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BROWARD COUNTY vs. SOUTH FLORIDA WATER MANAGEMENT DISTRICT AND DEPARTMENT OF ENVIRONMENTAL REGULATION, 80-001048 (1980)
Division of Administrative Hearings, Florida Number: 80-001048 Latest Update: Jan. 20, 1983

Findings Of Fact Existing Conditions Between 1952 and 1957 the United States Army Corps of Engineers (Corps) and the Florida Central and Southern Flood Control District (the forerunner of SFWMD) constructed a chain of levees, L-1, L-2, L-3 and later L-4 in eastern Hendry County, Florida. These levees which begin approximately 10 miles to the southwest of Lake Okeechobee run first east, then south and then east again for a distance of approximately 38 miles. The purpose of these levees is to shield the land5/ to the east of them from the natural sheet flow of water which comes from the west during the area's rainy season. The EAA which is protected from natural flooding consist of rich muck soils which have been successfully exploited for years by sugar cane farming. The present levees were created by excavating a "borrow" canal parallel to the southern and western sides of L-1, 2, 3 and 4. The borrow canal is no larger than was required to provide sufficient material for construction of the levees; nevertheless, the canal has a considerable water carrying capacity in the amount of 1,260 CFS 6/ at peak flow. The canal is a navigable fresh water of the state. It interconnects into other navigable canals which terminate in either Lake Okeechobee or the Miami River. The water carried by the borrow canal flows south and discharges into the Miami canal via either a pumping station designated S-8, or via the borrow canal next to L-28.7/ The water which enters the Miami canal ultimately travels to canal C-60 and then into the section of WCA-3 south of Alligator Alley (State Road 84). Flooding The rain water which once moved from west to east directly across the eastern portion of Hendry County, Florida into the EAA is now interdicted by L- 1, 2 and 3. As a result it ponds in the corner of the intersection of L-1 and L-2 (known in these proceedings as the L-1 angle). The area flooded is grass land used by Hendry County ranchers for the open grazing of beef cattle. Some of the pasture is improved, that is fertilized, but the majority of the area is unimproved range. During flood times the ranchers move their cattle to alternative pastures either to the north or to the west. The deepest flooding, when it occurs, is immediately next to the levees in the L-1 angle. The flooding has been known to reach depths as great as 10 feet and to extend westward for several miles. Because the land to the west of the L-1 angle is higher, the depth of the flooding decreases in a westerly direction. The duration of the ponding immediately in the L-1 angle has been as long as 80 days after a prolonged and heavy rainfall event. This flooding occurs despite the capacity of the borrow canal to remove 0.18 inch of flood water per day from the inundated area. When there is flooding in the L-1 angle there is also high water In the northeast corner of WCA-3A where some of the water from the borrow canal is presently discharged. During a dry season the land immediately adjacent to the present borrow canal suffers overdraining due to seepage of ground water into the canal and its resulting evaporation or conveyance south. Water Conservation Area 3A is part of a series of conservation areas established as their name implies to conserve water. Extending over portions of several South Florida counties including Palm Beach, Broward and Dade, they provide the recharge source for the Biscayne Aquifer and other aquifers which are the water supply for metropolitan South Florida. The water conservation areas are also wildlife refuges and provide natural habitats for numerous South Florida animals such as deer, alligator, and wading birds. Description of Project The Hendry County plan as described by the Corps in General Design Memorandum No. 2, 8/ envisions the construction of a flood control canal, C- 139, with two water flow control structures, S-239 and S-243. To create C-139, the Corps plans to further excavate the existing borrow canal next to L-2, L-3 and L-4 for a total distance of 37 miles. See Illustration I.* This excavation will result in the removal of 5.2 million cubic yards of earth and limestone. Some of the resulting spoil will be used to create a levee along the west side of C-139. Most of the excavation will be done by draglines on the canal banks. Upon its completion C-139 will be an immense water conveyance. At its northern end the canal will be only five feet across the bottom with a depth of 10.6 feet, but by the time the canal reaches WCA-3A it will have enlarged to a bottom width of 80 feet across and a depth of 19.5 feet. Its peak design capacity is 3,000 CFS. That is more than twice the present capacity of the existing borrow canal. Downstream from S-239 C-139 turns south to be designated C-139(S) and to gradually become increasingly shallower. This will cause a discharge pattern designed to create a sheet flow across WCA-3A. Benefits, Future Land Use It appears that when levees L-1, 2 and 3 were constructed the Corps failed to fully consider the adverse effect which would result from the impoundment of water by the new levees. According to the General Design Memorandum, Levees 1, 2, 3 and 4 were constructed in the mid 1950s to prevent flood waters originating on the then sparsely developed lands westward of the levees from contri- buting to flooding on the rich agricultural lands lying to the east of the levees. The original borrow canals were sized based on materials needed for the levee construction. The sparse economic development of the lands to the west precluded increasing the con- veyance capacity of these canals to prevent flooding on those lands. Construction of the levees and the subsequent increased de- velopment over the drainage area have aggra- vated flooding problems on the lands. Water stands on some of the land during practically the entire wet season virtually every year. As the landowners developed the land, they became increasingly vociferous about con- struction of works to alleviate the flooding for which they contend is project-induced. There is merit in their contention in that the adjacent project works adversely affected both depth and duration of flooding in the area west of Levees 1, 2 and 3. (Emphasis added) The facts presented at the instant final hearing are somewhat to the contrary, in that there was no showing of significant subsequent development west of the levees after their construction. For many decades vast family ranches have raised cattle on the mentioned lands as they continue to do today. The primary purpose of the proposed project is to now provide flood control to an approximately 261 square mile drainage basin west of the flood-causing levees.9/ With a design capacity of 3,000 CFS, C-139 can handle twice the water which drains through the present borrow canal. By way of comparison the present canal has a drainage capacity of .18 inches per day from the flooded area during a ten-year flood,10/ while C-139 has the capacity to drain .43 inches per day. This heightened discharge rate will cause land in the L-1 angle to flood less, and once flooded, to be underwater for a shorter period of time. For instance, an area which during a ten-year storm might have been submerged for 40 days prior to the construction of the project Is estimated to have an inundation period of only 10 days upon the project's completion. The significance of the reduced flooding to the landowners in the flooded area is difficult to gauge from the evidence. Because an intensification of land use would result in a lowering in the quality of the water which runs off the land and into C-139 and thence into the environmentally sensitive water conservation area,11/ the landowners supporting the project were understandably reluctant