The Issue Whether General Water Use Permit (WUP) Number 20012185.000 (Permit) meets the conditions for issuance as established in Section 373.223, Florida Statutes, and Rule 40D-2.301, Florida Administrative Code, and should be issued to Farmland Hydro Limited Partnership and Frank T. Basso, Jr. and Redland Growers Exchange, Inc.
Findings Of Fact The Parties DCAP is not-for-profit corporation incorporated in the State of Florida. Behrens is the President of DCAP. See also Findings of Fact 63-77. Farmland Hydro is a Delaware Limited Partnership authorized to transact business in Florida, and is the owner of the property leased by Basso/Redland, which is the subject of this WUP. Frank T. Basso, Jr., is a third generation farmer, who operates as Redland Growers Exchange, and seeks a General WUP to authorize groundwater withdrawals for crop irrigation. The District is the administrative agency charged with the responsibility to conserve, protect, manage, and control water resources within its boundaries pursuant to Chapter 373, Florida Statutes, and the rules promulgated thereunder as Chapter 40D, Florida Administrative Code. The Proposed Water Use An Application for a General WUP was submitted by Farmland Hydro and Basso, as co-applicants, and received by the District on April 11, 2001. After receipt of additional information, the Application was deemed complete on October 22, 2001. The Applicants seek a General WUP to authorize a new water use for the irrigation of 140 acres for the production of both Spring and Fall row crops, using a seepage-with-mulch irrigation system.1 Basso plans to grow tomatoes and/or peppers in the Spring, and squash and/or cucumbers in the Fall. Crop planting for both seasons will be phased-in over a one-month period. Water allocation quantities are calculated on a weekly phase-in basis of approximately 35 acres for each planting date. The total time that the parcel will be in use for farming, to include planting and harvesting for each crop, is approximately six months per year. The subject parcel is part of a 250-acre tract known as the Brushy Creek Tract and is located in Hardee County approximately two miles south of the town of Ona; approximately two miles south of the intersection of U.S. Highway 64 and County Road 663; and is within the Southern Water Use Caution Area (SWUCA). The subject parcel currently does not contain a water well. The Brushy Creek Tract is a larger parcel of approximately 1,230 acres leased from Farmland Hydro by Redland and also by Parker Farms for cattle grazing, farming, and hunting. The subject parcel is used for cattle grazing and is surrounded by land owned by Farmland Hydro and used for either cattle grazing or agricultural row crops. Farmland Hydro also operates an additional approximately 1,941 acres of property near the subject parcel, which is used for citrus groves. Farmland Hydro has consumptive WUPs for this property. The closest existing legal user to the proposed Basso well site is another well on the Farmland Hydro property. As is generally done with vegetable crop production in Florida, vegetable crops grown on the Farmland Hydro property are grown in rotation with pasture, and have been rotated in this manner for many years. Typically, farmers have farmed a piece of land for one, two or three years and then, to avoid the buildup of insects and diseases, have allowed the land to revert to pasture and have moved on to another field for crop production. The subject parcel for which the WUP is being sought will be similarly treated. Crop rotation is an important agricultural best management practice that is used to address pest management, soil conservation, and maximizing nutrients for obtaining favorable crop production. Soil conservation is important to Basso, notwithstanding that there is a response in the Application that no approved Soil Conservation Service plan exists for the operation included in the Application. If the WUP is issued and the subject parcel is placed into crop production, another parcel of land will be taken out of crop production by Basso, resulting in the discontinuation of another permitted well. As a result, the issuance of this WUP will not result in a "water use change." Determination of Reasonable Demand/Allocated Quantities In determining whether a proposed water use is reasonable-beneficial and in the public interest, the District calculates the appropriate permit quantities for the particular water use, which is a function of demonstrated need, or demand for water; efficiency of the water treatment and distribution systems; whether water is sold or transferred to other entities; whether acceptable water can be acquired from lower quality sources; and whether conservation practices are employed. District Basis of Review (BOR), page B3-1. The reasonable need for agricultural water use is generally composed of one or more demand components, depending upon the specific agricultural use. "Typically, the reasonable need for irrigation water uses is equal to the supplemental crop requirement divided by the system efficiency or the system design capacity, whichever is less." "The supplemental crop requirement is the amount of water needed for a particular crop beyond the amount of water provided by effective rainfall." The supplemental crop requirement is generally determined by using the Agricultural Water Use Calculation Program (AGMOD) Version 2.1, which is based on the modified Blaney-Criddle method. This program takes into account site specific information such as crop type, growing period, evapotranspiration rate, soil type, rainfall, irrigation method and number of irrigated areas. "In most cases, the supplemental irrigation requirement is determined for a 2 in 10-year drought condition." The AGMOD program determines an inch-application rate which, when applied to the number of acres to be irrigated, results in a calculation of total annual average and peak monthly quantities for the proposed water use. District BOR, pages B3-4 and 3-5. See also District Water Use Design Aids, pages C4-1 through C4-7. In determining the allocated quantities, or reasonable demand for water, the District seeks to avoid both over- allocating water and under-allocating water for the specific crop intended, to ensure that the permitted amount is sufficient for the "2 in 10-year drought condition." Consequently, the allocated quantities arrived at by District staff through use of the AGMOD methodology may be different from the quantities indicated on an applicant's initial application, which are generally estimated without benefit of an agricultural water use calculation program. The AGMOD program was used to calculate water use quantities for the proposed water use. The allocated quantities for Basso's proposed use are 454,000 gallons per day (gpd) on an annual average basis and 1,241,000 gpd, as a peak month quantity. No quantities were requested or allocated for crop protection. See Finding of Fact 52. Modeling for Simulated Impacts As part of the application review process, the District evaluates potential impacts to existing legal uses of water, the water resources and environmental features that may result from the proposed groundwater withdrawals. To assist in the review process, analytical and numerical models, which incorporate best available hydrogeologic parameters for the area being considered for a permit, are used to simulate drawdowns for the withdrawal of the proposed quantities. The results of these simulations are used in the evaluation of potential impacts to assess whether the application meets the conditions for issuance. The District undertook simulation modeling of the potential effects of the proposed water withdrawals to be authorized by the permit. The allocated quantities were entered into the MODFLOW 387 groundwater flow model, which is a three- layer model developed by the U.S. Geological Survey and is the generally accepted model for this purpose. Model layers were set up to represent the surficial, intermediate, and Upper Floridan aquifers. (The Applicants seek to pump water solely from the Upper Floridan Aquifer.) There are limitations to the model in that the model assumes a homogeneous isotropic aquifer, with no preferred flow direction. In actuality, there is variability in the geology of the area. Modeling is intended to serve as a screening tool for assessing localized impacts anticipated from a proposed water use and is based upon the best available information. As distance from the proposed withdrawal site increases, the reliability of the modeling decreases, due to the variability in the geology and other parameters or boundary conditions that can affect the model. Use of the MODFLOW groundwater model allows the District to look at potential impacts at the site, and in the proximity of the site, and assists the District in assessing possible cumulative impacts associated with a proposed use. To assist in assessing potential impacts from the proposed use, a Peak Month modeling simulation was undertaken by the District, which simulates the effect of pumping the proposed Peak Month withdrawal rate of 1,241,000 gpd for 90 consecutive days, with no recharge to the aquifer systems. The model essentially presents a worst case scenario that is a more severe prediction than what is actually likely to occur from the permitted use under normal conditions. Simulating the period of greatest demand on the hydrologic system is likely to provide maximum protection to existing legal water users and the water resources. The Peak Month simulation undertaken by the District predicts drawdowns in the potentiometric surface of the Upper Floridan Aquifer of approximately 2.6 feet at the proposed withdrawal site; less than 1.4 feet at the nearest property boundary (approximately 1,250 feet from the proposed withdrawal site); and less than 1.2 feet at the nearest existing legal user (a Farmland Hydro well approximately 3,500 feet from the proposed withdrawal site). These numbers did not raise a concern for District staff. ("Potentiometric surface" is "a surface defined by the level to which water rises in an open pipe that is constructed into or all the way through an artesian aquifer. This is measured in feet relative to NGVD or sea level. The level to which water rises inside this open pipe is a function of the pressures on the water in the artesian aquifer." District BOR, page B-xii.) The Peak Month simulation predicts drawdowns in the intermediate aquifer of approximately 0.9 feet at the proposed withdrawal site, and less than 0.9 feet at the property boundary, and at the nearest existing legal user. The Peak Month simulation predicts drawdowns in the water level of the surficial aquifer (water table) of approximately 0.01 feet or less at the proposed withdrawal site, property boundary and nearest existing legal user. Based upon the Peak Month simulations, the District reasonably determined that further cumulative impact modeling was not necessary in order to assess localized cumulative impacts resulting from the proposed use. To assess regional cumulative impacts, the District evaluated Regional Observation Monitoring Program (ROMP) data and found no significant trends in withdrawals in recent years, other than a slight decline attributed to the recent drought. Conditions of Issuance of the Proposed Permit In order to obtain a water use permit, an applicant must establish that the proposed use of water is a reasonable- beneficial use, will not interfere with any existing legal use of water, and is consistent with the public interest, by providing reasonable assurance, on both an individual and cumulative basis, that the water use meets the conditions for issuance as specified in Section 373.223(1), Florida Statutes, and Rule 40D-2.301, Florida Administrative Code. A permit must be obtained from the District prior to withdrawing water, where the withdrawal is from a well having an outside diameter of six inches or more at land surface, where the annual average withdrawal from all sources is 100,000 gpd or greater, or where the total combined withdrawal capacity from all sources is greater than or equal to 1 mgd. The proposed water use falls within these parameters. Rule 40D-2.041(1)(b) and (c), Florida Administrative Code. The quantities allocated for the proposed use have been determined by the District to be necessary to fulfill a certain reasonable demand, for the reasons specified herein. To assist in assessing impacts, the District utilizes a network of ROMP wells to obtain basic groundwater monitoring data over time and to help characterize the lithology, stratigraphy, aquifer depths, water levels and, in some cases, water quality for the various water resources. Data obtained from the ROMP and other wells is compiled to ascertain aquifer characteristics within the District and is also integrated into the District's modeling efforts pertaining to proposed water uses. ROMP well No. 31 is located just off the northeast corner of the Basso site. Having a ROMP well adjacent to the Basso site increases confidence in the specific geological information being used in the groundwater model to assess potential impacts from the proposed uses. ROMP well No. 17 is located approximately 1/2 mile from DCAP member Behren's well. Data from both wells were considered in assessing potential impacts from the proposed water use. Based on available information, the possible sources of groundwater for the proposed use at the Basso site are the surficial aquifer, intermediate aquifer, and the Upper Floridan Aquifer systems. To ensure sufficient quantities of water for the proposed use and to avoid potential impacts to environmental features, such as wetlands and surface waters, the District will require the proposed use to limit withdrawals to solely the Upper Floridan Aquifer. By examining stratigraphic cross sectional information generated from the ROMP wells, particularly ROMP No. 31 well, which is in close proximity to the Basso site, District staff were able to determine, with reasonable certainty, the approximate depths of the aquifers at the Basso well site. To ensure that the well will be open solely to the Upper Floridan Aquifer, the permit requires the Basso well to have a minimum of 400 feet of casing, with an estimated well depth of 1,000 feet. Based upon available information concerning the construction of other wells in the vicinity of the proposed Basso well, the District is reasonably assured that a well cased for a minimum of 400 feet will draw water only from the Upper Floridan Aquifer and will minimize the potential for water to move between the aquifers through the well. The well construction requirements imposed for Basso's well are in line with the best available stratigraphic information and with known construction of wells in the area. By casing the well to a depth of 400 feet and due to the extremely low leakage of the intermediate confining unit, the intermediate and surficial aquifers will be buffered from impacts associated with the proposed use. The District will deny a water use permit application if the proposed withdrawal of water, together with other withdrawals, would cause an unmitigated adverse impact on a legal water withdrawal existing at the time of the application. The District considers an adverse impact "to occur when the requested withdrawal would impair the withdrawal capacity of an existing legal withdrawal to a degree that the existing withdrawal would require modification or replacement to obtain the water it was originally designed to obtain." District BOR, page B4-14. Based upon an assessment of individual and cumulative regional information, there are no existing legal uses of water that will be adversely impacted as a result of the proposed withdrawals. Based upon an assessment of individual and cumulative regional information, no quantity or quality changes that adversely impact the water resources, including both surface and groundwaters, are anticipated from the proposed withdrawals. The District requires that consideration be given to the lowest water quality available, which is acceptable for the proposed use. Lower quality water includes reclaimed water, collected stormwater, recovered agricultural tailwater, saline water or other sources. District BOR, page B4-12. For the proposed water use, there is no viable lower quality water source and no reclaimed water available near the site to use as an alternative to groundwater pumping. The Applicants are proposing to use the lowest quality water that is available. There are no known concerns regarding the quality of water in the Upper Floridan Aquifer at this location in Hardee County. Restricting the proposed water use to the Upper Floridan Aquifer will not cause water quality concerns or result in pollution to any of the aquifers. Simulated drawdowns to the Upper Floridan Aquifer of approximately 2.6 feet at the proposed withdrawal site, less than 1.4 feet at the nearest property boundary, and less than 1.2 feet at the nearest permitted well, provide reasonable assurance that adverse impacts will not occur from the proposed water use. Simulated drawdowns to the intermediate aquifer of 0.9 feet at the proposed withdrawal site, and less as the distance from the proposed withdrawal site increases, provide reasonable assurance that adverse impacts will not occur from the proposed water use. Simulated drawdowns to the surficial aquifer of 0.01 feet or less at the proposed withdrawal site, and less as the distance from the proposed withdrawal site increases, constitute a nearly undetectable impact to the surficial aquifer, which is not an adverse impact. The modeling simulations demonstrate that the proposed withdrawals will have no significant effect on the surficial aquifer and, therefore, will not cause adverse impacts to environmental features such as wetlands, lakes, streams, fish and wildlife, or other natural resources. None of the simulated drawdowns are considered to be predictions of adverse impacts, not even in the localized vicinity of the well site. Mr. Jackson explained that because the localized modeling simulations were small or insignificant and showed no adverse impacts, cumulative modeling is not considered necessary. Reasonable assurance on a cumulative basis is determined by assessing the potential localized impacts in conjunction with existing cumulative data for the region, such as the available ROMP data and hydrographs, which depict the existing regional condition, taking into account, on a cumulative basis, all existing uses as well as rainfall conditions and climate. Based on an assessment of the cumulative data and the modeling for individualized impacts, and applying professional judgment, District staff reasonably concluded that the proposed water use presents no concerns that it will cause, on either an individual or a cumulative basis, adverse impacts to the water resource or existing legal uses. Minimum flows and levels have not been established by the District for the area where the proposed use is located. (The parties stipulated that the District has not established minimum flows and levels pursuant to Section 373.042, Florida Statutes, for the Southern Water Use Caution Area (SWUCA)). Therefore, Rule 40D-2.301(1)(d), Florida Administrative Code, (requirements for minimum flows and levels), is not applicable to the proposed permit. The proposed use presents no concerns for saline water intrusion. The proposed use raises no concerns regarding causing pollution to the aquifer. There are no offsite land uses that will be adversely impacted as a result of this permit. Basso currently uses best management practices for water conservation in his ongoing farming operations, and intends to use such practices with the new farming operation authorized under the permit. In keeping with such practices, irrigation is stopped when the water reaches the end of the watering ditch. Basso uses seepage irrigation and tries to regulate the ditches so that there is a minimum, if no, runoff. Also, a watering cycle generally lasts from three to seven days before irrigation has to be resumed. Any runoff goes into "filtering ponds, before reaching ditches or creeks" in its raw content. Basso does not intend to farm during months of likely frost so no separate allocation for frost/freeze protection was requested or needed. Given these irrigation practices, water is not reasonably expected to be wasted. All necessary and feasible agricultural water conservation activities will be implemented upon issuance of the WUP. In addition, Specific Condition No. 3 of the proposed WUP requires the incorporation of best water management practices in all irrigation practices. The proposed use presents no concerns that it will otherwise be harmful to the water resource. The Applicants have met all the requirements for issuance of a WUP. Southern Water Use Caution Area The proposed water use site is located within the SWUCA. The District established the SWUCA as a means of addressing on a regional scale concerns about long-term impacts to the water resource. Water use caution areas were created in recognition of regional water concerns. There have been drought conditions in the area which have caused reduced aquifer levels. The proposed water use site is not within the "Most Impacted Area" (MIA), which is located approximately 18 miles to the west of the site in Manatee County, nor within the "East Tampa Bay Water Use Cautionary Area" (ETB WUCA), which is approximately six miles to the west of the proposed site, also in Manatee County. (The SWUCA includes the MIA and ETB WUCA.) Pending final adoption of rules for the SWUCA, the District will continue to issue WUPs for proposed water uses that meet the conditions for issuance. The District cannot treat new uses and existing renewal uses any differently when considering the issuance of a permit. Once SWUCA rules and minimum flows and levels are established, the District expects to rely on a more regional approach to address long-term cumulative impacts over the entire use caution area, instead of relying on a permit-by-permit basis to address regional concerns. Standard Condition No. 9 of the proposed WUP requires the permittee to cease or reduce withdrawals as directed by the District, if water levels in the aquifers fall below the minimum levels established by the District Governing Board. The proposed withdrawal will use a seepage with mulch irrigation method, which has a 50 percent efficiency level. See footnote 1. This is the minimum efficiency level currently required for agricultural WUPs within the SWUCA, which approve the use of this irrigation method. As SWUCA rules come into effect, a higher percentage efficiency level probably will be required, as is now required in the Eastern Tampa Bay Water Use Caution Area and also in the Highlands Ridge Water Use Caution Area. Consequently, Standard Condition No. 11 of the proposed WUP requires that, when SWUCA rules are implemented, the permittee must comply with any higher efficiency level or other special regulation that may be required for the SWUCA area. DCAP's Challenge to the Proposed WUP DCAP does not keep official membership records. It does not maintain any list of current members. According to Behrens, there are five members of the board of directors. DCAP does not hold corporate meetings, annual meetings or maintain corporate records. Members do not meet. There are no means to document the existence of members for this organization. Behrens is a member of DCAP. He has owned five acres adjoining the west side of Horse Creek (in DeSoto County) since 1985. Behrens complains that the District does not look at the cumulative effect on his well and other people he knows, such as George Chase. Behrens is concerned with any lowering of the water level in the area, including Horse Creek. He believes that approval of wells in the area, including the proposed well, is the straw that is breaking the camel's back. Mr. Chase shares this view. Behrens relies on an artesian free-flowing, two-inch diameter well, for domestic water use, located in the intermediate aquifer, approximately 150 feet deep. (Behrens' well is approximately 18-20 miles from the proposed Basso well.) For most of the time he has lived there, the well had an electric pump for obtaining water. Approximately one year ago, the pump went bad, and a replacement system has not been installed. Currently, Behrens has no pump on the well, and in dry periods, has to obtain water for domestic uses from nearby Horse Creek, which is low during the dry season. (Behrens depends on Horse Creek to pursue his recreation, wildlife, and aesthetic values.) Having a flowing artesian well will enable him to obtain water from the well without having to install an electrical pump, a situation which is desired by Behrens, in part, because the property is in a flood plain and experiences frequent flooding and electrical outages. Not all artesian wells flow. Artesian wells are completed into confined aquifers in which the water in a tightly cased well, will rise to a level above the formation being measured. Water would have to rise above the land surface to be a flowing well. For a well to be artesian, the well must be under confined pressure. For a well drawing water from a confined aquifer, such as the intermediate or the Upper Floridan Aquifer systems, the measured water level in the well is a reflection of the amount of potentiometric pressure in the well. This level can be affected just as much by the amount of recharge as it can by the amount of water withdrawals. There is no evidence that the proposed water use will adversely impact the flowing nature of either Behrens' or Chase's well. The evidence demonstrates that the proposed water use will not adversely impact Behrens' well. George Chase is a member of DCAP. Mr. Chase lives in Arcadia, DeSoto County, Florida. His property is adjacent to the Peace River. Mr. Chase's well is a two-inch diameter well, believed to be about 150 feet deep and equipped with a 12-volt DC solar-powered pump. Mr. Chase has in the past relied on artesian pressure within the confined intermediate aquifer to supply water to his solar-powered home. The solar-powered pump assists in supplying water to the home. In recent years, Mr. Chase has experienced low water pressure in his well. In Spring 2000, Mr. Chase contacted the District to complain that when an adjacent citrus grove was irrigating the groves, it appeared to affect the water level in his well such that the well's ability to flow was impacted. (According to Mr. Chase, his neighbors have had problems obtaining sufficient water from their wells and reaching water with standard pumps.) This citrus grove is an existing legal user of water that pre-existed Mr. Chase's well. In recent years, numerous domestic wells have been constructed in the vicinity of the Chase home that are large diameter wells utilizing submersible pumps with 110-volt AC power. These wells are more efficient at producing water than the type of well and pump being used by Mr. Chase, are located within a few hundred feet of Mr. Chase's well, and are open to the intermediate aquifer as is the Chase well. Based upon the District's experience in other areas, where there is a cluster of domestic wells drawing from the same intermediate aquifer, such adjacent wells have a much greater impact on each other than do other more distant wells, such as the previously discussed citrus irrigation wells, that are open solely to the confined Upper Floridan Aquifer System. This conclusion is based upon monitoring of the ROMP sites in the affected areas. Mr. Chase's well is approximately ten miles from the proposed withdrawal site. There is no basis to conclude that the proposed water use will cause any adverse impacts to Mr. Chase's well. DCAP members' interests are not affected any differently by the proposed use than are the interests of the general public. DCAP has produced no evidence to support its assertion that the issuance of this permit will result in lowered water levels in the Horse Creek and Peace River or other surface waters. DCAP has produced no evidence to support its assertion that the permit will cause adverse impacts to surface water flows or surface waters or to environmental features such as vegetation, fish, and wildlife. DCAP has produced no evidence that its substantial interests are affected by the proposed agency action.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that Southwest Florida Water Management District enter a final order: Determining that Farmland Hydro Limited Partnership and Frank T. Basso, Jr. and Redland Growers Exchange, Inc., have satisfied the requirements of Section 373.223, Florida Statutes, and Rule 40D-2.301, Florida Administrative Code, regarding conditions for issuance of WUPs;3 Issuing proposed General Water Use Permit No. 20012185.000, as set forth in District Exhibit No. 4; and Finding that DCAP lacks standing to challenge the issuance of the permit. DONE AND ENTERED this 3rd day of June, 2002, in Tallahassee, Leon County, Florida. 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 3rd day of June, 2002.
Findings Of Fact Application No. 76-00292 is for a consumptive use permit for one well located in the Green Swamp, Lake County. The water withdrawn is to be used for industrial purposes. The application seeks a total withdrawal of 3.642 million gallons per day average annual withdrawal and 5.112 million gallons maximum daily withdrawal. This withdrawal will be from one well and a dredge lake and constitutes in its entirety a new use. The consumptive use, as sought, does not exceed the water crop as defined by the district nor otherwise violate any of the requirements set forth in Subsections 16J-2.11(2) , (3) or (4), Florida Administrative Code. The Southwest Florida Water Management District's staff recommends issuance of a permit with the following conditions: That the applicant shall install totalizing flowmeters of the propeller-driven type on the subject well. The applicant shall record the pumpage from the subject well on a weekly basis and submit a record of that pumpage to the district quarterly beginning on January 15, 1977. The permit shall expire on December 31, 1980. The procedural requirements of Chapter 373, Florida Statutes, and the rules promulgated pursuant thereto, have been complied with as they pertain to this application. The intended consumptive use appears to be a reasonable, beneficial use which is consistent with the public interest and will not interfere with any legal use of water existing at the time of the application.
