Findings Of Fact Based upon all of the evidence, the following findings of fact are determined: Background This controversy arose as the result of an application being filed by respondent/applicant, G. T. Williams (Williams or applicant), seeking a permit to construct a biological waste incinerator at 1530 North Beal Street Extension, Fort Walton Beach, Florida. The original application reflected that applicant intended to incinerate type 4 cardboard, paper and plastics furnished by area hospitals, laboratories and doctors' offices at a rate of 440 pounds per hour. Also, the proposed unit included a secondary chamber with a 3,000,000 BTU burner and controls for one second retention at 1800 degrees. However, on August 20, 1990, applicant amended its application to reflect that, instead of a one second retention chamber, it would employ a two second retention chamber to ensure total combustion in the secondary unit. After receiving the application and conducting a review and on-site inspection, respondent, Department of Environmental Regulation (DER), gave notice of its intent to grant the permit on August 23, 1990. The agency action also required applicant to publish notice of such intended action in a local newspaper of general circulation and to provide the agency with proof of publication. Because applicant had obtained a draft of the notice prior to its formal issuance by DER, it published notice of the intended action on August 1, 1990, or more than three weeks prior to the date of the formal proposed agency action. Considering such publication to be ineffective, DER gave notice on October 15, 1990, that it was reversing its earlier action and denying the permit. On October 20, 1990, applicant published notice of the agency action. After DER issued a final order denying the permit, applicant filed an appeal but later dismissed it after DER agreed to issue the permit subject to a petition for hearing filed by a third party prior to the issuance of the final order. On November 1, 1990, petitioner, Okaloosa County (County), the county in which the facility will be located, filed its petition for administrative hearing. As later amended on December 12, 1990, the petition contested the proposed issuance of a permit generally on the grounds that its employees working in nearby areas would be exposed to harmful emissions from the facility and the applicant had not given reasonable assurances that the facility would comply with all DER pollution standards. The Application Type of permit being sought In order for the facility to become operational, Williams is required to obtain both a construction and operating permit. This application concerns only a construction permit and, if approved, Williams will be allowed to construct the facility, have an initial start-up period, and perform compliance testing within the start-up period to demonstrate that the facility can meet the requirements and limitations set forth in the permit. Before obtaining an operating permit, Williams must first perform compliance testing under the auspices of a certified testing consultant employed by DER and submit those results to the agency. If the testing results do not meet all DER standards, an operating permit will not be issued until and if all deficiencies are corrected. The unit Applicant proposes to utilize an incinerator manufactured by Cleaver- Brooks, model CBU-500, with a design capacity to burn 500 pounds of Class 4 biological waste per hour. 1/ As a unit designed to burn no more than 500 pounds of waste per hour, the unit falls in the smallest of the three categories of incinerators regulated by DER. The unit was described by a DER witness as being a "relatively small" one and the size typically found "behind your medium sized hospital". It costs in excess of one hundred thousand dollars. The unit is a modular, factory built, packaged and tested system that burns combustible waste of varying heat content. The basic system consists of the main (pyrolysis) chamber, secondary chamber, which is the primary pollution control device, burners, stack and controls. The incinerator employs a two-stage waste combustion process. In more technical terms, the first stage is a pyrolysis process whereby combustible gases are generated under controlled air and temperature conditions. The main chamber receives waste through a manual batch door or from an optional hydraulically powered feeder, and with the aid of a temperature controlled burner and sub-stoichiometric underfire air supply, combustible gases with minimum particle entrainment are produced. Complete destruction of the fixed carbon and less volatile material takes place continually in the firebed. The second stage is an excess air combustion process whereby the combustible gases generated in the main chamber are ignited in the secondary chamber producing a high temperature carbon dioxide and water vapor flue gas. The secondary chamber supplies all the air for this combustion through temperature controlled forced air jets and employs temperature controlled burners to ensure complete ignition of the gases. The flue gas is then ducted to the stack and exhausted to the atmosphere. Although the applicant originally proposed to use a thirty foot stack on the unit, he has agreed to install a stack having a height that will be a minimum of two and one-half times the height of any building within one hundred fifty feet. Location The proposed site for the incinerator is on a flat, three-acre lot within an industrial park located approximately 1,150 feet east of North Beal Street Extension, a paved collector road that serves an industrial area north of the City of Fort Walton Beach. This location was selected by Williams because it was "run down", was basically "heavy industrial", and was "already polluted" with junk cars and plastic. Indeed, adjacent to or in the general vicinity of the site are undeveloped Eglin Air Force Base property, a plastic recycling plant, a landfill operated by the County, a City of Fort Walton Beach sewer plant and an auto salvage yard. According to the County engineer, the surrounding area "looks pretty bad" but is "probably an average industrial site." There is also an older residential area known as Pine Subdivision which, at its closest point, lies approximately 200 feet southeast of the edge of applicant's property. Applicant owns a 3,000 square foot metal frame building of an undisclosed height on the southeast end of his property and intends to lift up one of the garage bay doors in the front, slide the lower unit in place, peel back three or four sections of metal roof, set the horizontal unit on top, and replace the roof. A stack will then be added to the unit. The property is fenced and access may be had only by a dirt road leading into the area. Treatment process Applicant intends to provide service to various hospitals, physicians, and laboratories in the area. At the present time, approximately one-half of the medical waste in the Panhandle portion of the state is being transported to incinerators in central and south Florida for disposal because there are inadequate facilities in the Panhandle area. Williams will use a panel truck registered with the Department of Transportation to transport all materials to the site. He will also give all customers special sealed containers in which to place their waste materials. These containers, which are known as sharps containers, are designed to hold syringes, scalpels, and other objects capable of penetrating the skin, as well as cotton swabs saturated to the point of dripping. After arriving at the site the truck will be unloaded and the material and containers placed in the incinerator and burned. Because Williams contemplates burning waste as often as needed, waste materials will not be stored on premises except for very short periods of time. In addition, the unit will be operated by a state certified gas operator who has received special training from the manufacturer. The unit into which the waste is fed is approximately eight feet in diameter, nine feet high and cylindrically shaped. Through the use of natural gas, the burn chamber reaches a temperature of sixteen hundred degrees, a temperature at which no organisms can survive. The gases from the first burn chamber then circulate into the secondary burn chamber for two seconds, which is greater than the one second retention time required by DER rules. The only visible emission seen from the stack will be heat waves. All emissions will be well within the air quality standards utilized by DER. Any glass slag or ashes remaining in the unit can be handled as regular waste and disposed of in a class 2 landfill. Finally, the prevailing winds throughout most of the year are from the south and southeast and thus all emissions will blow primarily to the northwest across the sewage treatment plant area. d. DER's review of the application In connection with the processing of the application, DER reviewed it for completeness and accuracy and was satisfied that the application was complete and accurate in all respects, including the submission by applicant of a topographic map. In addition, DER staff conducted an on-site inspection of applicant's property. Also, during the course of the review, DER technical staff had a number of discussions with Williams to clarify the information submitted with the application. Finally, based upon its review of the data originally filed together with information provided by Williams during the review process, DER staff reached the preliminary conclusion that Williams had satisfied all applicable rules and statutes. Petitioner's Concerns In its amended petition, the County raised two principal concerns regarding the construction of the facility. First, it contended that its employees who worked in areas adjacent to the facility would be subject to harmful emissions from the unit. Second, it argued that the applicant had failed to give reasonable assurance that the unit would comply with all DER standards. During the course of the hearing, the County focused principally on the issues of (a) "hot spots", which are high concentrations of pollutants which may occur at a distance of ten feet up to as far as five hundred feet downwind from the point of emission if the stack height on the unit is not at an adequate height, (b) applicant's lack of a storage facility for waste to prevent the potential leaching into the ground of medical waste waiting to be incinerated, and (c) the agency's failure to require Williams to post proof of financial responsibility through a bond. These concerns will be addressed below. The agency does not have a have a specific stack height rule applicable to the incineration process but rather requires that the unit be constructed in accordance with good engineering practices and that it meet all emission requirements. At hearing petitioner's expert agreed that any potential "hot spots" problem would be resolved by applicant agreeing to utilize a stack having a height of at least two and one-half times the height of any building within one hundred fifty feet of the unit. Moreover, DER has required that Williams place a monitoring device on the stack so that all emissions can be measured 24 hours per day. Since the applicant has agreed to both of these conditions, this issue has been resolved. County employees occasionally work on several roads within Pine Subdivision, one of which is only 250 feet from the proposed facility. They also are engaged in the periodic maintenance of ditches which run along the sides of North Beal Street Extension, and eight to ten employees regularly work at the County landfill approximately 1,350 feet away. To this extent, then, it may be reasonably inferred that any potential injury suffered by County employees would differ in degree and kind from that suffered by members of the general public. Even so, with the resolution of the "hot spots" problem, the County's expert agreed that the proposed incinerator would meet all applicable requirements contained in Chapter 403, Florida Statutes, and that all pertinent agency rules would be satisfied. Thus, the employees would not be exposed to emissions that contravene DER's air pollution requirements. There is no evidence of record to support a finding that applicant should file a bond as a prerequisite to being issued a permit. Indeed, the only evidence on this issue suggests that DER requires a bond from an applicant when it believes the applicant has not proceeded in good faith or has a history of violating DER regulations. Neither situation is applicable here. As to the storage issue, the evidence shows that applicant will incinerate materials as often as needed, and waste materials will be kept on the premises only for brief periods of time when the unit is already filled and then only until those materials are burned and the unit is ready to receive new waste. Thus, as a practical matter, the facility will not be used to "store" waste materials within the meaning of that term. In addition, the area where waste materials will be kept until being fed into the unit will be an integral part of the treatment facility, and DER represents it has no authority to require Williams to submit information regarding storage areas associated with the incinerator. Put another way, in the construction permit review process, DER is concerned only with the air pollution source and the adequacy of the proposed control equipment. This was not contradicted. Finally, there was no evidence to suggest that the materials will leak into the ground. Indeed, petitioner's expert suggested only that the facility should be "secure" and that the material should be covered in the event of rain. The Required Reasonable Assurance Effective on an undisclosed date in 1991, new and more stringent DER rules became applicable to all new medical waste incinerators, including that proposed by Williams. Thus, his application was reviewed to determine its consistency with those new standards. An agency rule [rule 17-2.600(1)] provides that facilities with a capacity equal to or less than 500 pounds per hour, such as the Cleaver-Brooks 500 model, shall not have particulate matter emissions exceeding 0.100 grains per dry standard cubic foot of flue gas, corrected to 7% 0 or hydrochloric acid (HCL) emissions that exceed 4 pounds per hour. When operated as proposed by Williams, and as guaranteed by the manufacturer, emissions of small amounts of particulate matter and hydrocloric acid will not exceed those amounts allowed by rule. In addition, any emissions of water vapors and carbon dioxide will be in very small amounts and will not result in unlawful emissions. This finding is based upon the testimony of witnesses Middleswart and Dzurik which has been accepted as being persuasive on this issue. Thus, Williams has given reasonable assurance that the proposed facility will not cause air pollution in contravention of DER standards. The applicant has given reasonable assurance that the proposed facility will comply will all other applicable DER standards and rules. This was not controverted. Therefore, Williams has demonstrated his entitlement to the permit.