to testify that the project will allow them to use their land for more than continued cattle grazing. The testimony of Mr. Joe Hillard, a partner in Hillard Bros. of Florida, Inc., one of the larger ranches is illustrative: Q If this project, the flood control portion, were built, would your company change any of its land uses on this land that you described? A No, sir, not at all. Not with what I understand is going to be done with the project I wouldn't change anything. In response to the Hearing Officer's later inquiry, Mr. Hillard explained that the project would allow pasture land to be used for twelve months per year as opposed to the current nine months per year during a flood season. He does not anticipate grazing any more head per acre after the project. This evidence contrasted with the assumptions made by the Corps in that part of the General Design Memorandum which discusses the cost-benefit ratio of the project. The Memorandum states at p. 52: As noted previously, the existing activity within the area is predominately agricultural with major emphasis in beef cattle production. Local landowners and managers were asked to indicate the production changes they expected to make with the reduced flood hazards available under with (sic) project condi- tions. These expectations were prepared as a land use map with the basic control matrix. For the most part, these changes in land use represented more intensive types of agricultural cultivation. In some cases, existing beef pastures were expected to be replaced with sugarcane, truck crops, and citrus production. The majority of the changes were an upgrading of existing beef cattle operations. Such upgrading was affected (sic) by planting the more pro- ductive types of pasture such as clover and grass combinations, and the application of additional fertilizers and supplemental water. These expectations were assumed to exist under favorable cultivation conditions. Because of the nature of soil conditions in the project drainage basin, sandy with poor nutrient and water retention ability, it is unlikely that land use in the 261 square mile drainage basin will change significantly. As predicted by Mr. Hillard, it is likely that all the project would do is allow more grazing time on land which is now periodically flooded. Since it is not the function of this proceeding to inquire into whether the purported cost- benefit ratio of the project is accurate, no findings will be made concerning that issue. Project Permitting History The Hendry County portion of the Central and Southern Florida Flood Control project for flood control west of levees 1, 2 and 3 was authorized by the Congress of the United States in the Flood Control Act of October 27, 1965. The Army Corps of Engineers is the actual builder of the project, but SFWMD is the local sponsor and is the Corps' agent in applying for the necessary permits from DER. The Department as the permitting agency is in a curious position here. Its Bureau of Water Resources (BWR) was responsible for the State Public Works Program through which Florida requested Congress to fund the Hendry County Project. Mr. Charles Littlejohn who was head of the Bureau in 1976 had the responsibility of lobbying in Washington for funding of the project. The DER through its Bureau of Permitting is now asked to pass on the validity of a project which the BWR has so vigorously promoted. The Department's uncomfortable posture was recognized by its permitting staff. In a memorandum dated March 9, 1979 to Mr. E.D. "Sonny" Vergara, Mr. Forrest Fields at DER wrote: I told Mr. Brown, as I told you yesterday that I felt rather awkward in reviewing for permitting a project which the agency had endorsed for the public works list." Every year projects being sponsored for federal approval are reviewed by a process In the Division of State Planning called the A-95 Clearinghouse.12/ The Hendry County Project had a checkered history there. Serious objections concerning the environmental impact of the project were raised; nevertheless, DER through the BWR continued to seek and was successful in obtaining federal funding. On November 15, 1978, SFWMD filed an application with DER for the requisite permits to begin construction. During the course of DER's review of the project several issues arose between the parties. Among them were: Whether local approval pursuant to Section 253.124, Florida Statutes would be required? Would an exception from dissolved oxygen (DO) standards be necessary? Whether local water quality standards would apply if they were stricter than state standards? Local Approval As early as February 19, 1979, DER noted that plans submitted by the applicant proposed the placement of fill in waters of the state. In a letter to Mr. Lee M. Brown of SFWMD, Mr. Forrest Fields, the DER permit processor, observed: Second, on page 2/11 of your drawings, you indicated that approximately 5,800 cubic yards of fill material will be placed water- ward of ordinary mean high water. I pre- sume that this fill is associated with structures S-243 and S-239. Pursuant to Section 253.124, Florida Statutes, approval of this filling by resolution of the local government is required. To do this I will, upon receipt of the Department of Environ- mental Regulation field report, summarize and send this to the Hendry County Commission. The Commission will have to consider this report, and, by vote, adopt a resolution approving the project. I will send you a sample resolution. The requirement of local approval was reiterated numerous times. In March, 1979, Mr. Fields sent a staff report of a biological survey of the project to the Hendry County Commission for consideration in their approval of the project. During a meeting on March 21, 1979 in the DER Secretary's office representatives of SFWMD were told that local approval would be required. On April 10, 1979 the County Commissioners of Hendry County gave their approval to the project. In correspondence to Mr. Charles Lee of the Florida Audubon Society, Secretary Jacob D. Varn noted that the permit applications were still incomplete because local approval for filling associated with the two water control structures had not yet been received by DER. During a public meeting held on May 22, 1979, the County Commissioners of Broward County, after three and one-half hours of testimony, voted 6-0 against approving the project as it related to fill in Broward County. Subsequent to that vote the Corps and SFWMD asserted that local approval by Broward County was not required. In response to this assertion Mr. Charles Littlejohn, on behalf of the Secretary, requested a legal opinion from DER's General Counsel. On October 30, 1979, General Counsel's Legal Opinion 79- 72 concluded that the Department could assert Chapter 253 jurisdiction over the project and therefore "local approval" is a statutory requirement for its permitting. On March 17, 1980 Mrs. Evelyn Jackman of Jackman and Sons, Inc., one of the major ranchers in the project drainage basin, wrote to Governor Graham to urge the rapid approval of the project. Her correspondence was forwarded to DER for an appropriate response. Ms. Victoria J. Tschinkel as Assistant Secretary noted in her reply on April 3, 1980 that: Pursuant to Section 253.124(3), Florida Statutes approval must be obtained from the County Commissioners before we can complete the processing of a permitting application for fill in navigable waters. Approval has not been received from Broward County and there Is fill proposed for the Broward County portion of the project. Ms. Tschinkel did, however, assure Mrs. Jackman that: The Department of Environmental Regulation is sympathetic to the problems outlined in your letter, and for that reason the Depart- ment has made this project part of its public works package given each year to Congress. We still support this as a public works pro- ject and for that reason we are attempting to work out the permitting problems as ex- peditiously