Recommendation It is hereby RECOMMENDED that a consumptive water use permit in the amounts and manner sought for by the subject application be issued subject to the conditions set forth in paragraph 3 above. ENTERED this 5th day of October, 1976, in Tallahassee, Florida. CHRIS H. BENTLEY Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 COPIES FURNISHED: Jay T. Ahern, Esquire Florida Rock Industries, Inc. Staff Attorney Post Office Box 4667 Southwest Florida Water Jacksonville, Florida Management District Post Office Box 457 Brooksville, Florida 33512
Findings Of Fact The CLDD was established pursuant to Chapter 298, Florida Statutes, on August 4, 1967. Its purpose was to "reclaim" or render the land within its boundaries usable for agricultural purposes. The land comprising the CLDD consists of approximately 3,500 acres in Lee County, mostly planted in citrus trees. Pursuant to the requirements of Chapter 298, Florida Statutes, a "Plan of Reclamation" was prepared by consulting engineers for the CLDD's Board of Supervisors in August, 1967. That plan contains provisions for reclaiming lands within the CLDD's boundaries and for managing and controlling surface water within CLDD. The method of water control outlined in the 1967 reclamation plan included a dike and ditch system around the boundaries of CLDD with a series of interior canals to carry excess water away from the citrus trees. The land in the north part of he CLDD is higher than the south and water generally, naturally flows from north to south. The interior canals were designed to carry water in accordance with existing contours of the land and eventually discharge excess surface water to the rim ditches on the north and east sides of Spoil Area "M," which is south of the CLDD and which was then owned by the C&SFFCD, the predecessor agency to SFWMD. The system of drainage delineated in that 1967 plan, inaugurated pursuant to Chapter 298, Florida Statutes, was put into effect substantially as described therein. CLDD's 1967 plan was altered somewhat because of an agreement entered into on September 30, 1971, between the CLDD and neighboring landowner Kenneth Daniels. Pursuant to that agreement, the two parties agreed to extend the dike on the west side of the CLDD property and construct a ditch from a point 50 feet north of the northwest corner of the Petitioner Mellor's property, which new ditch was to run southwest across the Daniels' property and connect with Spanish Creek. That ditch or canal would thus connect the western rim ditch of the SFWMD's Spoil Area "M" with Spanish Creek and have the result that surface waters could be discharged from CLDD lands through the western rim ditch of Spoil Area "M" thence through the "Daniels' Ditch" finally discharging into the lower reaches of Spanish Creek. (see Exhibits 1 and 11) Because the western side or western rim canal of the SFWMD's Spoil Area "M" had not been used under the original plan of reclamation approved by the C&SFFCD, CLDD sought permission from C&SFFCD to use this western rim canal for the purpose stated pursuant to the agreement with Daniels. Thus, CLDD's proposed use of the rim canal of Spoil Area "M" would be confined to the western, northern and eastern perimeter canals and not the southern boundary canal. All affected landowners, Kenneth Daniels as well a Jake and Lilly Lee, agreed to those proposed installations and uses. The resulting agreement between CLDD and C&SFFCD was entered into on October 12, 1972, and describes the flood control District land to be used by CLDD as a 100 foot wide strip running along the west, north and east sides of Spoil Area "M," also know as "Aspic." This 100 foot wide strip of land running thusly is co-extensive with the rim ditch of Spoil Area "M." The CLDD was mandated by this agreement to install 72- inch pipes in the rim ditch at the southwest corner of the spoil area, just north of the Mellor property, giving a point of discharge from the western rim ditch into the Daniels' Ditch with similar pipes connecting that Daniels' Ditch with Spanish Creek, such that the canal between these two points could carry water from the west rim ditch to Spanish Creek. The easement incorporated in this agreement was to last for five years with an option for a five-year renewal, which option was exercised. At the end of this 10-year period, SFWMD, successor to C&SFFCD, notified CLDD that because its statutory authority had since changed, the easement could not be renewed and that CLDD would have to seek the subject permit so as to be authorized to use works and lands of the District. The requirements to be met by an applicant for a right-of-way permit such as this one are set out in Rule 40E-6.301, Florida Administrative Code, and SFWMD's permitting information manual, Vol. V, Criteria Manual for Use of Works of the District, July, 1981, which is incorporated by reference in that rule. In that connection, the permit at issue, if granted, would not cause an interference with the "works" of the District, that is dikes, ditches, flood control structures arid drainage structures because it would merely renew the pre-existing authorized use. The permit will not be inconsistent with an comprehensive water use plan developed by the District. Further, the permit applicant owns or leases the land adjacent to the portion of the "works of the District" involved herein that is the east, north and west rim ditches of Spoil Area "M," the Daniels' Ditch and the pipes at either end of it coupled with the water control structures at the southeast corner and southwest corners of Spoil Area "M," which control water entering the south rim ditch. CLDD has a surface water management permit, issued in August, 1980, which is a prerequisite to the granting of the subject right-of-way permit. It remains in full force and effect. That surface water management permit authorizes "operation of a water management system serving 3,642 acres of agricultural lands by a network of canals and control structures, with a perimeter dike and canal discharging into Cypress Creek." The "surface permit" authorized the system of drainage and discharge in existence at the time of its issuance, May 8, 1980. The system of drainage, at the day of the hearing, consisted of the same basic water flow and discharge pattern that existed for approximately 10 years, and this permit would allow that to be continued, thus, there will not be any additional effect on environmentally sensitive lands occasioned by an issuance of the subject right-of-way permit. The surface water management permit, by its terms, refers initially to the operation of a water management system" . . . discharging into Cypress Creek." The reference to "Cypress Creek" was an administrative error. The express language on the face of the permit authorization incorporates by reference the application, including all plans and specifications attached thereto, as addressed by the staff report, and those materials, including the staff report, are a part of the permit. The complete permit, including all those documents incorporated by reference, makes it clear that the authorization of the surface water management permit was that the system of drainage in existence at the time of permit issuance (1980) was that which was being approved, and that included discharge to Spanish Creek and not Cypress Creek. Discharge of water to Cypress Creek as an alternative was never recommended or authorized by that surface water management permit. This is clearly the intent expressed in the permit in view of the language contained in a special condition of that surface water management permit imposed by the SFWMD as a condition for issuance which stated as follows: Within 45 days of the issuance of this permit the permittee shall submit for staff approval a proposal and schedule for the elimination of the adverse impacts being created by the operation of the permittee's water management system, which can be legally and physically accomplished by the permittee. Adverse impacts are considered herein to be reduced flows to Spanish Creek and increased flows to Cypress Creek. Thus, it is obvious that the authorization of the surface water management permit was designed to provide for discharge into Spanish Creek and to enhance the flows to Spanish Creek pursuant to a required proposal which the permittee submitted to SFWMD. Thus, the right-of-way permit applied for herein is consistent with the valid surface water management permit held by the permit applicant in this proceeding. Petitioners William H. and Patricia H. Mellor are co-owners of parcels of property lying some distance south of Spoil Area "4" in the vicinity of the Caloosahatchee River. This property does not abut the spoil area at any point. Spanish Creek does cross their property several thousand feet south of the south boundary of the spoil area. In the past, particularly in 1982, water flowing from the south rim ditch of the spoil area through a break in the dike of that south rim ditch, has flowed through a ditch known as Dry Creek in a generally southerly direction under S.R. 78 and has washed out an access road constructed by William Mellor which leads from Highway 78 to his property. He had this washout repaired at his own expense in 1982. The washout was caused by water from CLDD flowing into the south rim canal of Spoil Area "M," that is, the ditch that traverses (and defines) the southerly boundary of the spoil area. Mr. Mellor admitted, however, that SFWMD had at least partially plugged the opening in the south rim ditch which had allowed flow down the Dry Creek ditch and wash out his road. If closed water control structures are maintained at the southwest and southeast corners of the spoil area ditches, then no water could flow into the south rim canal and no such injury could again be caused. Petitioner's Jim English and Patricia Mellor are co-owners of a 45- acre parcel of land located in the southwest corner of Spoil Area "M." The five acres forming the extreme southwest corner of the spoil area do not belong to these Petitioners, but are owned by one Lynwood Brown, who is not a party to this proceeding. The English/Mellor property forms a part of the spoil area, but does not adjoin or constitute any part of the spoil area which is sought to be used by CLDD through the proposed right-of-way use permit (as clarified by CLDD's stipulation). The south rim ditch, either part of, or adjoined by their property, has been used for water storage in the past (they maintain illegally) 1/ Mr. Tom Pancoast has observed Spanish Creek frequently over a nine- year period starting in approximately 1973. He has often used those waters during that period for fishing. During the early years of his use and observation of Spanish Creek, the water flowed out of Spanish Creek into the Caloosahatchee River. Beginning in about 1976, the water appeared to be flowing in the opposite direction, from the river into Spanish Creek. Contemporaneous with this hydrologic change, the creek has become increasingly characterized by siltation and hyacinth growth. Mr. William Mellor owns property along the course of Spanish Creek. He has used the stream for recreational purposes, picnicking where the stream traverses his property. In recent years there has occurred a marked increase in the growth or profusion of aquatic plants of unidentified types in the creek, reduced clarity and reduced flows or volumes of water in the creek. Witness English has made a similar observation. Witness James English has a substantial degree of training by formal education and experience in water management and drainage practices and methods, particularly as they relate to citrus grove development and management in southwest Florida. Mr. English has observed Spanish Creek regularly for most of his life, including the region of its headwaters in the "Cow Prairie Cypress," a remnant wetland cypress strand lying within the CLDD immediately north of Soil Area "M." The chief adverse impact of the CLDD water management system is reduced flow to Spanish Creek, especially its upper reaches since the advent of the "Daniels' Ditch" as a drainage route and discharge point into lower Spanish Creek. However, the only special condition on the issuance of the surface water management permit approving CLDD's extant water management system was the requirement that CLDD should submit a plan for eliminating that adverse effect, which it did (as Petitioner English admits). Beyond the submission of such a plan, no concrete action designed to restore historic flows to Spanish Creek has yet begun, however. The restoration of historic flows, adequate in volume and quality, to the entire creek system would require discharging water from CLDD's system to the Cow Prairie Cypress area at the headwaters of the creek rather than substantially further downstream at the present Daniels' Ditch site. The Petitioners' complaints (aside from the issue of adequacy of flows in Spanish Creek), although meritorious, are, because of stipulations asserted by CLDD during the course of this proceeding, now rendered moot. CLDD stipulated that it only seeks a permit to use the west, north and eastern spoil area ditches. It does not seek and stipulated that it will not use, at any time, the south rim ditch and will maintain water control structures so to block water from entering that ditch. This will alleviate the problem of potential storage of water on Petitioners English and Patricia Mellor's property and the erosion problem on Petitioners William and Patricia Mellor's property south of the spoil area. It was thus established that the issuance of the right-of-way permit will not cause the injuries these Petitioners have suffered in the past because of use of the south rim ditch for water drainage and storage.
Recommendation Having considered the foregoing Findings of Fact, Conclusions of Law, the evidence in the record and the candor and demeanor of the witnesses, it is, therefore RECOMMENDED: That the South Florida Water Management District grant the County Line Drainage District's application for a permit for utilization of works and lands of the District. Subject to the following special condition: Issuance of this right-of-way permit does not relieve the Respondent CLDD from the responsibility of complying with special condition number 1 of the surface water management permit number 36-00184-S. Respondent CLDD shall, within 30 days of date of permitting, submit a design to the satisfaction of the SFWMD staff which will prevent the ability of CLDD to discharge to the southern rim ditch, described above. DONE and ENTERED this 29th day of September, 1983, in Tallahassee, Florida. P. MICHAEL RUFF 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 September, 1983.
The Issue The issue is whether WRP, Inc.'s application for an Individual Water Use Permit to construct five 24-inch diameter wells in Walton County, Florida, and to withdraw an average of 4.84 million gallons per day for twenty years, should be issued, as proposed by the agency on June 5, 1998.
Findings Of Fact Based upon all of the evidence, the following findings of fact are determined: The Parties Respondent, Northwest Florida Water Management District (District), is an independent special district of the State of Florida created pursuant to Section 373.069, Florida Statutes. The District is charged with regulating consumptive uses of water in a sixteen-county area in Northwest Florida, including all of Walton and Okaloosa Counties. Respondent, WRP, Inc. (WRP), is a not-for-profit Florida corporation with its headquarters in Walton County, Florida. It is jointly owned by Destin Water Users, Inc. (DWU) and South Walton Utility Company, Inc. (SWUC). Both DWU and SWUC are not- for-profit Florida corporations that own and operate water supply systems (with thirteen operating wells) in and around the southern portions of Okaloosa and Walton Counties. Established in 1995, WRP was originally organized as a partnership made up of DWU, SWUC, and Petitioner, Florida Community Services Corporation of Walton County, d/b/a Regional Utilities of Walton County (RU). This partnership was established for the purpose of cooperating in the development of an alternate water supply for the utilities' service areas. Thereafter, the partnership was dissolved, which led to the establishment of WRP. RU is no longer a part of this organization. Petitioner, City of DeFuniak Springs, is a municipal corporation in Walton County, Florida. The city owns and operates its own public water supply system. At the present time, it serves approximately 15,200 persons who reside both inside and outside the corporate limits of the city. Petitioner, City of Freeport, is a municipal corporation in Walton County, Florida, and owns and operates its own public water supply utility. RU is a not-for-profit Florida corporation which, pursuant to a lease, operates a public water supply system in the coastal area of Walton County under a permit issued by the District. It presently serves around 500 customers representing a population of 17,000. A portion of its water supply is also obtained from the City of Freeport. Petitioner, Walton County (County), is a political subdivision of the State of Florida pursuant to Article 8, Section 1 of the Florida Constitution. The County owns the land and facilities used by RU for its public water supply system. However, under a lease agreement between those parties, RU operates the system. In addition, the County also owns a small well recently constructed near the Rock Hill area. Historical Background of the Area's Water Supply The District's overall responsibility in the consumptive use program is to provide for all citizens the sustainability of the water resources of Northwest Florida. It also seeks to allocate the resource in a manner that is reasonable and beneficial, that is in the public interest, and that will not interfere with the use associated with other existing legal users. This is often referred to as the three prong test. Ground water is measured by the location of its potentiometric surface in relation to sea level. The potentiometric surface is the level to which water will rise in a tightly cased well. In portions of coastal Okaloosa and Walton Counties, the potentiometric surface of the Floridan Aquifer is below sea level. At one coastal location the surface is at 110 feet below sea level as compared to elevations of more than 200 feet above sea level in the northern portions of those counties. When the potentiometric surface is below sea level it is called a cone of depression. As shown on District Exhibit 1, the cone of depression in the coastal area of Okaloosa and Walton Counties has grown from 1974 to 1995. The decline of these water levels in the coastal areas is further supported by the hydrographs found on the District's Exhibit 2 entitled Floridan Aquifer System Water Level Trends. These hydrographs document the reduction in the potentiometric surface over time. Of particular significance are the hydrographs of the "Okaloosa School Board" well which show the potentiometric surface to be 60 feet above sea level in the late 1930's when it was constructed and to be approximately 110 feet below sea level in 1996. As early as 1982, the District recognized a threat to the continued existence of a long-term sustainable water supply for the coastal regions of Walton and Okaloosa Counties. Significantly, the pumping of water from the Floridan Aquifer in this coastal region has caused a degradation to the aquifer and the water resources. As a result, the District began taking affirmative steps to protect the water resources in the coastal area of Walton and Okaloosa Counties. In 1982, the District undertook a regional water supply development plan entitled 1982 Regional Water Supply Development Plan (the 1982 Plan). The 1982 Plan assessed the sustainability of water resources in the coastal region of Okaloosa and Walton Counties, estimated the Floridan Aquifer's water supply capabilities in relation to expected long-term water demand, and addressed the need to find an alternative long-term water supply for these coastal regions. The 1982 Plan also discussed strategies for alternate water resource development including inland well fields, desalinization, conservation measures, and use of surface water from the Choctawhatchee River. In 1988, the District developed an addendum to the 1982 Plan, known as the 1988 Plan, which addressed similar issues. In particular, the 1988 Plan further emphasized the need for the coastal water utilities of DWU, SWUC, and RU to use inland well fields and/or desalinization as potential alternatives for the long-term water supply needs of the area. The 1988 Plan eliminated surface water from the Choctawhatchee River as a potential alternate source for the long-term water supply needs of the area because it was not technically, economically, and environmentally feasible. The thrust of these two studies is to encourage movement of withdrawals away from coastal areas. In 1989, the District implemented Rule 40A-2.801, Florida Administrative Code, which authorizes the declaration of areas of the District as "water resource caution areas." In that same year the District adopted Rule 40A-2.802(1), Florida Administrative Code, which designates the coastal area of Walton and Okaloosa Counties as a water resource caution area. This designation means that the water resources of the coastal area are limited and will not be sufficient to meet the water needs of the area within a period of twenty years. In addition, the rule prohibits non-potable uses of the Floridan Aquifer as against the public interest. Since 1989, the District has worked with DWU, SWUC, and other coastal water supply utilities to expedite the development of alternate water sources and implement water conservation measures. In Okaloosa County, the District has placed limitations on the diameters of wells and the amount of water that can be withdrawn from coastal wells. To promote conservation of water, the District has imposed stricter requirements for the reuse of wastewater; promoted the adoption by coastal utilities of inverted rate structures; required that utilities implement retrofit programs to replace old water fixtures with more efficient water-saving devices; required that utilities account for losses due to system leakage; required that utilities provide for education programs and public service announcements on the need to conserve water; and encouraged utilities to seek adoption of water efficiency landscape and irrigation ordinance by the appropriate local governments. The measures taken by the District are intended to address the harmful impacts to the Floridan Aquifer caused by increasing coastal water withdrawals. Because the District has determined that the water resources are limited, the District has mandated that alternative water supplies must be identified and developed in order to provide for a sustainable and long-term source of potable water in the coastal areas of Okaloosa and Walton Counties. There is no evidence to refute the District's concerns regarding the impact of continued coastal withdrawal and the need to find an alternative source of potable water to meet the region's long term demands. Based on the evidence, it is clear that coastal withdrawals of ground water cannot continue and that an alternate source of water must be found to meet the long-term water demands of the coastal areas of Walton and Okaloosa Counties. The Application In July 1996, WRP submitted a Consumptive Use Permit Application (CUPA) for the withdrawal of water from an inland wellfield in Walton County. The CUPA requested a maximum withdrawal of 7.2 million gallons of water per day (mgd) from two production wells with additional wells to be constructed on an as needed basis. The original application placed the wells along Highway 20 in the vicinity of the City of Freeport, or some twenty miles north of its present wellfields. This location concerned the District because of its proximity to the Choctawhatchee Bay and the saltwater/freshwater interface. In response to the District's concerns, WRP relocated the proposed wellfield farther north and inland to a 4,900 acre site approximately five miles north of the City of Freeport, known as the Rock Hill site. Under the proposed permit, WRP may withdraw an average of 4.84 mgd from the Floridan Aquifer from five 24-inch diameter wells. All withdrawals of water are authorized solely for public supply use. The proposed permit also authorizes a combined monthly withdrawal limit of 150,040,000 gallons. The permit is issued for a twenty-year period and has an expiration date of June 26, 2018. The proposed permit contains numerous conditions to issuance. They are primarily intended to implement water conservation and efficiency measures as well as monitor and mitigate any impacts to the Floridan Aquifer and existing legal users caused by the permitted water withdrawals. Compliance with Permitting Standards The District's overall responsibility in the consumptive use program is to provide for the sustainability of the water resources of Northwest Florida. In allocating water resources, the District seeks to do so in a manner that is reasonable and beneficial, that is in the public interest, and that will not interfere with the use associated with other existing legal users. WRP's compliance with these broad standards will be discussed in detail below. Reasonable and Beneficial Use of the Water In determining whether a water use is reasonable and beneficial, the District must consider the criteria set forth in Rule 62-40.410(2)(a)-(r), Florida Administrative Code. Quantity of Water Requested [62-40.410(2)(a)] In its original application, WRP requested withdrawals of 7.2 mgd. Because of the District's concern that the amount of withdrawals and projected annual rate of growth were too great, the permitted amount has been revised downward to 4.84 mgd. This quantity is not excessive, and the actual pumping under the permit will be less than the amount modeled for evaluation of impacts. Demonstrated Need [62-40.410.(2)(b)] The current water source for both DWU and SWUC is coastal Walton and Okaloosa Counties. That source is insufficient for future needs, and the demand placed on that resource should be reduced. As noted above, the need for coastal areas to develop an alternative wellfield was recognized by the District as early as 1982. This finding was reconfirmed in a District study completed in 1988. The record supports a finding that WRP has shown a demonstrated need for the alternative site. Suitability and Value of Use [62-40.410(2)(c) and (d)] WRP is requesting a withdrawal of water for public supply. This type of use within the Rock Hill area is a suitable use of that resource. Also, the Rock Hill area has long been identified as a good location for an inland wellfield. The suitability of the use to the source of water is demonstrated by the high quality of the raw water which can be easily treated for potable drinking water. The purpose is for domestic consumption, which is the highest use. The proposed wellfield is the closest available inland groundwater source with minimal impact. In terms of value, WRP is proposing to withdraw water from the Floridan Aquifer to provide the public with drinking water. The provision of a long-term, reliable source of water is a high value. It also helps to sustain the resource in coastal Okaloosa and Walton Counties by reducing future demands on the source. The Extent and Amount of Harm Caused [62-40.410(2)(e)] The evidence establishes that neither the resource nor the existing legal users will be harmed by the proposed activity. Harm would occur, for example, when a domestic user would be permanently denied water as a result of a proposed pumping activity. Although this condition should not occur, the permit contains conditions to mitigate this event. WRP conducted a test well program and extensive groundwater modeling at its proposed wellfield to establish the drawdown curve that would exist in the Floridan Aquifer. The extent and amount of harm caused is not significant, and WRP has demonstrated that there will be no significant environmental impact or impact to other users. There will not be any drawdown impacts in the surficial aquifer, nor should there be any discernible impact on the Floridan Aquifer. Drawdowns as a result of WRP pumping in the potentiometric surface in the Freeport area are expected to be two feet in the year 2005, and around five feet in the year 2018. These are not considered significant drawdowns for a public supply well. Under the proposed permit, WRP will be required to mitigate any impacts attributable to its withdrawal that interfere with domestic users in the vicinity of the wellfield. Any problems encountered in domestic wells in the area can be remedied by adding a length of pipe, or lowering the pumps in the wells. The water resource will not be significantly impacted by saltwater intrusion as a result of the proposed use. The greatest part of the advance of the saltwater wedge is due to the City of Freeport's own pumping; WRP's contribution to the advance is minimal. This is because the City of Freeport is closer to the coast. Any impacts on wells within the City of Freeport from chlorides will be the result of their own pumping, and not that of WRP's proposed pumping. Mitigation of Harm [62-40.410(2)(f)] The District does not anticipate that any harm to other legal users will occur. Even assuming arguendo that some harm might occur, there are two conditions in the permit that can be invoked to ensure that the issues are addressed. Standard Condition 11 entitles the District to curtail permitted withdrawal rates if such withdrawal causes significant adverse impacts on existing legal uses of water, or adjacent use, while Special Condition 17 requires that WRP mitigate any impacts to existing legal users if such interference should occur. The District envisions the latter condition to be implemented through a telephone hotline and arrangements with a water well contractor to remedy any adverse impact. To the extent that any harm to area domestic wells may occur, WRP has agreed to correct any individual adverse impacts by either lowering the pump, deepening the well, replacing the well, or whatever may be necessary. This is consistent with Special Condition 17, which requires that WRP mitigate impacts attributable to its withdrawal which interfere with users of water in the vicinity of their wellfield. Finally, the proposed permit has a system of checks and balances by which the District can look at actual water uses over time and adjust them while still providing for coastal reductions. Impacts on Other Lands [62-40.410(2)(g)] Although WRP purchased approximately five thousand acres on which to site its wellfield, not all of the property is necessary to run the wellfield. The parcel was purchased so that any adverse effects from the pumping would not affect landowners, and the majority of the drawdown would be confined to the purchased property. The test well program conducted at the remote wellfield, and the modeling conducted by WRP Witness Maimone, establish that the greatest impacts will be on lands owned and controlled by WRP. Method and Efficiency of Use [62-40.410(2)(h)] The method and efficiency of use by WRP is demonstrated by its utilization of water conservation measures to ensure that efficiency is maximized throughout the system. The use of ground water from the inland wellfield is an efficient method of providing potable water for public supply. Water Conservation Measures [62-40.410(2)(i)] The District has mandated that certain conservation steps be taken to protect the resource in the Okaloosa and Walton County area. This is consistent with the District's efforts to require implementation of conservation measures by coastal water supply utilities. Reuse of treated wastewater has been encouraged, and it is used to irrigate golf courses and private landscapes. Also, the District is requiring DWU and SWUP to account for and correct water losses, and to undertake retrofit programs among homeowners and commercial establishments to install water-saving devices and other types of efficiency measures. Except on rare occasions, all DWU treated effluent is used for irrigation. Indeed, DWU is currently achieving a 100 percent reuse rate. Reuse water currently supplied to customers of DWU is not available for aquifer storage. As part of a general conservation effort, DWU has replaced almost 6,000 water meters in the last five years. The City of Destin, which is within DWU's service area, has distributed low-usage shower heads, and it has implemented a low volume toilet ordinance which requires these types of fixtures in all new construction. Currently, DWU has a 12 percent water loss and is attempting to meet the District's recommended goal of 10 percent. SWUC has various programs in place to conserve potable water. The conservation methods include an inverted block structure, reuse, and public education. Currently, SWUC provides reuse irrigation water to golf courses and a subdivision. The evidence supports a finding that the water use proposed by WRP will not be wasteful. Conditions 3 through 12 in the permit require WRP to implement a comprehensive series of water conservation and efficiency measures. Without the new wellfield, it would be impossible to conserve a sufficient amount of water to be able to provide for the future needs of the citizens to be served by WRP. The District will require WRP to comply with a comprehensive water conservation and efficiency program. The conservation and efficiency program includes implementation of a retrofit program, reduction of unaccounted for losses to less than ten percent, five-year audits, landscape ordinances, and irrigation ordinances. Feasibility of Other Sources [62-40.410(2)(j)] The District has identified no available surface water body from which WRP could meet its anticipated demands. In 1988, the Choctawhatchee River was determined not to be a feasible source. Additionally, the Sand and Gravel Aquifer is not suitable for a large, public supply utility to access. In 1982, Eglin Air Force Base (Eglin) was projected to be a location for regional wellfields. The 1988 Plan, however, removed Eglin as a possible solution for long-term water supply problems due to Eglin's decision not to allow wells on the reservation. SWUC, DWU, and WRP all produced water masterplans in order to identify options available to address the additional water supply needs in the area. Upon its formation, WRP undertook an investigation to determine whether additional water supplies could be provided best by a remote wellfield or by a reverse osmosis (RO) plant. The study was undertaken because the the available water supply clearly would be insufficient and other options should be considered. After being formed, WRP immediately purchased options from the Champion Paper Company for six well sites along Highway 20. At considerable expense, WRP investigated the RO alternative as a water supply source along with other alternative sources such as reclaimed water, stormwater, brackish water, and saltwater. WRP constructed a RO test well to evaluate that option. The test well extended into the Lower Floridan Aquifer since that aquifer was considered as a possible source of brackish water from which potable water could be produced. The District provided a $30,000 grant toward the RO evaluation, and it also provided technical assistance and guidance to ensure that WRP obtained the type of data that the District desired. Assumptions made in evaluating the cost of the RO option were designed to predict the lowest possible construction and operating costs. Also, a number of problems were identified with the RO process. These included long-term water quality, contamination, and disposal of the waste (reject water) produced. These concerns are addressed separately below. The potential for long-term change in water quality is the most important factor in evaluating the feasibility of the RO option. WRP's test well showed chlorides at 1,800 parts per million; 200 feet below that, the test well was half seawater; and at another 200 feet below, the test well was full of seawater. These results indicated that saltwater upconing was a severe concern. The data strongly indicated that water quality would not remain constant for very long in the RO well. An analysis made by WRP estimated that saltwater upconing would occur in less than a year and probably within a matter of months. The analysis considered only vertical movement for upconing within the RO test well, and it did not consider the effects of horizontal movement. These assumptions produce the most reliable result possible. The possibility of lateral movement is an additional risk to the water quality in the RO test well. Together with the potential for upconing shown in the study conducted by WRP, a great amount of uncertainty existed in the raw water source in terms of long-term stability and water quality. If seawater occurred within the aquifer at some close proximity to the RO test well, then ultimately the whole system could convert from brackish water to a seawater system. This would change the entire economics of the treatment process and plant design, and it would diminish WRP's ability to obtain a concentrate disposal permit. Without some certainty as to the quality of water over time, RO is not a viable alternative. The data summarized in WRP's report demonstrates that copper values in excess of 2.9 micrograms per liter (mcg/l) were present in the water withdrawn from the well. Samples taken directly from the Lower Floridan Aquifer using the Packard Stem Test indicated that the copper came from the aquifer formation. The established water quality standard for copper in Class II waters is 2.9 mcg/l. As noted above, this standard would be violated. The concentrate or reject water from the RO process utilizing the subject source would be expected to contain five times the copper concentration of the raw water. In addition to this concern, gross alpha, Radium 226, and Radium 228 were also present in grab samples and constituted another potential problem. These types of contamination render the RO option unfeasible because of problems with disposal of the concentrate or reject water. A RO option necessarily includes a brine disposal element. The disposal would be in the form of a reject stream that would be continuously discharged from the RO facility while in operation. The concentrate from the RO process is classified as an industrial waste. In Florida, the method for disposal for the reject water includes deep well injection and surface water disposal. However, the deep well injection of