Recommendation Based on the foregoing findings of fact and conclusions of law, it is, RECOMMENDED that G. T. Williams' application for a permit to construct a biological waste incinerator adjacent to North Beal Street Extension, Fort Walton Beach, Florida, should be GRANTED subject to the following condition: That the applicant utilize a stack height of two and one-half times the height of any building within 150 feet of his unit. DONE AND ENTERED this 13th day of January, 1992, in Tallahassee, Leon County, Florida. DONALD R. ALEXANDER Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, FL 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 13th day of January, 1992.
Recommendation Based upon the findings of fact and conclusions of law recited above, it is recommended that petitioner's application for a permit to enlarge and expand its sewage treatment plant be DENIED. Respectfully submitted and entered this 30th day of December, 1976, in Tallahassee, Florida. DIANE D. TREMOR Hearing Officer Division of Administrative Hearings Room 530, Carlton Building Tallahassee, Florida 32304 COPIES FURNISHED: Mr. Harvey V. Delzer DELZER, EDWARDS, MARTIN, COULTER & PARKER P.O. Box 279 Port Richie, Florida 33568 Mr. Reynold L. Caleen, Jr. Acting General Counsel Department of Environmental Regulation 2562 Executive Center Circle, E. Montgomery Building Tallahassee, Florida 32301
The Issue Whether a permit should be issued to N. B. Willoughby Company to construct a 150 tons per hour asphalt plant.
Findings Of Fact N. B. Willoughby Company filed a construction permit application to construct a 150 tons per hour asphalt batch plant located three-fourths mile west of U.S. Highway 27, 800 feet south of Highway 544, and 700 feet east of Lake Hamilton Drive, in Winter Haven, Polk County, Florida. Mr. Jack Fross of Environmental Engineering Consultants, Inc. prepared the original application for submission to DER. Robert E. Wallace, a professional engineer registered in Florida who works for Environmental Engineering Consultants, certified that the engineering features of the project were in conformity with modern engineering principles applicable to the treatment and disposal of pollutants and that there was reasonable assurance that the pollution control facilities, when properly maintained and operated, would discharge an effluent that complied with all applicable statutes and rules and regulations of DER. Willoughby's application was reviewed by DER to ensure that all information required by law had been submitted and to determine whether Willoughby had provided reasonable assurance that the plant would meet the federal New Source Performance Standards. As a result of the review, DER determined that Willoughby had provided reasonable assurance and gave notice of its intent to issue a permit to the N. B. Willoughby Company to construct the asphalt batch plant in Winter Haven, Florida. The permit proposed to be issued to Willoughby is a construction permit which contains several specific conditions. The permit would allow Willoughby to construct the facility and would permit an initial period of operation for appropriate testing to determine compliance with DER rules. Thereafter, Willoughby would be required to apply for an operating permit. Other specific conditions imposed by the proposed permit include that the hours of operation of the plant shall not exceed 10 hours a day, 5 days a week; that the fuel used be number two fuel oil, with a maximum sulfur content of .3 percent, and that recycled asphalt shall not be used at the facility. Applications for permits must provide reasonable assurances that the installation will not cause pollution in contravention of DER rules. By rule, the Department of Environmental Regulation has adopted by reference the New Source Performance Standards contained in the federal regulations promulgated by the Environmental Protection Agency. There are two requirements that must be met by an asphalt plant. The plant must meet a emissions standard of no more than .04 grains per dry standard cubic foot, and the plant must meet a 20 percent opacity emission limitation. The .04 grains per dry standard cubic foot regulates the amount of particulate matter which can be emitted from the plant; the 20 percent opacity requirement limits the density of the smoke that emanates from the plant's stack. A construction permit application must provide reasonable assurance that the proposed facility will not discharge particulate matter in excess of .04 grains per dry cubic foot or discharge gases exhibiting 20 percent opacity, or greater. Reasonable assurance may be provided to DER by an applicant in three ways: the applicant may submit a written guarantee from the manufacturer that the facility will meet the prescribed standards; the applicant may provide test data from an identical facility; or the applicant may provide a professional engineer's certification that the source and its control equipment would meet the agency's requirements. In this case, Willoughby provided an engineer's certification and the manufacturer's guarantee. Test data from a similar plant was submitted, but DER could not substantiate the test data because the differences in the plants could not be determined from the information submitted. Therefore, DER required a manufacturer's guarantee. Although DER relied primarily on the manufacturer's guarantee as providing reasonable assurance that the plant would comply with the emission limitations, DER officials considered the entire application package in reaching their decision. The Willoughby application was routine and presented no unusual or novel difficulties. The asphalt batch plant proposed to be constructed by Willoughby is manufactured by Asphalt Drum Mixers, Inc. (ADM). ADM has been manufacturing asphalt drum mix plants since 1974 and has completed approximately 140 plants during that time. All of the plants manufactured by ADM have a similar design, but the model numbers vary based on differences in capacity and features. The model number for the Willoughby plant would be S7234-S. The first S indicates that a scrubber is on the frame; the 72 designates a drum diameter of 72 inches; the 34 reflects a drum length of 34 feet; and the last S shows that the plant is a stationary plant. The difference between a model number S7228-S and model number S7234-S would be six feet in drum length. A longer drum length provides a longer drying time and is used when there is a higher moisture content. No evidence was presented which would suggest that the length of the drum has any effect on the efficiency of the pollution control devices. The plant is equipped with a wet wash or scrubber which controls particulate emissions from the plant. The scrubber draws the hot gases from the drum. The gas travels at a high velocity through a venture, or throat, where it is sprayed with water. It is then spun in a separator. The water droplets, which have covered the particulate in the gas, go to the outside walls and are ultimately discharged into a settling pond. The rest of the gas goes into a center tube and through a- dewatering stack where more of the droplets are collected. The gas, cleaned of particulate, is then discharged into the atmosphere. The scrubber designed for the Willoughby plant is a sophisticated scrubbing operation, a state-of-the-art scrubber design. The scrubber will remove 99.95 percent of the particulate matter. The plant designed for Willoughby is rated at 150 tons per hour at 5 percent moisture and 280 degree product temperature. The capacity of an asphalt plant is determined largely by the moisture content. With a one or two percent moisture content the plant could produce a higher tonnage. However, a low moisture content is rare for Florida, and therefore the plant would normally be running at a lower capacity. At 150 tons per hour the particulate removed from the scrubber would be about 250-300 pounds per hour, or approximately three cubic feet. The pollution controls in the plant are designed to meet the .04 grains per dry standard cubic foot requirement, and ADM guarantees that the plant will perform at or below that level. In recent tests performed on four ADM plants similar to the proposed plant, emissions were under half the allowable level. An ADM portable plant located in Florida and manufactured in 1980 or 1981 meets state permitting requirements, yet it does not have the improved pollution controls incorporated into the Willoughby design. Although not required, a PTPLU computer modeling was conducted to measure the ambient air quality impact of the proposed plant. It revealed that the plant would have an insignificant impact on the ambient air quality. The test data provided to Willoughby from ADM and included in the application were from tests performed on a portable model 57228. The difference in the S7228-P and the proposed plant is that the Willoughby plant would have a drum six feet longer and would be stationary. A stationary plant is also equipped with a dewatering stack, and thus has better pollution control than a portable plant. The testing on the S7228-P showed an average emission of .0353 grains per dry standard cubic foot. The Willoughby application identified the specific emission point source as a "drum mix asphalt plant with venturi scrubber." However, in Section II, the project was described as construction of an "ADM Model S7232-P Drum Mix Asphalt Plant equipped with venturi scrubber." Obviously, the application gave the wrong model number based on ADM's method of assigning model numbers. Willoughby's plant will have a drum 34 feet long and will be stationary; therefore the model should have been designated 57234-5. However, the model number assigned is irrelevant in determining whether the plant will meet state pollution requirements. The permit application designates the project as an asphalt batch plant and designates the air pollution control device as a venturi scrubber. The manufacturer guarantees that the plant to be built for Willoughby will comply with the .04 particulate matter and opacity standards. The written guarantee does not mention any model number. The manufacturer's guarantee, as well as the test results on similar plants, provides reasonable assurance that the Willoughby plant will not discharge particulate matter in excess of .04 grains per dry standard cubic foot or discharge gases exhibiting 20 percent or greater opacity. The petitioners presented no evidence which would indicate that the proposed plant will not meet state air pollution requirements.