as possible. Shortly after Ms. Tschinkel's letter was sent there was another meeting in the Secretary's office to discuss the project. Mr. Lotspeich's interoffice memorandum outlines the Department's new position as it related to local approval. In addition, the issue of what constituted fill pursuant to Chapter 253, Florida Statutes, for local approval purposes was discussed. Helen Setchfield also partici- pated in this discussion. After Helen and I looked more closely at the project, it appeared that only a concrete structure (S-239) was to be placed waterward of OHW.13/ We both agreed that in past permitting practices we had not required local approval for the construction of structures waterward of OHW, but only when fill to extend existing lands or create new lands was involved. Since the application drawings did not clearly show the relation of the fill and structure relative to OHW and sheet 2 of 11 clearly indicates that fill will be placed "below MHW" Forrest must have assumed that local approval would be required if the canal was determined to be under Chapter 253, Florida Statutes jurisdic- tion. GCO-79-72 from Randie Denker indicated that the Department can assert Chapter 253, Florida Statutes jurisdiction in the canals and therefore local approval would be required. It would appear that there was really no clear understanding as to what the "fill" consisted of in the case of structure 239. Conversation with Mr. Walker [counsel for SFWMD] and Messrs. Parsons [counsel for Alico and other landowners] and Davis [SFWMD] indicated that there was no intention to place fill in the canal waterward of OHW and that the concrete structure would span the entire canal width. Since the application drawings did not clearly show the relation of the structure and fill re- lative to existing OHW, Mr. Walker said he would provide new drawings which would show this. Helen and I discussed the situation and we scheduled an appointment to talk the problem over the (sic) Terry Cole. It was agreed at the meeting that simultaneous "intent" letters would be sent on May 5, 1980 from permitting and the exception review people. May 16, 1980 DER entered into a Stipulation with SFWMD which states in its entirety: The SOUTH FLORIDA WATER MANAGEMENT DISTRICT and the DEPARTMENT OF ENVIRONMENTAL REGULA- TION for purposes of this proceeding hereby stipulate and agree that: The DEPARTMENT OF ENVIRONMENTAL REGULA- TION has jurisdiction under Chapter 253, Florida Statutes, to require permits autho- rizing construction and other activities described in the application which is the subject of this proceeding. None of the activities or construction, including the construction of the proposed Spillway S-239, as described in the appli- cation which is the subject of this pro- ceeding, constitute construction of islands or an addition to or extension of existing lands and islands so that approval of local governments as described in Section 253.124, Florida Statutes, is not required. This Stipulation is executed by counsel for each party on the date shown. On May 20, 1980 coordinated letters of intent to grant permits for the construction of the project were issued. Pursuant to the Stipulation local approval was no longer being required by DER. Alternative Site Specific Criteria After receipt of SFWMD's permit application for the construction of C- 139 and associated structures, DIR noted that it did not have adequate data on dissolved oxygen. In correspondence dated March 9, 1979, Mr. Forrest Fields said: Fourth, the dissolved oxygen data are not adequate. The available data were col- lected during daylight, only, and these data include occasional concentrations of less than 4.0 mg/l. In an effort to re- solve these deficiencies so that reasonable assurances may be provided, you, Walt Dineen, and I will discuss the South Florida Water Management District data on Thursday, March 15. The results of the March 15, 1979 meeting were memorialized by Mr. Fields in a file memorandum dated March 19, 1979. The memorandum stated in pertinent part that: On March 15, 1979, Mr. Lee Brown, Mr. Walt Dineen, and Mr. Fred Davis, from SFWMD, called to discuss the staff's request for "reasonable assurance" re. the Department's water quality standards. Mr. Davis, the applicant's chief chemist, said that, throughout the Everglades, in both canals and conservation areas, the water quality standards for both conductivity and dis- solved oxygen are frequently violated. He asserted that this is typical of the area. He believes that these data represent natural background. The situation regarding affirmative, reasonable assurance appears to be this: widespread and frequent observations of DO data which are less than the minimum for Class III waters commonly occur within the existing L-1, L-2, L-3 canals. The increase in depth associated with C-139 is predicted to exacerbate existing stress- es on the DO regime.... However, the SFWMD's response does not constitute reasonable assurance re. other Class III standards. The District's DO and conductivity data may conceivably supply assurances that these standards will be violated in C-139. (Whether background DO and conductivity violate the standards may become important.) The District appears to have two alternatives: 1) attack the Class III standard; 2) apply for variances for, at least, DO and conductivity. A follow-up meeting was held on March 21, 1979. Again, in a file memorandum dated March 28, 1979 Mr. Fields wrote: Consideration of reasonable assurance began at the March 15, 1979, conversation among Messrs. Brown, Davis and Fields. According to the SFWMD, widespread and frequent violations of the Class III water quality standard for dissolved oxygen, as contained in Chapter 17-3, F.A.C., occur throughout the Everglades, in the canals, agriculture areas, Lake Okeechobee, and the conservation areas. The existing borrow canals follow this pattern. The SFWMD alleges that this condition is natural back- ground. They agree that it is probable that any existing DO stresses exist in the borrow canal will be exacerbated in the proposed C-139. However, both the former and present editions of Chapter 17-3 F.A.C. allow for exceptions for natural background. The SFWMD will review these rules to determine which regulatory approach will be taken. In addition, the SFWMD will supply to DER data for the "benchmark" station in the L-28 canal and at Everglades National Park to demonstrate lower back- ground concentrations of DO. Furthermore, the SFWMD will apply, per Ch. 403.087, F.S., for a temporary operating permit for the completed structure. Conditions governing private connections and incor- porating BMPs may be included in the TOP. On April 5, 1979, SFWMD submitted in support of its original permit application a document called Evaluation of Natural Background Dissolved Oxygen in Conservation Area 3-A, South Florida. This evaluation received unfavorable reviews at. DER. Landon P. Ross, chief biologist, wrote in an April 9, 1979 memo that: I have reviewed the data provided by SFWMD regarding background DOs in the Everglades area and have the following comments: Indication that DOs are not harmful to local organisms are, in a legal sense, irrelevant to the question. The data provided give evidence of the occurrence of low DOs in the area. Since the measured low DOs seem to be from artificial drainage channels, they can hardly be supposed to be "natural". The measures that SFWMD provided, however, do not seem too different from the values that I would expect to find in a natural swamp habitat. The proposed "standard" cannot be logically derived from the DO measurements provided. This Evaluation was later submitted in support of first Petition for Exception noted infra. In his review of the data Mr. Fred Bartleson at DER wrote:14/ The data submitted by the South Florida Water Management District does not justify the requested exception for dissolved oxy- gen criteria for the Hendry County Project. The