reject concentrate is not feasible for the RO well because the Lower Floridan Aquifer has no internal confinement between the zone of withdrawal and a proposed zone of injection. Moreover, there is no zone in Northwest Florida sufficient to be used for this type of injection in these volumes. The only other remaining option would be surface water discharge which requires a National Pollutant Discharge Elimination System permit. Any surface water discharge with respect to RO would be to Class II waters, which would be far more difficult to permit than a Class III water, where such discharges have normally occurred. In addition, because of the high level of copper in the reject concentrate, it would be extremely difficult to receive a mixing zone for copper at the extended concentrations. Since 1982, the District has recommended that an inland wellfield be developed in the area north of the City of Freeport. An inland wellfield is a more reliable source of water with a greater amount of certainty, can be permitted within a reasonable period of time, and is less expensive. WRP's proposal for a remote, inland well in the Rock Hill area is consistent with these goals. Present and Projected Demand for Water [62-40.410(2)(k)] The District relied upon two studies to reach the conclusion that the average growth rate for water would be three percent per year in WRP's service area. This contrasts with WRP's projection that a five percent growth rate would be more accurate. Due to the high degree of uncertainty in the area of growth and water demand, the District has provided a mechanism to deal with underestimated growth which includes periodic review of the withdrawal amounts by the District and corresponding adjustments, if necessary. It is clear that the supply of water is adequate to provide water for WRP as well as other users in the area. Long-Term Yield Available from the Source of Water and Water Quality Degradation [62-40.410(2)(l) and (m)] Sufficient water resources exist in the Rock Hill area to meet projected water demands through the year 2018. No impact to the surficial aquifer is expected, while only minimal impact to nearby surface water is projected to occur. The movement of the saltwater wedge is not a factor. For some fifteen years, the District has taken steps to monitor and reduce coastal well withdrawals. More recently, it directed its staff to notify all existing non-potable users of the Floridan Aquifer that at the time of permit renewal, they may be required to find alternate sources. Starting two years ago, a number of these permits came up for renewal. In some cases, the applicants were given approximately two years to eliminate the Floridan Aquifer withdrawals, find an alternate source, and plug their wells. The potential for water quality degradation is evaluated through computer modeling. A modeling plan is a document that describes the approach that a modeler is going to use to build a model. It specifies the various components of the model, battery conditions, modeling techniques, model domain, and the modeler's conceptualization of the stratigraphy. WRP's model demonstrates a lack of degradation of the water resources. The modeling of the saltwater wedge indicates that the wells in the Freeport area will not be threatened. There will be negligible impacts to base stream and river flow and no impact to surface wetlands. Based on the present and projected demand for the source of water, no significant impact to the environment or to existing users will occur. To the extent water quality degradation might occur, it will cause a minimal amount of change in the position of the diffused chlorides in the coastal zone. The predicted impacts to water quality take into consideration the coastal reductions which will limit pumping of the coastal wells and switch withdrawals to the alternate inland source. Proposed Flood Damage [62-40.410(2)(n)] There is no indication that WRP's proposed withdrawal activity will cause any flood damage. The proposed use will not cause or contribute to flood damage due to its negligible affect on surface waters. Significant Inducement of Saltwater Intrusion [62-40.410(2)(o)] WRP's coastal saltwater intrusion model used worst case conditions when estimating the movement of the saltwater wedge. Indeed, the saltwater intrusion was computed so conservatively that the existing coastal wells were modeled pumping saltwater instead of the actual freshwater that they currently pump. The movement of the saltwater wedge is not projected to be dramatic over the next 50 years. The location of the saltwater wedge in the year 2050 would still be 600 feet below sea level. The wedge does not approach, nor would it threaten, the City of Freeport's wells. In fact, any potential risk of saltwater contamination in Freeport's wells is due to that City's current pumping rates. The Amount of Water Which Can be Withdrawn [62-40.410(2)(p)] The amount of water withdrawn by WRP will have no significant impact on the resource. This finding is supported by a WRP groundwater modeling study. The impacts of the wellfield on the potentiometric surface do not go below sea level. There will be no drawdown impact in the surficial aquifer or any discernable impact on the Floridan Aquifer. Adverse Effect on Public Health [62-40.410(2)(q)] No potential adverse effects on public health have been identified in the instant case, and there is no indication that WRP's withdrawals would affect public health. The resource is a high-quality use and would provide the public with a high-quality source of water for drinking purposes. Significant Effects on Natural Systems [62-40.410(2)(r)] The evidence established that there will be no impacts to surface wetlands and very minimal impacts to base stream flow. Base flow is the constant flow from groundwater into surrounding waters. Any reduction in the flow of groundwater to the Choctawhatchee River as a result of WRP pumping is negligible. Slight impacts were observed in the base flow of streams close to the proposed wellfield site. Impacts on the surface water are also minimal. Riparian wetlands would be unaffected by the water level decline that was simulated as a result of WRP pumping. Finally, any impacts associated with the construction of the transmission pipeline from the inland wellfield are temporary in nature and extend only through the period of construction. Consistent with the Public Interest The evidence demonstrates that the use of the water by WRP, as well as the water use reduction allocation, is consistent with the public interest. WRP is proposing to withdraw water from the Floridan Aquifer in the Rock Hill area to provide citizens with drinking water. The purpose of domestic consumption is the highest and best use of a water resource. The public interest is served through the proposed reduction in coastal groundwater withdrawals contained in the WRP permit. Reduction in the withdrawals from the coastal areas has been a long-term goal of the District in order to protect water resources in the area. WRP's proposed use is also consistent with the public interest in that the use will not affect natural systems in the area. Similarly, the use proposed by WRP is consistent with regional water supply planning needs. Finally, the proposed use is consistent with the comprehensive planning goals of Walton County as expressed in its Evaluation and Appraisal Report (EAR). The EAR commends WRP's efforts to fully analyze the alternative sources and its selection of the Rock Hill area on which to site a remote wellfield. Non-Interference with Existing Legal Users WRP purchased 5,000 acres on which to site its wellfield so that pumping from the well sites would not adversely affect adjacent landowners, and the majority of the drawdown would basically be confined to the property. Pertinent District rules only require that an applicant consider existing legal uses of water. However, WRP considered all existing legal uses of water and their future increases until the year 2018, and these existing and potential impacts were considered in its groundwater model. Even with the anticipated pumpage in the year 2018, the potentiometric surface at the WRP wellfield site location will not be drawn below sea level. The water level drawdowns associated with the withdrawal do not constitute a harm, they can be remedied, and the permit has been conditioned to provide for those remedies. For example, Standard Condition 11 and Specific Condition 17 provide protection to domestic wells users in the area. They should specifically address the legitimate concerns of public witnesses who testified at hearing. The Local Sources First Statutory Provision Section 373.223(3), Florida Statutes, (Supp. 1998), also known as the local sources first statutory provision, enumerates a number of factors which the District must consider when evaluating whether a proposed use of water is consistent with the public interest. However, the law provided that water use permit applications pending with the District as of April 1, 1998, were exempted. The legislation was not enacted until October 1, 1998, and the notice of proposed agency action on the instant permit was issued in June 1998. Therefore, the District took the position that the legislation does not apply to the WRP permit. In an abundance of caution, however, the District reviewed the application as if the local sources first exception applied, and then again as if the exception did not apply. Under either scenario, the District concluded that the application met the criteria enumerated by the law. Assuming arguendo that the new law applies, WRP has met all criteria necessary for the issuance of a permit. The proposed wellfield site is the best suitable site to move water withdrawals inland away from the coastal area, and other locations closer to the coast would have resulted in interference and impacts; there are no other impoundments in the vicinity of the proposed wellfield site that are technically and economically feasible for the proposed use; there are no economically and technically feasible alternatives to the proposed source; there are no potential environmental impacts from the wellfields; there are no adequate existing sources of water available on the peninsula; the District has had numerous interactions with area local governments; and the District did not allow WRP's investment in 4,900 acres of land to influence its decision. Standing The only alleged basis for standing which went to fact finding at hearing was an allegation in paragraph (5)(a) of the Petition that "[t]he withdrawal of up to 4.8 million gallons per day of groundwater by WRP will adversely impact the quantity and quality of groundwater available for withdrawal by Petitioners." As to RU, which currently serves 500 customers representing a population of 17,000, it has no wells in the vicinity of WRP's proposed wellfield; its wellfields are located along the coastal area of Highway 30-A from Santa Rosa Beach to the east of Inlet Beach, on the Bay County line, or some twenty- five to thirty miles south of the proposed wellfield. It also purchases 500,000 gallons of water per day from the City of Freeport to meet its customers' demand. Because of RU's own continued pumping, at least four of its coastal wells are "going bad" due to saltwater intrusion and upconing. This condition will continue to occur even if WRP's application is not granted. Although it has a permit application for new inland wellfields pending with the District, at the time of hearing the application was incomplete and is therefore irrelevant to a standing determination. There was no direct evidence that RU's coastal wellfields will be adversely affected by WRP's proposed operation. Indeed, the projected decline in water levels in that area will be less than one foot and will have a de minimus impact. As to Walton County, it owns the land on which RU's coastal wells are located as well as the production facilities. Under a lease agreement between those parties, RU operates the system. The County also had one small exempt well in the vicinity of WRP's proposed wellfields which was installed after this case was filed, but shortly before the hearing began. There was no evidence as to the depth of the well, the source of water, or the well's pumping capacity. Likewise, there was no evidence that the well has actually been used. In addition, there was no evidence that the County relies on groundwater from the Floridan Aquifer to supply potable water to its citizens or customers, or that WRP's proposed withdrawal will adversely impact the quantity or quality of groundwater available for withdrawal by the County. As to the City of DeFuniak Springs, it operates its own public water supply system serving approximately 17,200 persons. It has four water supply wells located approximately nine miles north of WRP's proposed wellfields, and upstream from WRP's site. WRP's model predicts that the City's wellfields will be impacted, albeit very slightly, by WRP's pumping over the lifetime of the proposed permit. To this limited extent, the proposed activity affects its substantial interests. Finally, the City of Freeport owns and operates its own public water supply utility. It has existing wells which are permitted by the District and which lie five miles directly south of WRP's proposed wellfield. Like the City of DeFuniak Springs, the City of Freeport will also experience drawdown impacts, although not considered significant, over the lifetime of the proposed permit. To this extent, the permit will impact the City of Freeport. This is true in spite of the City's admission that its principal concern in this case is WRP's intention to sell water to customers outside Walton County.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law set forth herein, it is, RECOMMENDED that the Northwest Florida Water Management District enter a Final Order granting Consumptive Water Use Permit No. I05349 to WRP, Inc., as proposed in its Notice of Proposed Agency Action issued on June 5, 1998. DONE AND ENTERED this 22nd day of April, 1999, in Tallahassee, Leon County, Florida. DONALD R. ALEXANDER 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 COPIES FURNISHED: Filed with the Clerk of the Division of Administrative Hearings this 22nd day of April, 1999. Douglas E. Barr, Executive Director Northwest Florida Water Management District Route 1, Box 3100 Havana, Florida 32333-9700 Douglas P. Manson, Esquire Jack R. Pepper, Jr., Esquire 712 South Oregon Avenue Tampa, Florida 33606-2543 George Ralph Miller, Esquire Post Office Box 687 DeFuniak Springs, Florida 32433-0687 Clayton J. M. Adkinson, Esquire Post Office Box 1207 DeFuniak Springs, Florida 32435-1207 Douglas L. Stowell, Esquire Stephen L. Spector, Esquire Post Office Box 11059 Tallahassee, Florida 32302-3059 Kenneth G. Oertel, Esquire Segundo J. Fernandez, Esquire Post Office Box 1110 Tallahassee, Florida 32302-1110 Paul R. Bradshaw, Esquire 1345 Dupont Road Havana, Florida 32333
The Issue The issue in this case is whether the Southwest Florida Water Management District (the District) should grant the application of the Misty Creek Country Club, Inc. (the Club), to modify MSSW Permit No. 400037.
Findings Of Fact Background Petitioners are owners of property adjacent to Lake No. 7 of the Misty Creek Country Club in a development called The Preserves at Misty Creek-- specifically, lot 113 (Robert and Lee Werner), lot 114 (Charles and Rosemary Biondolillo), lots 115 and 115A (Ignatius and Judith Bertola), lots 117 and 117A (Don and Halina Bogdanske), lots 118 and 118A (Louis and Betty Mitchell), lots 119 and 119A (George and Dorothy Holly), lots 120 and 120A (John and Maureen Higgins), and lot 121 (William and June Spence). Respondent, the Misty Creek Country Club (the Club), operates a golf course and country club located at The Preserves at Misty Creek under a 99-year lease with Gator Creek Lands, the developer of The Preserves at Misty Creek. Existing System Design and Application for Permit Modification In 1985, Respondent Southwest Florida Water Management District, issued a surface water management permit for development of a 730-acre residential development and golf course. The District subsequently issued to the Club operation phase authorization for the surface water management system associated with the golf course portion of the development in March of 1992. Under the original permit, Lake No. 7 was part of the overall stormwater management system for the golf course. The lake is approximately seven and half to eight acres in size and is part of a total drainage basin of approximately twenty-eight acres. As originally designed, Lake No. 7 is a detention with filtration system. An underdrain in the side of the bank provides water quality treatment, filtering out oils and greases, fertilizers and other contaminants. A control elevation of 31.02 was established for Lake No. 7 through construction of a weir. Between elevation 31.00 and 31.02, water discharges through the underdrain system providing water quality treatment. Above elevation 31.02, water flows over the control structure into Lake No. 6, and ultimately discharges to Cow Pen Slough, which is Class III waters of the state. The Club presently has a water use permit from the District which allows withdrawal of groundwater for irrigation of the golf course. Groundwater is stored in Lake No. 7 prior to use for irrigation when needed to augment water in the lake. Special Condition Number 2 of the water use permit required the Club to investigate the feasibility of using reclaimed or reuse water in lieu of groundwater for irrigation purposes at the golf course. As a result of the investigation required by Special Condition Number 2 of the water use permit, the Club filed an application with the District to modify its surface water management permit to allow for the introduction of reuse water into Lake No. 7. Under that application, there would have been no significant modifications to the stormwater management system. Reuse water would have replaced groundwater as a source for augmenting water in the lake when needed for irrigation. An eight-inch service line would convey the reuse water to Lake 7, and a float valve would control the introduction of reuse water into Lake No. 7. When water levels in the lake fell below elevation 30.5', the float valve would open the effluent line to allow introduction of reuse water into the lake; when the water elevation in the lake reached 31.0', the float valve would shut off the flow of water. There would be gate valves on either side of the structure that could be manually closed, if necessary, to stop the flow of reuse water into the lake if the float valve malfunctioned. Club personnel would have access to the gate valves and could manually stop the flow of reuse water into the lake if necessary. On August 9, 1995, just days prior to the final hearing in this matter, the Club proposed to modify its application to make certain structural changes in the design of the surface water management system. Specifically, the Club proposed to plug the window in the weir, raise the elevation of the weir or control structure to elevation 33.6, raise the elevation of the berm along the north end of Lake No. 7 adjacent to the weir to elevation 33.6, and plug the underdrain. The purpose of the proposed modifications to the design of the system was to assure that no discharge from Lake No. 7 would occur up to and including the 100-year storm event. A 100-year storm event is equal to 10 inches of rainfall in a 24-hour period. Source and Quality of Reuse Water The Club also entered into an agreement with Sarasota County to accept reuse water from the county's new Bee Ridge wastewater treatment facility. That agreement specifies the terms under which the Club will accept reuse water from the County. The County's Bee Ridge facility is presently under construction and is not yet operating. As permitted by the Department of Environmental Protection, the Bee Ridge wastewater treatment facility will use a Bardenpho waste treatment system which is a licensed process to provide advanced waste treatment. The construction permit establishes effluent limits for the facility that are comparable to a level of treatment known as advanced secondary treatment, but the County Commission for Sarasota County has instructed the County staff to operate the Bee Ridge facility as an advanced waste treatment plant. Advanced waste treatment is defined by the quality of the effluent produced. For advanced waste treatment, the effluent may not exceed 5 milligrams/Liter of biochemical oxygen demand (BOD) or total suspended solids (TSS), 3 milligrams/Liter of total nitrogen, or 1 milligram/Liter of total phosphorus. It also requires high level disinfection. Advanced secondary treatment requires the same level of treatment for TSS but the limit for nitrates is 10 milligrams/Liter. High level disinfection is also required for advanced secondary treatment. In Florida, reuse systems require a minimum of advanced secondary treatment. High level disinfection is the level of treatment that generally is accepted as being a reasonable level of treatment. The Bee Ridge permit issued to Sarasota County identifies the Club as one of the recipients of reuse water for irrigation. Condition Number 21 of that permit provides that the use of golf course ponds to store reuse water is not authorized under the County's permit until issuance of a separate permit or modification of the County's permit. Although the District did not require Misty Creek to submit any information about the modification of the County's permit, there was no basis for assuming that the County permit could not be modified. To the contrary, the permit provides that authorization may be obtained by permit modification. Under the late modification to the Club's application, the reuse water transmission line and float valve system, with backup manual gate valve system, is unchanged. So are the water elevations at which the float valve system will automatically introduce reuse water into Lake 7 and shut off. Sarasota County already has constructed the water transmission system that would deliver reuse water to the Club. At the request of the District, the Club provided copies of the drawings of the float valve structure as permitted by the Department of Environmental Protection. The District did not require certified drawings of that structure. But the District will require the Club to provide as-built drawings following completion of construction prior to the introduction of reuse water into Lake No. 7. Property Ownership Each of the Petitioners owns a residential lot adjacent to Lake No. 7. At the time of the Petitioners' purchase of the individual residential lots, the Club leased certain property immediately west of Lake No. 7 from the developer of The Preserve at Misty Creek. The leased premises included a piece of land extending into the lake known as the 19th green. As a result of negotiations between the Club and the developer, it was determined that the 19th green would be removed and the land between the approximate top of bank of Lake No. 7 and the private residential lots would be released from the Club's lease. The developer subsequently conveyed the property that had been released from the Club's lease to the individual lot owners (the "A" parcels listed in Finding 1). At the time of the conveyance of the additional parcels, the attorney for the developer prepared deeds for each individual parcel with a metes and bounds description off the rear of the residential lots to which they were being added. While the Club's application for modification of its surface water management permit was being processed by the District, counsel for Petitioners provided the District with copies of the individual deeds and questioned whether the Club had ownership or control of the land which was the subject of the application sufficient to meet the District's permitting requirements. In response to a request for information regarding the ownership of the property that was the subject of the application, the Club submitted to the District a topographical survey prepared by Mr. Steven Burkholder, a registered professional land surveyor with AM Engineering. The topographical survey depicted: the elevation of the water in the Lake No. 7 on the day that the survey was conducted, labeled "approximate water's edge"; the elevation of the "top of bank"; and the easternmost line of private ownership by Petitioners. Mr. Burkholder determined the line of private property ownership by reproducing a boundary survey attached to the individual deeds conveying the additional parcels to the Petitioners. He testified that he was confident that the topographical survey he prepared accurately represented the most easterly boundary of the Petitioners' ownership. The elevation of the line of private ownership as depicted on the survey prepared by Mr. Burkholder ranges from a low of approximately 34.5 to 35.2. The elevation of the line labeled "top of bank" ranges from a high of 35.6 to a low of 34.4. The elevation of the water in Lake No. 7 would be controlled by the elevation of the modified control structure which is proposed to be set at elevation 33.6. After modification of the surface water management system to retain the 100-year storm event, at no time would water levels in the lake rise above the existing elevation of the "top of bank." The Petitioners testified that they believed that they owned to the water's edge or edge of the lake, but Mr. Burkholder testified that a property boundary could not be determined based on an elevation depicting the water's edge because that line would change as the level of the water rose and fell. The Petitioners also presented evidence that the developer's attorney made representations to them that their ownership extended to the "approximate high water line." But there appears to be no such thing as an "approximate high water line" in surveying terms. Where the boundary of a lake is depicted on a survey it generally is depicted from top of bank to top of bank. In any event, the legal descriptions of the parcels conveyed to the Petitioners were not based on a reference to either a water line or the water's edge or the lake at all. Instead, the legal descriptions were based solely on a metes and bounds description off the rear of the residential lots. Notwithstanding some contrary evidence, if the Petitioners owned to the water's edge, such ownership would require the Petitioners to consent to or join in the amended application for the modification of the Club's surface water management permit. Information regarding the ownership or control and the legal availability of the receiving water system is required as part of the contents of an application under Rule 40D-4.101(2)(d)6. and 7., Florida Administrative Code. The amended application requires the ability to "spread" Lake 7 in the direction of the Petitioners' property. If the Petitioners own the property on which the Club intends to "spread" Lake 7 in order to make the amended application work, the Petitioners must consent or join. The issue of the legal ownership and control of the Petitioners and the Club currently is in litigation in state circuit court. If the state circuit court determines that the easterly boundary of the "A" parcels lies to the east of the "top of bank," consideration would have to be given to modifying any permit issued to the Club to insure that the designed "spread" of Lake 7 in a storm event up to and including a 100-year storm event does not encroach on the Petitioners' property. District Permit Requirements The District has never before processed an application for a surface water management permit allowing commingling of storm water and reuse water. The District applied Chapter 40D-4, Florida Administrative Code, in reviewing the Club's permit application. There are no specific provisions in Rule 40D-4 or the District's Basis of Review for Surface Water Management Permit Applications that address the commingling of stormwater and reuse water; on the other hand, no rules of the District prohibit the introduction of other types of water into a stormwater treatment pond so long as the requirements of Rule 40D-4 are met. The District has the authority to allow stormwater and reuse water to be commingled. Section 40D-4.301, Florida Administrative Code, contains the conditions for issuance of a surface water management permit. Permitting Criteria In order to obtain a surface water management permit to commingle stormwater and reuse water in Lake 7, the Club must provide reasonable assurances that the proposed modifications to its existing system will provide adequate flood control and drainage; not cause adverse water quality and quantity impacts on receiving waters and adjacent lands; not result in a violation of surface water quality standards; not cause adverse impacts on surface and groundwater levels and flows; not diminish the capability of the lake to fluctuate through the full range established for it in Chapter 40D-8, Florida Administrative Code; not cause adverse environmental impacts to wetlands, fish and wildlife or other natural resources; be effectively operated and maintained; not adversely affect public health and safety; be consistent with other public agency's requirements; not otherwise be harmful to water resources of the District; and not be against public policy. No surface or groundwater levels or flows have been set for this area of the District, so that permit criterion is not applicable to the Club's application. The Club's application will not impact wetlands or fish and wildlife associated with wetlands as described in F.A.C. Rule 40D-4.301(1)(f). There are no wetlands regulated by the District in the project site. The Club has submitted to the District an operation and maintenance plan for the modified surface water management system. The operation and maintenance plan is in compliance with the District's permitting criteria contained in Rule 40D-4.301(1)(g). The District's regulation with respect to the requirement that a project not adversely affect the public health and safety is based on the specific requirements of Chapter 40D-4, Florida Administrative Code, and the Club has complied with this criterion. The permitting criterion that a project must be consistent with the requirements of other public agencies was met by inclusion in the permit of Special Conditions Nos. 5 and 6, Limiting Condition No. 3 and Standard Condition No. 3, which require that the surface water management permit be modified if necessary to comply with modifications imposed by other public agencies. The District's regulation with respect to the requirement that a project not otherwise be harmful to the water resources within the District is based on the specific requirements of Chapter 40D-4, Florida Administrative Code, and the Club has complied with this criterion. The District's regulation with respect to the requirement that a project may not be against public policy is based on the specific requirements of Chapter 40D-4, Florida Administrative Code, and the Club has complied with that criterion. The project will not have an adverse impact on water quality or quantity in receiving waters or adjacent lands. Under the District's regulations, the project would not be permittable if it caused flooding on property owned by other persons. Two concerns regarding off-site flooding were raised by Petitioners: first, the potential for flooding of the Petitioners' property; and, second, the potential for flooding of secondary systems connecting to Lake No. 7 such as private roads in the development. The project would violate the requirements of Section 40D-4.301(1)(a), Florida Administrative Code, which requires that a proposed project provide adequate flood protection and drainage, if raising the weir and berm elevation to 33.6 would cause the level of water in Lake No. 7 to move laterally up the bank and encroach on property owned by Petitioners. However, the Club has given reasonable assurances that the Petitioners own only to the "top of bank" and that raising the weir elevation to 33.6 would not cause water levels to rise above the "top of bank" of the lake. If it is determined in pending state circuit court proceedings that the Petitioners own beyond the "top of bank," any permit for the Club's project might have to be modified to avoid flooding the Petitioners' property. With respect to potential flooding of secondary systems, such as adjacent roadways, raising the elevation of water in Lake No. 7 would decrease the capacity of the storm sewers draining into the Lake. However, the proposed modifications would not increase the area of impervious surface in the drainage basin or decrease the size of the lake, and water levels in the roadways probably would not rise much higher than under present circumstances. The existing storm sewer system is only designed for a 10-year storm event, so the supplemental effect on roadway flooding from retaining a 100-year storm event in Lake No. 7 probably would be negligible. The Club gave reasonable assurances that any increase in water levels on the roadways from the proposed modifications would not be considered a significant adverse effect because it still would not affect public access. Sarasota County's land development regulations allow flooding in streets of up to 12 inches for a 100-year storm event, nine inches for a 25-year storm event, and six inches for a 10-year storm event. No portion of the proposed project area is within the 100-year floodplain. The project will not have an adverse effect on water quantity attenuation or cause flooding of the Petitioners' property or secondary systems, such as adjacent roadways. Petitioners have protested the effect that this project will have on water quality within Lake No. 7, itself. Surface water quality standards do not apply within a stormwater pond. Stormwater ponds are essentially pollution sinks intended to receive polluted runoff. Where there is no discharge from a pond, water quality treatment is irrelevant. Lake 7 is not a "water resource within the District" pursuant to Section 40D-4.301(1)(j), Florida Administrative Code, and potential impact on water quality in Lake No. 7 should not be considered. Section 40D-4.301(1)(j) limits the issues to be considered by the District to downstream water quality, water quantity, floodplain impacts, and wetlands impacts. The commingling of wastewater effluent treated to a level of advanced secondary or advanced waste treatment (reuse water) would improve water quality within a stormwater treatment pond at least 90 to 95 percent of the time. Stormwater is very low quality compared to reuse water. In most respects, reuse water also will be better quality than the well water presently being used to augment the pond. It is expected to be better quality than unimpacted water in the receiving waterbody with respect to nitrogen content and only slightly worse with respect to phosphorus content. The addition of reuse water should not promote more algal growth; rather, it should reduce the likelihood of algal growth. It also should not increase the incidences of fish kills in Lake 7. Nor should it alter the nutrient concentrations in Lake 7 so as to result in an imbalance of the natural population of aquatic flora and fauna. In the draft permit originally proposed to be issued to the Club, permit conditions required that water quality be monitored at the point of discharge to waters of the state. This requirement was eliminated from the revised permit as the District determined that it was not necessary in light of the modification of the system to retain the 100-year storm event. The subject design does not account for recovery of the water quality treatment volume within a specified period of time. However, there is no such requirement in District rules when a pond entirely retains the 100-year storm event, as is the case with this project. Even if there were a discharge from the surface water management system in a storm event up to and including a 100-year storm event, the Club gave reasonable assurances that water quality standards in the receiving waterbody would not be violated because of the effects of dilution. This project will not cause discharges which result in any violations of applicable state water quality standards for surface waters of the state. Based on a number of factors, including the peak rate factor, the curve number and the seasonal high water elevation, the water level in Lake 7 would reach an elevation of 33.57 if a 100-year storm event occurs. This results in the retention of the 100-year storm in Lake 7. The District only considers the 100-year storm event, by itself. It does not consider other rainfall events before or after it. However, the District does presume that ponds are at their seasonal high water level when the 100-year storm event occurs and that the ground is saturated. With respect to the seasonal high water level, there was substantial conflicting testimony. The Club's consultant used a seasonal high water level of 31.0' for Lake No. 7 in his calculations. This was based on a geotechnical engineering report prepared by Ardaman & Associates. A seasonal high water elevation of 31.0' was also used in the original permit application in 1985. In concluding that the seasonal high water level should be 31.0, the Ardaman report relied on several assumptions, including plugging of the underdrain and overflow weir and no discharges into or pumping out of the lake. These assumptions were made to establish an historical water level. The Petitioners' consultant disputed the determination in the Ardaman report that the seasonal high for Lake No. 7 was 31 on the grounds that the report indicated groundwater levels of 32.8 on three sides of the lake. He also felt that water levels would rise in the lake over time as a result of it being, allegedly, a closed system. While he did not have an opinion as to what the appropriate seasonal high should be, he felt it would be higher than 31 but lower than 32.8. However, he did no modeling with respect to calculating a seasonal high water level and would normally rely on a geotechnical engineer, such as Ardaman & Associates, to calculate seasonal high water levels. The District generally does not receive information as extensive and detailed as that included in the Ardaman report when it reviews permit applications. Among other things, the Ardaman report indicates a gradient across Lake No. 7 which makes the determination of the seasonal high for the lake difficult. The groundwater flow gradient results from the fact that the elevation of Lake No. 6 is approximately three feet lower than the elevation in Lake No. 7. The elevation determined by Ardaman may well be conservative in that the seasonal high of 31 is above the midpoint of the gradient. Although Lake 7 will be designed as an essentially closed system, it will have inflow from rainfall, surface runoff, introduction of reuse water and groundwater inflow, and outflows by way of evapotranspiration, withdrawal for irrigation purposes, and groundwater outflows. To alleviate any concerns about the validity of the seasonal high, it would be reasonable to include a permit condition requiring the Club to monitor the water level in Lake 7 on a daily basis, using staff gauges, after modification of the control structure. If such monitoring indicated that the seasonal high water level exceeds 31.0, the District could consider options to address that situation, including reducing the level at which reuse water is introduced into the lake or requiring water quality monitoring at the point of discharge to receiving waters. Groundwater quality is regulated by the Department of Environmental Protection, not by the District. The DEP permit issued to Sarasota County for disposal of reuse water at the Club golf course requires the installation of two groundwater monitoring wells, one in fairly close proximity to Lake No. 7. The Overlooked Pond There is a small retention pond northwest of Lake 7, near lot 113. Neither the Club nor the District considered the effect of the Club's late modification of its application on the retention pond northwest of Lake 7 and adjacent properties. Lake 7 and the retention pond to its northwest are connected by an equalizer pipe. As a result, water levels in the pond will be affected by water levels in Lake 7. There was no evidence as to the elevations of the banks of the retention pond. There was no evidence as to whether the modifications to the Club's application will result in flooding of properties adjacent to the pond. There was no evidence that the Club owns or controls the retention pond or the properties adjacent to it that might be affected by flooding that might result from the modifications to the Club's application.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is recommended that the Southwest Florida Water Management District enter a final order denying the Club's amended application. RECOMMENDED this 19th day of October, 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 19th day of October, 1995. APPENDIX TO RECOMMENDED ORDER, CASE NO. 95-2196 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: Petitioners' Proposed Findings of Fact. 1.-2. Accepted and incorporated. Accepted and incorporated to the extent not subordinate or unnecessary. However, there was other evidence from which it can be determined that Lake 7 is part of the Club's lease. Accepted and incorporated. However, there was other evidence from which it can be determined that Lake 7 is part of the Club's lease and from which the western extent of the Club's leasehold interests in Lake 7 can be determined. Accepted and incorporated. But the topographic survey, together with other evidence, does show the eastern extent of the Petitioners' property in relation to the "top of bank" of Lake 7 and the western extent of the Club's leasehold interests in Lake 7. Rejected as contrary to the greater weight of the evidence that uses must be "specifically authorized" in that the lease authorizes the use of the premises for a "golf course," which is presumed to include uses inherent to the operation of a golf course that may not be further specified in the lease, such as drainage facilities, like Lake 7, and facilities for irrigation of the golf course. Otherwise, accepted and incorporated to the extent not subordinate or unnecessary. Rejected as contrary to the greater weight of the evidence. Accepted but subordinate and unnecessary. Rejected as contrary to the greater weight of the evidence that the Club does not pay for the maintenance of Lake 7, at least as between the Club and its lessor, which is the subject of the pertinent lease provision. (There was evidence as to a dispute between the Club and the Petitioners, or at least some of them, as to who is responsible for maintenance of land in the vicinity of the western extent of Lake 7 and the eastern extent of the Petitioners' property. Rejected as contrary to the greater weight of the evidence. Rejected as contrary to the greater weight of the evidence to the extent that there are "A" parcels between lots 115 through 120 and Lake 7. Otherwise, accepted and incorporated. Accepted and incorporated. Not clear whether all of the activities listed in the second sentence are done in the entire area up to the water's edge but, otherwise, accepted and incorporated. Accepted, but subordinate to facts contrary to those found, and unnecessary. Accepted; subordinate to facts found. Rejected. The intent of the parties is not clear and is the subject of litigation in state circuit court. 17.-18. Accepted that some probably used the words "to the water's edge"; others may have said "to the lake" or "to the approximate high water line." Regardless of what they said, the legal consequences are being litigated in state circuit court. Subordinate to facts contrary to those found, and unnecessary. 19.-20. Accepted and incorporated to the extent not subordinate or unnecessary.. Last sentence, accepted but subordinate and unnecessary. The rest is rejected as contrary to the greater weight of the evidence. Accepted but subordinate and unnecessary. The evidence was sufficient to place on Exhibit M-16 the boundary lines of the "A" parcels, as depicted on the Alberti boundary survey that was attached to the individual deeds to all of the "A" parcels, in relation to the "top of bank" of Lake 7 and other topographical features depicted on Exhibit M-16. The 0.679 acre total for the "A" parcels was merely transcribed from the Alberti boundary survey (probably incorrectly, as the boundary survey seems to indicate the acreage to be 0.674, plus or minus.) Rejected as contrary to the greater weight of the evidence. The modification itself would not cause the water level to rise. If, due to the combined influence of all the pertinent factors, the water level in Lake 7 rises, it will spread more than before the modifications, up to a maximum spread of approximately ten feet. Rejected as contrary to the greater weight of the evidence. The Club gave reasonable assurances that the spread would be contained within its leasehold interest. However, consideration would have to be given to modifying the permit if the state circuit court determines in the pending litigation that the easterly boundary of the "A" parcels lies to the east of the "top of bank." Accepted and incorporated to the extent not conclusion of law. Accepted. Self-evident and unnecessary. Accepted and incorporated. Accepted, but subordinate, and unnecessary. Accepted and incorporated. Rejected as contrary to the greater weight of the evidence. It does not prohibit it; it just does not authorize it. It provides that authorization may be obtained by permit modification. Accepted and incorporated to the extent not subordinate or unnecessary. 32.-36. Accepted but subordinate and unnecessary. (Evidence was presented at final hearing.) 37. Rejected as contrary to the greater weight of the evidence that discharges will be "likely." (Accepted and incorporated that no discharges are expected as a result of storm events up to and including a 100-year storm event unless preceding conditions predispose the system to discharge during a 100-year storm event.) 38.-39. Accepted but subordinate and unnecessary. (As for 39., very little construction will be required for the proposed project.) Rejected as contrary to the greater weight of the evidence. First, Lake 7 will not be "maintained" at 31'; rather, when it falls below 30.5', a half inch will be added. Second, it is not clear that the Ardaman report established an "artificially low seasonal high water level." (There is a hydraulic gradient across Lake 7 from east to west, approximately. The Ardaman report assumed no flow into or out of Lake 7; it also assumed no pumpage into or out of the lake.) Rejected as contrary to the greater weight of the evidence that it is based "solely" on that assumption. Accepted and incorporated that it is based on that and on other assumptions. Accepted and incorporated. Accepted but subordinate and unnecessary. (Evidence was presented at final hearing.) Rejected as not supported by evidence. Rejected as contrary to the greater weight of the evidence to the extent that the impact is obvious--the water level in the pond will be approximately equal to the water level in Lake 7. Rejected as contrary to the greater weight of the evidence. The modification itself would not cause the water level to rise. If, due to the combined influence of all the pertinent factors, the water level in Lake 7 rises, so will the water level in the pond. 47.-48. Accepted and incorporated. 49.-50. Accepted but subordinate and unnecessary. 51.-52. Accepted and incorporated. Respondents' Proposed Findings of Fact. 1.-7. Accepted and incorporated. 8. Rejected as contrary to the greater weight of the evidence in that there was more to the application than just substitution of reuse for well water. 9.-10. Accepted and incorporated. 11. Accepted and incorporated to the extent not subordinate or unnecessary. 12.-22. Accepted and incorporated. Rejected as not proven. (The two District witnesses disagreed.) Even if true, subordinate to facts contrary to those found. Accepted and incorporated. Accepted and incorporated to the extent not subordinate or unnecessary, or conclusion of law. Accepted and incorporated. Accepted and incorporated to the extent not conclusion of law. 28.-29. Accepted; subordinate to facts found, and in part conclusion of law. 30. Accepted. First sentence, incorporated; second sentence, subordinate to facts found, and in part conclusion of law. 31.-35. Accepted and incorporated to the extent not subordinate or unnecessary, or conclusion of law. Accepted and incorporated. Accepted and incorporated to the extent not subordinate or unnecessary, or conclusion of law. Accepted but subordinate to facts contrary to those found. 39.-40. Accepted and incorporated to the extent not subordinate or unnecessary. 41.-43. Accepted and incorporated. Accepted and incorporated to the extent not conclusion of law. Last sentence, accepted and incorporated to the extent not conclusion of law; rest, accepted but subordinate to facts contrary to those found, and in part conclusion of law. Accepted and incorporated to the extent not subordinate or unnecessary. Accepted, but subordinate, and unnecessary. Accepted and incorporated. First sentence, accepted but subordinate to facts contrary to those found; second sentence, accepted and incorporated to the extent not conclusion of law. Accepted and incorporated to the extent not subordinate or unnecessary. 51.-52. Accepted and incorporated. 53.-55. Accepted, but subordinate to facts found, and unnecessary. 56. Accepted and incorporated. 57.-62. Accepted and incorporated to the extent not subordinate or unnecessary. 63. Accepted and incorporated to the extent not conclusion of law. COPIES FURNISHED: Patricia A. Petruff, Esquire D. Robert Hoyle, Esquire Dye & Scott, P.A. 1111 Third Avenue West Bradenton, Flroida 34206 Mary F. Smallwood, Esquire Ruden, Barnett, McClosky, Smith, Schuser & Russell, P.A. 215 South Monroe Street, Suite 815 Tallahassee, Florida 32301 Mark F. Lapp, Esquire Assistant General Counsel Southwest Florida Water Management District 2379 Broad Street Brooksville, Florida 34609-6899 Peter G. Hubbell Executive Director Southwest Florida Water Management District 2379 Broad Street Brooksville, Florida 34609-6899 Edward B. Helvenston,Esq. General Counsel Southwest Florida Water Management District 2379 Broad Street Brooksville, Florida 34609-6899
The Issue The issue for consideration in this case is whether the Respondent, Hi Hat Cattle and Grove, should be issued water use permit 204387.03, to withdraw groundwater from the wells on its property, and if so, in what amount and under what conditions.
Findings Of Fact At all times pertinent to the issues herein, the Respondent, District, was the state agency responsible for the permitting of consumptive water use within its area of geographical jurisdiction. The Respondent, Hi Hat, is a family owned farming and ranching operation in eastern Sarasota County with water wells on its property. The Intervenor, City of Sarasota, is a municipality in Sarasota County which operates wells in the general area of those operated by Hi Hat, and which has an agreement with Hi Hat for the latter's use of treated wastewater pumped from the city's treatment plant to Hi Hat Ranch. The Petitioner, Wyatt S. Bishop, Jr., is a property owner and resident of Sarasota County whose property is located near the Hi Hat Ranch, and whose potable water is drawn from a well on his property which utilizes both the surficial and intermediate aquifers which are penetrated by the wells on Hi Hat Ranch. Hi Hat Ranch consists of 11,000 acres owned by Hi Hat Cattle and Grove, the family owned business which operates it, and an additional 3,227 acres leased from the City of Sarasota. Agricultural operations, including citrus farming, truck farming, sod farming, and grazing have been conducted on the ranch since the mid 1940's. In February, 1990, Hi Hat applied to the District for a permit to withdraw and use water from some 14 wells located on its property. It requested an annual average of 6,267,000 gallons per day, (gpd), and a peak monthly rate of 32, 668,000 gpd. Upon receipt by the District, the application was assigned a number, (204387.03), and was submitted for evaluation by the District staff for conformity with applicable District rules and policies. When the staff evaluation was completed, the District issued a staff report and proposed staff agency action in which it indicated its intention to issue a permit authorizing water to be drawn from the wells at a rate of 6,570,000 gpd, average annual, a peak monthly rate of 14,300,000 gpd, and a maximum daily rate of 5,210,000 gpd. In conducting its evaluation, the District staff relied upon the District's Basis of Review For Water Use Permit Applications which contains within it the provision for use of a "water use model" in assessing the need and appropriateness of water withdrawal amounts. This model, known as the Blaney- Criddle Model considers numerous factors in the evaluation, including rainfall, soil characteristics, irrigation methods used, and proposed crop types, all in an effort to determine a reasonable estimate of the applicant's supplemental water needs. Hi Hat's application was evaluated primarily by Marie Jackson, a Hydrologist III employed by the District, and an expert in hydrology, who has, over the years, reviewed between 350 and 400 permit applications, of which approximately 90 percent have been for agriculture. She is, therefore, quite familiar with the specifics of agricultural water use needs. Her evaluation of Hi Hat's application was done in the same manner as the others she has done and utilized the same tests, measurements and factors for consideration in arriving at her conclusion. In its application, a renewal with modification sought to increase average annual quantities due to a change in crop plans, Hi Hat indicated that its criteria for water use was based on certain agricultural uses and application rates. These included: low volume under tree spray irrigation of 778 acres of citrus at an application rate of 17.2 inches/year plus one inch/year for frost and freeze protection. open ditch irrigation of 135 acres of sod at an application rate of 30 inches/year. open ditch irrigation of 1,367 acres of improved pasture at an average application rate of 26.6 inches/year. overhead spray irrigation of 1,200 acres of improved pasture at an application rate of 20.3 inches/year. open ditch irrigation of 110 acres of spring peppers at an application rate of 30.0 inches/crop, and open ditch irrigation of 110 acres of fall peppers at an application rate of 45.2 inches/crop. Applicant also stipulated that the peak monthly quantities that it requested would be utilized for pasture, sod and citrus irrigation during the month of May. The proposed maximum quantities were for frost and freeze protection of citrus only. In January, 1989, Hi Hat entered into a contract with the City of Sarasota under which the City was obligated to deliver reclaimed water from its wastewater treatment plant to a "header" located on the ranch which thereafter distributes the water through pipes to "turnouts" located at various high points on the property. From these, the water is then discharged into a system of ridges and furrows for distribution of the water across the needed area. The reclaimed water is used to irrigate approximately 5,403 acres of ranchland. The Contract provides for minimum and maximum amounts of water to be delivered as well as for water quality standards which must be met. In periods of adequate rainfall, when irrigation is not required, any treated wastewater which is not needed is stored in a 185 million gallon holding pond on City property located adjacent to the ranch. When needed, water can be fed into the wastewater distribution system described above from the holding pond. This reclaimed water, whether from the pond or direct from the header, can also be utilized to irrigate citrus crops, but this requires a filter system which has not yet been able to operate properly. Therefore, no reclaimed water has yet to be utilized for citrus irrigation on the ranch. At an average annual flow of 6.2 million gallons per day, the pond has the capacity to hold enough treated water for almost 30 days. Not all wells on Hi Hat Ranch are active wells. Several of the wells are classified as standby wells which are intended to be used only to back up the reclaimed water delivery system and are located, normally, beside the "turnouts." In the event the reclaimed water is not available from the city, the standby wells can be utilized to provide water to the ridge and furrow system used to irrigate pasture land. The standby wells are numbers 1, 6, 7, 11, 13, 14, and 15. Well number 5, also identified as a standby well in the staff report and in the draft permit was mistakenly so identified. The draft permit contains several special conditions which impact on the drawing of water under the terms of the permit. Significant among these is Special Condition 33 which prohibits the withdrawal of water from any of the standby wells unless the reclaimed water supply from the city is interrupted. Special Condition 27 requires the installation of a flow meter on any standby well that becomes active as a result of permanent discontinuance of the reclaimed water supply. With regard to flow meters, Special Condition 22 requires flow meters on all of Hi Hat's wells. Ms. Jackson, however, indicated this was in error and has recommended that the standby wells be deleted from that Special Condition. When that is done, only those wells actively producing water on a regular basis would require the installation of flow meters. In its analysis of the application for permit, the District staff considered several factors pertinent to the impact the well would have on the water supply in the area and its effect on other users. These factors include hydrologic impacts, well condition, the history of water use at the ranch, the reliability of the reclaimed water system and its ability to provide a uniform source, and the city's water reuse policy. Addressing each individually, and starting with the hydrologic impact of the withdrawal of the requested amounts, the District considered the nature of the existing wells and how they are constructed and maintained. The District assumed, because the data regarding the construction of the existing wells was incomplete and insufficient to properly disclose the status of casing on each well, that they were shallow cased. As a result, the calculations incorporating this assumption indicate a situation that would occur in its most aggravated form. The parties agreed that Hi Hat's wells are shallow cased and probably go no deeper than 90 feet. To determine, as much as possible, the projected drawdowns in the surficial and intermediate aquifers that might be expected if Hi Hat withdrew the amounts of water proposed, the District utilized the "MODFLOW" computer model which factors in simultaneous peak withdrawals from all 14 of the wells along with a 90 day no rainfall drought condition. This, too, contributes to a worst case scenario, and the resultant figures are considered to be conservative estimates of the hydrologic impact of the water withdrawal. Notwithstanding, the application of this computer model resulted in the indication that, as to the surficial aquifer, the drawdown at Mr. Bishop's property located approximately one half mile from the ranch border, would be no more than .055 feet. Since normal fluctuations in the surficial aquifer during the course of the year can be as much as 6 feet, the projected drawdown as a result of Hi Hat's withdrawals was considered insignificant. Applying the same assumptions and utilizing the same computer model as it relates to the intermediate aquifer resulted in an indication of a drawdown of no more than 2.3 feet at Mr. Bishop's property. Since annual fluctuation in the intermediate aquifer can range from 15 to 20 feet normally, the District considers that any reduction of less than five feet in the intermediate aquifer is insignificant. The permit held by Hi hat currently allows for the withdrawal of more water than would be withdrawn under the proposed permit as conditioned and is consistent with the proposed reduction in allowable withdrawals. Considering that factor, as well as the prohibition against withdrawals from standby wells as long as reclaimed water is available, the actual impact of the water withdrawals consistent with the proposed permit would be substantially less than the computed prediction which includes production from all wells. Drawdown contours are defined across the entire effected area. One of the levels is a 4 foot contour, and when a computer simulation indicates that the 4 foot contour includes a withdrawal previously or otherwise permitted, the District will generally conduct a cumulative impact analysis. In this case, however, since there was only one golf course well within the area circumscribed by the 4 foot contour line, and since this withdrawal was too small to have effected an evaluation, it was not done. The condition of the wells on the Hi Hat Ranch has some bearing on whether or not the application for additional withdrawal of water should be granted. These wells are almost 30 years old, having been drilled in the 1960's. As a result, there is little information available regarding their construction detail. This is not necessarily unusual for agricultural wells, and there is evidence that there are many similar wells in use within the District. The reason for this is that at the time the wells were drilled, information regarding their depth, casing and other matters were not required to be kept or reported. However, there is no indication the wells are in any way violative of well construction criteria and their use has been authorized continuously since 1977. When he prepared Hi Hat's application, Mr. Turner included much the same information regarding the wells as pertains as to depth and diameter which he had previously submitted in earlier applications and which had been accepted. In each case, casing depths had been reported as unknown. Notwithstanding the information contained in some old well logs relative to only a few of Hi Hat's wells, this information is in no way definitive and it is difficult to describe anything specific with the majority of these wells. Nonetheless, as already found, it is stipulated that most are approximately 90 feet deep. It is reasonable to assume that the existing wells, however, are cased only to a shallow depth, and that in many cases, the existing casings have corroded away, either totally or in part. This can cause an intermixing of water from the separate aquifers, but whether this is in fact happening depends upon factors specific to that particular well. Petitioner did not present any evidence to show that as a result of the condition of Hi Hat's wells, any degradation is occurring in the more potable, surficial aquifer as a result of intermixing with water from the intermediate aquifer on or around the Hi Hat Ranch. In Ms. Jackson's opinion, and there appears to be no evidence to contradict it, the amount of drawdown which would occur as a result of maximum pumping at Hi Hat Ranch would not be sufficient to cause poorer quality water from the Floridan aquifer to percolate upward (upcone) into the better quality water of the two upper aquifers even during drought conditions. By the same token, there is no evidence that drawdown would encourage or permit salt water intrusion. Petitioner attempted to show by the records kept on the various Hi Hat wells that many of them have been abandoned and are no longer operative and should not be allowed to fall within the parameters of this permit. He testified clearly that over the years, the level of water in his potable water well has lowered and presumed that this was the result of increased water usage by other entities which draw from the aquifer into which his well is sunk. Water level, however, depends upon numerous factors, of which usage is only one. Others include recharging of the aquifer and the amount of rainfall and other recharge sources not only in the immediate area but across the large area which feeds the aquifer. Mr. Bishop did not present any evidence showing a causal connection between the lowering of the water in his well, or the degradation in water quality he claims to have experienced, and either the drawdown caused by Hi Hat's operation or by aquifer intermixing. He indicated, and it is not disputed, that within the past year, he has had to take measures to improve the water quality in his potable well, but, again, he has not presented any evidence to show this was caused by Hi Hat's ground water withdrawals. In its long range planning, the District intends to implement a program to rehabilitate old wells, and when that program is implemented, almost every agricultural well within the District may require recasing or redrilling. This program will not be implemented for several years, however. In an effort, however, to insure that all reasonable precautions are taken to see that approval of any petition for withdrawal does not have an unacceptable adverse impact on the water needs of the surrounding community, in its analysis of this application, and in all cases, the District makes certain assumptions when adequate empirical data is not available. In this case, pertaining to the unavailability of information regarding Hi Hat's wells, the District assumed that all wells were shallow cased, and this placed the application in the worst possible light. Shallow cased wells allow more upconing and aquifer intermixing. Nonetheless, the amount of water permitted to Hi Hat, even if not used, could impact on Mr. Bishop and other adjoining owner's use of additional water as a result of a possible change to their permitted quantities. However, to compensate for this, the District has also included a special condition, (#26), which requires Hi Hat to log all 14 of its wells within the term of the permit, (7 years), which will require at least 2 wells be done each year. The cost of that action will be between $800 and $2500 per well. Another condition, (#31), requires Hi Hat to look into any complaint from adjacent property owners regarding adverse impacts due to water withdrawal, to report the results of its inquiry to the District, and to mitigate, as much as possible, all adverse impacts due to its withdrawal. Mr. Bishop claimed, and introduced evidence purporting to demonstrate, that many of the wells on the Hi Hat Ranch, which are covered by the permit applied for here, are no longer in use and have been abandoned. In response, Mr. Turner, who has been actively engaged in the ranch's operations for at least the past four years, indicates from his personal knowledge, that all 14 wells included in the permit applied for have been operated within the past two years, and all are capable of producing water. It is so found. Not all wells, however, have been operated at all times. Crop rotation and a varying need for groundwater has resulted in some wells not being used at some times. This is, of course, commonplace in agriculture and to be expected as a result of crop planning programs. Admittedly, an accurate figure for the amount of water which has been withdrawn from the 14 wells cannot be established because these wells do not have, and were not required to have, flow meters. Two of the wells were fitted with hour meters in January, 1989, but because the capacity of the pumps on those wells is variable, a precise estimate of volume pumped cannot be determined. The meters measured only the number of hours the pumps were in operation and not the amount of water passed through the pumps. Evidence was presented, however, to show that wells have been utilized at the ranch since the 1960's, and in 1977, some 14 years ago, following District implementation of a consumptive water use permit program, the ranch first applied for water withdrawal permits. These permits have been renewed as required and all water usage since the implementation of the program has been permitted. Turning to the reclaimed water supply, the delivery system, incorporating a program to pump reclaimed water from the treatment plant all the way back out to the ranch site, is subject to material failure and operator error, and either one can occur at any number of places along the system route. Each could result in interruption of the delivery of the reclaimed water to the ranch. The system is far more complex than would be the use of on-site wells for delivery of ground water. One two week shutdown in the system was occasioned by a major pipe failure as a result of pressure building up in the pipes. Were it not for the fact that a contractor was already at the ranch with replacement parts on hand to effect expeditious repair of the system, the shutdown could have lasted considerably longer than it did. This is not the only interruption, however. Several main line leaks and valve problems have caused the system to be shut down on several occasions for short periods of time. The filter system required for the water destined for the citrus area is problematical, and so far this area of the ranch has not received any reclaimed water in the 10 months the system has been in operation. Mr. Bishop argues that the wet weather holding pond is a solution to the reliability problems with the pipe line, but the pond has had problems of its own. Sand in the water, which comes from the holding pond, has been the primary difficulty in the filter system for the citrus area, and algae growth in that pond has the potential to create other filter problems. Delivery of the water from the pond is not accomplished by a gravity system, but instead, requires the use of pumps powered by an electric motor. In the event of a power failure, this source would be unavailable. Discounting all of the above, however, and assuming, arguendo, that all systems were in top operating condition, the fact remains that the delivery system from the pond to the distribution system is not adequate to supply the amount of water that would be necessary to have an effective freeze protection program. In any case, the reclaimed water supply is not the panacea for all water shortage problems experienced at Hi Hat Ranch. In the first place, the quality of the reclaimed water is generally lower than that of the groundwater which would come from wells on the ranch. Also, the City's treatment process does not remove from the water all the pollutants that are of concern to the farm operators. For one thing, total dissolved solids in the reclaimed water are considerably higher than in the ground water, and high dissolved solid levels can be harmful to citrus crops. In fact, the Institute of Food and Agricultural Sciences recommends that citrus irrigation water not exceed total dissolved solid ranges of from 1000 to 1500 milligrams per liter, (mpl). Testing done on the reclaimed water delivered to Hi Hat Ranch showed it averaged between 1200 and 1500 mpl. Though within recommended parameters, it was toward the high end. Further, reclaimed water is not totally interchangeable with ground water for all agricultural purposes. It cannot, by law, be applied to certain types of ground crops such as melons, nor can it be used for overhead citrus irrigation. There is also a restriction on the use of reclaimed water for pastures on which dairy cattle will be grazed. This all results in a restriction on the options available to the farmer who chooses to use reclaimed water in his irrigation plan. As a result, many farmers try not to use reclaimed water if they have access to adequate amounts of groundwater from on- site wells. Notwithstanding all the above, the parties agree that the use of reclaimed water for irrigation purposed is in the public interest. The District encourages it but nonetheless concedes that even with the availability of reclaimed water, a farmer should have access to wells on his property, in a standby capacity, as an alternative source of water to support his farming activities. Not only that, the agreement between the City and Hi Hat provides for Hi Hat to maintain its water use permit even while receiving reclaimed water from the City. Hi Hat is not the only farm operation with whom the City has negotiated in a effort to expand its wastewater distribution program. It has found in those negotiations, that most farm producers are not willing to rely totally on reclaimed water for all their irrigation needs, and it has concluded that were it mandatory that a farmer give up his on-site ground water withdrawals in order to utilize reclaimed water for a part of his needs, most would be reluctant to use it at all. This would seriously interfere with the City's ability to dispose of its surplus reclaimed water consistent with its policy. Even though Hi Hat's property lies within the Eastern Tampa Bay Water Use Cautionary Area, the rule pertaining thereto is inapplicable to Hi Hat because Hi Hat filed its application for permit, which was deemed complete, prior to the adoption of the rule. Nonetheless, water use officials agree that the proposed permit is consistent with the rule emphasis on the use and reuse of reclaimed water, and the District does not object to backup wells being permitted as supportive of the District's desire to keep ground water within the ground.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is, therefore: RECOMMENDED that Hi Hat Cattle and Grove be issued water use permit No. 204387.03, within the limits of the authorized quantities as indicated in the intent to issue, subject to conditions contained therein; except that the permit be amended to show well No. 5 as a non-standby well, and to delete standby wells from the terms and requirements of Special Condition 22. RECOMMENDED this 17th day of May, 1991, in Tallahassee, Florida. ARNOLD H. POLLOCK, 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 17th day of May, 1991. APPENDIX TO RECOMMENDED ORDER The following constitutes my specific rulings pursuant to Section 120.59(2), Florida Statutes, on all of the Proposed Findings of Fact submitted by the parties to this case. FOR THE PETITIONER: Accepted Accepted and incorporated herein. Accepted and incorporated herein. - 6. Accepted and incorporated herein. 7. - 11. Accepted. - 15. Accepted and incorporated herein. Accepted. Accepted. & 19. Accepted and incorporated herein. - 22. Accepted and incorporated herein. Accepted and incorporated herein. Accepted and incorporated herein. - 28. Accepted and incorporated herein. Accepted and incorporated herein. Rejected. She testified that Condition 28 of the permit provides this. Accepted. Accepted. Accepted and incorporated herein. Accepted. & 36. Accepted. Rejected as not supported by the evidence except that the method permitted was the method being used. - 40. Accepted. Ms. Jackson indicated she "assumed" some wells were drilled into the Florida aquifer. Rejected. Accepted as qualified by the comment, "depending on the respective potentiometric heads." - 47. Accepted. Accepted but incomplete. This is because they did not feel it was necessary under the circumstances. - 51. Accepted. Accepted. Accepted. Accepted. Accepted. Accepted and incorporated herein. Accepted. Redundant. - 61. Accepted. - 66. Accepted and incorporated herein. Accepted. More a restatement of testimony than a Finding of Fact Accepted and incorporated herein. & 71. Accepted and incorporated herein. - 74. Accepted. Accepted. First sentence accepted. Second portion rejected since cited case involves active wells versus standby, as here. The comparison made is accepted. The conclusion drawn as to validity is rejected. & 79. Accepted. FOR THE RESPONDENTS AND INTERVENOR: & 2. Accepted and incorporated herein. Accepted and incorporated herein. Accepted and incorporated herein. & 6. Accepted and incorporated herein. 7. - 10. Accepted and incorporated herein. 11. - 13. Accepted and incorporated herein. - 17. Accepted and incorporated herein. Accepted. Accepted. Accepted and incorporated herein. Accepted and incorporated herein. & 23. Accepted and incorporated herein. Accepted. Accepted and incorporated herein. Not a Finding of Fact but a comment on the evidence. 27. Accepted. 28. & 29. Accepted and incorporated herein. 30. - 33. Accepted and incorporated herein. 34. - 37. Accepted and incorporated herein. 38. Accepted. 39. Accepted. 40. - 42. Accepted and incorporated herein. Accepted and incorporated herein, & 45. Accepted. 46. & 47. Accepted and incorporated herein. COPIES FURNISHED: Wyatt S. Bishop 5153 Tucumcari Trail Sarasota, Florida 34241 Bram D.E. Canter, Esquire Haben, Culpepper, Dunbar & French, P.A. 306 N. Monroe Street Tallahassee, Florida 32301 Edward B. Helvenston, Esquire Southwest Florida Water Management District 2379 Broad Street Brooksville, Florida 34609-6899 Barbara B. Levin, Esquire de la Parte & Gilbert 705 East Kennedy Blvd. Tampa, Florida 33602 Peter G. Hubbell Executive Director SWFWMD 2379 Broad Street Brooksville, Florida 34609-6899
The Issue Whether the application of Telegraph Cypress Water Management District to modify an existing surface water management system permit should be granted.
Findings Of Fact The South Florida Water Management District (District) is a public corporation in the State of Florida existing pursuant to Chapter 25270, Laws of Florida, 1949, and operating pursuant to Chapter 373, Florida Statutes, and Chapter 40E, Florida Administrative Code. The District is a multipurpose water management agency with principal offices in West Palm Beach, Florida. Telegraph Cypress Water Management District (TCWMD) is a water control district organized pursuant to Chapter 298, Florida Statutes. Agricultural operations have been conducted within the TCWMD for more than 30 years by the landowner, Babcock Florida Company. The TCWMD is the permittee of record. James D. English, Jr., owns, along with other members of his family, an orange grove and pasture in Lee County, Florida. The English family has owned the property for approximately 120 years. On November 10, 1992, James D. English, Jr., and the Panacea Timber Company filed a petition for formal administrative hearing challenging the District's intent to issue SWM Permit Modification No. 08-00004-S. Cypress Creek Partnership is a Florida General Partnership of which James D. English, Jr., is a principal. The partnership engages in agricultural activities in Lee County, Florida. The Alva Cemetery, Inc., is a Florida not-for-profit corporation which owns and manages a cemetery facility in Lee County Florida. The cemetery has been in active use for approximately 120 years. In recent years, Alva Cemetery has experienced occasions of excess water encroaching onto the cemetery property. On November 12, 1992, Alva Cemetery, Inc., filed a petition for administrative hearing challenging the District's intent to issue SWM Permit Modification No. 08-00004-S. James D. English, Jr., Cypress Creek Partnership and Alva Cemetery, Inc., are herein referred to as Petitioners. The TCWMD and the Petitioner English share a common property boundary. The Alva Cemetery is surrounded by the English property. All lands involved in this matter historically drain towards the Caloosahatchee River. The TCWMD includes approximately 89,120 acres of land located in Charlotte and Lee Counties, Florida. The land uses within the TCWMD include agricultural, cattle, and timber operations. Generally, the fields have been leased to third party farmers who use the field for several years. When the fields are not actively farmed, they are returned to a fallow state and used as pasture land until fertility is restored at which time they are reactivated for farming. Active farms fields are generally surrounded by a perimeter ditch and dike system. Pumps may be used to water and de-water the fields. When the field is returned to a fallow state, the ditch and dike system are not maintained and become less prominent either by action of weather or by intent. Pumps are not present. All of the TCWMD lies generally north to northwest of the property owned by the Petitioners. Surface waters flow onto the Petitioners' lands from the north. The Telegraph-Cypress system is unique and is the largest of its kind in South Florida Water Management District jurisdiction. The TCWMD system includes storage/detention facilities, control structures, pumping stations and an extensive network of internal canals. There are nine separate water management basins within the TCWMD. The Petitioners asserted that the water management basins identified by the District and the TCWMD are incorrect. The greater weight of the evidence establishes that the District's identification and delineation of the nine basins is based on historical hydrologic characteristics of the TCWMD and is a reasonable determination of basin boundaries. The land encompassed by the instant application for permit modification includes three of the nine basins and encompasses approximately 51,400 acres of the TCWMD. Surface water discharge from the relevant farm fields flows via the internal canal network and sheet flow to the three common detention basins: Telegraph Swamp, North Telegraph Swamp ("Telegraph North") and Curry Lake. The Telegraph North basin lies to the north of and discharges into the Telegraph Swamp basin and includes 13,799 acres of which 4,094 acres are farm fields. The drainage into the Curry Lake basin does not impact either the Telegraph North or Telegraph Swamp basins or the Petitioners' properties. The evidence establishes that as to the Telegraph North and Curry Lake drainage basins, the permit modification meets applicable permitting criteria. There is no credible evidence to the contrary. Telegraph Swamp is the largest of the three relevant detention systems. The Telegraph Swamp basin includes a total of 32,707 acres of which 4,381 acres are farm fields. Telegraph Swamp is a 4,390-acre wetland vegetated by cypress trees and sawgrass, with a base of muck soils, humus, topsoil, leaf litter and other organic material. Located at the south end of Telegraph Swamp are surface water management control structures (the Big Island Dike) built in 1975 and permitted in the original 1980 permit. The structures include three broad-crested weirs and one flash-board weir. Telegraph Swamp has been compared to a "sponge" capable of absorbing vast quantities of surface water discharges within the TCWMD before the control structures at the south end of the swamp are over-topped. Water discharged from the control structures flows through canals and creeks to the Caloosahatchee River. During storm events water is discharged over the control structures and into a swamp area south of Big Island Dike. From there, the water flows southerly, into Telegraph Creek, Big Island Canal and Cypress Creek and then into the Caloosahatchee. The Petitioners expressed concern that TCWMD could inappropriately discharge water from the control gates in the Telegraph Swamp weir. Based on evidence admitted at the hearing, the permit modification should include the following special condition: Discharge structures in the Telegraph Swamp basin shall remain fixed so that discharge cannot be made below the control elevations, except that structure gates and weirs may only be removed during emergency conditions upon notification to and consent by the District's Fort Myers Service Center regulatory area manager or designee. The Basis of Review for Surface Water Management Permit Applications within the South Florida Water Management District--September 1989, incorporated into Chapter 40E, Florida Administrative Code, provides the applicable water quantity permitting criteria relevant to this proceeding. The Petitioners assert that the control gates are required to be locked in accordance with Basis of Review section 3.2.4.1.b, which states: Discharge structures shall be fixed so that discharge cannot be made below the control elevation, except that emergency devices may be installed with secure locking devices. Either the District or an acceptable govern- mental agency will keep the keys for any such devices. The Petitioners are correct. The rule requires secure locking devices. Such condition should be added to the permit The keys may remain with the TCWMD as "an acceptable governmental agency." In 1980, the District issued Surface Water Management Permit No. 08- 00004-S for the TCWMD to operate an existing surface water management system for an existing agricultural operation. The 1980 permit specifically authorizes "[o]peration of a water management system serving 89,120 acres of agricultural lands by a vast network of internal drainage and irrigation canals, a major dike, a major canal and 4 water control structures discharging via small tributary creeks and sloughs into the Caloosahatchee River." Although the permit has been subsequently modified, the authorization to operate the system has not been amended. While District enforcement staff have occasionally noted "performance deficiencies" on the TCWMD property, there have been no permit violations by the permittee. Deficiencies which have been called to the TCWMD's attention have been resolved. Special condition number five to the 1980 permit provides that "[d]ischarges of water onto adjacent lands may be continued to the extent that increased problems are not caused by such discharges." The Petitioners assert that the District has failed to acknowledge that water discharged from the Telegraph Cypress system flows into the Cypress Creek canal and has failed to consider the impact on the Cypress Creek receiving body. However in the staff report to the 1980 permit states as follows: The Telegraph Cypress basin has three major drainage outlets. These are Trout Creek on the west, Telegraph Creek in the center and Cypress Creek to the east. There is a fourth outlet in the northeastern corner of the property known as Jack's Branch, however, this outlet is small compared to the three major ones. Much of Telegraph's southeastern area was previously drained by Spanish Creek and County Line Canal. This historical drainage pattern was blocked when a company which is presently known as Golden Grove constructed a dike across their northern boundary. This dike causes increased flow in a westerly direction around the west end of the dike, thence southerly towards Cypress Creek. This increased flow has caused excess water problems to property owners downstream. In addition, the dike has blocked virtually all flow to Spanish Creek. The evidence fails to establish that, as asserted by the Petitioners, the District has failed to acknowledge the discharge of water to Cypress Creek or to consider the condition of the Cypress Creek receiving body. In the instant case, the condition of the Cypress Creek receiving body was not re- addressed because the permit modification being sought will cause no additional adverse impacts on existing conditions. Although not individually numbered and identified in the original 1980 permit, the evidence establishes that in 1980, all of the farm fields which are subject to this permit modification application were in existence. The applicant seeks no new water control structures. Other than that required to reactivate fallow farm fields, there is no new construction proposed in the instant application. The Petitioners assert that the instant permit modification application will result in construction of new farm fields. The evidence is contrary to the assertion. Proposed permit special condition No. 10 states that the permit does not include the construction of any new farm fields. The farm fields covered in the staff report would be permitted for reactivation from a fallow state without further permitting activity in the future, and without individual retention for each farm field. The modifications to the original 1980 permit have increased the total farm land area. There is no evidence that, except as specifically permitted and approved by the District, there has been alteration of historical discharge rates or routes. There has been considerable confusion regarding the permitting status of the operations as farm fields have been reactivated. Such reactivation entails grading and leveling fields, reconstruction of ditches and dikes and installation of pumping equipment. In order to provide for standardization in farm field reactivation, and to better monitor such activities, the District requested that the TCWMD seek to modify the existing permit. On February 8, 1991, the TCWMD submitted an application to modify the existing permit for the purpose of reactivating the existing farm fields located within the Telegraph North, Telegraph Swamp, and Curry Lake drainage basins. The proposed SWM permit modification authorizes the continued use of the previously permitted surface water management system for existing active and fallow farm fields and allows the reactivation of currently fallow farm fields without further permit modification by the District. Proposed SWM permit special condition No. 16 states that the District requires notification in letter form 30 days prior to all farm field reactivation activities. The proposed modification of the permit will provide the District with an enhanced ability to inspect the reactivated farm fields. Inherent in such reactivation is ditching and diking of the fields. Such operations have been authorized since the 1980 permit was issued. The work associated with field reactivation will be conducted in accordance with existing design criteria as set forth in the application. Based on evidence admitted at the hearing, the permit modification should include the following special condition: Ditches and dikes associated with the farm fields encompassed by this authorization shall be constructed/maintained in conformance with the "Typical Field Layout And Detail Sheet," revised 10/12/93. The evidence establishes that the operations of the TCWMD as proposed by the permit modification application are within the authorization of the existing permit as previously modified. Otherwise stated, the award of this modification will have no substantial impact on the operation of the permitted surface water management system. The modification will result in no additional discharge of surface water from the control structures. The District has established water quantity criteria intended to insure that adverse impacts do not occur due to excess discharge. (Based upon the Hearing Officer's ruling on a District's Motion in Limine, water quality issues were not addressed at hearing.) The criteria are set forth at Chapter 40E-4.301, Florida Administrative Code, and in the Basis of Review. In relevant part, the District criteria require an applicant to provide reasonable assurances that the surface water management system provides adequate flood drainage and protection, that the system will not cause adverse water quantity impacts on receiving waters and adjacent lands, and that the system will not cause adverse impacts on surface and groundwater levels and flows. Modification of a permit must not result in additional adverse off-site impacts. In this case, reasonable assurances have been provided that the proposed modification will not exacerbate the historical and current drainage conditions. The permit modification application at issue does not propose to alter the rates or routes of water currently authorized for discharge from Telegraph Swamp. Reactivation of the farm fields will not impact receiving bodies in any manner different from that which presently exists under previous permits. In providing reasonable assurances, the TCWMD analyzed the water storage capacity available in the detention basins, performed flood routing projections and calculated peak discharge rates for the permit area. As required by the district, the TCWMD utilized a standard hypothetical 25-year/3- day storm event in order to determine whether sufficient capacity was available to handle the resulting stormwater. The projections provide reasonable assurances that the common detention areas have the capacity to provide adequate flood drainage and protection and are accepted. Rule 40E-4.091(1)(a), Florida Administrative Code, incorporates by reference a document identified as the "Basis of Review for Surface Water Management Permit Applications within the South Florida Water Management District--September 1989" Section 3.2.1.2.b requires that: the proposed project modification must meet the allowable discharge rate; and the allowable discharge rate for a previously permitted project is that which was set in the previous permit. The TCWMD prepared and submitted discharge calculations establishing that the post-development discharges will not exceed the discharge rate previously accepted by the District. Since 1984, the District has previously accepted a peak allowable discharge rate of 39 cubic feet per second per square mile (csm). The csm figure is based upon the historical TCWMD discharge rate within the Caloosahatchee River basin. As previously stated, reactivation of the farm fields will not impact the receiving bodies in any manner different from that which presently exists under previous permits. The District asserts that the 39csm discharge rate has been "permitted" since the 1984 modification was approved. The Petitioner asserts that the 39csm discharge rate has never been "permitted" by the District. The evidence establishes that since the 1984 application for permit modification, the discharge rate of 39csm has been utilized by TCWMD and has been accepted by the District, but that the actual permits do not specifically identify the discharge rate as 39csm. In projecting discharge rates, the TCWMD used a time of concentration of one hour. The time of concentration (T.O.C.) is the time in which water would move from the farm fields to the control structure in each sub-watershed. Otherwise stated, a projected T.O.C. of one hour means that the storm water would move from the field to the control structure in one hour. The T.O.C. of one hour is a conservative estimate and likely substantially overestimates the speed at which the water will move. The three basin areas contain a total of more than 80 square miles. Water will travel an average distance of two miles from field to detention basin through ditches, swales and existing low areas. Again conservatively, the TCWMD did not include projected travel time through such conveyances, resulting in a longer T.O.C. and resulting in a higher peak discharge rate than is probable. Although there appeared to be some confusion on the part of the District staff as to the application of the T.O.C. by the TCWMD, the TCWMD engineer who performed the calculation testified at hearing and was qualified as an expert witness in civil engineering, hydrology and surface water management. His testimony and projections are reasonable and are credited. Proposed SWM permit modification special condition No. 11 states that farm field discharge shall be directed to and conveyed via existing ditches, wetlands and/or sheetflow areas per existing site conditions. No new outfall ditches are permitted under this modification. Flood routings were calculated assuming all farm fields would be activated simultaneously and pumping the maximum capacity of 390 gallons per minute per acre (the equivalent of 20-21 inches of surface water pumped from each field daily). It is highly unlikely that all farm fields would be active simultaneously or that stormwater would continue to fall with such velocity to permit continued pumping at maximum capacity for an extended period. Even based on the conservative assumptions utilized by the TCWMD engineers, the projected peak discharge rate at the Telegraph Swamp control structure is 37csm to 38.5csm, within the maximum of 39csm previously accepted by the District. The computer modeling performed by the TCWMD engineer in calculating the peak discharge rate is accepted as reasonable. The TCWMD did not include offsite inflow in its analysis of projected capacity or discharge rates. There is anecdotal evidence that on occasion, water may flow into TCWMD from Jack's Branch or from across roadways to the north and west of the TCWMD; however, given the vast storage capacity of the TCWMD detention areas, there is no evidence that the quantity of offsite inflows is of such significance as to render the TCWMD projections unreasonable. As previously stated, the TCWMD calculations are reasonable and are accepted. The evidence establishes that the peak discharge rate resulting from approval of the instant permit modification will not exceed 39csm. The Petitioners offered their own peak discharge rate calculations, based on a "worst possible case scenario." The assumptions on which the Petitioners' projections are based are unreasonable and are rejected. Based on recommendations received at the hearing, the permit modification should include the following special condition: Pumped discharge from farm fields for which pumps are not currently installed shall be limited to 75 gallons per minute per acre of farmed area. Pumps are currently installed in fields number 7, 8, 9, 10, 12, 14, 15, 24 north and south, 28, east half of 34, 64, 67, 68, 69 and 80. The Petitioners assert that the system is currently causing adverse impacts to their properties in the form of flooding. The greater weight of the evidence establishes that the system presently does not cause adverse water quantity impacts on receiving waters and adjacent lands, and does not cause adverse impacts on surface and groundwater levels and flows. The evidence establishes that award of the application for permit modification will not adversely alter the current operations. It is clear that the Petitioners have been impacted by changes in the historical drainage patterns in the area; however, such changes had substantially occurred by 1980 when the original permit was issued. The greater weight of the credited evidence establishes that such impacts are not the result of the activities authorized in the original 1980 permit and in subsequent modifications, but instead are the result of unrelated actions by third parties not involved in this administrative proceeding. There is no credible evidence that the permit modification sought in the instant proceeding will adversely affect the Petitioners. The 1980 permit addresses existing water quantity problems in the area of the TCWMD project. For example, the construction of the Golden Grove Dike resulted in blockage of historical drainage towards Spanish Creek and the diversion of excess waters into Cypress Creek. During the 1980's the District required that culverts be installed in the Golden Grove Dike which eventually restored some surface water flow through the dike construction and on towards the south, although during some storm events water flow continues around the dike and into Cypress Creek. The Petitioners offered anecdotal evidence as to reduced water flows in some local creeks and increased flows thorough Cypress Creek. The Respondent offered evidence indicating that water flow through Cypress Creek may be less than 30 years ago, due to the digging of a canal between Spanish Creek and Cow Slough and the extension of the Clay Gully Canal's diversion of water into Telegraph Swamp. None of the evidence on this point was persuasive, however it is not relevant. Clearly, the instant permit modification application will not adversely affect the existing situation in the receiving bodies. The Petitioners assert that other receiving waterways have become clogged with vegetation, debris or soil, have accordingly reduced capacities, and are unable to accommodate historical discharge levels. Based on the lack of capacity, the Petitioners suggest that waters move towards the eastern portion of Telegraph Swamp and are discharged, flow towards, into and over the banks of Cypress Creek, and flood their properties. The TCWMD conducted a study of backwater profiles based upon credited field data. The study is found to be reasonable and is credited. Based upon the study, approximately 90 per cent of the water discharged from Telegraph Swamp is conveyed to the Caloosahatchee via Big Island Canal, Telegraph Creek and the swamp area south of the control structure. The remaining 10 per cent of the water enters the Bullhead Strand-Lightered Canal-Cypress Creek watercourse. Water flows from Telegraph Swamp into Cypress Creek via Bullhead Strand and the South Lightered Canal, however, the canal has become so restricted by vegetation that it provides little direct water flow between the strand and the creek and is more properly regarded as an area of enhanced sheet flow. The evidence does not establish that the surface water traveling from Bullhead Strand to Cypress Creek is of significance. Coupled with the existence of the Big Island Canal (which connects Telegraph Swamp to Telegraph Creek) it is unlikely that post-development surface water discharged from the Telegraph Swamp into Cypress Creek exceeds pre-development discharges. The Petitioners claim that two culverts in the Big Island canal restrict the flow of water through the canal and result in increased discharge to the east and to Cypress Creek. The greater weight of the evidence establishes that during period of time when the culverts are unable to accommodate water flow, the water travels into a broad flood plain, around the culverts and returns to the Big Island Canal. The evidence establishes that the proposed modification will not result in additional adverse off-site impacts. The adverse conditions affecting Cypress Creek existed at the time of the 1980 permit and are addressed in the staff report to that permit and to subsequent permit modifications. There is no credible evidence that modification of the permit as sought in this case will result in adverse impacts beyond those which have existed at the time of the award of the original permit. The Petitioners assert that the fields included within the permit modification application lack individual retention areas. The lack of individual detention areas is immaterial in this case where sufficient downstream detention capacity is available through the common detention areas. The Petitioners asserts that the Telegraph Swamp is an "above-ground impoundment" and that as such is fails to comply with requirements related to such water storage systems. The Telegraph Swamp is not a typical "above-ground impoundment" as that term is routinely applied by the District. The regulations addressed by the Petitioners clearly state that they are not intended to be inclusive and are intended to provide guidelines and basic performance criteria for commonly encountered south Florida situations. Telegraph Swamp is not a commonly encountered south Florida situation. There is no evidence that the decision not to apply the "above-ground impoundment" regulations to the Telegraph Swamp is unreasonable. The Petitioner suggest that the TCWMD application for permit modification is deficient and fails to provide information in compliance with the Basis of Review. The Basis of Review is directed towards applications for new construction. The District reasonably does not interpret the all elements of the Basis of Review to apply to existing operations. The original staff report for this permit modification application fails to acknowledge that Cypress Creek is a receiving body. However, as stated previously, the 1980 application and subsequent modifications have clearly addressed the fact that Telegraph Swamp waters discharge to Cypress Creek via intervening waterways. The failure to include the reference in the staff report to this application for modification is irrelevant.
Recommendation Based on the foregoing, it is hereby RECOMMENDED that the South Florida Water Management District enter a Final Order issuing Surface Water Management Permit Modification No. 08-00004-S including the additional permit conditions set forth herein, to the Telegraph Cypress Water Management District. DONE and RECOMMENDED this 1st day of April, 1994 in Tallahassee, Florida. WILLIAM F. QUATTLEBAUM 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 1st day of April, 1994. APPENDIX TO RECOMMENDED ORDER, CASES NO. 92-6900 and 92-6901 To comply with the requirements of Section 120.59(2), Florida Statutes, the following constitute rulings on proposed findings of facts submitted by the parties. Petitioners James D. English and Cypress Creek Partnership The proposed findings of fact submitted by Petitioners James D. English and Cypress Creek Partnership consist of unnumbered paragraphs. Pages forty-five through fifty-nine of the proposed findings of fact submitted by Petitioners James D. English and Cypress Creek Partnership were stricken as set forth in the Order On Motion To Strike issued March 29, 1994. The paragraphs of pages five through forty-four of the proposed findings of fact submitted by Petitioners James D. English and Cypress Creek Partnership have been consecutively numbered and are accepted as modified and incorporated in the Recommended Order except as follows: 1-2. Rejected, argument, not findings of fact. 7-9. Rejected, argument, not findings of fact. The staff report is not dispositive. 10-12. Rejected. The greater weight of the evidence establishes that, although the 39csm figure is not set forth in the permit, as of the 1984 modification, the TCWMD calculations have been based on a peak discharge rate of 39csm and that the District has accepted the calculations previously. The applicable criteria in the instant case require that the allowable discharge rate for a previously permitted project is that which was set in the previous permit. 13. Rejected, recitation of testimony is not finding of fact. 15-16. Rejected, argument, not finding of fact, irrelevant, cumulative. 17-18. Rejected, recitation of testimony is not finding of fact. 19. Rejected, contrary to the greater weight of credible and persuasive evidence which establishes that 39csm has been the peak discharge rate accepted by the District since 1984. The flow rate projected by the TCWMD does not exceed the accepted peak discharge rate. 24. Rejected, recitation of testimony is not finding of fact. 26-28. Rejected, recitation of testimony is not finding of fact. 29-30. Rejected, argument, not finding of fact. Rejected, irrelevant. Rejected, argument, not finding of fact. Rejected, irrelevant. The greater weight of the credible and persuasive evidence establishes that 39csm has been the District's accepted peak discharge rate and that this modification will not result in peak discharge rates in excess of that which has been previously accepted. Rejected, not supported by the greater weight of credible and persuasive evidence. The assumptions underlying the Petitioners' calculation of theoretical maximum discharge are rejected as unreasonable. Rejected, unnecessary. 36-45. Rejected, irrelevant. The anecdotal evidence fails to establish that offsite inflows are of such quantity as to render the TCWMD projections unreasonable. The proposed findings also consist of recitation of testimony or argument and are not findings of fact. 46-52. Rejected, contrary to the greater weight of credible and persuasive evidence. The evidence fails to establishes that the swamp is an "above-ground impoundment" as that term is routinely applied by the District. The proposed findings also consist of recitation of testimony or argument and are not findings of fact. 53-67. Rejected, irrelevant. An applicant for a permit modification is not required to supply every item on the checklist. An application for a modification to an existing permit often need not contain all the items described. 69. Rejected, cumulative. 70-71. Rejected, argument, not finding of fact. 72-81. Rejected, not supported by the greater weight of credible and persuasive evidence which establishes that the identification and delineation of the nine basins is based on historical hydrologic characteristics of the TCWMD and is a reasonable determination of basin boundaries. The proposed findings also consist of recitation of testimony or argument and are not findings of fact. 82. Rejected, subordinate. 83-85. Rejected, irrelevant. The confusion on the part of District staff as to what T.O.C. was utilized by the TCWMD engineer is irrelevant. This proceeding is not a review of preliminary staff activity. The applicant must establish entitlement to the permit at the hearing. 86-87. Rejected, recitation of testimony is not finding of fact. Rejected. The confusion on the part of District staff as to what T.O.C. was utilized by the TCWMD engineer is irrelevant. Rejected, unnecessary. Rejected, recitation of testimony is not finding of fact. 91-94. Rejected, irrelevant, the discharge projections calculated by the TCWMD as explicated at the hearing are credited. In any event, the evidence establishes that this modification will result in no additional discharge of surface water from the control structures. 95-97. Rejected, irrelevant. The evidence establishes that this modification will result in no additional discharge of surface water from the control structures. Petitioner Alva Cemetery Petitioner Alva Cemetery's proposed findings of fact are accepted as modified and incorporated in the Recommended Order except as follows: 2. Rejected, not supported by the greater weight of credible and persuasive evidence. 4-5. Rejected, irrelevant. Rejected, irrelevant. This is a de novo hearing, not a review of preliminary staff work. The evidence at hearing establishes that the permit modification will not cause additional adverse affect on existing receiving bodies. Rejected, irrelevant. The evidence fails to establish that Hall Creek and Fichter Creek are receiving bodies of such capacity that their omission from staff report is material. Rejected, irrelevant. Rejected, irrelevant. The evidence fails to establish that offsite inflows are of such quantity as to be relevant. 11. Rejected, not supported by the greater weight of credible and persuasive evidence. The Applicant's analysis is credited. As to T.O.C., even the less conservative T.O.C. projections indicate a peak discharge rate within that previously accepted by the District. 12-13. Rejected, irrelevant. Rejected, irrelevant. Such return overflows are unnecessary in this situation where the detention areas have the capacity to provide adequate flood drainage and protection. Rejected, not supported by the greater weight of credible and persuasive evidence. Rejected, not supported by the greater weight of credible and persuasive evidence. 18-20. Rejected, cumulative. 21. Rejected, immaterial. There is no evidence that this permit modification application will cause additional adverse impact on receiving bodies. The failure to address nonexistent impacts is immaterial. Rejected, errors in staff report are irrelevant. The evidence admitted at hearing is accepted as correct. First paragraph is rejected, cumulative. Second paragraph is rejected, not supported by the greater weight of credible and persuasive evidence. Rejected, anecdotal testimony is not supported by the greater weight of credible and persuasive evidence. Rejected. The greater weight of credible and persuasive evidence establishes that all farm fields affected by this permit modification application were in existence by the 1980 permit. Rejected, not supported by the greater weight of credible and persuasive evidence. The assumptions underlying the Petitioners' calculation of theoretical maximum discharge are rejected as unreasonable. Rejected, irrelevant. The greater weight of credible and persuasive evidence fails to establish that the cemetery flooding is related to actions by the TCWMD. Further, the evidence fails to establish that, even if the flooding was related to the TCWMD, the instant permit modification application will cause additional adverse impacts. Respondent Telegraph Cypress Water Management District Respondent Telegraph Cypress Water Management District's proposed findings of fact are accepted as modified and incorporated in the Recommended Order except as follows: 18. Rejected, subordinate. 19-20. Rejected, not credited and unnecessary. Rejected as to assertion that the 39csm discharge rate was set in the 1984 permit modification, not supported by the evidence. Review of the document admitted into evidence as the 1984 modification fails to reveal that the figure of 39csm is set forth therein. Rejected, cumulative. Rejected, unnecessary. Respondent South Florida Water Management District Respondent South Florida Water Management District's proposed findings of fact are accepted as modified and incorporated in the Recommended Order except as follows: 30. Rejected as to assertion that the 39csm discharge rate was set in the 1984 permit modification, not supported by the evidence. Review of the document admitted into evidence as the 1984 modification fails to reveal that the figure of 39csm is set forth therein. Pages 17-19 of the Proposed Recommended Order set forth revisions to the staff report which originally form the basis for the preliminary agency action in this matter. As the hearing is a de novo review of this matter, it is unnecessary for this Recommended Order to address the revision of the staff report, which has limited probative value. COPIES FURNISHED: Tilford C. Creel Executive Director South Florida Water Management District Post Office Box 24680 West Palm Beach, Florida 33416 Melville G. Brinson, Esquire 1415 Hendry Street Fort Myers, Florida 33902 Frank A. Pavese, Sr. Esquire 1833 Hendry Street Fort Myers, Florida 33902 Scott Barker, Esquire Post Office Box 159 Fort Myers, Florida 33902 John J. Fumero, Esquire Toni M. Leidy, Esquire South Florida Water Management District 3301 Gun Club Road West Palm Beach, Florida 33416
Findings Of Fact The Proposed Permit This case involves a 65-acre site in north Lee County owned by the City of Ft. Myers. At all material times, the land has been zoned under industrial- equivalent designations. By leases that are not part of this record, Ft. Myers has leased 21.4 acres of the 65 acres to various governmental agencies, including Lee County, Lee County Sheriff's Office, and possibly the Florida Department of Juvenile Justice (formerly known as Department of Health and Rehabilitative Services). The following facilities are presently located on the 21.4 acres: Juvenile Detention Center, Lee County Stockade, Price Halfway House, Sheriff's Office Aviation Department, and Emergency Operations Center. By lease dated September 20, 1993, Ft. Myers leased the remaining 43.6 undeveloped acres to Lee County for a term of 50 years. This lease allows Lee County to use the 43.6 acres for $1 per year, but only for the operation of a Juvenile Justice Facility. Under Paragraph 20 of the lease, Ft. Myers may terminate the lease if Lee County ceases to operate the facility. Likewise, Lee County may terminate the lease if the Department of Juvenile Justice ceases to fund the County's operation of the facility. Under the lease, preference is given to juvenile residents of Ft. Myers. Paragraph 22 of the lease allocates liability to Lee County for claims or damages arising from released fuels, including from pipelines. The lease is not assignable without Ft. Myer's consent. By agreement dated December 17, 1993, Ft. Myers consented to the sublease of the entire 43.6- acre parcel to the Department of Juvenile Justice for the purpose of the construction of a juvenile residential commitment facility. Lee County receives no rent from the Department of Juvenile Justice. In Paragraph 10 of the agreement, the Department of Juvenile Justice agrees to maintain, at its expense, "all improvements of every kind . . .." Lee County must make any repairs to improvements if the Department of Juvenile Justice fails to do so. By subsequent agreement, Respondent Department of Management Services (DMS) became the agent for the Department of Juvenile Justice for the design, permitting, and construction of the juvenile justice facility. By Application for a surface water management permit executed June 16, 1994, DMS applied for a surface water management permit for the construction and operation of a 10.9- acre project known as the Lee County Juvenile Commitment Facility. This 10.9-acre project is part of the 43.6 acres leased to Lee County and subleased to the Department of Juvenile Justice. The application states that the existing 21.4 acres of developed sites, which are leased under separate agreements to different governmental entities, "will be permitted as is." The Staff Review Summary of Respondent South Florida Water Management District (SFWMD) describes the purpose of the application as follows: This application is a request for Authorization for Construction and Operation of a surface water management system to serve a 10.9 acre Institutional project discharging to Six Mile [Cypress] Slough via onsite wetlands and road- side swales. The application also requests Authorization for Operation of a surface water management system serving a 21.4 acre existing facility and 32.7 acres to remain unchanged for a total permitted area of 65.0 acres. Staff recommends approval of both authorizations with conditions. The Staff Review Summary accurately states that the owner of the land is Ft. Myers. Of questionable accuracy is the statement that Ft. Myers leases to Lee County the 21.4 acres devoted to the five existing facilities. Although Lee County probably is a lessee of some of these parcels, the Lee County Sheriff's Office is the lessee (or perhaps sublessee) of at least two parcels. One of the other parcels may involve a state agency, again under either a lease or a sublease. The Staff Review Summary inaccurately states that the project developer is Lee County. The project developer is DMS or its principal, the Department of Juvenile Justice. The Staff Review Summary reviews the existing development on the 21.4 acres. The improvements consist of the 4.8-acre Juvenile Detention Center, 2.9- acre Price Halfway House, 4.7-acre Lee County Stockade, 5.1-acre Sheriff's Office Aviation Department, and 3.9-acre Emergency Operations Center. The Staff Review Summary states that the footer of the Juvenile Detention Center was inspected in February 1980. The site drains into a 1.2- acre retention pond, which was a natural pond dug out to accept the drainage from the Juvenile Detention Center. A small amount of surface flow drains from the Juvenile Detention Center to a perimeter swale that drains west into a ditch running along Ortiz Avenue. The Staff Review Summary states that the building permit for the Price Halfway House was issued in October 1982. The site drains into the 1.2-acre retention pond, which was apparently enlarged a second time to accept the additional flow. A small amount of the flow from the Price Halfway House also drains to the perimeter swale and west into the Ortiz Avenue ditch. The Staff Review Summary states that the building permit for the Lee County Stockade was issued on May 25, 1976. SFWMD issued an exemption and a determination that no permit was required for two additions to the stockade in 1988 and 1989. For the additional impervious surface added by these additions, one inch of water quality treatment was provided. After the abandonment of a pumping system, drainage of the stockade site consists of water building up in existing onsite ditches and sheet flowing into the Ortiz Avenue ditch. The Staff Review Summary adds that a small retention area constructed at the southeast corner of the site treats stormwater from the stockade and the Sheriff's Office Aviation Department. The summary adds that a small amount of stormwater drains north into an exterior swale that drains into the Ortiz Avenue ditch. The Staff Review Summary states that a building permit was issued for the Sheriff's Office Aviation Department in August 1977. Stormwater from the site sheetflows to exterior swales north and south of the building. When the swales fill up, the water flows into the Ortiz Avenue ditch. The Staff Review Summary states that a building permit was issued for the Emergency Operations Center on October 11, 1977. Drainage from the center flows directly into the Ortiz Avenue ditch. Under "Water Quality," the Staff Review Summary reports that SFWMD "did not require compliance with discharge rate or criteria" based on Section 1.6, Basis of Review for Surface Water Management Permit Applications within the [SFWMD] March 1994 (Basis of Review), which contains guidelines issued by SFWMD for the construction and operation of surface water management systems. The summary adds that there have been no "water quality or quantity complaints associated with this site over the past 18 years since its initial construction." Noting that a surface water management permit is requested for the entire 65-acre parcel, the Staff Review Summary states that the above-described drainage systems for the five existing facilities are "operational and will remain as they now exist." Turning to the proposed development, the Staff Review Summary states that the remaining 43.6 undeveloped acres "will also be leased to Lee County by the City for the proposed commitment facilities." The facilities are accurately described as a 5.2-acre halfway house and a 5.7-acre bootcamp, both of which will be drained by internal drainage swales and culverts flowing into detention areas, which will discharge through a control structure into onsite wetlands leading to the Ortiz Avenue swale. Addressing designed discharge rates, the Staff Review Summary acknowledges that the bootcamp's discharge rate will exceed the allowable rate for a 25-year, three-day storm event. The allowable rate is .33 cfs, and the design rate is .37 cfs. The Staff Review Summary explains that this discrepancy results from the use of the minimum size orifice (three inches) in the control structure. Addressing water quality, the Staff Review Summary reports that commercially zoned sites are required to provide one-half inch dry pretreatment for water quality unless reasonable assurance can be provided that hazardous material will not enter the surface water management system. Determining that no hazardous material will be stored or generated on the site, SFWMD did not require the one-half inch dry pretreatment of runoff. Noting that no surface water management permits have ever been issued for any part of the 65-acre parcel, the Staff Review Summary recommends that, subject to the customary Limiting Conditions, SFWMD issue: Authorization for Construction and Operation of a 10.9 acre Institutional Project discharging to Six Mile Cypress Slough via onsite wetlands and roadside swales, Operation of a 21.4 acre existing facility and 32.7 acres to remain unchanged for a total permitted area of 65.0 acres. Limiting Condition 4 states that the permittee shall request transfer of the permit to the "responsible operational entity accepted by [SFWMD], if different from the permittee." Limiting Condition 8 adds: A permit transfer to the operation phase shall not occur until a responsible entity meeting the requirements in section 9.0, "Basis of Review . . .," has been established to operate and maintain the system. The entity must be provided with sufficient ownership or legal interest so that it has control over all water management facilities authorized herein. Special Condition 11 states: "Operation of the surface water management system shall be the responsibility of Lee County." The Permittee and the Entity Responsible for Maintenance The proposed permit consists of two authorizations. The first authorization is for the construction and operation of the surface water management system on the 10.9-acre parcel on which will be constructed the bootcamp and halfway house. The second authorization is for the operation of the existing surface water management system on the already-developed 21.4 acres and the unimproved surface water management system on the remaining 32.7 acres. There are two problems with the designation of Lee County as the entity responsible for maintaining the permitted surface water management systems. Basis of Review 9.1.B states: To satisfy [P]ermit [L]imiting [C]ondition [8], the Permittee must supply appropriate written proof, such as either by letter or resolution from the governmental entity that the governmental entity will accept the oper- ation and maintenance of all the surface water management system components . . .. The authorization for operation of the systems on the 21.4-acre and 32.7-acre parcels does not await any construction. Once the permit is issued, the authorization is effective. Therefore, all prerequisites to the designation must have been satisfied before the operation permit issues. For the 21.4-acre parcel, DMS has not provided reasonable assurance that Lee County is the lessee or sublessee of all of the parcels underlying the five existing facilities. In fact, it appears that Lee County is not the lessee or sublessee of all of these parcels. Even if Lee County were the lessee or sublessee of these five parcels, DMS has not provided reasonable assurance that Lee County has assumed responsibility for the maintenance of the surface water management system for the five parcels. Contrary to Basis of Review 9.1.B, there is no written agreement by Lee County to assume operational responsibility, nor is there even an actual agreement to this effect. SFWMD's rules sensibly require that written consent be obtained before the operation permit is issued. Likewise, DMS has failed to show that Lee County has agreed to assume responsibility for the operation and maintenance of the surface water management system for the 32.7-acre parcel. Again, SFWMD must obtain written consent before issuing the permit because no construction will precede operation for the surface water management system on this parcel. Unlike the situation as to the 21.4-acre parcel, the 32.7-acre parcel is leased to Lee County as part of the 43.6- acre parcel. But in the December 17, 1993, agreement, the Department of Juvenile Justice, not Lee County, assumes responsibility for maintaining all improvements, which arguably includes drainage improvements. As between Ft. Myers and Lee County, Lee County assumes secondary liability for the maintenance of all improvements. But the failure of the Department of Juvenile Justice to do so would likely represent a default under the agreement. In such a case, the lease and separate agreement probably would either be in litigation or Lee County would have terminated its obligations under the contracts. In either case, it is unlikely that Lee County would perform its secondary responsibility to maintain the drainage improvements, especially where it is receiving no rent from the Department of Juvenile Justice and priority is given to Ft. Myers juveniles in admission decisions. Construction will precede operation as to the 10.9- acre parcel so the parties have an opportunity, even after the construction and operation permit is issued, to secure the necessary written consent before the operation permit goes into effect. But similar deficiencies exist with respect to the 10.9- acre parcel because the same agreement imposes upon the Department of Juvenile Justice, not Lee County, the obligation to maintain improvements. An additional complication arises as to the 10.9-acre parcel. The Department of Juvenile Justice intends to contract with one or more private entities to operate the bootcamp and halfway house, so there is at least one more party that Lee County could claim was responsible for maintenance of the surface water management system. The question of who is responsible for maintaining the surface water management systems is important. Drainage quantities and directions can change if swales clog up with vegetation or other matter. In this case, one roadside swale in the area of the 21.4-acre parcel is blocked with vegetation. DMS and SFWMD have thus failed to provide reasonable assurance that the designated entity has assumed responsibility for the maintenance and operation of the existing systems or will assume responsibility for the maintenance and operation of the proposed system following its construction. Permit for Existing Development Section 1.6, Basis of Review, states: [SFWMD] issues construction and operation permits for proposed surface water management activities and operation permits for existing systems. The criteria herein are specifically designed to apply to proposed activities (construction and operation permits). Therefore, some of the criteria may not be applicable to the permitting of existing systems (operation permits). For example, in some cases, existing systems may not meet flood protection criteria. Criteria deviation for existing systems will be identified in staff reports. SFWMD has produced no evidence explicating the extent to which existing systems, such as the systems on the 21.4- and 32.7-acre parcels, are entitled to operating permits without meeting some of the criteria applicable to proposed systems, such as the system on the 10.9-acre parcel. There is nothing whatsoever in the record to explain why certain existing systems might not have to meet certain criteria, such as flood protection criteria. Except for the quantity deviation discussed below, there is nothing in the record disclosing the extent to which SFWMD has waived, or even considered the applicability of, certain or all criteria prior to the issuance of operation permits for the existing systems. In practice, SFWMD does not adhere even to the vague standards implied in 1.6. According to the SFWMD witness, the practice of SFWMD, as reflected in this case as to the systems on the 21.4- and 32.7-acre parcels, is to permit existing systems "as is, where is," as long as they have had no reported problems. There are numerous deficiencies in the "as is, where is" unwritten policy, apart from the obvious one that it conflicts with the assurance of 1.6 that only "some of the criteria may not be applicable" to existing systems. First, the record does not define what a "problem" is. Second, the record discloses no means by which reported problems are collected and later accessed, such as by a parcel index. The "as is, where is" policy is an abdication of the limited responsibilities that SFWMD imposes upon itself in 1.6, especially when applied to the present facts. The facts are straightforward. Neither Ft. Myers, Lee County, nor any other party has ever obtained a permit for any surface water management system, despite numerous improvements in the past 20 years requiring such permits, including the construction of a heliport, at which maintenance and refueling of helicopters takes place. In two relatively minor cases, discussed below, SFWMD erroneously determined that no permit was required. In one of those cases, the applicant, Lee County, candidly admitted the existence of a flooding problem. Based on the present record, neither DMS nor SFWMD has justified the issuance of an operation permit for the systems on the 21.4- and 32.7-acre parcels based either on Basis of Review 1.6 or on the "as is, where is" unwritten policy. Construction of the five improvements on the 21.4 acres began between 1975 and December 1977 with construction of a portion of the Lee County Stockade building and parking, Emergency Operations Center building and parking, and a now- removed barn for the Lee County Sheriff's Office. At the same time, a lake was dug, probably for fill purposes. By the end of 1977, about 2.39 acres of the 21.4 acres were converted to impervious surface. From 1978 to March 1980, another 0.96 acres of the 21.4 acres were converted to impervious surface by the construction of a perimeter dike and road. During this period, construction commenced on the Juvenile Detention Center, adding another 1.63 acres of impervious surface. Between March 1980 and December 1981, additions were made to the Lee County Stockade building and the lake for an additional 0.45 acres of impervious area. Between December 1981 and March 1984, the Price Halfway House building and parking were constructed, adding another 0.79 acres of impervious surface. Between March 1984 and February 1986, a heliport facility and landing area were constructed for the Lee County Sheriff's Office, adding another 1.01 acres of impervious surface. Between February 1986 and February 1990, an additional 2.31 acres of impervious surface were added through additions to the Lee County Stockade and parking area, juvenile detention center, and Emergency Operations Center parking area. Between February 1990 and April 1993, another addition to the Lee County Stockade added 0.62 acres of impervious surface. An additional 0.17 acres of lake was excavated. During this time, applicable rules and statutes required permits for the construction of "works" affecting surface water, including ditches, culverts, and other construction that connects to, or draws water from, drains water into, or is placed in or across the waters in the state. The buildings, parking, other impervious surfaces, ditches, swales, dikes, lake excavations, and, at one point, addition of a now- abandoned pump all constituted "works" for which surface water management permits were required. In 1988, Lee County or Ft. Myers applied for an exemption for an addition to the Lee County Stockade. The basis for the claim of exemption was that the parcel consisted of less than 10 acres and the total impervious surface did not exceed two acres. Although rules in effect at the time required consideration of the contiguous 65 acres under common ownership and the total impervious surface for the 9.7-acre "parcel" exceeded two acres, SFWMD erroneously issued an exemption letter. The second instance involving a claim of exemption took place in 1989 when Lee County submitted plans for another addition to the Lee County Stockade, adding 0.51 acres of impervious surface. The submittal acknowledged a "flooding" problem, but promised a master drainage plan for the "entire site." SFWMD determined that no permit would be required due to the promise of a master drainage plan. No master drainage plan was ever prepared. The flooding problem precluded issuance of the operation permit on an "as is, where is" basis for the already-developed 21.4-acre parcel, even assuming that SFWMD adequately justified the use of this unwritten permitting procedure. In fact, SFWMD has not explained adequately its "as is, where is" permitting procedure or even the undelineated permitting criteria referenced in 1.6, Basis of Review. The 65- acre parcel is a poor candidate for preferential permitting of existing systems. The owner and developer constructed the existing systems in near total disregard of the law. The two times that the owner and developer complied with the permitting process involved small additions for which exemptions should not have been granted. In one case, SFWMD exempted the proposed activity due to its error calculating minimum thresholds as to the areas of the parcel and the impervious surface. In the other case, SFWMD exempted the proposed activity partly in reliance on a promised master drainage plan that was not later prepared. To issue operation permits for the existing systems on the 21.4- and 32.7-acre parcels would reward the owner and developer of the 65-acre parcel for noncompliance with the law and provide an incentive for similarly situated landowners and developers likewise to ignore the law. Before issuing operation permits on systems that have received no comprehensive review and that have been added piecemeal over the years, SFWMD must evaluate the surface water systems on the entire 65-acre parcel to determine whether they meet all applicable criteria. The "as is, where is" unwritten policy has no applicability where there have been reports of flooding. If SFWMD chooses to dispense with criteria in reliance upon Basis of Review 1.6, it must be prepared to identify and explain which criteria are waived and why. Water Quality Basis of Review 5.2.2 provides that projects that are zoned commercial or industrial, such as the present one, must provide one-half inch of "dry" detention or retention pretreatment, unless reasonable assurances are provided "that hazardous materials will not enter the project's surface water management system." There is no existing or proposed dry detention on the 65 acres. The existing development includes the Sheriff's Office Aviation Department, which serves as a heliport. The fueling and maintenance of helicopters means that contaminants may enter the stormwater draining off the site. The functioning of the surface water system on this site is therefore of particular importance. There also may be more reason to question the functioning of the surface water system on this site. It is south of the Lee County Stockade, where flooding has been reported. The heliport site has also been the subject of more elaborate drainage improvements, such as the location of a small retention pond near the Stockade boundary and a pump, the latter of which has since been abandoned. The existing system on the 21.4-acre parcel, as well as the existing and proposed systems on the remainder of the 65 acres, require dry pretreatment for reasons apart from the presence of the heliport. The materials likely to be used with the existing and proposed developments are similar to those found on residential sites. SFWMD and DMS contend that there is therefore no need to require dry pretreatment as to these areas. However, the existing and intended institutional uses, such as jails and bootcamps, represent an intensity of use that exceeds the use typical in areas zoned residential. This increased intensity implies the presence of typical residential contaminants, such as petroleum-based products or cleaning solvents, but in greater volumes or concentrations, if not also, in the case of solvents, different compositions. The lease addresses potential liability for released petroleum. In the absence of a showing that such hazardous materials are prevented from entering the runoff, SFWMD must require dry pretreatment for the systems occupying the entire 65-acre parcel. DMS and SFWMD have thus failed to provide reasonable assurance that the existing systems satisfy applicable water quality criteria or that the proposed system will satisfy applicable water quality criteria. Water Quantity The 65-acre parcel adjoins Ortiz Avenue on the west and property owned by Petitioners on the east and south that is undeveloped except for a borrow pit some distance from the 65- acre parcel. The parcel is roughly 1000 feet east- west and 2700 feet north-south. The proposed halfway house is at the north end of the parcel. The halfway house is situated between a proposed detention pond on the west and a recreation field on the east. A paved road divides the halfway house from the rest of the 65- acre parcel. South of the road are the Lee County Stockade on the west, which abuts Ortiz Avenue, and the Juvenile Detention Center on the east. A berm separates these two sites. The berm runs from the road along the west shore of the twice- enlarged 1.2- acre retention pond and the west boundary of the Price Halfway House, which is south of the Juvenile Detention Center. To the west of the berm, south of the Lee County Stockade, is the Sheriff's Office Aviation Department or heliport facility, which abuts Ortiz Avenue. South of the Aviation Department is an outparcel used by the Florida Department of Corrections that also abuts Ortiz Avenue. East of the outparcel is the proposed halfway house with a proposed detention pond west of the halfway house and south of the outparcel. The Emergency Operations Center, which abuts Ortiz Avenue, is south of the detention pond and surrounded on three sides by the 32.7 acres to be left undisturbed at this time. There are perimeter berms around all of the parcels except for the Juvenile Detention Center and Price Halfway House, which are served by a single berm, and the Emergency Operations Center, which appears not to be bermed. The prevailing natural drainage is not pronounced either by direction or volume because the land is nearly level. The natural direction of drainage is to the south and west and remains so on Petitioners' land to the east and south and the undisturbed 32.7 acres to the south. The variety of drainage directions within the remainder of the 65- acre parcel reflects the extent to which berms, swales, ponds, pumps, roads, buildings, parking areas, and other works have been added to the northerly parcels. Runoff reaching the northern boundary of the 65 acres will be diverted due west around the proposed detention pond to the swale running along the east side of Ortiz Avenue. Runoff from the recreation field and halfway house building and parking area drain into the proposed detention pond, which releases water through a gravity control device to the Ortiz Avenue swale. There appears to be a connection routing some runoff from the south side of the recreation field to the Juvenile Detention Center, where it travels west in a roadside swale to the Ortiz Avenue swale. A little less than half of the area of the Juvenile Detention Center site drains into perimeter swales along the north and east borders and then to the west before emptying into the Ortiz Avenue swale. The remainder of the Juvenile Detention Center drains into the retention pond. The same is true of the Price Halfway House. The Lee County Stockade drains to each of its borders where the water then runs west along the north or south border to the Ortiz Avenue swale. The southern half of the Lee County Stockade site drains into the small retention pond at the northwest corner of the Sheriff's Office Aviation Department. Most of the runoff from the heliport facility runs to the southwest corner of the parcel, which is the location of the abandoned pump. From there, the runoff continues to the Ortiz Avenue swale. Very little if any of the runoff from the heliport enters the small retention pond on the northwest corner of the parcel. The bootcamp drains into the detention pond, which then releases water by a gravity control structure into a portion of the undisturbed 32.7-acres before entering the Ortiz Avenue swale. The Emergency Operations Center site drains in all directions away from the building and parking area, eventually draining into the Ortiz Avenue swale. Stormwater discharge rates from the proposed halfway house and bootcamp are 0.28 cfs and 0.37 cfs. Under SFWMD rules, the allowable maximums in the Six Mile Cypress drainage basin are 0.30 cfs and 0.33 cfs, respectively. SFWMD and DMS contend that the excessive discharge from the bootcamp is acceptable because the gravity control device for the proposed detention pond is of the smallest size allowable, given the indisputable need to avoid clogging and ensuing upstream flooding. Initially, SFWMD approved the discharge rates for the halfway house and bootcamp because, when combined, they did not exceed the total allowable value. However, this approach was invalid for two reasons. First, the two sites contain entirely independent drainage systems separated by several hundred feet. Second, after correcting an initial understatement for the value for the halfway house, the actual total exceeds the maximum allowable total. SFWMD contends that the slight excess is acceptable because of the inability to use a smaller orifice in the gravity control structure. However, the discharge quantity easily could have been reduced by design alternatives, such as enlarging the detention pond, which is mostly surrounded by land that is to be left undisturbed. The ease with which the minimum-orifice problem could have been avoided rebuts the presumption contained in Basis of Review 7.2.A that excessive discharge quantities are presumably acceptable if due to the inability to use a smaller orifice. Also, SFWMD and DMS have failed to show that the effect of the excessive discharge quantities is negligible, so the exception in the SFWMD manual for negligible impacts is unavailable. Neither SFWMD nor DMS provided any reasonable assurance as to the quantity of discharge from the 21.4 acres. Rough estimates suggest it is more likely that the quantity of discharge may greatly exceed the allowable maximum. SFWMD must evaluate the water-quantity issues before issuing operation permits for the systems on the 21.4- and 32.7- acre parcels and a construction and operation permit for the 10.9-acre parcel. Obviously, if SFWMD determines that all water quantity criteria are met as to the existing systems, it may issue operation permits for the systems on the 21.4- and 32.7- acre parcels. Otherwise, SFWMD must quantify the extent of the deviation and, if it seeks to waive compliance with any or all quantity standards in reliance on Basis of Review 1.6, evaluate the effect of the waiver and explain the basis for the waiver. DMS and SFWMD have thus failed to provide reasonable assurance that the existing systems satisfy applicable water quantity criteria or that the proposed system will satisfy applicable water quantity criteria. Impacts on Adjacent Lands Petitioners' property is impacted by the above- described drainage in two ways. First, Petitioners' property abutting the east side of Ortiz Avenue, south of the 65 acres, is especially vulnerable to flooding because the Ortiz Avenue swale is not a V-notch, but a half-V. The closed side of the swale prevents the water from running onto Ortiz Avenue. The open side of swale abuts Petitioners' property, so, if the swale's capacity is exceeded, stormwater will be released onto Petitioners' land. Second, perimeter berming along the east side of the 10.9- and 21.4- acre parcels will impede flow off the part of Petitioners' property located to the east of the 65 acres. A swale between the proposed halfway house and the Juvenile Detention Center will receive runoff from a small portion of Petitioners' property to the east and mostly north of the 65 acres. But there is no indication how much runoff from Petitioners' property can be so accommodated, how much runoff is impeded by the existing berm along the east side of the Juvenile Detention Center and Price Halfway House, and how much runoff will be impeded by the addition of new berms along the east side of the proposed halfway house and bootcamp. Basis of Review 6.8 requires that swales and dikes allow the passage of drainage from off-site areas to downstream areas. Rule 40E-4.301(1)(b), Florida Administrative Code, requires that an applicant provide reasonable assurances that a surface water management system will not cause adverse water quality or quantity impacts on adjacent lands. Neither SFWMD nor DMS obtained topographical information for Petitioners' property, as required by the Basis of Review. Rough estimates suggest that the proposed project may require Petitioners' property to retain considerably more stormwater from the design storm event of 25 years, three days. DMS and SFWMD have thus failed to provide reasonable assurance that the proposed system would not have an adverse impact on Petitioners' upstream and downstream land.
Recommendation It is hereby RECOMMENDED that the South Florida Water Management District enter a final order denying the application of the Department of Management Services for all permits for the operation and construction and operation of surface water management systems on the 65-acre parcel. ENTERED on June 19, 1995, in Tallahassee, Florida. ROBERT E. MEALE 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 on June 19, 1995. APPENDIX Rulings on Proposed Findings of Petitioners 1-18: adopted or adopted in substance. 19: rejected as subordinate. 20-21: adopted or adopted in substance. 22-24 (first sentence): rejected as irrelevant. 24 (remainder)-46: adopted or adopted in substance. 47-53: rejected as subordinate. 54-64 (first sentence): adopted or adopted in substance. 64 (second sentence)-66: rejected as subordinate. Rulings on Proposed Findings of Respondent SFWMD 1-10: adopted or adopted in substance. 11: rejected as unsupported by the appropriate weight of the evidence. 12: rejected as unnecessary. 13: adopted or adopted in substance. 14-15: rejected as subordinate. 16: rejected as unsupported by the appropriate weight of the evidence. 17 (except for last sentence): adopted or adopted in substance. 17 (last sentence): rejected as unsupported by the appropriate weight of the evidence. 18-32 (first sentence): rejected as unnecessary. 32 (remainder): rejected as unsupported by the appropriate weight of the evidence. 33: rejected as subordinate. 34: rejected as unsupported by the appropriate weight of the evidence, except that the proposed ponds are wet detention. 35 (first sentence): adopted or adopted in substance. 35 (remainder): rejected as unsupported by the appropriate weight of the evidence. 36-45: rejected as unnecessary. 46-47: rejected as unsupported by the appropriate weight of the evidence. 48-50 (second sentence): adopted or adopted in substance. 50 (remainder): rejected as unsupported by the appropriate weight of the evidence. 51-52, 55-57 (first sentence), and 58: adopted or adopted in substance, although insufficient water quality treatment. 53: adopted or adopted in substance. 54: rejected as unsupported by the appropriate weight of the evidence. 57 (second sentence): rejected as unsupported by the appropriate weight of the evidence. 59: rejected as unsupported by the appropriate weight of the evidence. 60: adopted or adopted in substance, except after "therefore." None of remainder logically follows from what is said in 1.6. 61: rejected as unsupported by the appropriate weight of the evidence. 62-64: rejected as subordinate, unsupported by the appropriate weight of the evidence, and irrelevant. 65: rejected as subordinate. 66: rejected as irrelevant. The burden is on the applicant and SFWMD, if it wishes to issue the permits, to provide reasonable assurances as to the adverse impact of the drainage systems. 67-68: rejected as subordinate. 69: rejected as unsupported by the appropriate weight of the evidence. 70: rejected as unsupported by the appropriate weight of the evidence. 71: rejected as repetitious. 72: rejected as irrelevant, except for past report of flooding, which is rejected as repetitious. 73: rejected as repetitious. 74: rejected as irrelevant and subordinate. 75 (first three sentences): adopted or adopted in substance. 75 (remainder): rejected as unsupported by the appropriate weight of the evidence. 1 and 2: rejected as irrelevant insofar as the same result is reached with or without the permit modifications. Rulings on Proposed Findings of Respondent DMS 1-4: adopted or adopted in substance. 5: rejected as subordinate. 6: rejected as unsupported by the appropriate weight of the evidence. 7: adopted or adopted in substance. 8: rejected as subordinate. 9: adopted or adopted in substance, except that the excessive discharge was not "caused" by the minimum-sized orifice, only defended on that basis. 10: adopted or adopted in substance. 11-12: rejected as subordinate. 13: rejected as irrelevant. 14: adopted or adopted in substance. 15: adopted or adopted in substance, except for implication that no flooding problems existed. 16: rejected as recitation of evidence. 17: rejected as subordinate. 18: rejected as irrelevant. 19: adopted or adopted in substance, to the extent that separateness of systems is relevant. 20: rejected as subordinate. 21: adopted or adopted in substance, except for last sentence, which is rejected as unsupported by the appropriate weight of the evidence. 22: rejected as subordinate. 23-30: rejected as unsupported by the appropriate weight of the evidence, recitation of evidence, and subordinate. 31: rejected as unsupported by the appropriate weight of the evidence. 32: rejected as unsupported by the appropriate weight of the evidence, based on the present record. 33: rejected as unsupported by the appropriate weight of the evidence and relevance. COPIES FURNISHED: Tilford C. Creel Executive Director South Florida Water Management District P. O. Box 24680 West Palm Beach, FL 33416 Russell P. Schropp Harold N. Hume, Jr. Henderson Franklin P.O. Box 280 Ft. Myers, Fl 33902 O. Earl Black, Jr. Stephen S. Mathues Department of Management Services 4050 Esplanade Way, Suite 260 Tallahassee, FL 32399-0950 Vincent J. Chen Toni M. Leidy South Florida Water Management District 3301 Gun Club Road West Palm Beach, FL 33401
Findings Of Fact THE PARTIES CMI is a Florida corporation authorized to do business in Florida. CMI owns a mine site as is depicted in the permit application, which mine site is known as "Pine Level". Alan R. Behrens owns residential property approximately two miles from Pine Level, which abuts Horse Creek. He maintains an individual well for domestic and other purposes, and is a substantially affected person under the statute. Charlotte County is a government entity and a political subdivision of the State of Florida, and is a substantially affected person under the statute. The City of North Port is an incorporated municipality of the State of Florida, and is a substantially affected person under the statute. The Environmental Confederation (ECOSWF), a citizens group, is a substantially affected person under the statute. The District is the agency with the responsibility for reviewing and ruling upon CMI's water use permit application. APPLICATION AND PROCESS CMI proposes to operate a phosphate mine facility at "Pine Level" ("site"). The site is located approximately seven miles west of Arcadia, DeSoto County, Florida. The mine reserves at the site are approximately 17,700 acres. 9,000 to 10,000 acres are projected for mining. In 1978, Consumptive Use Permit No. 200103, was issued and in 1986, the current owners purchased the corporation which held the permit, and changed the name of the corporation to CMI. The Industrial Water Use Permit has not been used since it was issued to a prior owner of the site, and provided for average daily withdrawals of 13.6 mgd from wells. In 1984, this permit was renewed and modified to provide for average daily withdrawals of 12.8 mgd from deep wells. The groundwater withdrawals currently sought by CMI is 6.9 million gallons per day ("mgd") average daily withdrawal, which totals include 5.1 mgd from deep wells for use in the amine flotation process and 1.7 mgd for sealing the matrix slurry pumps. This reduction to 6.9 mgd in permitted withdrawals is a significant reduction. In addition, the proposed permit allows 3.7 mgd to be withdrawn from the surficial aquifer by dewatering mine cuts. In November, 1990, CMI submitted an application for renewal. In November 1991, CMI submitted to the District a revised Water Use Application No. 200103.02 ("application") to renew and modify the existing water use permit. The District requested more information, and CMI provided additional information and supplemental responses to aid in the review and evaluation of the application. The District prepared and submitted a Notice of Intent to Issue Permit and the District staff has prepared a "draft" Permit No. 200103.02 authorizing the withdrawal of the quantities requested in the application with certain conditions. In addition to renewal and modification of the water use permit, which is the subject of this proceeding, CMI will be required to participate in numerous regulatory reviews and permitting procedures (i.e. a development of regional impact evaluation, a federal environmental impact statement, federal approvals under the Clean Water Act [including a national pollutant discharge elimination system ("NPDES") permit], and a conceptual reclamation plan review) before CMI may commence mining, and consequently, begin any withdrawal of water. The mining process will utilize large walking draglines to excavate over burden and stack it beside the active mining area for land reclamation. The ore material called "matrix" will be dug up by the draglines, placed into an earthen pit where it will be slurried with a high pressure water jet. A pump will pick up this slurried matrix material, pump it back to the processing plant where it will first go through various separation devices, including screens and cyclones. The course material termed "pebble" will be separated and parts of that will be directly saleable as a product. The bulk of the phosphate product is contained in intermediate-sized material called concentrate feed. The concentrate feed consists of ore and sand. The ore is separated from the sand in a process called "flotation". The flotation process is a two stage process that ends up separating the tailings sand, which can then go back to the sand-clay flocculation and mixing units, and be pumped out ultimately for land reclamation back in the mine-out areas. The phosphate product which is called "wet rock", is placed in storage bins where it can drain, and be loaded onto rail cars for shipment. The "amine flotation process" is the second stage of flotation where sand and phosphates are separated. This process requires clean water for the amine flotation phase, because any amount of contaminants, including organic reagents, will adversely affect the process. Any mineral particles must be removed so that the amine may attach itself to the phosphate. Any contaminants will destroy or significantly and adversely affect not only the phosphate recovery, but the entire flotation process. Deep well water is requested for use in the amine flotation process because it is clean. All phosphate mines in Florida currently rely on deep well water. 5.2 mgd is the minimum amount of "clean" water needed to assure efficient processing of the amine flotation process of the mine beneficiation plant. Deep well withdrawals are also commonly used for the purpose of sealing or protecting the packing of pumps at various points in the mine system in order to avoid damage to the equipment. These wells are often referred to as "sealing water wells". The Pine Level mine will require 1.7 mgd for this purpose. Water for the sealing water wells must be clean and clear in order to effectively seal pumps for leaks. The Pine Level project will provide 400-500 construction jobs during the construction period. It will provide approximately 200 full-time jobs with an annual payroll of about five million dollars once it is in operation. It will result in about one thousand additional jobs providing services to the development. It will pay in excess of one million dollars a year to DeSoto County in ad valorem taxes. TECHNICAL CRITERIA The water use is a reasonable and beneficial use. 5.2 mgd groundwater withdrawal is "necessary to fill a certain reasonable demand." The technical criteria relating to water level or rates of flow impacts set forth in Rule 40D-2.301(1)(d), Florida Administrative Code, are not applicable in this proceeding because the District has not established any regulatory levels or rates of flow for the area encompassed by the application. In addition, this presumption only addresses surface water withdrawals. Phosphate mining is a beneficial activity and is consistent with the public interest. There is no significant risk of salt water intrusion. The water use withdrawal will not degrade the water quality in the aquifer by causing any contamination plume to spread. There have been no contaminant plumes identified on site. GROUNDWATER IMPACTS There is sufficient ground water at the site of a suitable quality and quantity to support the proposed phosphate mining and beneficiation activities. The local hydrogeology at the site consists of an upper layer known as the surficial aquifer. Rain penetrates the surficial aquifer to flow vertically to the water table. The water that is not consumed by vegetation at this layer will flow either to a nearby stream channel or will leak down through a semi- confining layer. The water continues to seep vertically into the lower underlying limestone aquifers. There are three limestone water-bearing layers: the intermediate, the Suwannee or Upper Floridan, and the Avon Park or Lower Floridan aquifers, respectively. The intermediate and the underlying Suwannee aquifer are separated by another semi-confining layer. Likewise, the Avon Park aquifer and the Suwannee aquifer are separated by another semi-confining layer. At the site, wells in the intermediate aquifer will draw water to seal the bearings on the matrix slurry pumps. There will be one deep well in the Suwannee and one deep well in the Avon Park to draw for the beneficiation plant. The groundwater modeling performed by CMI simulated the four aquifers, that is, the surficial aquifer and each of the three limestone aquifers. An Aquifer Performance Test ("APT") was performed at the site. The data generated from the APT was used to calculate various aquifer parameters, for example, transmissivity, storage coefficient, and leakiness. This information was then used in setting up the groundwater flow model that ultimately was incorporated into the application. During the District staff's review of the application, the deep well withdrawal quantities requested by CMI were compared with approximately 6 other phosphate mines of comparable size, acreage, and type of operation. As a result of this comparison, the staff found CMI's requested use to be less than the other six phosphate mines. The use of recycled water in the amine flotation process in place of deep well water in the past by CMI has proven unsuccessful because a constant temperature and a constant ph level could not be maintained with recycled water, and recycled water contains traces of fatty acids and oils, which also negatively affect the amine flotation process. C.F. Industries, Inc., has been operating a phosphate mine in Hardee County, Florida, since 1978. C.F. Industries, Inc., has since 1983 at the Hardee County mine, successfully substituted recirculation water for deep well water for operation of the amine flotation circuit on a routine basis. C.F. Industries, Inc., presently plans to employ substitution of some recirculation water for deep well water in a new yet-to-be permitted mine. C.F. Industries, Inc., at its existing Hardee County mine requires use of deep well water for start-up purposes to "charge" the system. C.F. Industries, Inc., at its existing mine, uses deep well water to respond to abnormal operational conditions, including excessive rainfall events, when the quality of the normal recirculation water is not suitable for substitution of deep well water. Neither CMI, nor District staff was aware prior to hearing, that the C.F. mine was successfully substituting recycled water for deep well water in the amine flotation process. At the time of making the representations to the District about necessary water quality requirements of the flotation process, CMI had a study, entitled, Amine Water Evaluation, Pine Level Project, July 27, 1984, ("Pilot Plant Study"), which concluded that deep well pumping and discharge could be reduced by use of water drawn from mine cuts. The Pilot Plant study was site specific to CMI's proposed phosphate mine. The Pilot Plant study bench tests were verified in the same pilot plant facility CMI uses to verify the grade of ore on the Pine Level Site. The Pilot Plant study or its results were known to CMI officials or experts involved in the permit application at issue in this case. CMI did not inform District staff of the existence or conclusions of the Pilot Plant study. The Pilot Plant study indicates that CMI could reduce its water usage by substituting water from mine cuts for deep well water. CMI did no studies to determine if the substitution of mine cut water for deep well water, as suggested by the Pilot Plant Study, was feasible to implement. SURFACE WATER IMPACTS The phosphate ore (matrix), is extracted by an excavation machine called a "dragline", which opens mining cuts of approximately 32 to 35 feet in depth, 330 feet wide, and up to 4,000 feet long. Seepage occurs into the mine cuts from the water table, and must be pumped out in order to see and extract the matrix. This dewatering is also necessary to protect the draglines against slope stability problems. Water pumped out of the mining cuts is introduced into the mine water recirculation system which is operated for purposes of collecting and recycling water within the mine complex. The matrix that is extracted from the mining cut is placed in a shallow excavation near the cut, and is converted to a slurry and, thereafter, transported hydraulically to the mine processing (or "beneficiation") plant. The beneficiation plant uses considerable quantities of water, utilizing supplies from within the mine system (i.e. surface water) and water from deep wells. Sand tailings and sand and clay mixture are by-products of the mining process. Recycled water is used to transport waste clay and sand from the plant to the disposal and reclamation areas. Reclamation takes 1-2 years for areas reclaimed with sand tailings and 5-6 years for areas reclaimed with a sand-clay mixture. Groundwater that is used in the processing plant is recycled. Water within the mine is recycled a number of times, and CMI's proposal calls for 90 percent of the total mine demand to be satisfied by this recirculation system and approximately 96 percent of the water used is recyclable water. DEWATERING AND WATER BALANCE CMI's mine pit dewatering activities result in the withdrawal of water from the surficial aquifer. A "water balance" demonstrates that requested quantities relate to reasonable mining, processing, and dewatering needs. The "water balance" for the mining operation evidences a balance between sources and uses/losses. The sources of water in the CMI water balance that input to the mining operation include groundwater from wells (6.9 mgd), mine cut dewatering or water table drainage (3.7 mgd), and collected rainfall (3.1 mgd). Uses and losses associated with the mining operation include water retained in clays (6.7 mgd), water shipped with final product (.7 mgd), evapotranspiration and evaporation (3.0 mgd), water used for agricultural irrigation (5.0 mgd), and water seeping from the Mine Water Surge Area ("MWSA") (1.2 mgd). The water balance matrix moisture component of 2.9 mgd is not a withdrawal of water for water use permitting purposes. The District's modeling of the impacts resulting from mine cut dewatering resulted in a finding of 2.34 MGD as opposed to the 3.7 mgd derived by CMI. For calculation purposes, rainfall is collected at the rate of 3,974 gallons per acre per day. CMI calculates that it will collect 3.1 mgd of rainfall, and use it in its recirculation system. The 3.1 mgd calculation is based on the amount of rain that will fall on 600 acres of mine water surge area, 80 acres of plant site, and two 50 acre mine cuts. CMI plans to mine 450 acres each year at the Pine Level Site over a period of 22 years. Runoff over disturbed areas on the CMI mine site must be captured, and will become part of the recirculation system. Assuming only one year of disturbed area during the permit term, CMI has failed to account for nearly 1.8 mgd in its water balance (450 acres x 3,974 gallons/acre/day). CMI plans to pump any rainfall collected from all disturbed areas to the mine water surge area (MWSA). CMI has not included any acres of disturbed area in its calculations of the amount of rainfall it will collect for the current permit. CMI has not submitted a mine plan. Without a mine plan, the number of disturbed acres cannot be determined. Because CMI's water balance does not include rainfall collected over disturbed areas, the water balance is incorrect. The rainfall collected from the disturbed areas will increase the amount of water that CMI will need to discharge or use for agricultural purposes. Excavation of the Mine Water Surge Area will cause dewatering of the surficial aquifer. No analysis was done of how much dewatering of the surficial aquifer will occur as a result of the excavation of the MWSA, or of the potential impacts to wetlands as a result of the dewatering activities. The District's one foot draw down presumption applies to dewatering as well as to groundwater pumping. The proposed dewatering setback from wetlands was set at 660 feet. The 660 foot setback distance is in lieu of mitigation if CMI wishes to mine within the setback distance, it will be required to implement mitigation procedures. Dewatering draw downs in the surficial aquifer as great as six and one-half to seven feet could occur on the CMI site at 660 feet from a mine cut under dry weather conditions. At 660 feet, the predicted draw down is nearly one and one-half feet using a mine pit depth of 26 feet, based on a three foot water table and a 29 foot average mine cut depth for the area expected to be mined during the term of the permit. Actual mine cut depths during the term of the permit would be as deep as thirty-seven feet which result in a draw down in the aquifer that is greater than one and on-half feet. Combining the dewatering calculations with the surficial aquifer draw downs resulting from CMI's planned well pumping from the intermediate and Floridian aquifers result in greater than predicted draw downs. CMI's water balance did not account for changes in water needs due to variability of the ore body. WATER QUALITY CMI has not demonstrated that the water quantities requested for the operation of the phosphate mine and beneficiation plant, and land reclamation and water handling will utilize the lowest water quality to the greatest extent practicable. Nevertheless, the Pine Level mine is innovative in comparison to other operating mines. It proposes to reduce its groundwater requirement by increasing the amount of recycled water used in the amine flotation process; employ an innovative sand/clay mixing technique for land reclamation, thus eliminating the need for conventional large, above-ground day settling areas or slime ponds; and use surplus water for irrigation of agricultural crops or pasture. CMI plans to mine the Pine Level Site for a period of 22 years. For phosphate mines, neither DNR, nor SWFWMD analyze impacts with respect to surface water during the mining process. For phosphate mines, no state agency looks at off-site surface water impacts from the standpoint of draw downs, with the possible exception of cities and counties. The District has not required CMI to submit an application for the management and storage of surface waters permit, since the District staff believes that phosphate mines are exempt from obtaining any MSSW permit from the District. A gap exists in the regulatory scheme for phosphate mines with respect to the reduction of surface water flows during the mining process if SWFWMD exempts phosphate mines from obtaining an MSSW permit. INTERFERENCE WITH EXISTING LEGAL USERS The City of North Port is an existing legal user of water. The City of North Port has a public water supply facility which draws its water from the Big Slough. The Big Slough normally gets a portion of its flow from high quality water in the surficial aquifer. CMI's proposed Pine Level phosphate mine is located in the watersheds which feed the Big Slough and the Peace River. In the initial years of the mine, virtually all of the collected rainfall will be diverted from the Big Slough watershed. No analysis has been done to see how dewatering might affect the City of North Port. Any significant reduction in flow to the City of North Port's facility during the low flow season will interfere with North Ports existing legal use of water. Diversion of 3.1 mgd of rainfall from the Big Slough will have an adverse impact on the City of North Port's water facility. The City of North Port is currently under a consent agreement with the Florida Department of Environmental Regulation because the water supplied by its facility violates drinking water quality standards for sulfates and total dissolved solids ("TDS") regularly during periods of low flow in the Big Slough. The MWSA, the plant area and the initial mining areas are primarily within the Big Slough drainage area. Seepage of 1.2 mgd from the MWSA will flow into the Big Slough. The only analysis done of the quality of the seepage from the MWSA was a rough analysis which showed that sulfates will likely be around 550 grams per liter. The legal standard for sulfates in drinking water is 250 grams per liter. Seepage from the MWSA will be high in total dissolved solids ("TDS") since a good portion of it was pumped from deep wells which have very high levels of TDS. No analysis was done of the potential of this seepage water to interfere with North Port's facility. Charlotte County is an existing legal user of water whose water supply is drawn from the Peace River downstream from the proposed CMI phosphate mine at Pine Level. Discharge of 5.0 mgd from the Pine Level mine could adversely affect Charlotte County's drinking water facility located on the Peace River. AGRICULTURAL USE CMI proposes to use 5.0 MGD of surplus water for irrigation of pasture grasses for cattle. CMI has not conducted any specific tests to determine the feasibility of using the discharge or the quality of the water that they plan to use for agricultural irrigation. The water for irrigation will be drawn out of the mine water surge area. The determination of whether the 5.0 mgd discharge can be used for agricultural irrigation has been postponed. The staff's position is that the proposed special conditions provide reasonable assurances that the discharge will comply with the requirements of the Basis for Review. WETLANDS Isolated wetlands occur throughout the CMI mine site. The isolated wetlands on the CMI property provide habitat for endangered and threatened species. Sandhill Cranes and Wood Storks, both threatened or endangered species, were sighted on the CMI property by wetlands experts during their site visit prior to the hearing. Small isolated wetlands on CMI property would be adversely affected by less than a one foot draw down. Wetland peat soils oxidize if exposed to the air. Oxidation results in subsidence of the wetland soils, which adversely impacts wetlands. Too much water as well as too little water can adversely impact wetlands. The combined effects of aquifer pumping and dewatering planned at the CMI site will adversely affect wetlands. No analysis was completed of the impacts to wetlands as a result of the combined effects of dewatering and pumping from the aquifer. No information regarding the normal range of wetland hydroperiods for preserved wetlands or other onsite unmined wetlands was introduced. No information was provided regarding the habitat functions provided by the wetlands on the CMI site either for threatened or endangered species or otherwise. ENVIRONMENTAL IMPACT The Applicant did not provide reasonable assurance that the water use will not cause unacceptable adverse impacts to environmental features on or off- site. The Applicant did not provide reasonable assurances that the water use will not have an adverse impact to surface water bodies such as lakes, ponds, impoundments, springs, streams, canals, estuaries or other water courses. The Applicant did not provide reasonable assurances that there will be no adverse environmental impact to wetlands, lakes, streams, estuaries, fish, and wildlife or other natural resources. The Applicant did not provide reasonable assurances that there will be no adverse impacts to the surface water system or vegetation as a result of groundwater withdrawal. The Applicant did not provide reasonable assurances that the water use will not have an adverse impact by altering or impairing the habitat of threatened or endangered species. The Applicant did not provide reasonable assurances that the projected draw downs will not result in any adverse impact to any protected or non-protected plant or animal species. The Applicant did not provide reasonable assurances that the water use will not have an adverse environmental impact to wetlands.
Recommendation Based on the foregoing findings of fact and conclusions of law, it is RECOMMENDED that the Governing Board of Southwest Florida Water Management District enter a Final Order DENYING the issuance of a Water Use Permit to the Applicant, CMI. DONE and ENTERED this 20th day of April, 1993, in Tallahassee, Florida. DANIEL M. KILBRIDE 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 20th day of April, 1993. APPENDIX The following constitutes my specific rulings, in accordance with section 120.59, Florida Statutes, on proposed findings of fact submitted by the parties. Proposed findings of fact submitted by Petitioner. Accepted in substance: paragraphs - 13, 14, 15, 21, 24, 31, 35, 38, 70, 71, 73, 75, 91, 97, 100, 104, 105, 114, 115, 116, 125, 126, 127, 128, and 129. Rejected as subsumed or irrelevant and immaterial: paragraphs - 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11, 12, 16, 17, 19, 20, 22, 23, 25, 27, 28, 29, 30, 33, 34, 36, 37, 37A, 39 40, 43, 44, 45, 48, 49, 50, 51, 52, 53, 54, 55, 56, 57, 58, 59, 60, 61, 62, 63, 64, 65, 66, 67, 68, 72, 74, 76, 77, 78, 79, 80, 81, 82, 83, 84, 85, 86,87, 92, 93, 94, 95, 96, 98, 99, 101, 102, 103, 106A, 106, 107, 108, 109, 110, 111, 112, 113, 117, 120, 121, 122, 123, 124, 130, 131, 132, 133, and 134. Rejected as against the greater weight of the evidence: paragraphs - 18, 26, 32, 41, 42, 46 (omitted), 47 (omitted), 69, 88 (omitted), 89 (omitted), 90 (omitted), 118 (omitted), 119 (omitted), and 135 (omitted). Proposed findings of fact submitted by Petitioner, Charlotte County. Accepted in substance: paragraphs - 1, 2, 7, 18, 19, 20, 22, 25, 28, 29, 36, 40, 41, 51, 59, and 62. Rejected as argument, subsumed or irrelevant and immaterial: paragraphs - 3, 4, 5, 6, 8, 9, 10, 11, 12, 13, 14, 15, 16, 17, 21, 23, 24, 26, 27, 30, 31, 32, 33, 34, 35, 37, 38, 39, 42, 45, 46, 47, 48, 49, 50, 52, 53, 54, 55, 56, 57, 58, 60, and 61. Rejected as hearsay: paragraphs - 43 and 44. Proposed findings of fact submitted by Petitioner, City of North Port. Accepted in substance: paragraphs - 1, 2, 3, 5, 6, 7, 9, 19, 20, 21, 22, 24(in part), 25, 26, 27, 28, 29, 30, 31, 32, 34, 35, 36, 37, 38, 39, 40, 41, 42, 45, 47, 48, 49(in part), 50, 51, 52, 53, 54, 56, 57(in part), 58, 59, 60, 61, 63(in part), 65, 66, 67, 68, 69, 70, 71, 72, 73, 74, 75, 78, 79, 80, 83, 84, 85, 86(in part), 87, 92, 93, 95, 96, 99, 104, 107, 108(in part), 109(in part), 112, 113, 114, 115, 116, 120, 122, 123, 126, 138, 139, 140, 141, 142, 143(in part), 144, 150, 153, 154, 155, 156, 159, 167, 168, 170, 171, 172, 173, 176, 177, 179, 180, 187, 193, 194, 195, 197, 198, 199, 200, 201, 202, 204, 205. Rejected as argument, subsumed or irrelevant and immaterial: paragraphs - 4(contained in Preliminary Statement), 8, 10, 11, 12, 13, 14, 15, 16, 17, 18, 23, 24(in part), 33, 43, 44, 46, 49(in part), 55, 57(in part), 62, 63(in part), 64, 76, 77, 81, 82, 86(in part), 88, 89, 90, 91, 94, 97, 98, 100, 101, 102, 103, 105, 106, 108(in part), 109 (in part), 110, 111, 117, 118, 119, 121, 124, 125, 127, 128, 129, 130, 131, 132, 133, 134, 135, 136, 137, 143(in part), 145, 146, 147, 148, 149, 151, 152, 157, 158, 160, 161, 162, 163, 164, 165, 166, 169, 174, 175, 178, 181, 182, 183, 184, 185, 186, 188, 189, 190, 191, 192, 196, 203, 206, 207, 208, 209, 210, 211, 212, 213, 214, 215, 216, 217. Proposed findings of fact submitted by Respondent/Petitioner Consolidated Minerals, Inc. and Southwest Florida Water Management District. Accepted in Substance: paragraphs - 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11, 14, 17, 18, 19, 20, 21, 22(in part), 23, 24, 25(in part), 26, 27(in part), 28, 29(in part), 32, 33(in part), 39, 40, 41, 42, 43, 44, 45, 46, 47, 49, 50, 52(in part), 53, 54, 55, 56, 57(in part), 58, 62, 71, 82, 85, 87, 88, 91, 92(in part), 93, 94(in part), 95(in part), 96(in part), 97(in part), 100(in part), 101, 115, 119, 120, 123, 124(in part), 125(in part), 126(in part), 127(in part), 130(in part), 133(in part), 137, 138(in part), 139, 145. Rejected as argument, subsumed, or irrelevant and immaterial: paragraphs - 12, 13, 15, 16, 31, 36, 37, 38, 48, 51, 52(in part), 57(in part), 59, 60, 63, 80, 81, 83, 84, 86, 90, 94(in part), 105, 106, 107, 108, 109, 110, 111, 112, 113, 114, 116, 117, 118, 124(in part), 126(in part), 127(in part), 130(in part), 134, 135, 136, 138(in part), 140, 141, 142, 143. Rejected as against the greater weight of evidence: paragrahs - 22(in part), 25(in part), 27(in part), 29(in part), 30, 33(in part), 34, 35, 61, 64, 65, 66, 67, 68, 69, 70, 72, 73, 74, 75, 76, 77, 78, 79, 89, 92(in part), 95(in part), 96(in part), 97(in part), 98, 99, 100(in part), 102, 103, 121, 122, 125(in part), 128, 129, 131, 132, 133(in part), 144. Proposed findings of fact submitted by Petitoner, Environmental Confederation of Southwest Florida, Inc. Accepted in substance: paragraphs - 1, 2, 3, 4 6, 7, 17, 22, 26, 27, 28, 29, 30, 33(in part), 34, 35, 39(in part) 41, 42, 43, 45, 48, 53, 56, 57, 59, 60, 61, 62, 71, 73, 80, 81, 82, 85, 86, 87, 92(in part), 106, 107, 110, 112, 113, 114, 115, 116, 117, 121, 122, 123, 124, 125, 126, 127, 128, 129, 130, 131, 132, 133, 134, 135, 136, 137, 138, 139(in part), 140, 141, 142, 143, 144, 145, 148, 149, 150, 151, 152, 154, 155, 157, 158, 162, 163, 164, 165. Rejected as argument, subsumed, or irrelevant and immaterial: paragraphs - 5, 8, 9, 10, 11, 12, 13, 14, 15, 16, 18, 19, 20, 21, 23, 24, 25, 31, 32 33(in part), 36, 37, 38, 39(in part), 46, 47, 49, 50, 51, 52, 55, 58, 63, 64, 65, 66, 67, 68, 70, 72, 74, 75, 76, 77, 78, 79, 83, 84, 88, 89, 90, 91, 92(in part), 93, 94, 95, 96, 97, 98, 99, 100, 101, 102, 103, 104, 105, 108, 109, 111, 118, 119, 120, 146, 147, 153, 156, 159, 160, 161, 166, 167, 168. Rejected as against the greater weight of evidence: paragraphs - 44, 54, 69, 139(in part). COPIES FURNISHED: Rory C. Ryan, Esquire Roger W. Sims, Esquire HOLLAND & KNIGHT Suite 2600 200 S. Orange Avenue P. O. Box 1526 Orlando, Florida 32802 Vivian Arenas, Esquire Assistant General Counsel Southwest Florida Water Management District 2379 Broad St. Brooksville, Florida 34609 Mr. Alan R. Behrens Route 2, Box 725-A-32 Arcadia, Florida 33821 Matthew G. Minter, Esquire County Attorney 18500 Murdock Cr. Port Charlotte, Florida 33948-1094 David M. Levin, Esquire ICARD, MERRILL, CULLIS, TIMM, FUREN & GINSBURG PO Box 4195 Sarasota, Florida 34237 Kenneth B. Wright, Esquire Sierra Club Legal Defense Fund PO Box 1329 Tallahassee, Florida 32302 Peter G. Hubbell Executive Director 2379 Broad Street Brooksville, Florida 34609-6899
Findings Of Fact The Parties and the Property. The Respondent, Saddlebrook Resorts, Inc. (Saddlebrook), is a corporation organized and existing under the laws of Florida, and is wholly owned by the Dempsey family. Saddlebrook is located on approximately 480 acres in central Pasco County, east of I-75 and south of State Road 54. The Petitioner, Wiregrass Ranch, Inc. (Wiregrass) is a corporation organized and existing under the laws of Florida, and is wholly owned by the Porter family ("the Porters"). Wiregrass owns approximately 5,000 acres of property which extends from Saddlebrook west approximately one mile to State Road 581 and south for approximately four miles. The Respondent, the Southwest Florida Water Management District (SWFWMD), is a political subdivision created pursuant to Chapter 61-691, Laws of Florida, which exists and operates under the Water Resources Act, Fla. Stat., Ch. 373. SWFWMD is charged with regulating, among other things, surface water management systems in Pasco County. Saddlebrook discharges surface water onto Wiregrass at two locations on the southern and western boundaries of Saddlebrook, known as the south outfall and the west outfall. Saddlebrook's property is part of a drainage basin totalling approximately 1400 acres that contributes runoff to Wiregrass' property. Until approximately 1973, the Saddlebrook property was undeveloped and owned by the Porters. In approximately 1973, the Porters sold the Saddlebrook property to the Refram family, which began developing the property. In approximately 1979, Saddlebrook acquired the property from the Reframs. The Saddlebrook property includes residential development, a conference center, and golf course and tennis facilities. Wiregrass' property, which is largely undeveloped and used for ranching, consists of pine-palmetto flatwoods, wetland strands, isolated wetlands, and improved pastures. The Porters' Civil Action Against Saddlebrook. The Porters instituted a civil action against Saddlebrook, Porter, et al. v. Saddlebrook Resorts, Inc., Case No. CA 83-1860, in the Circuit Court of the Sixth Judicial District, Pasco County, complaining that post-development discharges from Saddlebrook exceed pre-development discharges. In the civil litigation, the Porters contended that Saddlebrook's peak flow discharges should be returned to pre-development, or 1973, levels. A primary purpose of Saddlebrook's proposed redesign is to return peak flow discharges to those levels that existed in 1973, in response to the Porters' complaints in the civil action. Saddlebrook's current surface water management system is deemed by SWFWMD to be in compliance with Rule 40D-4, and SWFWMD's regulations do not require redesign or modification of the current system. Prior to Saddlebrook's submission of its application, SWFWMD advised Saddlebrook that, because Rule 40D-4 became effective on October 1, 1984, SWFWMD considered that date to be the "pre-development" condition for purposes of evaluating Saddlebrook's discharges. Saddlebrook requested that SWFWMD evaluate its application using 1973 as the pre-development condition. SWFWMD advised Saddlebrook that it would apply 1973 as the pre-development condition if the Porters consented. By letter from the Porters' counsel to SWFWMD dated January 31, 1990, the Porters provided their express consent to SWFWMD's use of 1973 as the pre- development date for purposes of evaluating those discharges relevant to Saddlebrook's MSSW permit application. Saddlebrook's MSSW Permit Application. On or about February 8, 1990, Saddlebrook submitted its application for MSSW permit no. 497318.00, seeking SWFWMD's conceptual approval of the redesign of Saddlebrook's surface water management system. The proposed redesign calls for modification of most of the existing drainage control structures at Saddlebrook and installation of new control structures at several locations, including the south and west outfalls. After submission of its initial application, Saddlebrook made various subsequent submittals in response to SWFWMD requests for additional information. Saddlebrook's response to SWFWMD's requests culminated in final submittals on March 7, 1991 and April 5, 1991. In its various submittals, Saddlebrook provided, among other things, detailed descriptions of all proposed modifications to its drainage system, engineering reports, and computerized flood-routing analyses of runoff from Saddlebrook under pre-development (1973) and post-modification conditions. Saddlebrook provided all information requested, and SWFWMD thereafter deemed its application complete. SWFWMD's Review of Saddlebrook's Application. In the fifteen months following Saddlwbrook's initial February, 1990, submittal, SWFWMD conducted an intensive review of the application. During the course of this review, SWFWMD staff performed numerous field inspections, made an independent determination of all input data to the computer analyses of Saddlebrook's discharges, and made six separate formal requests for additional information. SWFWMD's requests for additional information required, among other things, that Saddlebrook modify various input data and rerun its computer analyses of discharges under the pre-development and post-modification conditions. In addition, SWFWMD required Saddlebrook to perform computer modelling analyses of discharges from Wiregrass' property onto the property of downstream landowners. Because, unlike the Porters, these downstream owners had not provided consent to use 1973 as the relevant pre-development date, SWFWMD required Saddlebrook to model this downstream discharge using a "pre- development" date of 1984. SWFWMD performed its standard review procedures in connection with Saddlebrooks' application. In addition, SWFWMD also performed its own computer-modelling analyses of Saddlebrook's discharges. This modelling was based on input data independently collected by SWFWMD staff in the field and from other sources. SWFWMD staff also met with the Porters' hydrologist, Dr. Gerald Seaburn, and thoroughly reviewed concerns he expressed in connection with Saddlebrook's application. In addressing these concerns, SWFWMD performed additional work, including conferring with an independent soils expert, performing additional field inspections, and modifying the SWFWMD computer modelling analyses based on alternative input parameters suggested by Dr. Seaburn. In reviewing Saddlebrook's application, SWFWMD applied the design and performance criteria set forth in its "Basis of Review for Surface Water Management Permit Applications" ("Basis of Review"), which is incorporated by reference in F.A.C. Rule Chapter 40D-4. Based upon its review of Saddlebrook's application, SWFWMD concluded that Saddlebrook had demonstrated compliance with the design and performance criteria set forth in SWFWMD's Basis of Review and the conditions for permit issuance under F.A.C. Rule 40D-4.301. By a Staff Report dated April 29, 1991, and Notice of Proposed Agency Action dated May 3, 1991, SWFWMD recommended approval of Saddlebrook's application. Compliance With SWFWMD Permitting Criteria. The design and performance criteria for MSSW permitting set forth in SWFWMD's Basis of Review fall into four categories: (1) water quantity, in terms of peak flow discharges for projects, like Saddlebrook's, located in open drainage basins; (2) flood protection; (3) water quality; and (4) wetlands impacts. Water Quantity. Under the Basis of Review's water quantity standards, SWFWMD requires that projected peak flow discharges during a 25-year, 24-hour storm event under the proposed system be reasonably similar to peak flow discharges under the pre- development condition. The evidence presented at the formal hearing demonstrated that Saddlebrook's application satisfies SWFWMD's water-quantity standards. This evidence demonstrated that peak flow discharges during a 25-year, 24-hour storm event under the proposed system will be less than, but reasonably similar to, pre-development (1973) peak flow discharges. The evidence presented at the formal hearing also demonstrated that, under the proposed system, peak flow discharges during a 25-year, 24-hour storm event from Wiregrass' property onto downstream landowners will be less than, but reasonably similar to, 1984 peak flow discharges. The evidence presented by Saddlebrook further demonstrated that storage will be increased under the proposed redesign versus the pre- development, 1973 condition. On Saddlebrook's property, there will be approximately 35 percent more storage than existed in 1973, and the total storage for Saddlebrook and the contributing drainage basin upstream of Saddlebrook will be increased by approximately 15 percent over that existing in 1973. Flood Protection. Under the flood-protection standards of the Basis of Review, SWFWMD requires that the applicant demonstrate that under the proposed condition the lower floor of all residential and other buildings on-site, and in areas affected by the site, will be above the 100-year flood elevation. SWFWMD also requires that there be no net encroachment into the flood plain, up to that encompassed by the 100-year event, which will adversely affect conveyance, storage, water quality or adjacent lands. The evidence presented at the formal hearing demonstrated that Saddlebrook's application satisfies SWFWMD's flood-protection standards. The testimony of Mr. Fuxan and Wiregrass' related exhibit, Ranch Ex. 35, purporting to show that in a 25-year, 24-hour storm Saddlebrook's proposed redesign will "flood the [Saddlebrook perimeter] roads and just sheet flow onto the Porter property" is not accurate. As part of its redesign, Saddlebrook will construct an additional berm along the southwestern and southern perimeters of its property. This berm will detain water on Saddlebrook's property during a 25-year, 24-hour storm event and prevent it from "sheet-flowing" onto the Wiregrass property. Water Quality. Under the water-quality standards of the Basis of Review, SWFWMD requires, for systems like Saddlebrook's involving wet detention and isolated wetlands, that the applicant provide sufficient storage to treat one inch of runoff from the basins contributing runoff to the site. This volume must be discharged in no less than 120 hours, with no more than one-half of the volume being discharged within the first 60 hours. The evidence presented at the formal hearing demonstrated that Saddlebrook's application satisfies SWFWMD's water-quality standards. Wetland Impacts. Under the wetland-impacts standards of the Basis of Review, SWFWMD requires that the applicant provide reasonable assurance that the proposed system will not adversely impact on-site and downstream wetlands. The evidence presented at the formal hearing demonstrated that Saddlebrook has provided reasonable assurance that the proposed redesign will cause no adverse impacts to on-site wetlands. Saddlebrook's proposed redesign will impact only approximately .167 acres of on-site wetlands, for which Saddlebrook will fully mitigate by creating .174 acres of forested wetlands and buffer area. The evidence presented at the formal hearing also demonstrated that Saddlebrook has provided reasonable assurance that the proposed redesign will cause no adverse impacts to off-site wetlands. Reasonable assurance that off- site wetlands will not be adversely impacted was demonstrated by, among other things, evidence establishing that: (1) discharge points will not change under the proposed condition; (2) discharge elevations will be reasonably similar under the proposed condition; (3) there will be no significant variation in the water fluctuations in the wetlands adjacent to the south and west outfalls as a result of the proposed condition; (4) the drainage basin areas will be reasonably similar under the proposed condition; and (5) the proposed redesign will satisfy SWFWMD's water quality requirements. Wiregrass' Petition. In its Petition for Formal Administrative Hearing, Wiregrass focused primarily on water quality issues and stormwater runoff rates (or peak flow discharges), alleging the following "ultimate facts" which it claimed "entitle [it] to relief": The application, as submitted, contains insufficient storage to meet water quality criteria. The application, as submitted, will result in storage volumes on the project site which will not be recovered within 72 hours [sic] as required by the DISTRICT criteria. The application, as submitted, contains calculations based on erroneous hydraulic gradients. The application, as submitted, will result in storage volumes insufficient to meet water quality criteria as required by DISTRICT criteria. Post development stormwater runoff rates are underestimated in the application, resulting in system design with insufficient retention storage capacity to meet the DISTRICT's water quantity criteria. The failure to store stormwater or irrigation runoff impacts the substantial interest of the RANCH in that it deprives it of groundwater resources necessary for the successful operation of the ranch. Further, the lack of storage of stormwater and irrigation water is a prohibited waste of the water resources. At the formal hearing, Wiregrass presented no evidence to support any of the foregoing allegations of its Petition. Objections Raised by Wiregrass At The Hearing. At the final hearing, Wiregrass' opposition to Saddlebrook's permit application focused on three different grounds: For purposes of evaluating peak flow discharges, SWFWMD does not have jurisdiction to use a pre-development date prior to October 1, 1984. Under F.A.C. Rule 40D-4.301(1)(i), which provides that an applicant must give reasonable assurance that the surface water management systems "is consistent with the requirements of other public agencies," SWFWMD must apply not only its own permitting criteria but also those of other governmental entities, including county planning ordinan Under F.A.C. Rule 40D-4.301(1)(b), which provides that a permit application must give reasonable assurances that the surface water management system "will not cause adverse water . . . quantity impacts", SWFWMD must consider whether the annual volume of runoff will increase as a result of the proposed surface water management system. None of the foregoing objections was raised in Wiregrass' Petition as a basis for denying Saddlebrook's application. (Annual volume was alluded to in the Petition only as being pertinent to the question of Wiregrass' "substantial interest" for purposes of standing.) In any event, for the reasons set forth below, each of these objections was refuted by the evidence presented at the formal hearing. The 1973 Pre-Development Date. In their civil action against Saddlebrook, the Porters took the position that Saddlebrook's surface water management system should be redesigned so that discharges approximate those levels existing in 1973, before development of the Saddlebrook property. Dr. Gerald Seaburn, a hydrologist retained by the Porters, testified in the civil action that 1973 is the appropriate pre-development date for purposes of evaluating Saddlebrook's peak flow discharges. David Fuxan, a civil engineer retained by the Porters, took the position in the civil action that Saddlebrook should modify its surface water management system so as to return peak flow discharges to 1973 levels. At the formal hearing in this proceeding, Mr. Fuxan testified that it is still his position that Saddlebrook should modify its surface water management system so as to return peak flow discharges to 1973 levels. By letter from the Porters' counsel to SWFWMD dated January 31, 1990, the Porters provided their express consent to SWFWMD's use of 1973 as the pre- development date for evaluating those discharges relevant to Saddlebrook's MSSW permit application. Use of a 1984 "pre-development" date would prevent Saddlebrook from making the modifications the Porters claim in the civil litigation that it must make. Saddlebrook's existing system, about which the Porters complain in the civil litigation, is in all material respects the same system that was in place on October 1, 1984. Use of this existing system as the benchmark of comparison for attenuation of peak flows, therefore, would mean that substantial modifications to the existing system could not be made without substantially increasing retention storage on Saddlebrook. Substantially increasing retention storage on Saddlebrook is not possible due to the high water table and proximity of the lower aquifer. See Finding of Fact 70, below. In addition, a primary claim of the Porters in the civil action is that duration of flow under Saddlebrook's existing system exceeds 1973 levels and has resulted in expanded wetlands on the Porter property. But duration of flow and peak flow discharges are inversely related: duration of flow can be decreased only if peak flow discharges are increased. Accordingly, the only way that Saddlebrook can reduce the duration of flow onto Wiregrass to 1973 levels, as the Porters have demanded, other than increasing retention storage on Saddlebrook, is to return peak flow discharges to 1973 levels. Other Governmental Agencies' Requirements. F.A.C. Rule 40D-4.301(1)(i) provides that a permit applicant must give reasonable assurance that the surface water management system "is consistent with the requirements of other public agencies." SWFWMD has consistently interpreted this provision to be "advisory", i.e., to apprise applicants that they must also comply with other applicable laws and that issuance of an MSSW permit by the District does not relieve them of the responsibility to obtain all necessary local and other permits. SWFWMD's long-standing and consistently-applied interpretation and practice is not to require applicants to prove compliance with the regulations of other govermental agencies in order to obtain an MSSW permit. There are two primary reasons for this interpretation and practice. First, the Southwest Florida Water Management District includes 16 counties and 96 municipalities. In addition, other state and various federal agencies have jurisdiction within its territory. It is impracticable for SWFWMD to become familiar with, and to apply, the permitting and other regulations of more than 100 other agencies. Second, SWFWMD has concluded that, under Part 4 of Secton 373 of the Flordia Statutes, it does not have authority to deny a permit application based on its interpretation of another governmental agency's regulations. In any event, the evidence demonstrates that Saddlebrook has provided reasonable assurance that the proposed redesign will be "consistent with the requirements of other public agencies" as provided in F.A.C. Rule 40D- 4.301(1)(i). Limiting Condition No. 3 of the proposed permit requires that Saddlebrook must comply with Pasco County and other local requirements: The Permittee shall comply with all applicable local subdivision regulations and other local requirements. In addition the permittee shall obtain all necessary Federal, State, local and special district authorizations prior to the start of any construction or alteration of works authorized by this permit. In addition, Standard Condition No.3 ensures that SWFWMD approval will not supersede any separate permitting or other requirements imposed by Pasco County: The issuance of this permit does not . . . authorize any . . . infringement of federal, state or local laws or regulations. (Emphasis added.) Finally, the Pasco County ordinance upon which Wiregrass relies imposes requirements that are in substance identical to SWFWMD's with respect to MSSW permit applications. Saddlebrook's compliance with SWFWMD's regulations likewise would satisfy the substance of the requirements of the county ordinance. Annual Volume of Runoff. F.A.C. Rule 40D-4 (incorporating the Basis of Review) does not address, and SWFWMD does not regulate, the annual volume of runoff in open drainage basins. If annual volume of runoff is relevant under Rule 40D-4.301, as Wiregrass contends, that rule requires only that the applicant provide reasonable assurance that "the surface water management system" will not cause adverse quantity impacts. Saddlebrook's existing surface water management system has not caused a significant increase in the annual volume of runoff onto Wiregrass' property. The increase in the annual volume of runoff from Saddlebrook that has occurred over the pre-development 1973 condition has resulted from the urbanization of Saddlebrook's property. The increase in the annual volume of runoff from Saddlebrook over that existing prior to development (1973) is approximately 3.4 inches. This increase is only a small fraction of the natural year-to-year variation in runoff resulting from differences in rainfall alone. Rainfall can vary up to 30 inches on an annual basis, from 40 to 70 inches per year. The resulting year-to-year variations in runoff can total as much as 20 inches. The approximately 3.4 inches increase in the annual volume of runoff from Saddlebrook due to urbanization has caused no adverse impact to Wiregrass. The natural drainage system on the Wiregrass property has in the past and throughout its history received and handled increases in the annual volume of runoff of up to 20 inches due to rainfall differences. Such increases simply flow through Wiregrass' property. Of the approximately 3.4 inch increase in annual runoff due to urbanization, only approximately one-third of an inch is due to the filling in of bayheads by Saddlebrook's prior owner. This increase is insignificant and has not caused a substantial adverse impact to Wiregrass. Any reduction of storage resulting from the filling of bayheads will be more than compensated for under the proposed redesign. Storage on Saddlebrook's property will be increased by approximately 35 percent under the proposed condition over that existing in 1973, before the bayheads were filled. In open drainage basins, like Saddlebrook's, downstream flooding is a function of the rate of peak flow of discharge, not the annual volume of runoff. This is one of the reasons why, in the case of open drainage basins, SWFWMD regulates peak flow discharges and not the annual volume of runoff. Because Saddlebrook's proposed redesign will attenuate peak flow discharges to those levels that existed in the pre-devlopment 1973 condition, Saddlebrook has provided reasonable assurance that there will not be increased flooding on Wiregrass' property in the future. The evidence does not establish that Wiregrass has suffered, or will suffer, any adverse impact due to an increase in the annual volume of runoff from Saddlebrook as a result of the design, or redesign, of the system, or as a result of urbanization, or otherwise. It is not possible to design a surface water management system at Saddlebrook that would reduce the annual volume of runoff. Such a system, which involves the percolation of surface water from retention ponds into a deeper, aquifer system, requires a deep water table. At Saddlebrook, the water table is near the ground surface. As a result, it is not possible to store a significant quantity of water in retention ponds between storm events. In addition, the water levels in the deeper and the shallower aquifer systems at Saddlebrook are approximately the same and, therefore, there is insufficient hydraulic pressure to push the water through the confining layer between the two systems and into the deeper aquifer system.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is recommended that the Southwest Florida Water Management District enter a final order granting Saddlebrook's application for surface water management permit no. 497318.00, subject to the terms and conditions in the SWFWMD Staff Report. RECOMMENDED this 31st day of March, 1992, 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 31st day of March, 1992. APPENDIX TO RECOMMENDED ORDER, CASE NO. 91-3658 To comply with the requirements of Section 120.59(2), Fla. Stat. (1991), the following rulings are made on the parties' proposed findings of fact: Petitioner's Proposed Findings of Fact. 1.-4. Accepted and incorporated. Rejected as not proven and contrary to the greater weight of the evidence. Accepted and incorporated to the extent not subordinate or unnecessary. 7.-9. Rejected as not proven and contrary to the greater weight of the evidence. First sentence, accepted. Second sentence, rejected as not proven and contrary to the greater weight of the evidence. Accepted but not necessary. 12.-13. Rejected as not proven and contrary to the greater weight of the evidence. Accepted but not necessary. The extent of the wetland expansion is rejected as not proven and contrary to the greater weight of the evidence. The rest is accepted. However, the increased volume is due in large part to urbanization, not to the surface water management system. It also is due in part to alterations to the property done by the Porters. Accepted but subordinate and unnecessary. Accepted. However, this would occur only during a 25-year, 24-hour storm event, and there was no evidence that one has occurred or, if it has, whether Mr. Porter was there to observe it. 18.-20. Accepted but subordinate and unnecessary. Characterization "much of" is rejected as not proven and contrary to the greater weight of the evidence. Otherwise, accepted but subordinate and unnecessary. Accepted and incorporated. Rejected as not proven and contrary to the greater weight of the evidence. Rejected as not proven and contrary to the greater weight of the evidence. Rejected as not proven and contrary to the greater weight of the evidence that lichen lines, by themselves, are ordinarily are sufficient to set jurisdictional lines. 26.-29. Rejected as not proven and contrary to the greater weight of the evidence. Even if it were proven that the wetlands had expanded, it was not proven, and is contrary to the greater weight of the evidence, that Saddlebrook (and, especially, Saddlebrook's surface water management system) caused the expansion. First sentence, accepted but cumulative. The rest is rejected as not proven and contrary to the greater weight of the evidence. Accepted but subordinate and unnecessary. In any event, both factors are undeniably significant. 32.-34. Rejected as not proven and contrary to the greater weight of the evidence. Accepted but subordinate and unnecessary. Rejected as not proven and contrary to the greater weight of the evidence. Accepted but subordinate and unnecessary. Rejected as not proven and contrary to the greater weight of the evidence. 39.-41. Rejected as not proven and contrary to the greater weight of the evidence that SWFWMD does not apply it. The evidence was that SWFWMD interprets it differently than Wiregrass proposes and applies its own interpretation. Under the SWFWMD interpretation, the permit conditions requiring compliance with other legal requirements constitute the necessary "reasonable assurance." In addition, SWFWMD's review and evaluation is not complete until this formal administrative proceeding is completed, and the Pasco County ordinance has been considered as part of this proceeding. Rejected as not proven and contrary to the greater weight of the evidence. Again, SWFWMD's review and evaluation is not complete until this formal administrative proceeding is completed, and annual volume has been considered as part of this proceeding. That consideration has affirmed SWFWMD's position that, at least in this case, the proposed stormwater management system does not cause an increase in annual volume that would result in denial of the application. Accepted but subordinate and unnecessary. Rejected as not proven and contrary to the greater weight of the evidence. First sentence, accepted (although the characterization "far exceed" is imprecise) and incorporated. Second sentence, rejected as not proven and contrary to the greater weight of the evidence. Accepted but subordinate and unnecessary that no "stipulation" was entered into. But the evidence is clear that Wiregrass, Saddlebrook and SWFWMD all agreed to the use of 1973 as the point of comparison for peak flow discharges. Rejected as not proven and contrary to the greater weight of the evidence. Accepted but subordinate and unnecessary. Respondents' Proposed Findings of Fact. The proposed findings of fact contained in the Proposed Recommended Order of Respondents Saddlebrook Resorts, Inc., and Southwest Florida Water Management District are accepted and incorporated to the extent not subordinate or unnecessary. COPIES FURNISHED: Douglas P. Manson, Esquire Foley & Lardner 101 East Kennedy Boulevard Suite 3650 Tampa, Florida 33602 Stephen R. Patton, Esquire Jeffrey A. Hall, Esquire Kirkland & Ellis East Randolph Drive Chicago, Illinois 60601 Enola T. Brown, Esquire Lawson, McWhirter, Grandoff & Reeves East Kennedy Boulevard Suite 800 Post Office Box 3350 Tampa, Florida 33601-3350 Mark F. Lapp, Esquire Edward Helvenston, Esquire Assistant General Counsel Southwest Florida Water Management District 2379 Broad Street Brooksville, Florida 34609-6899 Peter G. Hubbell Executive Director Southwest Florida Water Management District 2379 Broad Street Brooksville, Florida 34609-6899