Recommendation Based on the foregoing findings of fact and conclusions of law, it is RECOMMENDED that the Department of Environmental Regulation enter a final order granting Willoughby's application for the construction of the asphalt plant, and issue the permit in question subject to the same conditions specified in the Notice of Intent to Issue. DONE and ORDERED this 29th day of April, 1987, in Tallahassee, Florida. DIANE A. GRUBBS Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32301, (904)488-9675 Filed with the Clerk of the Division of Administrative Hearings this 29th day of April, 1987. APPENDIX TO RECOMMENDED ORDER, CASE NO. 85-1032 Petitioners' Proposed Findings of Fact: Accepted as stated in paragraph 6. Accepted as stated in paragraph 13. 3 - 6. Rejected in that these paragraphs do not state factual findings but merely recite testimony given; however, paragraphs 6, 7, 12, and 13, address the substance of the paragraphs. 7 - 9. Rejected for reasons stated in paragraphs 12 and 13. Respondent Willoughby's Proposed Findings of Fact: Accepted in paragraph 1. Accepted in paragraph 2. Accepted in paragraph 3. Rejected as not finding of fact but recitation of testimony; however, substance accepted generally in paragraphs 2, 4, and 14. Accepted in paragraph 5. Accepted generally in paragraph 6. Accepted, to the degree not a recitation of testimony in paragraph 13. Accepted in paragraph 14. Respondent DER's Proposed Findings of Fact: 1. Accepted in paragraphs 1 and 2. 2. Accepted in paragraph 3. 3. Accepted in paragraph 5. 4. Accepted in paragraph 6. 5. Rejected as unnecessary and irrelevant, although would be accepted if deemed relevant. 6 - 9. Rejected, not factual findings but recitation of testimony; however, paragraphs 6, 8, 11, 7, 12, and 9 address substance. 10. Accepted in paragraph 9. 11. Rejected as irrelevant. DER did not indicate in the prehearing stipulation that standing was an issue. Therefore, petitioners were unaware that each of the 2,781 petitioners would have to testify to establish standing, and thus only a representative group of petitioners testified. COPIES FURNISHED: Thomas L. Boll, Esquire Murphy & Clark, P.A. Post Office Box 5955 Lakeland, Florida 33807-5955 Andrew R. Reilly, Esquire Reilly & Lasseigne Post Office Box 2039 Haines City, Florida 33844 Douglas M. Wycoff, Esquire Assistant General Counsel Department of Environmental Regulation 2600 Blair Stone Road Twin Towers Office Building Tallahassee, Florida 32301 Dale Twachtmann, Secretary Department of Environmental Regulation 2600 Blair Stone Road Twin Towers Office Building Tallahassee, Florida 32301
The Issue The issue is whether Respondent violated Subsection 489.129(1)(q), Florida Statutes (2008),1 by allegedly failing to satisfy within a reasonable time the terms of a civil judgment relating to the practice of the licensee's profession.
Findings Of Fact Petitioner is the agency charged with regulating building contractors in Pinellas County, Florida. Respondent is a building contractor, pursuant to license number C-6811 (RB0042337).2 Respondent is the primary qualifying agent for Timberlore Construction, Inc. (Timberlore). The business address of Timberlore is 2142 B Palm Harbor Boulevard, Palm Harbor, Florida 34683. On February 14, 2002, Timberlore contracted with Cox Air Conditioning and Heating, Inc. (Cox), for the installation of an air-conditioning system at a construction site at 19636 Gulf Boulevard, Indian Shores, Florida 33785. A dispute arose between Timberlore, as the general contractor, and Cox, as the subcontractor. As a result of the dispute, Timberlore sued Cox for breach of contract and negligence and for attorney’s fees and costs. After a non-jury trial, the court entered two final judgments. The first final judgment, entered on December 4, 2008, was a determination of liability. The court found that Cox was not liable for the failure of the air-conditioning unit that Cox had installed. Rather, the court found that excessive humidity caused the failure of the air-conditioning unit and damage to the premises and that the condition was aggravated by Timberlore. The court found that Cox was the prevailing party entitled to attorney’s fees and costs from Timberlore. The second final judgment against Timberlore determined the amount of attorney’s fees and costs. The court ordered Timberlore to pay attorney’s fees of $80,775.00 and costs of $30,423.79 plus annual interest of eight percent. Timberlore repaired the damaged air-conditioning system at the construction site. There is no harm to the consumer. Respondent disputes whether attorney’s fees and costs awarded by a court in a dispute between a contractor and a subcontractor relate to the practice of the licensee's profession within the meaning of Subsection 489.129(1)(q). The only evidence relevant to this issue was the testimony of Petitioner's witness.3 The fact-finder finds the testimony of Petitioner's witness after cross-examination to be credible and persuasive and agrees that the judgment for attorney’s fees and costs, under the facts and circumstances in this case, relates to the practice of the licensee's profession. Respondent has failed to satisfy a civil judgment obtained against the business organization qualified by the licensee within a reasonable time in violation of Subsection 489.129(1)(q).
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Pinellas County Construction Licensing Board enter a final order finding Paul W. Bourdon guilty of violating Subsection 489.129(1)(q) and suspending Paul W. Bourdon's license until the judgment is satisfied. DONE AND ENTERED this 27th day of April, 2010, in Tallahassee, Leon County, Florida. S DANIEL MANRY Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 27th day of April, 2010.
The Issue The issue presented is whether Respondent, S.M.G., Inc. (SMG), has provided reasonable assurance that its existing air curtain incinerator will be operated in accordance with applicable statutory and rule provisions.
Findings Of Fact The Parties The Department is the state agency responsible for receiving applications for, and the issuance of, permits for the construction and operation of air curtain incinerators in the State of Florida. SMG is a contracting company, with residential, trucking, agricultural, and commercial driver's license divisions. SMG is the applicant for a permit to operate an air curtain incinerator. Petitioners reside in Citrus County, Florida, in the vicinity of the constructed and operational air curtain incinerator. For the most part, Petitioners reside northeast, east, or southeast of the site. The Petitioners demonstrated their standing in this proceeding. SMG's Construction Permit On May 23, 2001, SMG submitted an application for an air construction permit to the Department's Southwest District Office. The application sought authorization to construct an air curtain incinerator "[o]n the east or west side of 6844 N. Citrus Avenue, Crystal River," Citrus County, Florida. 1 The general purpose of pursuing this permit was to burn wood waste. On July 9, 2001, the Department issued SMG a Notice of Intent to Issue the Proposed Air Construction Permit (Permit No. 0170360-001-AC). A copy of the Notice of Intent was published in the Citrus Times in Citrus County on July 19, 2001. On August 6, 2001, the Department issued SMG an air construction permit for the proposed air curtain incinerator. The construction permit authorized the construction of a McPherson Systems, Inc. - Model M30E air curtain destructor (incinerator) with under fire air at a natural non-Title V facility. Pursuant to the terms of the construction permit, in November 2001, SMG constructed an air curtain incinerator on approximately 500 acres of land on the east side of State Route 495 north of Crystal River in Citrus County, Florida, on property owned by the Gerrits family. See Endnote 1. Pursuant to the construction permit, SMG installed a McPherson Systems, Inc. - Model M30E air curtain incinerator with under fire air, a refractory lined burning pit, three upper chamber refractory lined walls (ten feet high), and a stainless steel spark arrester screen. The manifold blower and under fire air fans are powered by an electric engine. The manufacture designs and specifications for the McPherson model were submitted with the application for the air construction permit and admitted in evidence. Construction of a portable air curtain incinerator with a blower/fan system powered by a diesel-fired engine was contemplated by the air construction permit. Although cheaper, SMG instead chose to install the McPherson model that would produce the cleanest burn, i.e., one with fewer emissions, that was operated by electricity. The McPherson model used by SMG is recognized as an efficient, reliable model of air curtain incinerator. The diesel-fired blower/fan/engine system contemplated by the construction permit is considered exempt from permitting. An engine operated by electricity has no emissions and therefore does not require an air permit from the Department. The Department could not require a permit for the blower/fan system alone. The operating permit supercedes the construction permit, except as amended. Testing after Construction of the Incinerator On November 23, 2001, SMG began operating the air curtain incinerator. Pursuant to Special Condition 22 of the air construction permit, an initial visible emissions (VE) (opacity test) compliance test was performed on November 23, 2001, by Bernard A. Ball, Jr., an environmental engineer with Southern Environmental Services, Inc. The results of the initial VE compliance test were within the opacity limits contained in the construction permit. Specific Condition 19 of the construction permit requires SMG to maintain daily operating logs of the air curtain incinerator's daily operations. In order to obtain an air operating permit, a permit applicant is required to demonstrate compliance with the Department's rules and with the conditions of the construction permit. The Department requires an applicant for an operating permit to submit copies of recent daily operating records for the facility and copies of the emissions test required by the construction permit. These operating records are submitted in order for the Department to determine whether the applicant is complying with the applicable emissions standards and that the applicant is, in fact, maintaining the required operating logs as required by the construction permit. In order for SMG to obtain the operating permit for the incinerator, Specific Condition 28 of the construction permit required SMG to file an application for an air operating permit with the Department within 45 days of testing and required the application to include a copy of the VE test report and copies of at least two recent weeks of daily operating logs. On March 14, 2002, a second VE test was conducted by Mr. Ball, which also indicated that emissions were within the construction permit's opacity limits. On April 1, 2002, SMG submitted its application for the air operation permit to the Department. The application was signed by Sean Gerrits, and contained copies of the VE test reports for the November 2001 and March 2002 tests, as well as three and one-half months of daily operating logs, certificates showing that the incinerator operators were trained, and photographs of the incinerator in operation. SMG submitted the documentation required under the construction permit. On April 19, 2002, Robert E. Soich, Jr., air compliance inspector for the Department's Southwest District Office, performed an unannounced inspection and conducted a VE test in response to a complaint by Mr. Leonard Kaplan (a Petitioner), complaining of odors present. Excessive visible emissions were observed by Mr. Soich on April 19, 2002. The incinerator did not pass the VE test because of the improper alignment of the blade angle on the manifold of the blower system and because of green leaves and inadequate drying of the materials to be burned in the incinerator. Mr. Soich also observed, in part, that "materials need to be prepared better for burning." As a result of this unannounced inspection and the negative VE test, the Department requested SMG to provide an explanation of the VE test results and of the type of changes SMG planned to implement to correct the problem. On learning of the problem, SMG shut down the incinerator and called a McPherson mechanical contractor to come out and adjust the blade angle. Southern Environmental Services conducted another VE test to ensure the problem had been corrected. On April 22, 2002, a VE test was conducted by Southern Environmental Services on-site which showed compliance with the construction permit. On April 30, 2002, SMG advised the Department that adjustments were made to the baffles to correct the angles. SMG provided the Department with the April 22, 2002, VE test results. SMG also implemented better operational procedures. On May 30, 2002, with Mr. Soich present, SMG, by Byron E. Nelson, performed another VE test. The test results showed compliance with the opacity limits in the construction permit and the results were submitted to the Department.2 Mr. Nelson, an environmental engineer with Southern Environmental Sciences, testified that he has been involved in preparing approximately two dozen applications for air curtain incinerators and has conducted probably "thousands" of visible emissions tests. Mr. Nelson is certified by the State of Florida to conduct VE tests. He has seen "two or three dozen" air curtain incinerators in operation and has conducted VE tests on about 20 of them. Based on his experience, Mr. Nelson testified that SMG employed the same practices and controls to control odor, smoke, and fugitive emissions as other such incinerators he is familiar with. He testified that the amount of smoke and odors from the SMG incinerator is similar to that emitted from other air curtain incinerators, and that the fugitive emissions from the SMG incinerator were probably less than others he is familiar with. Based on his experience, Mr. Nelson opined that SMG has taken reasonable measures to minimize odor, smoke and dust/particulates from the operation of the incinerator. Mr. Nelson likewise opined that the SMG incinerator is well run, perhaps better run than other incinerators. (Mr. Nelson had been on the SMG site twice when the incinerator was operating and burning wood products.) Based on his experience, Mr. Nelson opined that SMG meets the requirements necessary to obtain an air operating permit from the Department and has demonstrated that it has complied with the conditions of its construction permit. Mr. Soich is the air compliance inspector for the Department's Southwest District Office. He testified that he has inspected the operations of other air curtain incinerators over the last 15 years. Mr. Soich testified that SMG is one of the "better operators" of air curtain incinerators he is familiar with. (Mr. Soich visited the SMG site approximately nine times from March 13, 2002, to October 15, 2002.) Mr. McDonald is the Air Permitting Engineer for the Southwest District Office of the Department. He is responsible for reviewing all applications for air curtain incinerators in the Southwest District and has reviewed applications for between 25 and 30 incinerators. Mr. McDonald reviewed the SMG permit applications. Based on the latest VE test results, copies of the records attached to the operating permit application, and his experience, Mr. McDonald, for the Department, determined that SMG had demonstrated compliance with the conditions of the construction permit and recommended issuance of the operating permit for the incinerator. He maintained the same position at hearing. SMG provided assurance that the DeRosa Fire Department would respond in the event of a fire at the incinerator. On June 19, 2002, the Department issued the proposed air operating permit. Operation of the Air Curtain Incinerator Emissions from the incinerator are controlled by a curtain of forced air at a very high static pressure over and around the burning pit. The air curtain traps smoke and small particles and recirculates them to enhance combustion and reduce smoke. The underfire air introduces air underneath the air curtain to ensure complete combustion and minimize opacity at start-up. The refractory-tiled ceramic concrete burn pit provides a safe combustion chamber, and the refractory panels keep excess heat from escaping. The upper chamber refractory panels, which surround three sides of the burn pit, allow more retention time in the burner to better control opacity and sparks. The stainless screen spark arrestor also controls sparks and debris from leaving the burner. The operating permit application proposed the use of an air curtain blower along with a manifold to provide forced air to the burning pit. According to the manufacturer specifications, the blower can force air into the pit at velocities of between 100 and 120 mph. This ensures that the flames in the burn pit receive enough oxygen to combust completely. The air circulates inside the burn pit to ensure a complete burn, which reduces smoke and odor. The combustion temperature for the burning pit ranges from approximately 1,800 to 2,500 degrees Fahrenheit. The operating permit allows a maximum charging rate of ten tons per hour on a daily average basis and 31,200 tons per any consecutive 12 month period. The incinerator has been operating below the maximum charging rate. The operating permit limits the hours of operation (charging) to 3,120 hours per year, i.e., ten hours/day, six days/week, 52 weeks/year. According to various SMG operating and maintenance logs, the incinerator has been operated below this limit. The operating permit, in accordance with Rule 62- 296.401(7), Florida Administrative Code, allows the burning of only wood waste, yard waste, and clean lumber, and prohibits the burning/incineration of materials such as sawdust, paper, trash, tires, garbage, rubber material, plastics, liquid wastes, Bunker C residual oil, roofing materials, tar, asphalt, railroad cross ties, or other creosoted lumber, chemically treated or painted wood, and other similar materials. Biological waste shall not be burned in the incinerator. During its operation, the incinerator only burned wood and yard waste, and Mr. Gerrits testified that the waste materials are inspected before being burned in order to ensure that no prohibited materials are burned. If any non-authorized materials are observed, they are removed before the waste is burned. See Finding of Fact 24. The operating permit allows visible emissions during start-up periods (not to exceed the first 30 minutes of operation) of an opacity up to 35 percent, averaged over a six- minute period, as provided for in Rule 62-296.401(7)(a)-(b), Florida Administrative Code. The McPherson model is designed to meet the requirements of the above-referenced rule, and the VE tests run during start-up periods (except one performed by Mr. Soich on April 19, 2002) demonstrated compliance with this requirement. Id. The operating permit limits visible emissions outside of start-up periods (the first 30 minutes of daily operation) to no more that five percent opacity, with visible emissions of up to ten percent opacity allowed up to three minutes in any one hour as provided for in Rule 62-296.401(7)(a), Florida Administrative Code, and 40 Code of Federal Regulations Part 60, Subpart CCCC, adopted and incorporated by reference in Rule 62- 204.800(8)(b)74, Florida Administrative Code. (Rule 62- 296.401(7)(a) permits up to 20 percent opacity. The ten percent rate is required by the new federal standard. See SMG Exhibit 13, page 3 of 9.) The opacity limits in the operating permit are more stringent than those contained in the construction permit, which allows visible emissions of up to 20 percent opacity up to three minutes in any one-hour period. (By definition, a "visible emission" is "[a]n emission greater than 5 percent opacity or 1/4 Ringelmann measured by standard methods." Rule 62-296.200(278), Florida Administrative Code.) The VE test results submitted by SMG demonstrate compliance with the opacity limits in the operating permit and with the opacity limits in the construction permit for the days tested. See Findings of Fact 18, 22, 27, and 29. The operating permit requires that the incinerator must be attended at all times while materials are being burned and that public access to the incinerator must be restricted. A certified operator is in attendance whenever the incinerator is operated, i.e., when something is burning in the incinerator. A fence has been constructed around the property. The operating permit prohibits starting the incinerator before sunrise and requires that all charging of the incinerator be completely stopped before sunset as required by Rule 62- 296.401(7)(h), Florida Administrative Code. Mr. Gerrits testified that the incinerator is never started before sunrise and is typically started after 8:00 a.m. Mr. Gerrits testified that the incinerator is never charged after sunset and that charging typically stops at 4:00 or 5:00 p.m. See Endnote 4. These practices are consistent with the Operations and Maintenance Guide for the incinerator. The operating permit limits the height of the ash in the burning pit to one-third of the depth of the pit or to a point where the ash begins to impede combustion, whichever occurs first as provided in Rule 62-296.401(7)(m), Florida Administrative Code. The one-third depth line is marked on the outside of the incinerator. Mr. Gerrits testified that ash is regularly removed from the burning pit every third day to keep the ash level low, which helps ensure better combustion and reduces smoke. The operating permit provides that material shall not be loaded into the incinerator in such a way that it will protrude above the air curtain. Testimony established that the SMG incinerator is properly loaded. The operating permit requires that all operators of the incinerator be trained in the proper operation and maintenance of the incinerator and that an operations and maintenance guide be maintained at the facility at all times. All of the operators of the SMG incinerator have taken a four-hour training course to learn how to operate the incinerator in accordance with Department regulations and good operating practices, and certificates attesting to that training were submitted with the application for the operating permit. An Operations and Maintenance Guide was submitted with the application for the construction permit. The operating permit requires the maintenance of a daily operating log. The daily operating log must be maintained at the facility for at least five years and must be available for inspection by the Department upon request. SMG currently maintains a daily operating log that meets the requirements of the construction permit. SMG submits those daily logs to the Department on a monthly basis after the Department requested that SMG do so. The log includes a date and site location, daily operating hours, total charges, total material charged in tons, average hourly charging rate, any maintenance performed, fuel usage in gallons, and the operator's signature. The logs of record contain this information and have been initialed by SMG's operator for each day when the incinerator has been operated. SMG operators responsible for preparing the logs have no incentive to indicate the incinerator is not operating on days or during hours when it is running, as a deliberate misstatement on the operating logs could result in enforcement action by the Department and being fired by SMG. The operating permit requires that all reasonable precautions be undertaken to prevent and control the generation of unconfined emissions of particulate matter in accordance with Rule 62-296.320(4)(c), Florida Administrative Code. SMG takes reasonable precautions to prevent and control the generation of unconfined emissions of particulate matter, including paving the road that leads to the incinerator to reduce dust, wetting the ashes removed from the burn pit, wetting the ash piles and ramp that addresses the incinerator, approaching the incinerator at a slow rate, and placing a charge into the incinerator slowly and carefully. SMG voluntarily added a sprinkler system on all four corners of the burning pit that was not contemplated by the construction permit. The Department witness Mr. McDonald testified that this provided an additional method to control unconfined emissions. Although the construction permit and proposed permit do not contain conditions prohibiting the burning of green wood or wet wood waste, SMG takes precautions at the request of Mr. Soich to ensure that the wood is properly dried before being burned. See Finding of Fact 24. This helps to reduce smoke and emissions from the incinerator. (Moisture is the primary factor that inhibits burning and causes smoke and potentially odor.) As part of the routine practice in handling the wood waste before it is burned, trucks bringing wood waste to the incinerator are instructed to dump it into a pile. SMG operators then use a loader to flatten out the pile and remove dirt, prohibited materials, and harvestable pieces of wood. Harvestable pieces of wood and dirt are removed to separate staging areas. The remaining wood waste is separated into long windrows, with the oldest row closest to the incinerator. The windrows are flipped or rolled over in the direction of the incinerator, allowing the waste to dry. The waste in the row closest to the incinerator is burned, and subsequent windrows are rolled over in its place. Ash is generally removed from the burn pit every third day; it is wetted on removal to reduce dust, and the ash piles adjacent to the incinerator are also kept wetted by the sprinkler system. The ash is eventually mixed with the dirt in a composter for use as Class-A unrestricted compost. The SMG operator in charge on a particular day decides whether the incinerator will operate that day, in accordance with standard operational practices. The operator checks the weather forecast. If it is raining or if there are high winds (over 20 miles per hour), the incinerator will not be operated that day, and SMG typically waits four days after a rain to begin operating the incinerator again. These procedures are not contained in any permit conditions. The purpose of not operating during or immediately after a rain and taking steps to ensure the wood is dry is to reduce smoke; wet wood smokes more. Rainy weather can also affect odor. The purpose of not operating during windy conditions is to reduce the possibility of fire on SMG's property, but wind can also affect odor and visible emissions. On days when the incinerator is not operating, SMG conducts yard maintenance, maintains the waste windrows, and runs the composter. The composter is a source of noise and is located adjacent to the incinerator and is run when the incinerator is shut down. To ensure that the visible emission limitations are not exceeded and objectionable odors3 not generated, the operating permit requires that the incinerator's fan shall continue to operate after the last charge of the day until all combustion (presence of any flame or smoke) has ceased. Generally, the incinerator keeps burning an hour to an hour and one-half. Mr. Gerrits testified that the fan is kept running until the flames and smoke die out and that a certified operator is present until the fan is switched off. The operating permit requires that the testing of visible emissions must be conducted within 90-100 percent of the maximum allowable charging rate of 10 tons/hour and shall be conducted when the highest emissions can reasonable be expected to occur.4 Testing of the SMG incinerator was conducted at within 90-100 percent of the maximum allowable charging rate of 10 tons per hour, and the May 30, 2002, test results indicated that the incinerator was operating within the opacity limits of its permit even when operating at close to maximum capacity. Evidence established that the May 30, 2002, VE test complied with the specific conditions of both the construction and operating permit. See Finding of Fact 29. The test method for visible emissions required by both the construction permit and the operating permit is EPA Method 9, adopted and incorporated by reference at Rule 62- 204.800(8)(b)74, Florida Administrative Code. (Method 22 is not required pursuant to Department rules for compliance testing of an air curtain incinerator.) Testimony established that Method 9 was the method used for the VE tests conducted on the SMG incinerator. As required by both the construction and operating permits, the incinerator is located in excess of 300 feet from any pre-existing occupied building located off site as required by Rule 62-296.401(7)(j), Florida Administrative Code. The closest residences, that of Mr. Gerrits' father and his tenant, are approximately 1,500 feet away. Petitioners' Challenge For the most part, Petitioners reside northeast, east, or southeast of the incinerator. One Petitioner resides approximately three-tenths of a mile southeast of the incinerator; others reside at greater distances, up to approximately a mile and one-half away from the incinerator. Each of the Petitioners who testified have resided in this area for many years, pre-dating the operation of the incinerator. The Petitioners who testified were credible and well- intentioned. Each of these Petitioners maintained daily logs covering several months when the incinerator was authorized to operate. Some kept logs for several months, while others kept logs for several days. They noted their observations and perceptions in the logs. Admittedly, Petitioners are not experts in the detection of odors or noise levels. Nevertheless, they recorded their own experiences as to what they saw, heard, and/or smelled, believing that the odors and noise came from the incinerator. Some recorded that they smelled the strong odor of smoke, an "acrid smell," a "pungent smell," for example; "it makes your eyes burn and throat burn" said another during the hearing. One witness described the experience as being a prisoner in his house. Another does not go outside when the smell is bad. Generally, the level of odor varied with the weather conditions, i.e., a stronger odor was noticed on foggy and wet days or nights and when the wind blows from the west, which Petitioners contend is the prevailing wind. Some witnesses only smelled the odor during the night and not during the day, and not all of the time. Some complained about the odor and noise, or one and not the other. Some believed the noise coming from the incinerator was a major problem. At least two witnesses who live approximately three-tenths of a mile and 3,500 feet, respectively, from the incinerator site, described the noise as being like a jet airplane. One witness shuts her windows to keep out the noise. (SMG also operates a "wood chipper" or "composter" on site which is loud. Mr. Gerrits stated that he did not think the sound was the same as made by the incinerator fan. He also stated that "[i]t doesn't exceed the noise decibels. It doesn't exceed background noise levels at [their] property line.") Petitioners documented their concerns which are described, in part, above, and also documented their complaints to the Department and local government. It appears that each of the logs prepared by the Petitioners (who kept logs) were given to Petitioner Martha Futscher, who summarized and compiled a hand-written master list of the complaints. Then, Mr. Harvey inputted this data on the master list (spread sheet) of complaints, which appears as Petitioners' Exhibit F1. The master list contains recorded observations from May 2002 through January 2003. The master list contains a representation of when the incinerator started and stopped for various days and when it was operational or not, and this information was derived, according to Mr. Harvey, from the logs maintained by SMG. The master list also provides tons per hour of waste burned on particular days, the observer's initials, and the approximate distance each observer lived from the incinerator, and the comments, with time of observation or perception noted. There are discrepancies between the master list and the actual logs maintained by SMG as to when the incinerator was operational. There also appears to be several differences in observations between the Petitioners' master list and other evidence which indicates when Mr. Soich inspected the incinerator and determined that the incinerator was operating satisfactorily. Compare Petitioners' Exhibit 2 with Petitioners' Exhibit F1. For example, the master list records an observation from May 30, 2002, when the incinerator was operating, when there was noise and smoke noted at 8:00 a.m., and flames at the incinerator and odor at 5:30 p.m. Conversely, Mr. Soich was on-site on May 30, 2002, and observed the scheduled VE test. No problems were noted with the operation on this date by Mr. Soich. Mr. Soich also noted that "wood waste was properly dry and free of debris." The VE test on May 30, 2002, was performed from 10:29 a.m. to 11:59 a.m. and showed compliance with opacity limits. The master list indicates that black smoke was observed (no time given) on May 7, 2002, when the incinerator was operational, yet Mr. Soich inspected the incinerator on that day and there is a notation in the record that the incinerator was operating between 0-5 percent visible emissions. (Mr. Soich opined that it should be very rare to smell objectionable odors if the visible emissions run at a 5 percent level.) For October 15, 2002, there is a notation in the master list that a Petitioner commented that the incinerator was running during the day ("AM/PM Running") and that there was a strong smell at approximately 7:05 p.m. A strong smell at the person's house was also noted at approximately 9:30 p.m. on that day. However, Mr. Soich performed an annual inspection of the incinerator on October 15, 2002, and there is a notation on the master list, Petitioners' Exhibit 2, that the incinerator was not operating due to recent rain. As one Petitioner testified, her point was that the inspectors are not there when she hears the noise, sees smoke, and smells the odor. Mr. Soich confirmed that he does not inspect the facility in the evening. Petitioners also provided, as evidence in support of their position, six videotapes of the incinerator for September 19, October 3, October 23, November 25 (2 tapes), 2002, and January 10, 2003. (Mr. Harvey took the videotapes from the same location, across the street and west of the incinerator.) Each tape, except for September 19, 2002, showed smoke emanating from the operational incinerator. On September 19, 2002, the incinerator was not running according to the SMG log. There was a malfunction which was reported to the Department. The SMG log indicates that the pit was cleaned out, site cleared and rows moved. There is also a notation in the SMG log for this date that there was a power failure/malfunction at the incinerator at 9:00 a.m., and that the power was out. According to Mr. Gerrits, the malfunction caused smoke. (One Petitioner observed smoke from ashes on September 19, 2002.) While the Petitioners proved that there was smoke emanating from the operation of the incinerator on the days which were videotaped, with the exception of September 19, 2002, this did not necessarily prove that the emissions exceeded the requirements of the Department rules or that there was an objectionable odor emanating therefrom. Mr. Stoich observed the videotapes played during the hearing. In particular, with respect to the January 10, 2003, videotape, Petitioners' Exhibit 12, Mr. Stoich stated that a level of opacity cannot be determined from photographs and videotapes. He also noted that there was "a lot of white smoke," an atypical situation according to him, emanating from the incinerator and that he, as a compliance inspector, would have investigated further and performed an inspection, including a VE test, to determine if there was a violation, had he seen this smoke. However, he stated that without actually seeing the operation, he could not determine whether a violation had occurred. There was persuasive evidence that compliance with the opacity limits of a permit can only be determined through VE tests conducted using the Department-approved EPA Method 9. The VE test takes into account wind, the angle of the plume, the position of the sun, and other factors, and must use appropriate averaging to ensure that the test is valid. A smoke plume can look quite dense at the wrong angle or if the light is reflecting off the plume in a certain way, when in fact it is in compliance with Department rules. The VE tests for the incinerator have, with one exception, see Finding of Fact 24, demonstrated compliance with the opacity limits in the construction permit. As noted herein, upon receipt of notice that one VE test failed, SMG implemented corrective actions, and two VE tests conducted after the time showed the incinerator was operating in compliance with the opacity limits of the permit. See Findings of Fact 27 and 29. The Department relies on its compliance inspectors, such as Mr. Soich, to make a determination of whether an air emission source is causing an objectionable odor. There does not appear to be an approved Department method for measuring odors from incinerators. (Mr. Nelson stated that odors are difficult to test and that "odor is done collecting samples." No samples were taken or analyzed.) On the other hand, Mr. Soich testified that, based on his years of experience, he has developed certain methods for determining whether a facility is emitting an objectionable odor under the rules. If he receives an odor complaint, which he has in this case, he goes to the site and checks the prevailing winds. He also travels around the facility to determine the source of the odor. An odor can be deemed objectionable if it is very strong and overpowering, such that he cannot stay on- site and breathe in the odors. An odor can also be deemed objectionable if, after being on-site for some extended period of time, he begins to develop symptoms such as runny eyes, a scratchy throat, or a headache as a result of the smell. Finally, he may bring along another Department employee to determine whether the other individual finds the odor objectionable. Enforcement actions can be taken if objectionable odors are detected. Mr. Soich testified that he has inspected the incinerator at least nine times in the past year and never detected an objectionable odor. On some of the visits, the incinerator was not operational. On rebuttal, several residents of the area testified that they had not experienced objectionable odors from the incinerator. David Stevens, the Chief of the DeRosa County Fire Department, testified that an open land-clearing burn emits black smoke, more so than he observed from the incinerator. This fire department only had to respond to false alarms at the incinerator. Mr. Stevens personally inspected the operation of the incinerator and thought it was a very safe operation. Randy Morgan, a wildlife firefighter and certified burner with the Division of Forestry with over 16 years of experience in fire control, testified that approximately 50,000 acres of the state land burns occurred in Citrus County last year. These land burns can be a significant source of smoke and odor. In addition, approximately 50 open burn authorizations are issued each day. He also testified that controlled burns of approximately 15 fires of approximately 50 to 2,000 acres a day occurred in 2002 in proximity of the SMG incinerator which is a source of smoke and odor. The state also conducts open burns of some kind approximately ten months out of the year. Other witnesses testified that, given the rural nature of the community, open burning of trash, wood, and leaves occurs on a regular basis. Ultimate Findings of Fact Credible evidence established that SMG meets or exceeds the requirements in the construction permit to reduce smoke, dust, and odor, and these requirements are carried over to the operating permit. Credible evidence established that SMG employs the same, if not better, practices and permit conditions to control smoke, dust, and odor as other air curtain incinerators in the state. Credible evidence established that the SMG incinerator is operated in accordance with its construction permit. Credible evidence established that the SMG incinerator can be expected to be operated in accordance with its operating permit. Credible evidence established that the SMG incinerator is operated in accordance with Department rules. In light of the foregoing, SMG has demonstrated reasonable assurance that its air curtain incinerator has been operated in compliance with the construction permit and that the incinerator can continue to be operated in accordance with the conditions of the operating permit.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Environmental Protection enter a final order granting SMG's application and issuing Permit No. 0170360-002-AO, as amended, and subject to all conditions, including but not limited to the Specific Conditions set forth in the Department's Notice of Intent to Issue, for the operation of an air curtain incinerator in Citrus County, Florida. It is further recommended that Petitioners' challenge to the amendment to the operating permit be dismissed. See Preliminary Statement. DONE AND ENTERED this 21st day of April, 2003, in Tallahassee, Leon County, Florida.5 CHARLES A. STAMPELOS Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 21st day of April, 2003.
Findings Of Fact On January 23, 1985, following the filing of the and its on-site inspection, DER issued its notice of intent to grant the air construction permit, pursuant to Chapter 403, Florida Statutes (F.S.), and Chapters 17-2 and 17-4, Florida Administrative Code (F.A.C.). The notice stated that the proposed equipment, with a cyclone primary dust collector followed by a Dustex Baghouse Model DW-14-28W dust collector, was adequate to insure compliance with DER particulate emission standards. The ambient air standards for sulfur dioxide emissions by the plant were to be controlled by the use of low sulfur fuel oil (maximum 0.5 percent sulfur). Subsequent to the issuance of the notice of intent, DER received a Petition for Administrative Hearing regarding the issuance of the permit. The petition alleged, inter alia, that the plant would emit particulates and gases in contravention of Chapter 17-2, F.A.C., and that stormwater run-off from the plant would be contaminated with oil, scum and debris. The petition further asserted that this run-off would cause water pollution in contravention of Chapters 17-3 and 17-25, F.A.C., and would introduce pollution into Dry Branch and Bayou George, a Class I Water. The permit application covers only the proposed batch plant site and the immediately adjacent property consisting of 2.15 acres. The location of the building would be at the northern end of the parcel, approximately 0.10 miles from both Star Avenue and U.S. Highway 231. There is no residential use of property immediately adjacent to the project site. However, Petitioners all reside in the immediate area, and will be affected to some extent by this facility. Dust from construction activity has already been experienced. In this regard, it must be recognized that the area has no zoning restrictions and is therefore subject to industrial uses such as that proposed here. The Applicant owns several acres of property surrounding the location of the proposed batch plant. The permit application at issue covers only the request to construct the facility on a 2.15 acre portion of the larger parcel. Anticipated environmental problems caused by activity not on the immediate parcel are not related to this permit application and thus are not germane to a determination whether the permit should be issued or denied. Further, the construction permit will only allow the applicant to build the proposed air pollution source. Before such a source can actually be operated, a separate operation permit application must be made, and testing for compliance with standards by the facility must be satisfactorily completed. Petitioners demonstrated that the individuals who own Triangle Construction Company, Inc. were previously employed by Gulf Asphalt Company, which was occasionally out of compliance with state air emission standards. Petitioners asserted that these individuals would likely fail to operate the proposed facility in compliance with DER standards. Although these individuals did have managerial responsibility at Gulf Asphalt, final decisions concerning financial expenditures for repairs and maintenance were made by the owner of the plant, rather than the Applicant's owners. It was also established that the Gulf Asphalt Plant continued to have emission problems after such individuals left as employees. Petitioners contend the Applicant's unrelated dredging activities in an adjacent borrow pit area caused turbidity in Dry Branch Creek, and characterized the Applicant as a habitual violator who could not be expected to comply with state pollution control regulations in the operation of the proposed facility. Testimony revealed that the Applicant constructed a culvert in Dry Branch, which flows through a borrow pit area and did some other incidental dredging in areas within the landward extent of waters of the state. However, when the Applicant became aware that activities in the proposed borrow pit area were potentially in violation of DER rules, it ceased activities and applied for the appropriate permits. An asphalt concrete batch plant is a relatively simple operation in which sand and aggregate are dried, then mixed with hot liquid asphalt and loaded directly into trucks. It is the drying process which emits the particulates which the cyclone and the baghouse are designed to control. Baghouse operations are similar to those of a vacuum cleaner. Particulate-laden air from the drying process is vented into the baghouse, where it is filtered through a number of cloth bags. The bags trap the particulates, and pass the filtered air through the bag cloth and out of the building. When enough air has been filtered to cause a build-up of trapped particulates, a portion of the baghouse is taken off cycle and reverse air is blown through the bags. The reverse air causes the trapped particulates to fall into a hopper where they are removed for disposal. The baghouse was designed to function efficiently in conjunction with a plant producing up to 120 tons per hour of asphalt concrete. Applicants's plant will produce only 80-85 tons of asphalt concrete per hour due to the limited size of the dryer. The estimated air to cloth ratio in the amended permit application is 6:1, which will result in emissions substantially lower than DER standards. Air to cloth ratio is not a specific standard or requirement, but is a figure which is used by engineers to determine projected emissions which may reasonably be anticipated from facilities which use an air pollution control mechanism. A projected air to cloth ratio of 6:1 for this baghouse may be reasonably expected to yield emissions of approximately 0.014 micrograms per dry cubic foot, which is approximately one-third of the DER standard of 0.04 mg. per dry cubic foot. The equipment to be installed is used and in need of minor repairs. The testimony established that necessary repairs will be accomplished prior to plant activation, and that operations will not be adversely affected when such repairs are complete.
Recommendation Based on the foregoing, it is RECOMMENDED that the Department of Environmental Regulation issue a final order granting Triangle Construction Company an air construction permit. DONE and ENTERED this 21st day of June, 1985, in Tallahassee, Florida. R. T. CARPENTER Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32301 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 21st day of June, 1985. COPIES FURNISHED: Lynn C. Higby, Esquire BRYANT, HIGBY & WILLIAMS, P.A. Post Office Box 124 Panama City, Florida 32402 E. Gary Early, Esquire and Clare E. Gray, Esquire Department of Environmental Regulation 2600 Blairstone Road Tallahassee, Florida 32301 Richard Smoak, Esquire SALE, BROWN & SMOAK Post Office Box 1579 Panama City, Florida 32402 Victoria Tschinkel, Secretary Department of Environmental Regulation Twin Towers Office Building 2600 Blairstone Road Tallahassee, Florida 32301
Findings Of Fact This cause comes on for consideration based upon the petition of John C. Walker and others, residents of Fort Myers, Florida, who have challenged the Respondent, State of Florida, Department of Environmental Regulation's intention to grant a Complex Air Source Permit to the Respondent, Lee County Board of County Commissioners, for purposes of constructing a four-lane road at Daniels Road, Lee County, Florida. The Respondent, State of Florida, Department of Environmental Regulation, is an agency charged with the promotion and protection of air quality within the State of Florida. The authority for this function is found in Chapter 403, Florida Statutes, and various rules enacted to implement the provisions of this statute. Specifically, as it pertains to this dispute, the Respondent, State of Florida, Department of Environmental Regulation, is charged with the maintenance of Ambient Air Quality Standards. The standards are set forth in Chapter 17-2, Florida Administrative Code. To carry out this function, Rule 17-2.06, Florida Administrative Code, has been enacted, which establishes maximum limiting levels for Ambient Air Quality Standards. This sets the allowable limits for pollutants existing in the ambient air, the purpose for such standards being the protection of human health and public welfare. It involves the consideration of the pollutants, sulphur dioxide, particulate matter, carbon monoxide, photochemical oxidants (by measurement and correction for interference due to nitrogen oxide and sulphur dioxide), hydrocarbons (used as a guide in devising implementation plans to achieve oxidant standards, to be measured and corrected to methane), and nitrogen dioxide. The Respondent, Lee County Board of County Commissioners, is a unit of local government in the State of Florida charged with the function of carrying on the business of government for that county, to include the construction of those roads necessary to accommodate the needs of the public. To that end, on February 1, 1978, the Respondent, Lee County Board of County Commissioners, applied for a Complex Air Source Permit to be granted for the construction of a four-lane road at Daniels Road, Lee County, Florida. Subsequent to that initial application, revisions of the data provided in support of the application were made on October 12, 1978, and again on January 19, 1979. That application, as revised, may be found as the Respondent's (Lee County) Exhibit No. 1 admitted into evidence and includes aerial photographs. On May 4, 1978, through the person of Phillip R. Edwards, District Manager of the State of Florida, Department of Environmental Regulation, South Florida District, an indication was given that the department intended to issue a Complex Air Source Permit to the Lee County Board of County Commissioners. This exhibit is found as the Respondent's (Lee County) Exhibit No. 2 admitted into evidence. An engineer for the South Florida District, State of Florida, Department of Environmental Regulation, has made a review of the revisions in addition to the original application and is still of the persuasion that the Complex Air Source Permit should be granted. This letter of intent to grant the permit makes reference to the permitting chapter of the Florida Administrative Code pertaining to Complex Air Source Permits and other types of permits. Rule 17-4.07, Florida Administrative Code, sets out the general criterion which must be met prior to the issuance of the Complex Air Source Permit. That provision establishes the need for the applicant to affirmatively provide reasonable assurances based on its plans, test results and other information that the construction of the road and operation on that road will not discharge, emit or cause a violation of the Ambient Air Quality Standards set forth in Rule 17-2.06, Florida Administrative Code, previously referenced. In this case, those assurances have been given. In examining the particular pollutants set out in the Ambient Air Quality Standards table, sulphur dioxide and particulate matter are not items of significant concern, because motor vehicles do not promote the emission of those pollutants in quantities sufficient to exceed the maximum limiting levels. In measuring the amount of carbon monoxide, Lee County utilized a technique known as the representative site method, to be applied in the Cal-Air Model. The ecolyzer which measures this pollutant, was placed in various locations near the intersection of U.S. 41 and Daniels Road, with the object in mind to achieve the gravest readings as a basis for projecting the future amounts of carbon monoxide that would be present in the area of the proposed road expansion. The traffic projections and average speed at the intersection were factored in by Joseph Ebner, P.E., an expert in traffic engineering. The most recent statement of those traffic projections may be found in the January 19, 1979, revision to the application offered by the Respondent, Lee County Board of County Commissioners, which is a part of that Respondent's Exhibit No. 1. In that revision, as was the case of the revision of October 12, 1978, and the original application, the average speed at the intersection was established at fifteen miles per hour, calculated from an engineering textbook, "Highway Capacity Handbook (1975), Highway Research Board, Special Report No. 87". This represents the lowest average speed for an eight-hour period in a signalized intersection of an urban area. In arriving at the traffic count calculations, Mr. Ebner relied on the Lee County Transportation Study, Technical Report No. 6, which contains traffic projections for the year 1990. A copy of this report may be found as Petitioner's Exhibit No. 10 admitted into evidence. The statistics found in that report take into account the projected construction of a regional airport located east of Interstate-75 on Daniels Road, to be opened in the year 1982, and the Opinion that Canal Road, which will intersect with Daniels Road, will be opened in that same year. Calculations made in the January 1, 1979, revision are based upon the belief of a rate of increase in traffic to be eight percent per annum in the area of the intersection of U.S. 41, Cypress Lake Drive and Daniels Road. (At this point it should be indicated that the calculations in the revision of January 1, 1979, labeled, 8-hour Co. Concentrations, U.S. 41 & Cypress Lake Drive [natural traffic mix], are improperly depicted in the columns entitled, "U.S. 41 and Cypress Lake Drive" and must be transposed in their labeling to arrive at the proper mathematical result.) When that adjustment is made, it is established that the highest concentration of carbon monoxide in an eight-hour period in the intersection of U.S. 41 and Cypress Lake Drive in the location of the northwest quadrant for the years 1980 through 1990 was in the year 1980. In that year the measurement would be 9.13 mg/m3 in an eight-hour period. The second most severe year is 1981, in which the measurement is 9.10 mg/m3 as the highest eight-hour carbon monoxide concentration levels in that intersection. The balance of those measurements for the years 1982 through 1990 may be found in the Respondent's, Lee County Board of County Commissioners, Exhibit No. 1 in the January 19, 1979, revision to the permit application. Finally, it should be indicated that the projections made by the Lee County Board of County Commissioners in its application are premised upon a vehicular mix of ninety-four percent automobiles and six percent trucks. Tom Davis, an engineer for the Department of Environmental Regulation, who has the responsibility to review permit applications for Complex Air Source Permits, was involved in advising the applicant on the requirements for compliance for the granting of the permit. Through his involvement, Mr. Davis has been satisfied with the techniques used by the applicant in its efforts at measuring the carbon monoxide and the modeling necessary to answer the ultimate question of whether or not this project will violate the Ambient Air Quality Standards. In this instance, Mr. Davis does not believe those air quality standards will be violated. His testimony established that there are no models designed specifically for the measurement of photochemical oxidants, hydrocarbons or nitrogen dioxide. The hydrocarbons and nitrogen dioxide are area wide phenomena and are not subject to such specific site measurement. However, the area wide monitoring which has been done for nitrogen dioxide throughout the State of Florida, and more particularly in Lee County, Florida, has never shown that pollutant to exceed ten percent of the maximum limiting level. Moreover, carbon monoxide, hydrocarbons and nitrogen dioxide are felt to decrease at roughly the same percentage rate throughout the years, so that the decrease in the carbon monoxide levels at the project site beyond 1980 would reflect a similar decrease at that site in the amounts of hydrocarbons and nitrogen dioxide. Therefore, if there are no problems with carbon monoxide there is no reason to believe that there would be a problem with hydrocarbons and nitrogen dioxide, nor with the photochemical oxidants which are a bi-product of hydrocarbons and nitrogen dioxide combinations. These opinions stated herein are those of Mr. Davis, and David Barker, Ph.D., an air quality expert who testified in behalf of the Respondent, Lee County Board of County Commissioners, agrees. As indicated, these opinions are well founded. Notwithstanding the belief that the Respondent, Lee County Board of County Commissioners, has complied with the requirements of law, an examination of the Petitioners position would seem to be indicated. The Petitioners' argument against the approval of the Complex Air Source Permit falls into two broad categories. The first of those categories has to do with the allegation that the Respondent, Lee County Board of County Commissioners, failed to comply with the instructions in the application form. After considering the testimony in this cause and the exhibits submitted, this contention on the part of the Petitioners is rejected. The second basis for attacking the application concerns the techniques for gathering and applying the data which was utilized by the Respondent, Lee County Board of County Commissioners, in their efforts to establish reasonable assurances that the project would not violate Ambient Air Quality Standards in terms of the maximum limiting levels set forth in Rule 17-2.06, Florida Administrative Code. To this end, the Petitioners offered a series of competing statistics through their exhibits, in terms of traffic projections. In addition, their expert on air quality, Dr. Detar, was of a different persuasion on the question of the average automobile speed through the signalized intersection U.S. 41 and Daniels Road. In Dr. Detar's mind the average speed would be eight miles per hour as the low average speed for an eight-hour period. In view of all the testimony, this projection of the low average speed is not found to be acceptable. Finally, the Petitioners were of the persuasion that the average mix of automobiles and trucks in the area of the project would be more along the lines of the national average of eighty percent cars and twenty percent trucks. The studies conducted by the Respondent, Lee County Board of County Commissioners, in prior projects demonstrated the efficacy of the ninety- four percent automobiles and six percent trucks standard. In measuring other sources of pollution than sulphur dioxide and particulate matter (which the Petitioners do not question in this case), Dr. Detar believed that hydrocarbons and nitrogen dioxide could be modeled. His explanation of the modeling technique, when contrasted with the argument of the Lee County Board of County Commissioners and the State of Florida, Department of Environmental Regulation, to the effect that those two substances may not be modeled on a specific site basis, failed to be persuasive. In summary, in contrasting the evidence offered in behalf of the Petitioners with that offered in behalf of the Respondent; the Respondent, Lee County Board of County Commissioners, has demonstrated reasonable assurances that maximum limiting levels of the applicable pollutants will not be exceeded in the area of the project. The various memoranda and proposed findings of fact and conclusions of law have been reviewed by the undersigned, and to the extent that those items are not inconsistent with the findings of fact rendered herein and conclusions of law and recommendation, they are hereby acknowledged by the entry of this Order. To the extent that those aforementioned items are inconsistent with the findings of fact, conclusions of law and recommendation by the undersigned, they are rejected.
Recommendation It is recommended that the Respondent, Lee County Board of County Commissioners, be granted a Complex Air Source Permit for the construction of the improvements at Daniels Road, Lee County, Florida. DONE AND ENTERED this 1st day of March, 1979, in Tallahassee, Florida. CHARLES C. ADAMS Hearing Officer Division of Administrative Hearings Room 101, Collins Building MAIL: 530 Carlton Building Tallahassee, Florida 32304 COPIES FURNISHED: E. G. Couse, Esquire Grace & Couse, P.A. Suite 202, Courtney Building Post Office Drawer 1647 Fort Myers, Florida 33902 L. Caleen, Jr., Esquire General Counsel Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32301 Beverly E. Myers, Esquire Assistant County Attorney Lee County Post Office Box 398 Fort Myers, Florida 33902 ================================================================= AGENCY FINAL ORDER =================================================================
The Issue Whether Respondent is in violation of various provisions of Chapter 403, Florida Statutes, as alleged in the Notice of Violation and Orders for Corrective Action dated October 30, 1991.
Findings Of Fact BEI's composting facility is a potential source of water and air pollution and to operate the facility, BEI requires a permit issued by DER. The original permit issued to DER for this facility expired on June 1, 1991 and has not been renewed. Although its permit had expired, BEI was allowed to continue to operate while informal proceedings were ongoing between BEI and DER. When these informal proceedings were terminated by DER on May 20, 1992, further operation of this composting facility was in violation of Chapter 403.707(1), Florida Statutes, and Rule 17-709.400(1), Florida Administrative Code. On at least two occasions while this composting facility was in operation, the air around the facility was polluted by foul odors. During the period following the expiration of BEI's license, BEI failed to submit monthly operating reports and did not conduct quarterly samplings and testing of the compost and submit the testing to DER as required.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Secretary of the DER enter a Final Order finding that BEI has violated Section 403.161(1)(b), Florida Statutes, on each of five counts; and that BEI should immediately cease operation of its solid waste facility, volume reduction plant, until and unless it obtains an appropriate and valid permit from DER and in that regard, BEI shall: Immediately cease acceptance of all materials on the property. In the event that Respondent does not receive a permit from the Department to resume operations at the facility, within 90 days of the effective date of the Final Order, Respondent shall remove all solid waste from the property to an approved solid waste management facility and provide the Department written documentation of its disposal within 30 days of removal. In the event that Respondent does receive a permit from the Department to resume operation at the facility, Respondent shall remain in strict compliance with all terms and conditions of such permit. Within 30 days of the effective date of the Final Order, Respondent shall, if it has not already done so, provide the following to the Department: All records of testing and monitoring conducted on the compost material since January 1, 1990, including daily reports on the temperature and moisture content of compost material, and any testing of compost material conducted prior to distribution. All records documenting application rates of stillage, manure, and leachate to the compost withdrows since January 1, 1990. All records, documenting distribution of composted or mulch material, including amount of compost or mulch material delivered, date of delivery, specific destination of compost or mulch, and intended use of compost or mulch material delivered, since January 1, 1990. All records documenting amount of yard trash received at the facility since January 1, 1990. Within 30 days of execution of the Final Order, Respondent shall make payment to the Department for costs and expenses in the amount of $500.00. Payment shall be made by, cashier's check or money order to the "State of Florida Department of Environmental Regulation". Payment, specifying Office of General Counsel Case No. 91-2006, shall be sent by certified mail to Administrator, Division of Waste Management, Department of Environmental Regulation, 3804 Coconut Palm Drive, Tampa, Florida 33619. DONE AND ENTERED this 16th day of June, 1993, in Tallahassee, Florida. K. N. AYERS Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 16th day of June, 1993. COPIES FURNISHED: Tracey S. Hartman, Esquire Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Howard C. Batt, Esquire 611 Druid Road East Suite 712 Clearwater, Florida 34616 Virginia B. Wetherell, Secretary Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Ken Plante, Esquire General Counsel Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32399-2400