petition alleges that D.O. concentra- tions lower than 1.0 mg/l occur in the re- ceiving waters of Conservation Area 3A. However, the data submitted from that area indicate a minimum value of 2.3 mg/l. The value cited in the petition of less than 1.0 mg/l was recorded in the L-3 borrow canal adjacent to the conservation area. This canal drains an agricultural area. Similar data from the L-28 east canal which is less affected by cultural activity depicts minimum D.O. values between 3 - 2 mg/l. The low D.O. values found naturally in fresh- water wetlands during the warmer months ob- viously result in stress to the biota. The introduction of larger quantities of water from the proposed Hendry County Project, which is anticipated to have lower D.O. values as well as nutrients and pesticides from agricultural runoff, could adversely affect the ecosystem. The proposed exception allowing discharge of water with not less than 1.0 mg/l for more than two consecutive hours in any 24-hour period is arbitrary and not supported by data. It may well be that an exception could be granted for some lowering of the D.O. criteria with time constraints. However, more defini- tive and conclusive data are required to in- sure that this action would not cause adverse effects. The burden of supplying this infor- mation should rest with the petitioner. His views were supported by Messrs. Kevin Edwards, Vernon Myers, and G. J. Thabaraj. Mr. Edwards also noted the difference in DO readings between the WCA- 3A and the borrow canals. SFWMD filed a Petition for an Exception on July 23, 1979. The Petition alleged that the receiving waters of the proposed discharge are located in WCA-3A and that due to natural causes that portion of WCA-3A which will receive the discharge does not meet the state standards for DO as set out in Section 17-3.121, Florida Administrative Code. The DO levels of the proposed discharge are alleged to be similar to those levels already present in the water conservation area. In response to the Petition DER requested more information by a letter from Stephen Fox dated August 29, 1979. The letter requested: Data which supports the contention that the condition of the waters is the re- sult of natural causes, that is, there is an absence of man-induced alteration; or Data which supports the contention that the condition of the waters is the re- sult of man-induced causes which cannot be controlled or abated with technology or management practices. Data which supports the contention that the biota have not been adversely af- fected or will not be affected adversely. The data submitted with the application did not address the possibility that the low dis- solved oxygen levels may be caused by the practice of pumping water off the agriculture areas during the summer wet season. Compari- son with similar subtropical, undisturbed aquatic environment should be made. The dis- solved oxygen data should be compared with pumping schedules and with dissolved oxygen values of water pumped. Comprehensive water- shed and land use data is needed for a thorough review. Further, the data submitted did not support the contention in the petition of a corre- lation between C.A. 3A and canals L-3 and L-28. Also, the contention that in C.A. 3A dis- solved oxygen concentrations were below 1.0 mg/l were recorded was unsupported. The data array was not adequate in terms of distri- bution and frequency of sampling, to demon- strate that the dissolved oxygen regime ap- proaches the proposed alternative criteria. On October 2, 1979, E. D. Vergara summarized the status of the SFWMD application for the DER Secretary, Jacob D. Varn. His memorandum with respect to dissolved oxygen states: ... (permits) originally requested under old 17-3 rules, it was found quality assurances could not be made due to a naturally occurring condition of low DO. The Department requested information sup- portive of the low DO background, but due to differences in opinions among the biologists, the district elected to re- quest an exception under the provisions of the new 17-3 rule instead. Additional information has now been requested by the Department to support the request for an exception, and the District is cur- rently putting this together. It is the general feeling that with this additional data, granting the exception should be possible. SFWMD responded to Mr. Fox's letter above by submitting in the Spring of 1980, an Amended Petition for Exception from Criteria. In its Amended Petition the District abandoned the comparison, found in the original petition, of the proposed discharged waters' dissolved oxygen levels to the levels found in the water conservation district. Instead the District concentrated on a comparison of the dissolved oxygen levels in the proposed discharge waters to the levels in the relatively clean canals in the South Florida area, specifically the L-28 canal system. The District proposed that as an alternative to Class III standards the following criterion be established: During any 24-hour cycle the dissolved oxygen concentration within the photic zone shall exceed 1.0 mg/l, except during the extreme low point when values shall not be less than 1.0 mg/l for more than two consecutive hours. (Emphasis added) Accompanying SFWMD's Amended Petition was a report (Supporting Report) dated February, 1980, which provided a voluminous compilation of data to justify the alternative standard proposed.15/ On April 8, 1980, Ms. Helen Setchfield sent a memorandum to DER staff requesting that they review the Amended Petition and report back to her within five days. Also on April 8, 1980, after a meeting attended by both SFWMD representatives and DER representatives, it was decided that DER would issue coordinated letters of intent on May 5, 1980 for both the exception and the dredge and fill applications. In spite of the decision to issue letters of intent, DER permitting staff were not satisfied with the concept that ban-made canals were "natural" background or that the proposed DO standard was reasonable. On April 16, 1980, Rick Lotspeich wrote to Suzanne Walker, Chief of the Bureau of Permitting, that: I have reviewed the referenced "request for exception" and it appears that the petition and supporting report are suf- ficiently complete to allow evaluation of the merits of the request. It would appear that the proposed dis- solved oxygen standard of 2.0 mg/l over 24 hours and 1.0 mg/l "during the extreme low point" for not more than two hours, is excessively low and not warranted by the data presented. A review of the data from figures 4 and 5 generally indicate that the following standard would be appropriate: Dissolved Oxygen: The concentration should not average less than 4.0 mg/l in a 24-hour period and not less than 3.0 mg/l except during the months of June--September, when the concentra- tion shall not average less than 3.0 mg/l in a 24-hour period and never less than 1.0 mg/l. Later, after having received comments from Rick Cantrell and Bob Siciler, Mr. Lotspeich wrote to Ms. Walker the following: My recollection from reading the request for exception was that SFWMD had indeed recognized the fact that the canals and their design had contributed to the de- pressed DO values of the water in them. Pursuant to Subsection 17-3.031(1), Florida Administrative Code, there may be a consideration for "man-induced causes which cannot be controlled or abated I am in full agreement with Cantrell and Siciler's discussion of the adverse impacts that canals in general, and the specific canal involved in this project, have on water quality and biological resources. However, I disagree with the conclusions that they reached. Clearly, there are extenuating circumstances involved in this case which set it apart from other dredge and fill cases. In light of these circum- stances, the fact that the depressed DO levels have resulted from man-induced causes which cannot be controlled, and Cantrell and Siciler's own statement that approval of this project has little probability of worsening the existing water quality of L-2, L-3 and WCA-3, I would recommend that the exception be granted. However, the alternate DO standard which I recommended in my previous memo is still applicable. (Emphases added. The "extenuating circum- stances" were never explained.) Subsequently, on May 20, 1980, the Department issued a coordinated letter of intent to grant an exception but for the standard proposed by Mr. Lotspeich, not that requested by the Water Management District. Dissolved Oxygen and Exception Section 17-3.121(14), Florida Administrative Code requires that discharges into fresh waters of the state must exhibit dissolved oxygen concentrations of 5.04 mg/l or more. Normal daily and seasonal fluctuations above that level must be maintained. Dissolved oxygen in certain concentrations is required for aquatic life. The amount of oxygen contained in water is subject to numerous variables, many of which are interrelated. They include: amount of sunlight entering the water, ability of the water to transmit light, photosynthetic activity of aquatic plants, water temperature, mechanical oxygenation, mixing with other water which may have either a higher or lower dissolved oxygen content, depth of water, rate of oxygen consumption by resident biota, and time of day. It is undisputed that during certain seasons and times of day the water in the existing borrow canal does not meet the state dissolved oxygen standard. Readings as low as 0.9 mg/l have been obtained there. These low readings usually occur in the months of heavy rainfall, primarily July through September. See the data on Figure 4 of SFWMD's Supporting Report. Similar, though not so low measurements have been obtained in neighboring man-made canals such as L-28. L-28 has been used by water quality experts as a "benchmark" for canal water quality since it does not receive large amounts of runoff from agricultural areas where pollutants such as fertilizers are used. There are numerous times during a given year that the dissolved oxygen levels in L-28 are below the 5.0 mg/l state standard. It is also possible to find at least two locations in WCA-3A wetlands where dissolved oxygen readings are below Class III standards. At Gauge 3-2 in the northwest corner of WCA-3A near where the project would discharge, dissolved oxygen levels have varied from 2.3 mg/l to 10.8 mg/l; however, the mean value for the measured levels has been 5.5 mg/l as reported on Table 2 of the Supporting Report.16/ Unfortunately, the data regarding dissolved oxygen concentrations in the proposed discharge area are scant. This paucity was recognized by the Supporting Report which states at page 6: "No systematic study of the dissolved oxygen conditions or requirements for fresh water wetlands in general, or WCA-3A in particular, have yet been conducted." Despite the limited data on WCA-3A, certain comparisons between DO readings in it and in the borrow canal which would discharge into the area can be made. Readings taken at Gauge 3-2 do not sink to levels as low as those found in L-3. Compare Figure 4 of the Report to Table 2. The minimum readings taken in L-3 were during those periods of greatest discharge. If the discharge from the existing borrow canal were presently sent into the area of Gauge 3-2 during months of peak discharge, the waters entering WCA-3A would have a lower dissolved oxygen concentration than would exist naturally in the area. It is not surprising that water in the borrow canal exhibits unusually low dissolved oxygen levels. The levee sides limit reaeration which could occur due to wind movement. The surface-to-volume ratio is also unfavorable. Much oxygenation occurs at the interface between the water and surrounding air, but because the canal is relatively deep compared to its surface area, the proportion of water coming into direct contact with the air is low.17/ The depth of the photic zone, i.e., the section of water penetrated by light, is limited due to the naturally high color of canal water. Construction of C-139 will add somewhat to a lowering of dissolved oxygen levels in the entire canal water column. To increase its conveyance capacity, the existing borrow canal will be deepened significantly, particularly in its southern reaches. This deepening will result in a lowering of the ratio between the area of water surface to the depth of the canal. No mathematical data were presented by which the lowered ratio can be computed; however, an examination of Plates A-24 and A- 25 of the General Design Memorandum indicates that completed C-139 will contain a higher ratio of water below the photic zone than is presently contained in the borrow canal.18/ This is true only during those times when the canal is relatively full of water. As the canal level drops during a drought the photic zone will approach the canal bottom in the shallower sections. Both SFWMD and DER have proposed site specific DO alternative standards. These have been set out in the foregoing discussion of the permitting history. There is a significant difference between the proposals. SFWMD's proposal includes only the waters contained in the photic zone. It fails to recognize that during times of discharge, the waters of C-139 which are deposited in WCA-3A will not be only those of the photic zone, but will come from the entire water column of the canal. While SFWMD's standard might be acceptable for C-139 when it is in a no discharge state, the standard is completely unacceptable when the canal is discharging. Neither the standard proposed by DER nor SFWMD recognizes the difference between the dissolved oxygen regime which can be predicted for C-139 and that presently existing in WCA-3A. The data submitted would justify an exception from the present 5.0 mg/l Class III standard. There are certainly times when both the water existing in relatively unpolluted canals and in the water conservation area contain less than the present minimal content of dissolved oxygen. When C-139 is not discharging an exception, which would have a range now exhibited by the existing borrow canal, would be justified for the new canal. Sufficient data was not presented here to suggest the precise figures for such an exception. The information given for L-3 for instance, is compiled from samples taken only once during a given day. The water depth of the sample is not given. Accurate data would account for the diel variation and the effect of water depth on each sample. Without data which gives a daily average, it is impossible to determine if the water either standing in, or discharging from C- 139 will meet any proposed alternative criterion. For the same reason the data obtained for the present DO concentrations in WCA-3A is incomplete for establishing appropriate levels for discharge waters entering that area. The establishment of site specific alternative criteria must await the submission of more complete dissolved oxygen readings from the applicant. One of the elements in considering whether to grant an exception to established standards is whether the existing biota have adapted to the background DO levels. The proof here shows that the fish and other biota now living in the borrow canal either tolerate or have adapted to the present low DO regime there. It has also been proven that the biota in WCA-3A are tolerant of the naturally occurring low DO levels in that area. It was not shown how they would respond to a massive influx of low DO water when C-139 would be discharging. Hydroperiod in WCA-3A The northwest corner of WCA-3A, where C-139 and C-139(S) will discharge, has a higher ground elevation than that of the southern portion of the water conservation area. The highest elevation in the extreme northwest corner is approximately 17 feet above mean sea level (MSL). It tapers down to approximately ten feet MSL at the southern boundary of WCA-3A. The project is designed to facilitate the sheet flow of discharge water from the northwest area towards the southeast with an ultimate destination being flow into the Miami canal. The construction of the Miami canal, C-123, which runs on a northwest- southeast diagonal across the area, causes overdrainage of the northwest section. The borrow canal along Alligator Alley also contributes to excess runoff. This overdrainage has shortened the hydroperiod in the northwest corner from approximately 9 to 10 months to approximately 5 to 7 months. "Hydroperiod" is the span of time during which land is inundated by ponded water. The shorten hydroperiod has a profoundly destructive impact on the natural environment. The muck soil when not submerged oxidizes at an accelerated rate. At the present time the rate of oxidation in the northwest corner is more rapid than the replacement rate. Since the natural hydroperiod has been altered muck fires have been more severe and frequent. These fires destroy existing tree islands which dot the Prior to 1974 WCA-3A received discharges from the waters of the L-1, 2 and 3 borrow canal. The outlet of the canal at L-4 was determined to be inadequate for flood control purposes in the L-1 angle. To increase the discharge rate of the borrow canal culverts G-88 and G-89 were installed at the L-3/L-4 intersection in October of 1974. G-89 directs part of the flow from the L-3 canal into canal L-28 west, and then into pumping station 5-140 and into C- 60 (parallel to Alligator Alley). G-88 directs another part of the flow from the L-3 canal into the L-4 borrow canal and then into S-8 where it is pumped into the Miami canal. Rather than being allowed to flow in a shallow sheet across the water conservation area, the direct water flow is now sent southeast in canals for ultimate discharge outside the area. This waste would be eliminated by the proposal to have C-139 discharge into WCA-3A via C-139(S). There is no dispute that more water is needed annually in the northwest corner of the water conservation area. What is at issue here is the timing of placing additional water there. Generally when there is flooding in the L-1 angle and C-139 would be discharging at its maximum rate there is already flooding in WCA-3A. Rainstorm events are somewhat regional and cover both areas. The applicant estimates that if the volume of water discharged by C-139 in a two-week period were to be instantaneously spread over the northwest corner of WCA-3A 20/ it would raise the water stage by 0.4 feet. This would occur during a one in ten year storm. At that time the wildlife in the water conservation area would already be stressed by high water levels. A 0.4 foot increase in stage could kill deer and other terrestrial animals and destroy alligator nests, but it also could benefit the more aquatic animals. The result of this increase cannot be accurately predicted on the data supplied by the applicant.21/ While expert witnesses on behalf of the applicant were willing to express an opinion that the influx of drainage water from C-139 would be beneficial, the opinions were simplistically based on the unsupported assumption that because WCA-3A currently suffers from overdrainage, any additional water at any time would be beneficial. It is possible that those opinions were based on studies conducted which prove that a discharge of water such as will come from C-139 may create a beneficial increase in the marsh hydroperiod. Unfortunately, no evidence of the existence of such studies is in this record. The applicant's expert witnesses' opinions are therefore given little weight. In the present situation WCA-3A receives some water from the borrow canal during the dry season when additional water is most beneficial. At the expense of overdraining the land west of the borrow canal, ground water seepage now enters the canal and travels south through L-1, 2 and 3. After the construction of S-239, designed to prevent overdrainage, any possible flow into WCA-3A during dry periods will be cut off. No evidence was presented on what quantity of water WCA-3A will lose during a dry season due to S-239. Also the record does not reflect what effect that reduction will have on biota in the water conservation area. S-239 and Fill When the level of water in the borrow canal drops below the nearby water table, there is groundwater seepage laterally into the canal. If C-139 were to be constructed without any water control devices, it would exacerbate the overdrainage because it will be a far more efficient conveyance than is the borrow canal. S-239 has been designed to prevent this overdrainage. The structure will be located in Broward County. On May 22, 1979 the County declined to give its approval of the use of any fill, as the term is used in Section 253.124, Florida Statutes, for the construction of this project in Broward County. The Department of Environmental Regulation has not maintained a consistent unwritten policy on what is "fill" in navigable waters of the state.22/ Testimony from past and present Department employees indicated that at times a "use" concept was employed to determine what was fill. If additional dry land were created which would be used for commercial purposes, then the newly created land was called fill which required local approval. At other times use was unimportant. The test was whether or not the result of the additional material would be moving the point, at which the high water mark intersected the land, in a waterward direction. It is found that what constituted fill in past permit cases depended upon the personal interpretation of each Department employee. S-239 as proposed is a massive structure which will cost 1.32 million dollars 23/ to build. It will contain 11,000 cubic yards of fill and backfill; 530 cubic yards of 1' by 1' pieces of stone rip-rap; 1,230 cubic yards of concrete and 647,000 pounds of cement. 153,800 pounds of reinforcing steel will be required. The structure will be over 50 feet high and will span C-139 where it is 60 feet wide. Each of the two vertical lift gates which control the water flow will be 27 feet wide. See Illustration II.* In between them will be a concrete pier three feet wide and approximately 38 feet long. The cement bottom of the structure will rise from an elevation of 8.0 feet MSL to a crest of 3.3 feet MSL for a total height of 11.3 feet. In order to allow service vehicles to pass across the canal a bridge 13 feet wide will span from one bank to the other. This bridge will support large trucks. The stone protection provided for in the plans consists of 1 foot square pieces of rip-rap to be placed 40 feet immediately upstream from the control gates and 30 feet immediately downstream of the gates. The purpose of this protection is to prevent erosion of the canal bottom and sides where the water flows by at a relatively high velocity. The majority of rip-rap will be placed below the ordinary high water mark. Local Water Quality Standards The issue of local water quality standards arose late in the permitting process. DER had already issued two letters of intent to SFWMD before the Department gave consideration to standards promulgated by Broward County. It appears from the record that the Broward County standards were formally brought to DER's attention through the County's Petition for Formal Hearing filed on June 3, 1980. On June 26, 1980, DER issued an amended letter of intent which said: This letter is an amendment of the letter of intent to issue signed by the Department on May 20, 1980. In that letter, the Depart- ment stated: "This intent to issue is contin- gent upon the applicant being granted an exception from the criteria for dis- solved oxygen, for Class III waters, pursuant to Section 17-3.031, Florida Administrative Code." The preceding paragraph is hereby amended to include a provision that the applicant must obtain relief from the dissolved oxygen stan- dards that appear in Section 27-5.072(19), Broward County Code, through a variance or other legal mechanism, in addition to the exception from state standards for dissolved oxygen. Section 27-5.072(19), Broward County Code, states that DO is to have a "daily average not less than 5 mg/l; single reading never less than 4 mg/l. The May 20, 1980, letter also contained a paragraph that read: "However, should the Department grant an exception from the dissolved oxygen criteria pursuant to Section 17-3.031, Florida Administrative Code, the Division intends to issue the permit." This paragraph is hereby stricken and the following paragraph substituted: "If the Department grants an exception from the State dissolved oxygen criteria pursuant to Section 17-3.031, Florida Administrative Code, the Division intends to issue a conditional permit which will only become valid upon the granting of relief by Broward County from its existing local standards for dissolved oxygen." The Department is taking this position upon consideration of Section 403.182(6), Florida Statutes, which requires the Department to en- force all stricter or more stringent rules, regulations or orders in the jurisdiction where they apply. It is the Department's position that it is without discretion to grant relief from Broward County's local standard for dis- solved oxygen. By its Petition the County alleged that it has an approved local pollution control program and that the proposed project will violate its local standards for dissolved oxygen and nutrients found in Sections 27-117(b)(9) and 27-117(11) of the Broward County Code.24/ Neither SFWMD nor the Corps has applied to the Broward County Environmental Quality Control Board for either a license under Chapter 27 of the County Code or for a variance from the standards established therein. On April 20, 1972, the Florida Department of Pollution Control (the predecessor of the Department of Environmental Regulation) gave temporary and conditional approval for six months to the Broward County Pollution Control Program. This approval provided that the County has full authority to enforce its own laws, rules and regulations, provided that they must be as strict or stricter than those of the State. The County was also required to modify its rules if the State subsequently adopted the regulations in conflict with those of the County. On November 7, 1972, the Department of Pollution Control gave Broward County full and final approval pursuant to Section 403.182, Florida Statutes. Subsequently, in 1974 and 1976 the State and Broward County entered into new agreements. These agreements were the result of DER's desire to make uniform all its agreements with all qualified local programs. The Broward County pollution control program including the portion administered by the Environmental Quality Control Board, continues to be an approved local program as defined at Section 403.182, Florida Statutes.

Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED: That the Department of Environmental Regulation enter an Order denying South Florida Water Management District's application for a water quality permit and for a dredge and fill permit. DONE and RECOMMENDED this 13th day of October, 1982, in Tallahassee, Florida. MICHAEL PEARCE DODSON Hearing Officer Department of Administration Division of Administrative Hearings Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32301 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 13th day of October, 1982. * NOTE: Illustration I, noted in paragraph 8 and Illustration II, noted in paragraph 49 are not a part of this ACCESS document. Illustrationn II is available for review in the Division's Clerk's Office.

Florida Laws (6) 120.57120.60253.12403.087403.18290.803
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ANGELO`S AGGREGATE MATERIALS, LTD. vs SUWANNEE RIVER WATER MANAGEMENT DISTRICT, 01-004383RX (2001)
Division of Administrative Hearings, Florida Filed:Live Oak, Florida Nov. 09, 2001 Number: 01-004383RX Latest Update: Oct. 22, 2002

The Issue Whether Rules 40B-1.702(4); 40B-4.1020(12) and (30); 40B-4.1030; 40B-4.1040(1)(b) and (c); 40B-4.2030(4); 40B-4.3000(1)(a); 40B-4.3010; 40B-4.3020; 40B-4.3030; 40B- 4.3040; and 40B-400.103(1)(h), Florida Administrative Code, of the Suwannee River Water Management District, are an invalid exercise of delegated legislative authority for reasons described in the Second Amended Petition to Determine Validity of Rules.

Findings Of Fact Stipulated Facts Angelo's is a Florida Limited Partnership, whose address is 26400 Sherwood, Warren, Michigan 48091. The District is an agency of the State of Florida established under Chapter 373, Florida Statutes, with its address at 9225 County Road 49, Live Oak, Florida 32060. Angelo's owns property in Hamilton County approximately four miles to the east of Interstate 75 and to the north of U.S. Highway 41, immediately to the east of the Alapaha River. Angelo's conducts commercial sand mining operations on a portion of its property pursuant to various agency authorizations, including an Environmental Resource Permit (ERP) issued by the Florida Department of Environmental Protection (Department), Permit No. 158176-001, and a Special Permit issued by Hamilton County, SP 98-3. The ERP was issued by the Department pursuant to its authority under Chapter 373, Part IV, Florida Statutes. Angelo's mining operations constitute a "mining project" as that term is used in Section II.A.1.e of an Operating Agreement Concerning Regulation under Part IV, Chapter 373, Florida Statutes, and Aquaculture General Permits under Section 403.814, Florida Statutes, between the District and the Department (Operating Agreement). The Operating Agreement has been adopted as a District rule pursuant to Rule 40B-400.091, Florida Administrative Code. Angelo's has filed with the Department an application to modify its ERP to expand its sand mining operations into an area of its property immediately to the west of its current operations (the "proposed expanded area"). Angelo's application is being processed by the Department at this time. Angelo's ERP modification application is being processed by the Department under the Operating Agreement. The District has asserted permitting jurisdiction over the proposed expanded area because the proposed sand mining activities would occur in what the District asserts to be the floodway of the Alapaha. The District asserts that an ERP would be required from the District so that the District can address the work of the district (WOD) impacts. Petitioner has not filed a permit application with the District regarding the project. It is Petitioner's position that to do so would be futile. The Challenged Rules The rules or portions thereof which are challenged in this proceeding are as follows: Rule 40B-1.702(4), Florida Administrative Code, reads as follows: (4) A works of the district permit under Chapter 40B-4, F.A.C., must be obtained prior to initiating any project as outlined in (3) above within a regulatory floodway as defined by the District. Rule 40B-4.1020(12) and (30), Florida Administrative Code, read as follows: (12) "Floodway" or 'regulatory floodway" means the channel of a river, stream, or other watercourse and adjacent land areas that must be reserved in order to discharge the 100-year flood without cumulatively increasing the 100-year flood elevation more than a designated height. Unless otherwise noted, all regulatory floodways in the Suwannee River Water Management District provide for no more then one-foot rise in surface water. * * * (30) "Work of the district" means those projects and works including, but not limited to, structures, impoundments, wells, streams, and other watercourses, together with the appurtenant facilities and accompanying lands, which have been officially adopted by the governing board as works of the district. Works of the district officially adopted by the board are adopted by rule in Rule 40B-4.3000 of this chapter. Rule 40B-4.1030, Florida Administrative Code, reads as follows: The implementation dates of this chapter are as follows: January 1, 1986 for Rule 40B- 4.1040(1)(a) which requires persons to obtain surfacewater management permits. April 1, 1986 for Rule 40B- 4.1040(1)(b) and Rule 40B-4.3040 which require persons to obtain works of the district development permit if the proposed development is in one of the following areas adopted as a work of the district. The Alapaha River and its floodway in Hamilton County, Florida; The Aucilla River and its floodway in Jefferson, Madison, or Taylor counties, Florida; The Suwannee River or its floodway in Columbia, Hamilton, Lafayette, Madison, or Suwannee counties, Florida; or The Withlacoochee River and its floodway in Hamilton or Madison counties, Florida. (c) July 1, 1986 for Rule 40B-4.1040(1)(b) or 40B-4.3040 which require persons to obtain work of the district development permit if the proposed development is in one of the following areas adopted as a work of the district. The Santa Fe River and its floodway in Alachua, Bradford, Columbia, Gilchrist, Suwannee, or Union counties, Florida; or The Suwannee River and its floodway in Dixie, Gilchrist, or Levy counties, Florida. Rule 40B-4.1040(1)(b) and (c), Florida Administrative Code, reads as follows: (1) Permits are required as follows: * * * Works of the district development permit prior to connecting with, placing structures or works in or across, discharging to, or other development within a work of the district. When the need to obtain a works of the district development permit is in conjunction with the requirements for obtaining a surfacewater management permit, application shall be made and shall be considered by the district as part of the request for a surfacewater management permit application. Otherwise, a separate works of the district development permit must be obtained. Rule 40B-4.2030(4), Florida Administrative Code, reads as follows: (4) The new surfacewater management systems or individual works shall not facilitate development in a work of the district if such developments will have the potential of reducing floodway conveyance. (emphasis supplied) Rule 40B-4.3000(1)(a), Florida Administrative Code, reads as follows: The governing board is authorized to adopt and prescribe the manner in which persons may connect with or make use of works of the district pursuant to Section 373.085, Florida Statutes. Further, Section 373.019(15) provides that works of the district may include streams and accompanying lands as adopted by the governing board. In order to implement the non-structural flood control policy of the district, the governing board finds it is necessary to prevent any obstruction of the free flow of water of rivers and streams within the district. Therefore, the governing board does hereby adopt the following rivers and their accompanying floodways as works of the district: The Alapaha River and its floodway in Hamilton County, Florida; . . . . Rule 40B-4.3010, Florida Administrative Code, reads as follows: A general works of the district development permit may be granted pursuant to the procedures in Rule 40B-1.703 to any person for the development described below: Construction of a structure for single-family residential or agricultural use including the leveling of land for the foundation and associated private water supply, wastewater disposal, and driveway access which is in compliance with all applicable ordinances or rules of local government, state, and federal agencies, and which meets the requirements of this chapter. A general permit issued pursuant to this rule shall be subject to the conditions in Rule 40B-4.3030. Rule 40B-4.3020, Florida Administrative Code, reads as follows: Content of Works of the District Development Permit Applications. Applications for a general work of the district development permit shall be filed with the district and shall contain the following: Form 40B-4-5, "Application for General Work of the District Development Permit," Suwannee River Water Management District, 4-1-86, hereby incorporated by reference and which contains the following: The applicant's name and complete address including zip code; The owner's name and complete address if applicant is other than the owner; If applicable, the name, complete address, phone number, and contact person of the applicant or owner; Copies of all permits received from local units of government, state, or federal agencies, specifically a copy of the building or development permit issued by the appropriate unit of local government, including any variances issued thereto, and a copy of the onsite sewage disposal system permit issued by the Florida Department of Health and Rehabilitative Services under Chapter 10D- 6, Florida Administrative Code; A site plan to scale showing all improvements, work, or works with any conditions or limitations placed thereon; and Any supporting calculations, designs, surveys, or applicable documents, which in the applicant's opinion, may support the application. Applications for individual or conceptual approval works of the district development permits shall be filed with the district and shall contain the following: Form 40B-4-4, "Application for Surfacewater Management System Construction, Alteration, Operation, Maintenance, and/or Works of the District Development", Suwannee River Water Management District, 10-1-85, hereby adopted by reference and which contains the following: The applicant's name and complete address including zip code; The owner's name and complete address if applicant is other than the owner; If applicable, the name, complete address, phone number, and contact person of the owner. General project information including: The applicant's project name or identification number; The project location relative to county, section, township, and range, or a metes and bounds description; The total project area in acres; The total land area owned or controlled by the applicant or owner which is contiguous with the project area; A description of the scope of the proposed project including the land uses to be served; A description of the proposed surfacewater management system or work; A description of the water body or area which will receive any proposed discharges from the system; and Anticipated beginning and ending date of construction or alteration. Copies of all permits received from, or applications made to, local units of government, state, or federal agencies. A site plan to scale showing all improvements, work, or works with any conditions or limitations placed thereon. Any supporting calculations, designs, surveys, or applicable legal documents, which in the applicant's opinion, support the application. Copies of engineer or surveyor certifications required by this chapter. Rule 40B-4.3030, Florida Administrative Code, reads as follows: Conditions for Issuance of Works of the District Development Permits. The district will not approve the issuance of separate permits for development in a work of the district for any proposed project that requires a district surfacewater management permit pursuant to Part II of this chapter. For such projects, development in a work of the district may be authorized as part of any surfacewater management permit issued. The district will not approve the issuance of a works of the district development permit for any work, structures, road, or other facilities which have the potential of individually or cumulatively reducing floodway conveyance or increasing water-surface elevations above the 100-year flood elevation, or increasing soil erosion. The district will presume such a facility will not reduce conveyance or increase water-surface elevations above the 100-year flood elevation or increase soil erosion if: Roads with public access are constructed and laid out in conformance with the minimum standards of local government. Where roads are not required to be paved, the applicant must provide design specifications for erosion and sediment control. Where roads are required to be paved, swales will generally be considered adequate for erosion and sediment control; