The Issue Whether Petitioner should be granted a water pollution operation permit for the Bennett Road Sewage Treatment Facility under Chapter 403, Florida Statutes.
Findings Of Fact Petitioner owns and operates a sewage treatment plant known as the Bennett Road Sewage Treatment Facility in Orlando, Florida. The plant was originally built in the 1950's and its method of treatment has been modified and improved over the years. At the present time, the plant serves about 60 percent of the sewage treatment needs of the city. The sewage is first treated for the removal of biological compounds by means of trickling filters, followed by chemical treatment for removal of BOD, suspended solids, and phosphorus. In the latter process, aluminum sulfate is used, together with a polymer to assist in forming larger particles for more rapid settlement. These processes are followed by final settling, clorination and discharge through an outfall pipe approximately five miles to the Crane Strand Creek and thence to the Little Econlockhatchee River (Little Econ) which meets the Big Econlockhatchee River approximately twelve miles downstream and flows into the St. Johns River twenty- seven miles downstream. About 60 percent of the flow from Crane Strand Creek into the Little Econ is derived from the Bennett Road plant and there is no other significant source of pollutants from the remainder of the discharge. (Testimony of Jewett, Matthes, Petitioner's Composite Exhibits 1,2) In 1973, Respondent's predecessor, the State Department of Air and Water Pollution Control, issued a temporary operation permit to Petitioner, subject to certain conditions, for the Bennett Road plant. The permit was effective until June 1, 1976, "or sooner pursuant to the permittee upgrading his facility to provide 90 percent treatment and obtaining an operation permit in accordance with the rules and regulations of the Department Of Pollution Control." On May 7, 1976, Petitioner submitted an application for an operation permit wherein it was stated that the facility would be abandoned as soon as the Orlando Easterly Regional Facilities were constructed with a new treatment plant to be located in the vicinity of Iron Bridge Road. Respondent's manager of the St. Johns River District advised Petitioner by letter of July 21, 1976, of the Department's intent to deny the application for an operating permit. The reasons given were that (1) available data was insufficient to show sustained secondary treatment as defined in Chapter 403, Florida Statutes, and Chapter 17- 3, Florida Administrative Code; and (2) the facility's discharge caused violation of Section 17-3.09(3), F.A.C. The latter provision establishes one of the criteria for classification of Class III waters and provides generally that the concentration of dissolved oxygen in all such surface waters shall not average less than 5 mg/l in a twenty-four hour period and never less than 4 mg/l. Class III waters are designated in Rule 17-3.09 as "Recreation - propagation and management of fish and wildlife." In its above-mentioned letter, Respondent suggested that the Petitioner apply for a temporary operation permit. Petitioner chose to request an administrative hearing on the proposed denial and did so by petition filed herein on August 5, 1976. At the commencement of the hearing, the parties orally stipulated that Petitioner has been meeting the statutory and regulatory requirements as to secondary treatment so as to warrant withdrawal of Respondent's objection to granting the permit on that ground. The parties also agreed that the only matter remaining in issue is the question of whether Petitioner's discharge violates water quality criteria. (Petitioner's Exhibits 6,7) Petitioner began consideration of the need to replace or expand the Bennett Road plant about 1968. These plans have reached a stage where the Petitioner is now in the process of purchasing land and concluding a planning study required under federal law to construct a regional facility to service the eastern part of Orlando and a few of the northerly communities, including some in Seminole County. Such regionalization of sewage treatment facilities is encouraged by the federal government which provides 75 percent of the funding necessary for construction under Public Law 92-500 . It is anticipated that the proposed facility will be completed in 1980 at which time the Bennett Road plant will cease operations. The regional facility is to be located at Iron Bridge Road and its discharge would flow into the Little Econ several miles downstream of the present Bennett Road discharge. (Testimony of Matthes, Schneider, Petitioner's Composite Exhibit 2) Operation permits have been granted from 1971 to 1976 to a number of sewage treatment plants that will tie-in to the proposed regional facility. These permits were issued even though the discharge of most of the plants did not meet water quality standards. However, practically no secondary treatment plant can meet water quality standards in Central Florida without an extensive mathematical "modeling." These calculations made by Respondent are formulated from surveys of the body of water in question and result in what is termed "a waste load allocation." This term deals with a treatment standard that is computed to ascertain the assimilative capacity of a receiving body of water to take in pollutants from a particular source in order that water quality standards in terms of dissolved oxygen levels may be maintained. The waste load allocation is the standard which the treatment from the source must perform before it can be discharged. None of the above-mentioned plants nor the Bennett Road plant had been provided an assigned waste load allocation at the time of Respondent's adverse action on Petitioner's application. Neither had it been a past requirement of Respondent to require information concerning dissolved oxygen from an applicant in order to issue an operation permit. However, a preliminary survey of the Little Econ had been completed by Respondent by February 1976, and from this, a mathematical model was later computed based on chemical analysis of water samples taken from designated areas in that body of water. In the aforesaid permits that were granted, a clause provided that the plants would have to work with the City of Orlando in resolving discharge problems and cooperate in the achievement of a regional system. Although water quality criteria had not changed in recent years, they had not been enforced because Respondent had had insufficient background water data. At the time Petitioner's permit application was recommended for denial, the primary basis therefor was the fact that the Bennett Road plant had not then reached 90 percent treatment capability over a sustained period. The question of water quality was incidental in view of the fact that that office did not then have the final determination of water quality as evidenced by the intensive survey of the Little Econ and the final math modeling. (Testimony of Jewett, Davenport; Petitioner's Exhibit 4) By interoffice memorandums from the Respondent's Director of the Division of Environmental Permitting to district and subdistrict managers, dated January 28 and April 13, 1976, Subject: Temporary Operating Permits, the said managers were instructed that no operating permits should be issued for any source not achieving secondary treatment of its wastes or not meeting water quality standards. In such cases, only temporary operating permits were to be issued. Further, it was stated in the April 13 memorandum that enforcement action would be initiated against municipal facilities if they were either not achieving 90 percent removal Of BOD and suspended solids or not meeting water quality requirements, and had either (1) not applied for a federal grant, (2) was not following up to ensure receipt of the grant, or (3) had received a federal grant but was not expeditiously accomplishing the grant requirements. It was stipulated at the hearing that the memorandums had not been promulgated as rules by Respondent under Chapter 120, F.S. (Respondent's Exhibits 1, 2, Stipulation) Although the Little Econ is a highly degraded body of water, upstream of the Bennett Road discharge point it has a dissolved oxygen level of over 6 mg/l. After mixture with the Bennett Road discharge, the level drops to about 2 1/2 mg/l. Based upon the intensive survey taken by the Respondent in 1976, it was determined that water quality violations existed below the Bennett Road plant's discharge point but not above that point. It was further determined that the Bennett Road facility was contributing about 89 percent of the oxygen demanding substances in the system. In fact, the dissolved oxygen levels downstream from the Bennett Road discharge reached as low as one milligram per liter at several points. They ranged from that level up to approximately four and one-half milligrams per liter throughout the entire 27 miles of the system. The foregoing was the conclusion of Respondent's environmental specialist based on field data taken on August 30, 1976, at a time of the day when the dissolved oxygen levels would be at their highest. However, the drop in dissolved oxygen level to an even greater extent at certain points occurs in Respondent's mathematical model prediction that does not take into account any discharge from the Bennett Road plant. In fact, in such a "no discharge" situation, Respondent's prediction is that the dissolved oxygen level at points immediately following several control structures in the waters will produce an even greater drop than with the Bennett Road discharge taken into consideration. Although the control structures do not affect the actual oxygen demand on the system, they do increase the residence time of the water and permit substances to settle out. However, when the water flows over the dam, it creates reaeration that increases the oxygen level again. Therefore, although the control structures aggravate the problem, the Bennett Road discharge is in turn further aggravating the situation because some of the pollutants continue downstream. Part of the problem is due to the effect of deposits already on the bottom of the system and it is unknown to what extent they would be eliminated if the Bennett Road facility were taken out of the system. Although it is not anticipated that there would be a great rise in dissolved oxygen levels if the Bennett Road plant discharge were to be discontinued, Respondent's experts are of the opinion that there would be a definite increase in dissolved oxygen levels overall. Further, the field data and model predictions were based on high flow conditions but the 89 percent figure for pollutants from the Bennett Road facility was based on a low flow condition where it would be of more significance. Although the field data showed that at no point in the 27 mile course did the dissolved oxygen level of the water reach state standards of 5.0 milligrams per liter dissolved oxygen for Class III waters, the model prediction with no discharge from the Bennett Road facility shows that the dissolved oxygen level still would not meet state standards under high flow conditions. Under low flow conditions, though, the dissolved oxygen level without discharge from the Bennett Road plant would reach the state standards roughly halfway down the system. High flow conditions are more representative of an average of dissolved oxygen level during the year than under low flow conditions. The Bennett Road plant contributes approximately 60 percent of the total water flow reaching the St. Johns River. Even if the plant were to achieve advanced waste treatment standards, it still would not meet water quality standards. No evidence was presented as to the possibility of Petitioner using alternative methods of waste disposal, such as deep well injection, land irrigation, or the use of lakes and ponds. In fact, no discharge from the Bennett Road plant could be such as to raise the entire stream to meet the state requirement of 5.0 milligram per liter dissolved oxygen. (Testimony of Sawicki, Davenport, Armstrong, Horvath, Brown, Petitioner's Composite Exhibit 2, Respondent's Exhibit 3) An interoffice memorandum of Respondent's Grants section, dated October 28, 1976, pointed out that enforcement action had been shown to be a "great motivator in the area of bringing awareness to governmental agencies of their responsibilities in the field of pollution abatement." The memorandum sought compliance investigations of the various governmental entities within the area where the proposed regional sewage treatment system for East Orlando was to be undertaken, with recommendations that enforcement action be taken in the case of any violations of state standards. The memorandum further stated that enforcement action was already underway against the City of Orlando. The author of the memorandum denied that it was an attempt to force Respondent to proceed more vigorously with the regional system. (Testimony of Schneider, Petitioner's Exhibit 5) The Orange County Pollution Control Board requires variances from its rule that no treated effluent shall be discharged into the surface waters of the county. The Bennett Road plant operates under such a variance and at the present time is meeting county standards for sewage treatment. On May 19, 1976, the Orange County Assistant Pollution Control Director advised Respondent that the Bennett Road plant was meeting current state performance requirements and recommended approval of the operation permit. Although the county maintains records of the Little Econ River at various points, it has not used a mathematical model to determine whether the Bennett Road plant causes water quality violations. (Testimony of Sawicki, Petitioner's Exhibit 3)
Recommendation That the application of Petitioner City of Orlando, Florida for a water pollution operation permit for the Bennett Road sewage treatment facility be denied. DONE and ENTERED this 25th day of May, 1977, in Tallahassee, Florida. THOMAS C. OLDHAM Division of Administrative Hearings Room 530, Carlton Building Tallahassee, Florida 32304 (904) 488-9675 COPIES FURNISHED: Vance W. Kidder, Esquire Assistant General Counsel Department of Environmental Regulation 2562 Executive Circle East Montgomery Building Tallahassee, Florida Gretchen R. H. Vose, Esquire Assistant City Attorney 16 South Magnolia Avenue Post Office Box 793 Orlando, Florida 32802 ================================================================= AGENCY FINAL ORDER ================================================================= STATE OF FLORIDA DEPARTMENT OF ENVIRONMENTAL REGULATION CITY OF ORLANDO, FLORIDA, Petitioner, vs. CASE NO. 76-1573 STATE OF FLORIDA, DEPARTMENT OF ENVIRONMENTAL REGULATION, Respondent. /
Findings Of Fact By letter dated August 10, 1979, Indian River County (hereafter "County") submitted to the Department of Environmental Regulation (hereafter "Department" or "DER") applications for construction permits for the Gifford Area sewer treatment plant and collection improvements thereto, a domestic wastewater treatment and disposal system located in the County. (DER Exhibits Nos. 1 & 2). After receiving the permit applications submitted by the County, the Department's Orlando District Office requested additional information to determine whether reasonable assurances were provided that the facility would not discharge, emit or cause pollution in violation of Department standards. (Testimony of William Bostwick; testimony of Chancellor; DER Exhibits Nos. 3, 4, 5, 6, 7 & 8). The County, through its consulting engineers Sverdrup & Parcel and Associates, Inc., responded to the Department's requests for additional information. (DER Exhibits Nos. 3, 4, 5, 6, 7 & 8). The Department presented testimony of two professional engineers in its employ, Mr. William M. Bostwick and Mr. Gerald Chancellor, both of whom were accepted as expert witnesses in the field of sewage treatment technology and the processing and evaluation of permit applications for sewage treatment plants. Both witnesses testified that in their expert and professional opinion, based on their review of all plans, test results and other information submitted by the County, the applicant provided the Department with reasonable assurances that the proposed construction and operation of the sewage treatment facility and its collection system would not discharge, emit or cause pollution in violation of Department standards. (Testimony of Bostwick; testimony of Chancellor). The standards applicable to the subject construction permit applications involve (a) treatment level and (b) ambient standards of the receiving waters. The proposed system provides a minimum of ninety (90) percent treatment to incoming wastewaters. Because of the added features of surge tanks, gas chlorination, and dual blowers and motors, the ninety (90) percent minimum treatment was expected to be exceeded. (Testimony of Bostwick; testimony of Chancellor). The secondarily treated effluent from the proposed sewage treatment plant will be dispersed by spray irrigation. Because the effluent is expected to percolate to area groundwaters, the ambient groundwater standards of Section 17-3.101, Florida Administrative Code are applicable. The discharge from the facility will not cause any violation of the groundwater quality standards of the Florida Administrative Code. (Testimony of Bostwick; testimony of Chancellor; testimony of Aront). Although the design of the plant does not contemplate surfacewater discharge, if it did, it would meet the waste load allocation of Indian River County which permits discharge to surfacewaters. When the treated waste leaves the sprinkler head, it will meet secondary water treatment standards. (Testimony of Bostwick; testimony of Chancellor). In the course of evaluating a permit application for a wastewater treatment plant, the Department considers only Chapter 403, Florida Statutes, and its implementing rules and regulations and does not consider local issues relating to zoning, the propriety of expenditure of public funds or the like. (Testimony of Bostwick). There is presently no state standard regulating permissible levels of viruses in effluent discharged to either surface of groundwaters. Large numbers of viruses exist in the effluent discharged from spray irrigation treatment plants which operate at a ninety (90) percent treatment level. The viruses contained in the discharge remain viable as they percolate through the soil. The greatest concern exists when humans are in physical contact with such discharge. However, the present sewage treatment facility in its existing condition is a greater threat to public health than the proposed spray irrigation system. (Testimony of Dr. Welling, Petitioner's Exhibits Nos. 1, 2 & 3). Research concerning viral standards for effluent discharge is in an experimental stage. The Department is examining this question for possible future rule drafting. Neither the federal government nor any state, with the exception of Maryland, has adopted viral standards. (Testimony of Welling) The design of Use Gifford plant contemplates a series of perimeter monitoring wells through which groundwater samples can be attained and tested for compliance with groundwater standards end the presence of viruses. (Testimony of Aront) The plant will spray irrigate effluent at the rate of one (1) inch per week. Although surface run off is not expected, any that occurs due to heavy rains, etc., will be discharged into a perimeter ditch surrounding the plant. The plant design is formulated to retain effluent on site. (Testimony of Chancellor). There are four (4) different types of soil on the site with a water permeability of moderately rapid to very rapid. These soils have a percolation rate which makes the site suited for the intended purpose provided surface drainage is obtained. On a conservative basis the site could accept up to fourteen (14) inches of water per day or ninety-eight (98) inches per week. (Testimony of Connell; testimony of Eng; DER Exhibit No. 6). The parties stipulated prior to the hearing to the following: The project complies with local zoning laws; and The applicable provisions of law are Sections 403.086, 403.087, 403.088, Florida Statutes, and Rules 17-3.091, 17-4.03, 17-4.07 and 17-4.26, Florida Administrative Code.
Recommendation Upon consideration of the foregoing, it is RECOMMENDED: That the Department issue a construction permit to the County on condition that sample effluent from the monitoring wells on the subject facility be regularly analyzed for compliance with Department rules and the existence of infectious viruses. DONE and ENTERED this 3rd day of March, 1980, at Tallahassee, Florida 32301. SHARYN SMITH Hearing Officer Division of Administrative Hearings 101 Collins Building Tallahassee, Florida 32301 COPIES FURNISHED: Sherman N. Smith, Jr., Esquire Post Office Box 1030 Vero Beach, Florida 32960 George G. Collins, Jr., Esquire Post Office Box 3686 Vero Beach, Florida 32960 Segundo J. Fernandez, Esquire Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32301
The Issue The parties have raised myriad issues hare. Petitioner has alleged being capriciously and arbitrarily denied its permit because similar treatment plants have been licensed nearby. The parties disagree over whether local Lake County Pollution Control Board rules are applicable to Petitioner's plant. If the rules are applicable, they disagree over their interpretation. The parties further disagree over whether Petitioner has pending an application for a waste water treatment plant operating permit. It is this last issue which is discussed below because it is dispositive of the case.
Findings Of Fact Petitioner operates a waste water treatment plant in Lake County, Florida which serves four motels at the intersection of U.S. Highway 27 and SR 19 immediately to the south of Interchange 27 on the Florida Turnpike. On October 27, 1972, DER issued a construction permit to Petitioner to construct the plant at a design capacity of 250,000 gallons per day (gpd). The treated effluent was proposed to be discharged via a spray irrigation system to the ground water on Petitioner's site. The plant has never operated at capacity. Its normal volume has ranged from between a low of 40,000 gpd to a peak of 140,000 gpd. Petitioner's plant is situated on a 12.5 acre site over a clay hard pan. The hard pan which is immediately below the ground surface prevents adequate percolation of the plant's effluent down to the underlying ground water. During periods of heavy rain the effluent from the plant has breached a retaining dike and flowed directly into a marsh area known as the Little Everglades to the north. Petitioner has submitted four permit applications to the Department. The first, submitted in September of 1972 was for the construction permit already mentioned. The next applications dated October 22, 1973, was for an operation permit. The application indicated that there would be no discharge to surface waters but there would be a discharge to ground waters. The application also indicated that the availability of space for the expansion of the plant was limited to the site at that time. Petitioner later purchased additional land not reflected in this application. The operation permit was never granted by the Respondent. As stated by Mr. Potter, President of Lake County Utilities, Inc., "In the fall of 1973, I made an application as engineer for the utility company to the Florida DPC [Department of Pollution Control] and to Lake County for an operation permit. That permit was denied by the Department on the ground that we had not satisfied Lake County as to the total containment of our effluent." Subsequently on August 30, 1976, Petitioner submitted a construction permit application to DER for permission to add a 1.32 acre oxidation-polishing pond, to regrade and regrass the existing spray irrigation field, to construct a 0.40 acre denitrification pond and to add a nutrient uptake. No increase in the design capacity was proposed. On that application Petitioner indicated that there would be a discharge to the surface waters of the state. In answer to that part of the application which asked for proposed drainage path of the effluent Petitioner stated, "From treatment plant to 'on-site' ponds to 'on-site' grassy pond and marsh would overflow to ajacent Florida DOT [Department of Transportation] borrow pit: thence via developed drainage waste to the 'Little Everglades' swamp: then, via developed canal and ditches and through natural ponds and marshes to 'Little Lake Harris' and ultimately the Atlantic Ocean." This permit was denied by DER because the Lake County Pollution Control Board did not approve the plan. Finally on September 29, 1978, Petitioner applied for another construction permit. Thee construction would include: Construction of storm water control structures and culverts: Regrading of water and sewer plant sites; Construction of percolation pond "A" and enclosing dikes; and Construction of percolation pond "B" and enclosing dikes. This application was made in response to advice from DER that Petitioner's plant should be in a no discharge condition in order to comply with Lake County Pollution Control rules. On November 2, 1979, the Department issued a Letter of Intent to deny the last permit application because the application was deemed to be incomplete and because the further data which DER requested was not provided. In response to DER's intent to deny the construction permit Petitioner on November 20, 1979, filed its Petition for an Administrative Hearing. Petitioner does not now intend to construct the proposed facilities for which it requested the construction permit in September of 1978. The following colloquy is from the final hearing. Mr. Stephens Have you-- Can you describe briefly the nature of the changes proposed in your 1978 construction permit application? Mr. Potter 1978 construction permit application on nominally the five acre parcel to create a diked pond or lake. Mr. Stephens Uh-huh. Mr. Potter Solely that. The part on the nominally two and a half acre parcel, give or take, was to create a deep percolation pond in which I proposed digging through the clay to the sand and shell below. Mr. Stephens Uh-huh. Mr. Potter So that waters that entered that pond, A, because of its depth, would denitrify and release nitrogen contents to the atmosphere; and, the water would, because of its hydraulic head in relation to the soil below, would push its way into the soils below. Mr. Stephens Uh-huh. Mr. Potter But in the event I could not dispose of the water through that form of percolation, it would overflow into the five acre diked area. And thereby I hoped to satisfy Lake County and the D.E.R. and solve this lingering festering problem. Mr. Stephens Uh-huh. You are the Petitioner in this case. Is it your desire or intention to complete those. . .that construction? Mr. Potter Now that I have been made aware of the law, the law of Chapter four oh three, the rules of Florida D.E.R. and become clear as to the ordinances adopted by the County Commission and the Lake Pollution Board of Lake County as to Class 3-B waters, I have no intention of squandering my money, and, in effect, the money of my customers, in such a wasteful pursuit. Mr. Stephens So you're saying here under oath you don't intend to perform that work even if granted a permit? Mr. Potter Not shy of a court order. As the result of Mr. Potter's testimony on behalf of the Petitioner at the final hearing, it is found that Petitioner has withdrawn its September 1978 application for a construction permit. There is not now pending before the Department of Environmental Regulation a valid permit application for the Petitioner to operate its waste water treatment plan. On May 9, 1980 Lake County Utilities, Inc. served Petitioner's Fourth Interrogatories to Respondent which asked by Interrogatory 10: Please state when and by whom the Department of Environmental Regulation has caused field studies to be made and samples to be taken out of the waters of Lake County (and specifically the geographical vicinity of U.S. 27 - S.R. 19 - Fla. Turnpike) periodically and in a logical geographic manner so as to determine the levels of water quality of the waters as such studies and sampling is within the powers and duty of the Department as mandated by the Florida Legislature in Chapter 403 of the Laws of Florida. (emphasis in original) The Department responded: 10. The Department conducts sampling in the waters of Lake County in conjunction with individual permit applications and not on a systematic basis throughout the County. Respondent objects to this interrogatory as being irrelevant to this proceeding in that the subject permit was not denied on the basis of anticipated water quality violations, but rather, as a result of the pollution control ordinances of Lake County, Florida, which prohibit any discharge to surface waters from the subject facility, and which the Department is required to enforce pursuant to Section 403.182(6), Florida Statutes.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it Is RECOMMENDED: That the State of Florida, Department of Environmental Regulation enter a Final Order dismissing the Amended Petition for Administrative Hearing without prejudice, however, to the filing of a new application by Petitioner for a waste water treatment plant operating permit. DONE and RECOMMENDED this 12th day of May, 1981, in Tallahassee, Florida. MICHAEL P. DODSON 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 12th day of May, 1981.
Findings Of Fact Application 7500165 requested average withdrawal of water of 1,804,750 gallons per day from 4 wells located about a mile east of Highway 41 and a mile north of Apollo Beach. The four wells would be for irrigation of tomato crops on total acreage of 4 acres located in Hillsborough County (Exhibit 1, Testimony of Elsberry and Boatwright). Notice of hearing as to the application was published in a newspaper of general circulation in accordance with statute and rule (Exhibit 3). A letter of objection from Joseph S. Benham, Apollo Beach, Florida, dated November 19, 1975 was submitted to the Water Management District, wherein he expressed concern regarding water shortages and, although he does not seek to totally deny the application, is of the belief that the district must insure sufficient controls and management of irrigation activities so that resources are not wasted, water runoff to drainage ditches is eliminated and renewed justification is given each year for the withdrawal (Exhibit 2). A representative of the District staff established that there would be no violation of statutory or regulatory requirement for issuance of a consumptive water use permit in this case except as to the fact that potentiometric level of the applicant's property would be lowered below sea level as a result of withdrawal. It was agreed at the hearing that a period of thirty days should be granted both parties to formulate a stipulation as to control of runoff. An unsigned stipulation was received from the Water Management District by the hearing officer on March 1, 1976, which provided that the permit would be granted with the following stipulations: Runoff from the property will be limited to 25 percent of the quantity pumped and by December 31, 1980 shall be reduced to 16.5 percent of the quantity pumped. The District may at its own expense install metering devices for the purpose of monitoring runoff. The permittee will be notified in advance of such action. The Permit will expire on December 31, 1980. (Testimony of Boatwright, Exhibit 4).
Recommendation That application 8500165 submitted by Elsberry and Elsberry, Inc. Route 2, Box 70 Ruskin, Florida, for a consumptive water use permit be granted with the conditions as follow: Runoff from the property will be limited to 25 percent of the quantity pumped and by December 31, 1980 shall be reduced to 16.5 percent of the quantity pumped. The District may at its own expenseinstall metering devices for the purpose of monitoring runoff. The permittee will be notified in advance of such action. The Permit will expire on December 31, 1980. That the Board grant an exception to the provision of Rule 16J- 2.11(4)(e), F.A.C., for good cause shown. DONE and ENTERED this 15th day of March, 1976, in Tallahassee, Florida. THOMAS C. OLDHAM Division of Administrative Hearings Room 530, Carlton Building Tallahassee, Florida 32304 (904) 488-9675 COPIES FURNISHED: Jay T. Ahern, Esquire Southwest Florida Water Management District Post Office Box 457 Brooksville, Florida 33512 Elsberry & Elsberry, Inc. Route 2, Box 70 Ruskin, Florida
Findings Of Fact B. D. Taylor, Respondent, is the owner of a wastewater treatment facility near Panama City, Florida, which serves a community of some 125-150 mobile homes at Lane Mobile Home Estates. The facility has a 24,000 gallons per day capacity to provide secondary treatment of wastewater with percolating ponds. It was first permitted in 1971 upon construction and has been in continuous operation since that time. In 1980 Respondent employed the services of a consultant to apply for a renewal of its temporary Permit to operate a wastewater treatment facility. This application stated the temporary operating permit (TOP) was needed to give Respondent time to connect to the regional wastewater treatment facility. The schedule contained in the following paragraph was submitted by Respondent at the time needed to accomplish this objective, Following inspection of the facility, a TOP was issued December 5, 1980 (Exhibit 1), and expired January 1, 1983. TOPs are issued to facilities which do not comply with the requirements for Wastewater treatment. Exhibit 1 contained a schedule of compliance to which Respondent was directed to strictly comply to stop the discharge of pollutants from the property on which the facility is located. These conditions are: Date when preliminary engineering to tie into regional will be complete and notification to DER. July 1, 1981; Date when engineering to tie into regional system will be complete and notification to DER - June 1, 1982; Date construction application will be submitted to phase out present facility - March 1, 1982; Date construction will commence - June 1, 1982; Date construction is to be complete and so certified - October 1, 1982; and Date that wastewater effluent disposal system will be certified "in compliance" to permit - January 1, 1903. None of these conditions or schedules has been met by Respondent. The regional wastewater treatment facility was completed in 1982 and Respondent could have connected to this system in the summer of 1982. This wastewater treatment facility is a potential source of pollution. The holding ponds are bordered by a ditch which is connected to Game Farm Greek, which is classified as Class III waters. The size of Game Farm Creek is such that any discharge of pollution to this body of water would reduce its classification below Class III. On several occasions in the past there have been breaks in the berm surrounding the holding ponds which allow the wastewater in the holding ponds to flow into the ditch and into Game Farm Creek. Even without a break in the berm, wastewater from these holding ponds will enter Game Farm Creek either by percolation or overflow of the holding ponds caused by the inability of the soil to absorb the effluent. On January 28, 1983, this facility was inspected and the results of the inspection were discussed with the operators of the facility. The plant was again inspected on February 8 and February 18, 1983. These inspections disclosed solids were not settling out of the wastewater in the settling tanks; inadequate chlorination of the wastewater was being obtained in the chlorination tanks; samples taken from various points in the system, the ditch along side the holding tanks and in Game Farm Creek, disclosed excess fecal coliform counts; and that very poor treatment was being afforded the wastewater received at the plant as evidence by high levels of total Kejhdal nitrogen and ammonia, high levels of phosphates, high biochemical oxygen demand, and low levels of nitrates and nitrites. In July, 1983, in response to a complaint about odors emanating from the plant, the facility was again inspected. This inspector found the aeration tanks anaerobic, effluent had a strong septic odor, the clarifier was cloudy, the chlorine feeder was empty, no chlorine residual in contact tank, final effluent was cloudy, both ponds were covered with duckweed and small pond was discharging in the roadside ditch (Exhibit 14) Expenses to Petitioner resulting from the inspections intended to bring Respondent in compliance with the requirements for wastewater treatment facilities are $280.32 (Exhibit 9)
Findings Of Fact Upon consideration of the oral and documentary evidence in the record, as well as the pleadings and joint prehearing stipulation, the following relevant facts are found: Cast-Crete owns and operates a concrete batch plant in Hillsborough County, Florida, and manufactures concrete products such as reinforced beams, lintels, seals and drainage structures on the property. The plant is located on the west side of State Road 579, 3/4 mile north of Interstate 4, Section 28, Township 28 South, Range 20 East. The concrete products are manufactured in various forms which are laid out over a large portion of Cast-Crete's property. Lubricating oils are utilized to facilitate the removal of the product from the confining forms. During this process some of the lubricating oil is spilled onto the ground. Also, cleaning solutions containing degreasers are utilized to wash the concrete trucks eight to ten times per day. This solution ends up on the ground. Aggregate limerock (crushed limestone) is used in the concrete formulation process and is stored in large piles on the property. In order to contain the dust, water is sprayed on the aggregate piles 24 hours a day. The wash water from the continuous process of wetting the aggregate, other waste water and some stormwater is channeled through the property and into a settling pond in the northwest corner of Cast-Crete's property. This pond discharges continuously off the property by way of a concrete flume into a county maintained ditch. Water in the ditch travels in a westerly direction approximately 200 to 300 yards before it passes under Black Dairy Road, where the watercourse deepens and widens. The ditch discharges into a marshy area which drains into Six Mile Creek and other water bodies. The pond at the northwest corner of Cast-Crete's property is equipped with a metal skimming device to remove oils and greases floating on the surface of the pond. Nevertheless, it is estimated that approximately 100 gallons of oil per year are discharged by Cast-Crete. Oil and grease in the outflow water is occasionally above 5 mg/L. Oil and grease layers have been observed on water at both Black Dairy Road and Six Mile Creek, probably resulting from road run- off. Approximately 90 percent of the water discharged from the property is a result of the wetting or washdown of the aggregate piles. The excess water which comes from the aggregate piles is laden with dissolved limestone, lime and limestone particles. This limestone dust raises the pH level of the water. Because of the continued wetting of the aggregate, water flows through the settling ponds and off of Cast-Crete's property at a rate of approximately 4.8 gallons per minute, or 7,200 gallons per day or 2.5 million gallons per year. During a rain event, the flow increases markedly. Except during times of heavy rainfall, water flowing from the respondent's property provides a thin stream of water in the drainage ditch approximately six inches wide and several inches deep. The pH of the wastewater from Cast-Crete's discharge flume is between 10 and 11 units. During high volume flows, the pH remains at or above 11 units. An increase of one unit of pH in the wastewater means that the wastewater has become 10 times more basic, since pH is measured on a logarithmic scale. The natural background of unaffected streams in the area of and in the same watershed as the Cast-Crete property is less than 8.5 units. Specific conductance or conductivity is the measure of free ions in the water. Typical conductivity readings from other water bodies in Hillsborough County range between 50 and 330 micromhos per centimeter. The specific conductance of Cast-Crete's wastewater ranges from 898 to 2000 micromhos per centimeter. This is due to the presence of calcium carbonate and calcium hydroxide in the water. Blue-green algae is the dominant plant species in the ditch between the Cast-Crete discharge flume and the first 150 meters of the ditch. A biological survey of the ditch system indicates that the diversity of species east of Black Dairy Road is low. This is attributable in part to the high pH of the wastewater. The low diversity can also be attributed to the fact that the County maintains the ditch by use of a dragline on an annual basis. Background samples from a site within one mile to the northwest of the Cast-Crete property were taken. The site (a stream passing under Williams Road) is an appropriate place to take background samples because the water there is unaffected by Cast-Crete's discharge or other man-induced conditions. The pH background sample ranged from 4.6 units to 5.1 units. The specific conductance background samples ranged from 70 to 100 micromhos per centimeter. Samples taken from a site potentially impacted by Cast-Crete's discharge showed a pH level of from 6.35 to 7.37 units and specific conductance of from 592 to 670 micromhos per centimeter. Cast-Crete discharges water from its concrete plants operation without a permit from the DER.
Recommendation Based upon the findings of fact and conclusions of law recited herein, it is RECOMMENDED that a Final Order be entered requiring respondent to submit a complete application for an industrial wastewater permit within thirty (30) days, and that, if it fails to do so, it cease discharging wastewater from its property until such time as an appropriately valid permit is issued by the DER. Respectfully submitted and entered this 3rd day of May, 1985, in Tallahassee, Florida. DIANE D. TREMOR 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 3rd day of May, 1985. COPIES FURNISHED: David K. Thulman Assistant General Counsel Department of Environmental Regulation Twin Towers Office Building Blairstone Road Tallahassee, FL 32301 W. DeHart Ayala, Jr. 501 E. Jackson Street Suite 200 Tampa, FL 33602 Victoria Tschinkel Secretary Department of Environmental Regulation Twin Towers Office Building 2600 Blairstone Road Tallahassee, FL 32301 ================================================================= AGENCY FINAL ORDER ================================================================= STATE OF FLORIDA DEPARTMENT OF ENVIRONMENTAL REGULATION DEPARTMENT OF ENVIRONMENTAL REGULATION, STATE OF FLORIDA, Petitioner, vs. CASE NO. 84-1647 CAST-CRETE CORPORATION OF FLORIDA Respondent. /
Findings Of Fact Ed Smith is the President of Riverside Village Mobile Home Park, Inc., which in turn is the owner of the mobile home park in question in this case. The mobile home park is located in Ruskin, Hillsborough County, Florida. Petitioner was served with an Administrative Complaint alleging that the chlorine residual in the park water supply distribution system was inadequate and that this constituted a violation of Chapter 513 and Section 386.041(1)(f), Florida Statutes, as well as Rule 10D-26.67(1), Florida Administrative Code. Specifically, the Administrative Complaint alleges violations occurring between July 16, 1986 and July 29, 1986, and seeks the imposition of a civil penalty in the amount of $500 per day which "shall be calculated when this complaint is received by the (Petitioner), and will run until the violation has been corrected." Petitioner requested a hearing to contest these allegations, and his request was filed with Respondent's Clerk on October 8, 1986. It was not established by competent substantial evidence when Petitioner "received" the Administrative Complaint which is the subject of this action. The only evidence of any violation occurring between July 16 and July 29, 1986 was the testimony of Harry Messick who signed an Official Notice and Notice of Intended Action which were both dated July 16, 1986, and which alleged that "chlorine reading found at time of inspection (was) between 0.1 ppm and (a) trace." However, Messick did not perform any test to either produce or confirm this result. He testified that someone else performed the field test, but there was no testimony from anyone else who may have actually conducted a test on Petitioner's water supply system on July 16, 1986. Therefore, it has not been established by competent substantial evidence that Petitioner's water supply system on July 16, 1986, was in violation of the requirement that .2 mg/1 of free chlorine residual be maintained. Testimony from Respondent's other witnesses, Norman Vik and Neil R. Schobert, indicates Vik was not even at Petitioner's mobile home park between July 16 and 29, 1986, and the only test conducted by Schobert found that Petitioner's water supply system was in compliance on July 24, 1986. Design modifications in Petitioner's water supply distribution system were approved by the Hillsborough County Health Department on July 9, 1986.
Recommendation Based on the foregoing, it is recommended that Respondent enter a Final Order DISMISSING the Administrative Complaint filed against Petitioner. DONE AND ENTERED this 19th day of February 1987 in Tallahassee, Florida. DONALD D. CONN Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 19th day of February 1987. APPENDIX (DOAH Case No. 86-4094) Rulings on Respondent's Proposed Findings of Fact: 1. Adopted in Finding of Fact 1. 2-3. Rejected in Findings of Fact 4, 5. COPIES FURNISHED: James A. Sheehan, Esquire Florida Federal Building One Fourth Street North Suite 800 St. Petersburg, Florida 33701 Carol M. Dittmar, Esquire 4000 West Buffalo Avenue Suite 520 Tampa, Florida 33614 Gregory L. Coler Secretary Department of Health and Rehabilitative Services 1323 Winewood Blvd. Tallahassee, Florida 32301 John Miller, Esquire General Counsel Department of Health and Rehabilitative Services 1323 Winewood Blvd. Tallahassee, Florida 32301 =================================================================
The Issue The issue in this case is whether the Department of Health and Rehabilitative Services (HRS) should grant the Petitioner's applications, filed under F.A.C. Rule 10D-6.045, for variances from the F.A.C. Rule 10D-6.046(1)(c) requirement that on-site treatment and disposal systems (OSTDS's) be placed no closer than 200 feet from public drinking water wells serving a facility with a sewage flow of more than 2,000 gallons per day (gpd).
Findings Of Fact The Petitioner, Joseph DiGerlando, owns three lots (1, 2 and 26) in the San Remo subdivision in Hillsborough County, which was platted in 1977. There is a public water well located between lots 1, 2 and 26. The well serves the entire San Remo subdivision, a 55-lot residential development having a total sewage flow much greater than 2,000 gallons per day (gpd) (although the sewage flow from homes built on lots 1, 2 and 26 can be expected to total no more than approximately 1350 gpd.) There is no way for the Petitioner to construct an on-site sewage treatment disposal system (OSTDS) on each of the three lots so that no part of any OSTDS will be closer than 200 feet from the San Remo well, measured horizontally across the ground surface to the well head. Measuring horizontally across the ground surface to the well head: an OSTDS on lot 1 could be placed no farther than 156 feet from the well; an OSTDS on lot 2 could be placed no farther than 184 feet from the well; according to drawings in the Petitioners' application, an OSTDS on lot 26 could be placed no farther than approximately 185 feet from the well. (Although lot 26 is larger than the others, it is contiguous to a surface water body, and the required setback from the surface water body decreases the area available for siting an OSTDS on the lot. The evidence was not clear exactly how far an OSTDS on lot 26 would be from the San Remo well.) HRS concedes: (1) that requiring 200-foot setbacks from the San Remo well will place the Petitioner under a hardship that was not caused intentionally by his own actions; and (2) that no reasonable alternative exists for the treatment of sewage on his lots 1, 2 and 26. (It is not clear how or why HRS determined that utilization of a joint OSTDS to serve all three lots through the imposition of cross-easements on the lots would not be a reasonable alternative to at least one or two of the variance applications.) The San Remo well, which is 400 feet deep, has a steel casing from the surface of the well to 100 feet below the ground surface. The steel casing prevents the entry of ground water into the well above the bottom of the casing. If the distances between the proposed OSTDS's and the San Remo well were measured diagonally, through the ground, from the proposed OSTDS's to the bottom of the steel casing of the well: the proposed OSTDS on lot 1 would be 185 feet from the well; the proposed OSTDS on lot 2 would be 209 feet from the well; and the proposed OSTDS on lot 26 would be even farther from the well. (The evidence was not clear exactly how much farther.) In fact, due to the draw-down effect of the well, the path groundwater would travel from the proposed OSTDS's to the bottom of the steel casing of the San Remo well would curve upward somewhat from, and be somewhat longer than, the diagonal line running directly between those two points. (The evidence is not clear exactly how much longer the curved path would be.) If the distances between the proposed OSTDS's and the San Remo well were measured first horizontally across the ground surface to the well head and then vertically down to the bottom of the steel casing of the well: the proposed OSTDS on lot 1 would be 253 feet from the well; the proposed OSTDS on lot 2 would be 281 feet from the well; and the proposed OSTDS on lot 26 would be even farther from the well. (Since the bottom of the OSTDS's will be three feet below the ground surface, the vertical component of the measurement is only 97 feet instead of the full 100 feet between the well head and the bottom of the casing.) When applying the HRS rules on distances required between OSTDS's and existing public water wells, HRS measures from the OSTDS horizontally across the ground surface to the well. The evidence was that HRS's method of measurement is consistent both with the methods used by the federal EPA and with the scientific data on which the technical advisory board based the distances in the HRS rules. The Petitioner's expert witness testified that there is a 17-foot thick layer of sand and clay between 53 and 70 feet below the ground surface in the vicinity of the San Remo well and that the sand and clay layer would prevent contamination from the OSTDS's from reaching the bottom of the steel casing of the well. (He also testified that is a white lime rock layer between 70 and 90 feet below the ground surface and inferred that the white lime rock layer would add some degree of protection.) The opinions of the Petitioner's expert are accepted. Petitioner's expert is a civil, sanitary and environmental engineer, not a geologist or hydrogeologist; however, his experience is in the area of wastewater treatment and disposal is extensive. Meanwhile, HRS presented no competent evidence whatsoever to contradict the Petitioner's expert. The Petitioner proposes to use Norweco Singulair Bio-Kinetic Waste Water Treatment Systems. These systems treat waste better than a standard septic tank system. Instead of the single septic tank, they have three distinct chambers: first, a retreatment chamber; second, an aeration chamber to reduce biological oxygen demand (BOD) and total dissolved solids (TDS); and, finally, a clarification or filter chamber that further reduces BOD and TDS. With the proposed systems, BOD and TDS will be reduced to approximately a fourth of the BOD and TDS levels that would enter the drainfield from a septic tank system. In addition, unlike in a septic tank system, the proposed systems utilize chlorine tablets in conjunction with the clarification chamber to kill bacteria and viruses. It is found that the evidence presented in this case, taken as a whole (and in particular in the absence of any competent evidence to contradict the credible opinions of the Petitioner's expert) was sufficient to prove that the proposed OSTDS's would not adversely affect the health of members of the public. Except for a fleeting reference in its Proposed Recommended Order, HRS has not taken the position that the Petitioner's proposed OSTDS's will significantly degrade the groundwater or surface waters. The reference in the Proposed Recommended Order would seem to reflect that HRS's concern about the impact of the Petitioner's proposed OSTDS's on groundwater quality is limited to its public health concerns.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is recommended that the Department of Health and Rehabilitative Services (HRS) enter a final order granting the Petitioner's applications for variances, on the condition that the Petitioner utilizes the proposed Norweco Singulair Bio- Kinetic Waste Water Treatment Systems. RECOMMENDED this 30th day of June, 1995, in Tallahassee, Florida. J. LAWRENCE JOHNSTON 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 30th day of June, 1995. APPENDIX TO RECOMMENDED ORDER, CASE NO. 94-6483 To comply with the requirements of Section 120.59(2), Fla. Stat. (1993), the following rulings are made on the parties' proposed findings of fact: Petitioner's Proposed Findings of Fact. Accepted but conclusion of law, subordinate and unnecessary. Accepted and incorporated. 3.-6. Accepted but subordinate and unnecessary. Accepted and incorporated. Rejected as to "significantly degrade the groundwater or surface waters"; HRS did not make this an issue, except with respect to public health concerns. Otherwise, accepted and incorporated. Rejected as not proven and contrary to the greater weight of the evidence. However, accepted that HRS presented no evidence sufficient to support a finding on the issue. See Section 120.58(1)(a), Fla. Stat. (Supp. 1994). Accepted but subordinate and unnecessary. Rejected as to "relevant criteria"; not proven and as contrary to the greater weight of the evidence. Otherwise, accepted and incorporated. Accepted and incorporated. Respondent's Proposed Findings of Fact. Accepted but conclusion of law, subordinate and unnecessary. Accepted and incorporated. 3.-7. Accepted but subordinate and unnecessary. Accepted and incorporated. Rejected as contrary to facts found and as contrary to the greater weight of the evidence. (As found, HRS did not contend that the Petitioner's OSTDS's would "significantly degrade the groundwater or surface waters." HRS only raised this issue with respect to public health concerns.) 10.-12. Accepted but subordinate and unnecessary. (These were hearsay statements that were not sufficient to support findings as to the matters asserted. See Section 120.58(1)(a), Fla. Stat. (Supp. 1994).) COPIES FURNISHED: Raymond R. Deckert, Esquire Department of Health and Rehabilitative Services 4000 W. Dr. Martin Luther King, Jr., Boulevard Tampa, Florida 33614 Nelson D. Blank, Esquire Trenam, Kemker, Scharf, Barkin Frye, O'Neill & Mullis, P.A. 2700 Barnett Plaza 101 E. Kennedy Boulevard Tampa, Florida 33601-1102 Robert L. Powell Agency Clerk Department of Health and Rehabilitative Services 1323 Winewood Boulevard Tallahassee, Florida 32399-0700 Kim Tucker, Esquire General Counsel Department of Health and Rehabilitative Services 1323 Winewood Boulevard Tallahassee, Florida 32399-0700
The Issue The issue presented for determination in this proceeding is whether the City of Bartow is entitled to a renewal of its operating permit to discharge into the Peace River effluent from its sewage treatment plant at the design capacity of 2.75 million gallons per day.
Findings Of Fact Upon consideration of the oral and documentary evidence adduced at the hearing, the following facts are found: Petitioner owns and operates a sewage treatment plant located at 2505 East Wabash Avenue in Bartow, which discharges effluent into the Peace River. On April 13, 1977, petitioner applied to respondent for a renewal of its operating permit, with the plant designed to treat and discharge a maximum of 2.75 million gallons of wastewater per day. By letter dated May 11, 1977, respondent notified petitioner of its intent to enter a final order denying the permit application for the reason that petitioner's proposed discharge at design capacity (2.75 mgd) would reduce the quality of the Peace River below its established classification. The respondent was specifically concerned with the deleterious impact which operation of petitioner's plant at design flow would have upon the level of dissolved oxygen in the Peace River. The May 11, 1977, letter also set a wasteload allocation which would have to be met by petitioner's plant in order not to depress the water quality of the Peace River below established levels. The allocations were later revised to provide for secondary treatment with nitrification. As noted above, these allocations were challenged in a Section 120.56, Florida Statutes, proceeding. By final order entered on September 14, 1978, it was held that said wasteload allocations did not constitute a rule within the meaning of Chapter 120 and thus were not subject to an attack of invalidity on the ground that they were not adopted pursuant to the rulemaking requirements of Section 120.54, Florida Statutes. The Peace River is classified as a Class III water body. This classification contains criteria designed to promote the use of the water for recreational purposes, including swimming, and for the maintenance of a well- balanced fish and wildlife population. Rule 17-3.09, Florida Administrative Code. In Class III waters, the concentration of dissolved oxygen is not to average less than 5 milligrams per liter (mg/l) in a 24 hour period and should never be less than 4 mg/l. Water quality problems exist in the Peace River even where no sewage treatment plants are discharging, and the River does not consistently meet the dissolved oxygen standards for Class III waters. At low flow conditions, the dissolved oxygen content in the River ranges from two to three mg/l up to six to seven mg/l. Sewage treatment plant effluent contains components known as total Kjeldahl nitrogen (TKN) and biochemical oxygen demand (BOD5). When these components decay they use up free dissolved oxygen, thereby depressing dissolved oxygen levels. In order to maintain the desirable dissolved oxygen (DO) level, it is necessary to control the amount of oxygen demanding substances such as TKN and BOD5 entering the receiving waters. The limitation on the concentration of such effluent components which must be met to assure that water quality standards will not be depressed below the level set for a given classification are known as wasteload allocations. Wasteload allocations are calculated by the respondent for each sewage treatment plant and industrial discharger which discharge effluent into the surface waters of the state. They are determined by use of a mathematical computer model based upon the physical, biological and chemical characteristics of the receiving body of water. In this case, the water system modeled was a segment of the Peace River extending from approximately 1.4 miles above petitioner's discharge point to approximately 46 miles downstream. The respondent conducted two surveys during low flow conditions in November of 1976. During low flow conditions, tributary input is minimal and nonpoint contributions are almost negligible. Point source contributions such as sewage treatment plants and industrial dischargers have their greatest impact during low flow conditions. Based upon the model run by respondent, respondent predicted that the operation of petitioner's plant at design capacity (2.75 mgd) would have a significant deleterious impact upon dissolved oxygen during low flow conditions. Specifically, respondent found that petitioner's discharge causes a DO drop of one milligram per liter at a point less than five miles from the petitioner's point of discharge and a drop from 2 1/2 mg/l to zero from mile ten through fifteen. Much of the testimony presented by the petitioner at the hearing was directed to the reliability of the data used by respondent in its model. Petitioner presented evidence tending to illustrate that nonpoint sources in the River's tributaries are the cause of the depressed DO in the Peace River. However, as noted above, the respondent's model utilized low flow conditions wherein such sources are almost nonexistent. The evidence further tends to illustrate that several coefficient values utilized by the respondent in its model resulted in a less restrictive allocation for petitioner. Even on the date of the hearing, Respondent's witnesses were satisfied and confident that there were no technical inaccuracies in the model used to develop the wasteload allocations for petitioner's plant. Petitioner adduced no conclusive evidence that any of the data or assumptions made by the respondent were erroneous. The petitioner's plant presently discharges about 1.44 million gallons of wastewater per day. This meant that Bartow is presently operating at approximately 50 percent of its capacity. On a monthly average, petitioner's treatment level is well in excess of ninety percent. Five years from now, in 1983, petitioner projects that its flow will approximate 1.7 million gallons per day. It is predicted that petitioner will not reach its design capacity of 2.75 million gallons per day for twenty years. As, noted above, the respondent's model predicted dissolved oxygen violations based upon the design capacity of 2.75 mgd, for which the petitioner applied. The respondent ran no intermediate low alternatives to predict how close to design capacity the petitioner could come before a violation occurred. Nor did respondent find present DO violations directly attributable to petitioner's discharge. In order to meet the wasteload allocations calculated by the respondent, it will be necessary for petitioner to make capital expenditures approximating $1,676,400.00. This figure is for a discharge of about 1.9 mgd. Such an expenditure would result in an increase to consumers of about 50 percent per month. The least expensive means of disposing of effluent would be for petitioner to recycle it to area phosphate mining companies, and not to discharge into the Peace River at all.
Recommendation Based upon the findings of fact and conclusions of law recited herein, it is recommended that the application of the petitioner to discharge effluent into the Peace River at design capacity (2.75 million gallons per day) be denied. It is further recommended that petitioner submit to the respondent a revised application which clearly indicates the amount of discharge expected for the permit period, and that respondent review said application anew. Respectfully submitted and entered this 4th day of October, 1978, in Tallahassee, Florida. DIANE D. TREMOR, Hearing Officer Division of Administrative Hearings Room 530, Carlton Building Tallahassee, Florida 32304 (904) 488-9675 COPIES FURNISHED: William S. Blakeman Campbell, Dunlap, Coward and Blakeman Post Office Box 916 Lakeland, Florida 33802 Louis F. Hubener Twin Towers Office Bldg. 2600 Blair Stone Road Tallahassee, Florida 32301 Mr. Jay W. Landers Secretary, Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32301
The Issue The issues in this case are whether penalties should be imposed and investigative costs and expenses assessed against Respondent for water supply system violations; and, if so, the amount of the penalties and assessments.
Findings Of Fact Respondent, Premier Construction Group, Inc., owns and operates a water treatment plant and associated piping in a commercial building it owns and leases at 2315 Highway 41 North in Inverness. The water treatment plant consists of a 500- gallon tank that holds groundwater pumped from a well. The water in the tank is treated with chlorine and distributed throughout the building for potable water use. The water system serves 25 or more people daily for at least 60 days a year and serves the same people for over six months a year. Respondent owned and operated the water system for 18 and a half years with no violations. Respondent hired a licensed water treatment plant operator to monitor and ensure compliance with applicable DEP rules. In August 2009, Respondent’s licensed operator increased his price substantially. Rick Suggs, as Respondent’s owner and president, disputed the increase and asked the licensed operator to reconsider. Family obligations then required Mr. Suggs to travel to South Carolina for an extended period of time, and Respondent did not attend to the matter further. By the end of August 2009, Respondent’s licensed operator notified DEP that he would no longer be servicing Respondent’s water system as of the end of the month. On August 24, 2009, DEP mailed Respondent a letter relaying this information and putting Respondent on notice that a new licensed operator would have to be hired for September. Notwithstanding Respondent’s communications with its licensed operator and DEP in August, Respondent did not hire a new licensed operator. Mr. Suggs testified that Respondent did not know its licensed operator actually quit until later in September. When this was brought to Mr. Suggs’ attention, he instructed his office manager to hire a replacement. Respondent thought the matter was resolved, but the supposed replacement did not proceed with the work. While Respondent was without a licensed operator, the residual chlorine in the system dropped to zero when tested by DEP on September 17, 24, and 30 and on October 7 and 13, 2009. As a result, the water system did not comply with disinfection requirements during September and October 2009. Respondent did not notify DEP of its failure to comply with disinfection requirements in September and October 2009. No monthly operation reports were submitted to DEP for Respondent’s water system for September or October 2009. No bacteriological samples were collected from Respondent’s water system for the months of September and October 2009. Respondent did not notify DEP of its failure to collect bacteriological samples in September and October 2009. While without a licensed operator, Respondent did not provide public notification of its failure to collect bacteriological samples in September and October 2009. Well into October 2009, Respondent became aware that the supposed replacement licensed operator was not doing work for Respondent. Mr. Suggs hired a replacement licensed operator named Mike Watson, who began servicing Respondent’s water system on November 17, 2009. Public notification of Respondent’s failure to collect bacteriological samples in September and October 2009 was given on November 25, 2009. On December 11, 2009, Respondent submitted a completed DEP Form 62-555.900(22), Certification of Delivery of Public Notice, as to its failure to notify the public of its failure to collect bacteriological samples in September and October 2009. By not having a licensed operator in September and October 2009, Respondent saved $332. By not having bacteriological samples collected and tested in September and October 2009, Respondent saved $60. There was evidence that DEP spent approximately $678 investigating and enforcing the violations. More may have been spent, but no evidence of any additional costs or expenses was presented. There was no evidence of any other water treatment violations by Respondent after October 2009. Although there was a potential that the violations could have posed a health threat, there was no evidence that the public’s health actually was threatened by Respondent’s violations. The water system was tested on November 18, 2009, and did not have any coliform bacteria. The NOV includes corrective actions (essentially coming into and staying in compliance), which Respondent already has taken. The NOV requests that penalties be paid within 30 days by cashier’s check or money order made payable to the “State of Florida Department of Environmental Protection” and including the notations OGC File No. 09-3847-09-PW and “Ecosystem Management and Restoration Trust Fund” to be mailed to DEP’s Southwest District office at 13051 North Telecom Parkway, Temple Terrace, Florida 33637. Respondent believes the penalties sought by DEP in this case are excessive. Mr. Suggs cited Respondent’s clean record for 18 and a half years, his personal and financial difficulties during the two months when the violations occurred, and his responsiveness in correcting violations beginning in November 2009. Mr. Suggs testified that, during mediation, DEP informed him that the penalties could have totaled $115,000 if an unexplained “matrix” had been used to calculate the penalties. Mr. Suggs thought $115,000 was “ludicrous.” Mr. Suggs also requests that the lesser penalties sought in the NOV be further reduced, especially considering that Respondent paid a lawyer $2,800 for representation earlier in the proceeding, until the lawyer withdrew from the case.
