citizens raised many health-related concerns. DHEC requested that citizens with those concerns submit medical records to DHEC’s epidemiologist, James J. Gibson, M. D. for further review. After consideration of all issues including the health concerns raised by the citizens concerning the proposed agricultural permit, DHEC issued State Agricultural Permit No. 18,991-AG for the construction of four (4) poultry broiler houses to Respondent Brian Tippett.

The proposed poultry farm will be located in a rural, agricultural area of Oconee County. It will produce 720,000 birds per year with an average live weight at any one time of 351,000 pounds. The waste produced in one year will be approximately 732 tons. The poultry farm will be operated as a dry manure system and thus the broilers will be housed and raised on earthen floors covered with wood shavings. Importantly, the permit is a no-discharge (agricultural manure and animal by-products treatment and storage system) permit which requires that the facility be operated to prevent discharges to the environment. The permit also does not allow land application of manure on the 84-acre tract where the poultry farm will be constructed.[2] Rather, Mr. Tippett is required to contract for handling of the manure by a permitted manure broker. Waste from the facility is to be disposed of in accordance with the Animal Facility Management Plan developed by Joy Shealy and the Manure Broker Contract with Melvin Stephens, a licensed manure broker, for the Purchase of Waste. Furthermore, the following special conditions are required by DHEC in the permit:

The proposed farm must be operated in accordance with State and federal law to prevent discharges to the environment; dead birds must be disposed of in an approved burial pit; and the applicant is prohibited from using Irene Drive, which runs adjacent to Coneross Baptist Church.

The Coneross Citizens contested the issuance of this permit on the grounds that air and water pollution will be increased by the poultry barns and that emissions generated from the poultry facility will unreasonably interfere with their use and enjoyment of the properties and that air contaminants from the poultry barns will exacerbate existing health problems experienced by various members of the group and reduce their property values. The Coneross Citizens also contend that the issuance of the permit will affect the use and enjoyment of the Coneross Baptist Church, to which several of the Petitioners belong. In addition to the church building, the surrounding facilities consist of a gazebo, a basketball court, a public picnic area, and the church cemetery, all located approximately 1,000 to 1,450 feet from the proposed poultry facility.

In determining whether or not to grant a permit, DHEC, and thus the ALC, is required to evaluate the impacts of the permit to water resources and air quality, including downwind receptors.

Water Quality

2. As part of the water resources review required under S.C. Code Ann. Regs. 61-43, Part 200.70(E), permitted point source discharges, water quality monitoring stations, drinking water intakes, state approved source water protection areas, groundwater public supply wells, impaired water bodies, heritage corridors, state and national parks and forests, and other non-point sources located in the watershed are considered in determining whether to issue this permit. The proposed barns are to be located on the highest spot of the land, 40 to 50 feet above Coneross Creek which is to the immediate west. The waters of Coneross Creek are only about 800 feet downslope from the proposed barns. Furthermore, there is an impaired water body adjacent to the proposed poultry farm, which is impaired due to copper and fecal coliform bacteria.[3]

These facts would create grave concerns if the facility allowed the discharge of animal waste. However, the evidence did not establish that the production houses will adversely impact any of the State’s waters. The proposed poultry houses will be fully enclosed to prevent rainwater from entering the houses and coming in contact with the poultry litter inside of the houses. Manure removed from the proposed poultry houses is to be managed by a permitted manure broker as required in the permit and Facility Management Plan. Because the proposed facility is a no-discharge facility, neither copper nor fecal coliform bacteria will enter the stream and thus should not impact the impaired water body of Coneross Creek. Furthermore, the setbacks in the regulations for ditches and swales serve to provide a buffer to prevent particles from entering adjacent water bodies, should there be any runoff. Moreover, the Coneross community receives its drinking water from a public water system. The intake for that system is located up-stream from the proposed poultry farm.

Nevertheless, when the manure is removed from the barns, the Animal Facility Management Plan allows stockpiling on site in excess of 3 days if placed on a pad or other acceptable surface and covered with a vented tarp. The cover and pad are intended to prevent the manure from washing downhill into surface water. However, though this site has undulating areas, the permit places no restriction on the location of a manure stockpile. If a heavy rainfall occurred before the manure was covered it could wash down into the creek. On the other hand, Mr. Tippett testified that it is his intent to have the manure hauled off the same day it is cleaned out of the house. There is, however, no requirement to that effect in the permit.

Air Quality and Odor

3. Live animal operations often produce odors and particulates. In particular, both ammonia and hydrogen sulfide may be produced in poultry barns. Additionally, odorous compounds may be produced as a result of anaerobic decomposition. However, poultry farms are the least, or at least one of the least, environmentally offensive of the live animal operations. Moreover, a dry litter facility is the easiest to manage and the best, most environmentally friendly manure management system available today in animal production. Additionally, an important aspect in controlling the emissions of those odors and particulates is the design and management of the facility.

The basic design of the proposed facility is typical in this industry. It employs a ventilation system with exhaust fans which help maintain temperature and moisture control. Though both ammonia and hydrogen sulfide may be produced under anaerobic conditions in poultry barns, when anaerobic activity ceases, both ammonia and hydrogen sulfide cease to be produced. The goal of a dry litter system is to reduce the moisture content of the litter to about 25%. At that moisture level the manure becomes dry and the biological process slows down to where there is very little odor generated within the manure.

The proposed facility uses a state of the art design to regulate the environment in the houses and, in particular, the moisture content of the litter. The houses will have computers which control ventilation and tunnel fans for cooling in the summer as well as, cooling cells for evaporative cooling when temperatures are very hot. In the event there should be a power outage, the facility will be equipped with a back-up generator capable of running all systems needed for heating, cooling, and ventilating the poultry barns. The back-up generator will be capable of operating three to four days without having to be refueled. The houses will also have solid poured walls and an earthen floor graded to near perfect level to inhibit moisture in the houses.

In addition, the watering system for the birds can be a source of excess moisture in the barns. Here, the houses will be equipped with a nipple-drinker watering system which does not require open drinking water sources for the birds. The system will also have a water meter which will be read every day showing how much water is being consumed by the birds. That information will allow the operator to quickly identify leakage problems so that it can be repaired promptly, thereby preventing the excess accumulation of moisture.

If this facility is built according to its design and operated in accordance with its permit, no ambient air quality standards[4] will be exceeded.[5] There would thus be no impacts to downwind receptors from the proposed poultry farm.[6] More specifically, though ammonia is produced in the anaerobic decomposition, it degrades quickly and is usually at very low concentrations in poultry barns. One study that measured ammonia levels downwind from poultry farms exhaust fans indicated that at 100 and 300 feet, the levels of ammonia would be less then 1 part per million and at 500 feet, the levels would be virtually zero. Another study regarding hydrogen sulfide emissions found that there is virtually no hydrogen sulfide emitted from broiler houses. Finally, studies regarding particulate matter associated with broiler houses have found that at approximately 100 feet downwind from exhaust fans on the house, particulate matter was measured to be at background levels.

In addition to the general issue of ambient air quality standards, the Department’s regulations require consideration of the “downwind receptors” which include a consideration of the impact the odors produced at the facility may have on the community. The management of the facility is an important key to minimizing the production of odor and thus any transport of odor away from the facility. As addressed above, in a dry manure system, when the manure is kept properly dry, the odor-producing biological processes slow down until very little odor is generated within the manure. In other words, if a poultry farm operator is instituting best management practices, a dry manure system should preclude the generation of anaerobic odorous compounds. Furthermore, if a poultry farm operator follows best management practices in the operation of his broiler houses, when manure is removed from the poultry houses, the discharge of odors should be minimized.[7] Thus, the odors from the operation of Mr. Tippett’s facility will be minimal as long as the facility is operated in accordance with his Permit and Facility Management Plan.

Brian Tippett has over twelve (12) years of experience in the poultry business. In his current position as assistant broiler manager for Fieldale Farms Corporation, Mr. Tippett is responsible for supervising ten (10) flock supervisors throughout South Carolina and Georgia. Mr. Tippett graduated from Clemson University with a Bachelor of Science Degree in Poultry Business. In addition to his educational background, Mr. Tippett has taken courses during his 12 years in the poultry industry in the area of odor management.

Moreover, in the event that the facility does produce a bad odor, the location and design of the facility is important in minimizing its impact. Odors exhausted from poultry facilities are transported through the environment by two principal mechanisms - first, by wind or air movement. When it is windy, odors are quickly diluted to the point where they are not detectable after short distances. Thus, the impact of odors is greater when there is just a slight breeze. The second method of transport is air drainage or ground inversion. In the late spring, summer and early fall, the air next to the ground becomes cooler as the ground cools. Since cool air is heavier than the warm air, the air will flow downhill. The odors in that air will likewise flow downslope. The odor during an inversion is often more pronounced because the air movement is not sufficient to disperse the odors.

Coneross Baptist Church[8] and the residents closest to the proposed facility are located predominately to the east. Though the Church and these residents are located relatively close to the outer edge of the facility, the exhaust fans of the poultry houses, where virtually all of the exhaust from the houses will be emitted, will be located on the end of the facility which is the greatest distance from the Church and residents. The land to the east is also up gradient of the facility which helps in reducing the impact of odor. The vegetative and tree buffers surrounding most of the track site will also further reduce any impact of odors to the local residents. Additionally, though the wind in the area usually blows to the northeast, the exhaust from the fans will also be initially pushing the exhausted air away from the Church and residents. This will further attenuate the impact of odors from the facility.

Furthermore, the location where the air will be dispersed is sloped to the west. Coneross Creek is located down gradient to the west of the site. The grade of the land in that area will thus result in the odors and particulates flowing down to the Creek during nighttime inversions. Since Coneross Creek will capture any odor from temperature inversions during the summer, it is very unlikely that these inversions would cause odor problems to the east of the facility. Nevertheless, there are a few residences which are located downhill from the barn site along Hesse Highway to the south. However, these residences are not as close as the residences to the east and there are no residences in the area of the Creek in which the odor from the facility will naturally flow. Furthermore, though the odors would likely follow the creek, the distance and density of the vegetation would significantly dissipate their impact.

4. The application estimates a five percent die off rate of Mr. Tippett’s flocks. Thus, Tippett would need to dispose of approximately 1,500 dead birds from each 30,000 bird flock. He proposes to do so in two burial pits on the northeast border of the site, one less than 500 feet and the other 800 to 1,000 feet from Mr. Crowe’s residence. These pits are a potential, though apparently minimal, source of odor.

Health Concerns

5. The Petitioners presented a variety of potential health concerns related to the permitting of the Tippett poultry farm. For instance, Oliver Medlin whose home is located approximately two thousand seven hundred fifty (2,750) feet from the center of the proposed Tippett site has been diagnosed with ALS, a degenerative disease commonly known as Lou Gehrig’s Disease. He and his wife are concerned that the poultry farm could cause him to require mechanical breathing and worsen his condition both physically and mentally. Grant Crowe’s home is located approximately one thousand one hundred fifty (1,150) feet from the corner of the proposed poultry barns on the Tippett property. Though he does not currently suffer from any health complications, he fears his health could be adversely affected in the future. Tanya Mize’s home is located approximately one thousand two hundred (1,200) feet from the proposed Tippett poultry facility. She fears another incident of encephalitis, which she suffered about twenty-one (21) years ago. She believes that fleas and mosquitoes on her family farm caused her encephalitis and that Tippett’s facilities would attract fleas and mosquitoes that could again result in her contracting encephalitis. Mrs. Mize also suffers from bronchial problems, Lupus, and torticollis and is currently on various medications for these illnesses. Finally, James Holliday lives one thousand three hundred fifty (1,350) feet from the proposed barn site. Mr. Holliday suffers from emphysema and asthma and is concerned that air pollutants will aggravate his existing condition.

Though these Petitioners’ have understandable concerns that absolutely must be considered, I find no scientific basis to warrant the denial of Tippett’s permit. Rather I am persuaded by the testimony of Dr. James J. Gibson, an employee of the Bureau of Disease Control at DHEC.[9] Dr. Gibson examined the Petitioners’ health concerns. In addition to the application, Dr. Gibson reviewed letters sent in by a number of the residents, phone calls from a number of the residents describing their health conditions, medical records submitted by some of the residents’ physicians, and if documents were not clear, he called the doctor for clarification. Part of his job is to determine whether the underlying illnesses that people have could be made worse by the levels of ammonia or particles from the facility, “and then you try to determine, best you can, the level of ammonia particles at their home going to get into that range where it would reasonably make their illness worse.”

After reviewing all medical evidence presented by the Coneross Concerned Citizens, in some cases speaking with their doctors and reviewing various air documents and reports, Dr. Gibson concluded that in his “best judgment,” a person living at a distance of over one thousand (1,000) feet from the proposed poultry barns would not experience enough increased particulates or ammonia to cause significant objective worsening of their clinical condition because of the proposed poultry barns. As explained by Dr. Gibson, in making an evaluation regarding health impacts, distance is important because distance attenuates particles and ammonia emissions. It is also important to consider the nature of the facility itself.

Therefore, the evidence did not establish any probable health consequences from the poultry barns as long as the barns are one thousand (1,000) feet away from their homes. In other words, at a distance of 1,000 feet there would be a substantial attenuation of any compounds produced at the facility such that there would not be any significant or measurable increase in particulates or ammonia for a person located at that distance. Though in other cases a 1,000 foot setback may be insufficient, in this case the distance of the above residences from the poultry barns is sufficient to safely conclude that there will be no adverse health impacts.[10]

CONCLUSIONS OF LAW

Based upon the foregoing Findings of Fact, I conclude the following as a matter of law:

General Conclusions

1. The Administrative Law Court has jurisdiction over this contested case matter pursuant to S.C. Code Ann. § 1-23-600(B) (Supp. 2005) and 24A S.C. Code Ann. Regs. 61-43, Part 200.70(G) (Supp. 2005). In contested case hearings, the Administrative Law Judge is the fact finder. Brown v. S.C. Dep’t of Health and Envtl. Control, 348 S.C. 507, 560 S.E.2d 410 (2002). In weighing the evidence and deciding the merits of the case, the Administrative Law Judge must make findings of fact by a preponderance of the evidence. Anonymous (M-156-90) v. State Bd. of Medical Examiners, 329 S.C. 371, 496 S.E.2d 17 (1998). Furthermore, Petitioner bears the burden of proving its case by a preponderance of the evidence. Nat’l Health Corp. v. S.C. Dep’t of Health and Envtl. Control, 298 S.C. 373, 380 S.E.2d 841 (Ct. App. 1989).

Here, the Petitioner opposes the issuance of a State Agricultural Permit. The review of an Agricultural Permit application for a poultry facility is specifically controlled by 24A S.C. Code Ann. Regs. 61-43, Part 200 (Supp. 2005). The Petitioner thus has the burden of proving by a preponderance of the evidence that the evidence fails to support the issuance of a State Agricultural Permit to Mr. Tippett for a poultry farm pursuant to Part 200 of Regulation 61-43.

2. As trier of fact, the Administrative Law Judge (ALJ) is not compelled to accept an expert’s testimony, but may give it the weight and credibility the ALJ determines it deserves. Florence County Dep’t. of Social Serv. v. Ward, 310 S.C. 69, 425 S.E.2d 61 (Ct. App. 1992). Nevertheless, it is appropriate to give due consideration to the Department’s staff’s utilization of its specialized knowledge and expertise in determining this matter. See S.C. Code Ann. § 1-23-330(4) (Supp. 2005).

Involuntary Non-Suit

3. The Petitioners allege that the operation of the proposed poultry farm violates the State’s nuisance law and would diminish their property values. Several of the Petitioner’s witnesses testified about their concerns that the value of their property would decline if Mr. Tippett is allowed to construct and operate the broiler facility. At the close of Petitioners case, Respondent Brian Tippett moved for an Involuntary Non-Suit on the issue of civil nuisance law and diminished property value.

Regulation 61-43, Part 200 provides that the purpose of the Regulation is:

To establish criteria for animal facilities and manure utilization areas location as they relate to protection of the environment and public health. The location of animal facilities and manure utilization areas as they relate to zoning in an area is not covered in this regulation. Local county or municipal governments may have zoning requirements and these regulations neither interfere with nor restrict such zoning requirements. Permit applicants should contact local municipal and county authorities to determine any local requirements that may be applicable.

24A S.C. Code Ann. Regs. 61-43, Part 200.10 (A)(5) (Supp. 2005). While Regulation 61-43, Part 200 gives fairly broad discretion in determining separation distance concerning environmental factors, it is not the purpose of the regulation to establish a land use mix within an area. Those decisions are primarily the responsibility of the local zoning authorities. See Bear Enter. v. County of Greenville, 319 S.C. 137, 459 S.E.2d 883 (Ct. App. 1995). Moreover, Regulation 61-43, Part 200 does not give the Department the authority to decline a permit merely because it believes that the operation of a poultry farm at the location would effect property values. In fact, generally the use of one’s property which does not create a nuisance cannot be enjoined merely because it lowers property values. Winget v. Winn-Dixie Stores, Inc., 242 S.C. 152, 130 S.E.2d 363 (1963). Furthermore, the ALC is not the proper forum to pursue nuisance claims.[11] See O'Cain v. O'Cain, 322 S.C. 551, 473 S.E.2d 460 (1996). Therefore, I granted an Involuntary Non-Suit with respect to the general aspects of nuisance, with exception to those factors relevant to the permitting decision making process as set forth in 24A S.C. Code Ann. Regs. 61-43, Part 200.70 (Supp. 2005). I likewise granted an Involuntary Non-Suit with respect to claims of diminished property value.

Separation of Facility from Residences and State Waters

4. The Petitioners remaining objection to Tippett’s permit is primarily that the “agricultural facility” is located too close to the waters of the state and nearby residences. Here, the applicable regulations provide that at a minimum, Tippett’s animal facility must be 200 feet from the lot line of real property owned by another person or 1,000 feet from the nearest residence unless by written consent of the adjoining property owner. 24A S.C. Code Ann. Regs. 61-43, Part 200.80 (A)(1) and (G) (Supp. 2005). The facility also must be at least 100 feet from any “waters of the State (including ephemeral and intermittent streams) located down slope from the facility” and 50 feet from a ditch or swale that is not constructed for site drainage. 24A S.C. Code Ann. Regs. 61-43, Part 200.80 (A)(2) and (3) (Supp. 2005). These minimum separation distances may reduced “if a permanent vegetative water quality buffer, that meets NRCS standards at a minimum, is installed and maintained.” Id.

In addition, in making the decision of whether or not to grant a permit for this animal facility, DHEC, and thus this Court, must also reasonably seek to prevent an increase “in pollution of the waters and air of the State.” 24A S.C. Code Ann. Regs. 61-43, Part 200.70 (E) (Supp. 2005). The minimum separation distances listed above may also be extended if various factors warrant an additional separation distance. 24A S.C. Code Ann. Regs. 61-43, Part 200.80 (F) (Supp. 2005). Those factors include, “classification or impairment of adjacent waters,” “slope of the land” or “down-wind receptors.” Part 200.70 (F)(4), (7) and (11).

The Petitioners contend that DHEC so narrowly defined air pollution as to exclude all of the odorous emissions from the animal waste except hydrogen sulfide, which they then assumed would not be discharged from the facility. Thus, DHEC simply defined the problem of air pollution away. To the contrary, I find that the evidence established that there would not be an increase in air pollution from the proposed poultry farm. Furthermore, the exhaust from Tippett’s barns will not create adverse health consequences to the neighboring property owners or unreasonably impact “down-wind receptors.” Moreover, with the additional special conditions set forth below, the facility is located at a sufficient distance from both ephemeral streams and waters of the State. Therefore, I find that the evidence establishes that the facility’s barns are sufficiently separated from the waters of the State and the downwind receptors (nearby residences and church).

Nevertheless, the evidence established that one of the burial pits would be located less than 500 feet from Mr. Crowe’s residence and the other between 800 and 1,000 feet from his residence. The Respondents contend that this is both reasonable and permitted by the Regulations. However, as noted above, an “animal facility” must be 1,000 feet from the nearest residence, unless waived by written consent of the adjoining property owner. Regulation 61-43 defines an “animal facility” as:

an agricultural facility where animals are confined and fed or maintained for a total of forty-five days or more in a twelve-month period and crops, vegetative, forage growth, or post harvest residues are not sustained in the normal growing season over any portion of the lot or facility. Structures used for the storage of animal manure and other animal by-products from animals in the operation also are part of the animal facility.

24A S.C. Code Ann. Regs. 61-43, Part 50(F) (Supp. 2005) (emphasis added). As when seeking to determine the meaning of statutes, the rules of statutory construction apply to the interpretation of the meaning of regulations. See Converse Power Corp. v. S.C. Dept. of Health and Envtl. Control, 350 S.C. 39, 564 S.E.2d 341 (Ct. App. 2002). “Where a word is not defined in a statute, our appellate courts have looked to the usual dictionary meaning to supply its meaning.” Lee v. Thermal Eng’g Corp., 352 S.C. 81, 91-92, 572 S.E.2d 298, 303 (Ct. App. 2002). The normal meaning of the word “by-product” is “1. Something produced in the making of something else. 2. A secondary result; a side effect.” The American Heritage College Dictionary 193 (3d ed. 1993). This definition is echoed in Merriam-Webster Online Dictionary defining “by-product” as “1: something produced in a usually industrial or biological process in addition to the principal product; 2: a secondary and sometimes unexpected or unintended result. . . .” Merriam-Webster Online (2005). Therefore, the proposed facility fails to meet the siting requirements of Regulation 61-43, Part 200.80(A)(5), with respect to the dead bird disposal pits.

ORDER

Based on the foregoing Findings of Fact and Conclusions of Law,

IT IS HEREBY ORDERED that State Agricultural Permit No. 18,991-AG be issued to C. Brian Tippett with the following special conditions:

1. The Permittee, C. Brian Tippett, shall give all residents whose homes are within one thousand three hundred twenty (1,320) feet of the facility twenty-four (24) hours notice prior to removing manure from the poultry houses. Once removed from the houses, the manure shall be hauled off of the 84 acre tract within 24 hours of its removal. In no event shall the Permittee allow manure to be exposed to rain;

2. The exhaust from the poultry barns shall be vented from the westerly end of the facility; and

3. No land application of any manure shall occur on the 84 acre tract of land upon which the Permittee’s facility is located.

IT IS FURTHER ORDERED that this case be remanded to the Department to determine a suitable location or means for disposing of the dead birds. The Department shall also determine a suitable location for the storage of manure removed from the barns.

AND IT IS SO ORDERED.

________________________________

Ralph King Anderson, III

Administrative Law Judge

September 6, 2006

Columbia, South Carolina



[1] The application also reflected that one residence was located less than 1,000 feet from the proposed poultry farm. However, Mr. Tippett obtained a waiver from that property owner.

[2] Mr. Tippett testified that he has no plans of spreading manure on his 84 acres of property at this time. As set forth below, in light of the proximity to the Coneross Creek, the slope of the land and the proximity of this facility to local residences and the Coneross Church, I find that there must be a special condition to this permit that no land application will occur upon the 84 acre tract of land where this facility is located. In other words, I find that land application in conjunction with the existing concerns set forth below would sufficiently exacerbate the air including downwind receptors and water quality as to warrant the denial of this permit. All findings below are presumptive on that special condition.

[3] Petitioners introduced the Department’s 2005 Annual Report for Non-Point Source Pollution Management. That report states that Coneross Creek is an impaired water body under the Clean Water Act’s Section 303(d) for fecal coliform bacteria and copper. One of the sources of the fecal coliform bacteria according to the report is nonpoint agricultural sources in general. The report, however, does not distinguish between types of animal facilities, including swine, cattle, or free-range sources and does not indicate that the type of poultry facility proposed by Mr. Tippett would be a source of fecal coliform bacteria.

[4] Ambient air quality standards are federal or state enforceable concentration limits. With regard to Mr. Tippett’s proposed poultry farm, there are not ambient air quality standards for all constituents produced by a poultry farm. In particular, there is no ambient air quality standard for ammonia, but there is a standard for hydrogen sulfide.

[5] This conclusion is supported by the testimony of Paul Christopher Martin and Dr. Michael Lacy. Mr. Martin has a Bachelor of Science degree in Atmospheric Science from the University of North Carolina, Asheville and is employed by the DHEC, Bureau of Air Quality as an Air Quality Meteorologist. His job duties entail air quality forecasting and air permit modeling for industrial sources. Dr. Michael Lacy is Professor and Department Head of the Department of Poultry Science at the University of Georgia. Dr. Lacy has a Master’s Degree in Poultry Science and a PhD in Animal Science with a poultry specialty. Poultry science includes the study of odor issues related to poultry farms. Dr. Lacy has authored or co-authored thirty-three (33) refereed extension and scientific journal articles; thirty-five (35) scientific abstracts; one hundred and thirty (130) educational trade journal articles and one hundred and fifty (150) extension education newsletter articles in the area of poultry science. The topics of those articles include broiler housing design, operation and ammonia emissions. I found the testimony of these two witnesses persuasive.

[6] Petitioner’s expert, Dr. Richard K. White testified that if a facility was not properly operated, air emissions of hydrogen sulfate, ammonia, and other contaminants could be emitted and such emissions could create a nuisance or health impacts off-site. Dr. White testified that the standards promulgated by the American Society of Agricultural and Biological Engineers (ASABE) recommend that facilities be sited at least one-half (½) mile from residences and one (1) mile from public areas to avoid nuisance complaints. However, the ASABE Standard is not one of the federal or State standards listed as factors to consider in S. C. Code Ann. Regs. 61-43, Part 200.70(E). In fact, there is no evidence that any state has adopted the distance standards for setback of animal facilities recommended by the ASABE. Moreover, the compounds identified in the ASABE Standard at Table 1, titled “Typical Compounds Resulting from Anaerobic Decomposition of Animal Manure”, would only be emitted inside a poultry house at insignificant levels because a dry manure system is not an anaerobic situation. In fact, using the OFFSET Model referenced in the ASABE Standard EP379.3 to calculate an odor emission factor for the proposed poultry farm, the models worst-case scenario, which included giving Mr. Tippet no credit for any odor abatement procedures indicated a result of a 98% odor-free number. In other words, 98% of the time there would be no significant odor from Mr. Tippet’s farm at 1,000 feet. Finally, practically any facility that is improperly operated could create excess air emissions that could result in a nuisance or health impacts off-site. The issue here is if the facility is operated properly, what will be the environmental impact. In that regard, even Dr. White testified that when best management practices are utilized, minimal air emissions or odors will result.

[7] Mr. Tippett testified that it is his intent to haul off the manure the same day that it is removed from the house.

[8] Coneross Baptist Church which holds many public events is located only 1,200 feet from the barn site. In considering the efficacy of this permit and the additional conditions, I considered the impact of the poultry barn emissions on the church and these events.

[9] Dr. Gibson was the only medical professional to testify in this case and Petitioners presented no evidence to contradict Dr. Gibson’s conclusion. Dr. Gibson has been employed by DHEC for thirteen (13) years. He has a Doctor of Medicine from the University of Pittsburgh’s School of Medicine and his training was in the area of internal medicine and infectious disease. Dr. Gibson currently spends the majority of his time in the area of public health and environmental health. In keeping with those duties, he is responsible for reviewing applications for agricultural permits and giving an opinion as to whether the conditions that are proposed would add a significantly increased severity of illness to the people who live near the proposed facility. Dr. Gibson has conducted health evaluations for approximately ten to twelve agricultural permits during his tenure at DHEC.

[10] Dr. Gibson testified that the 1,000foot setback provides a good margin of error for attenuation of particles and ammonia, unless there is an unusually large barn or people with atypical sensitivity. Nevertheless, as noted below the setbacks may be increased based upon an evaluation of the site and other factors. See 24A S.C. Code Ann. Regs. 61-43, Part 200.70(F) (Supp. 2005). Thus, I base my determinations in this case upon the overall facts, and not merely on the 1,000 foot set back required by the state regulations.

[11] The issue of the impact or nuisance as it pertained to “downwind receptors” within the parameters of Regulation 61-43, Part 200, Section 70 is nevertheless a consideration in determining the appropriate separation of the facility from the nearby residences.


Brown Bldg.

 

 

 

 

 

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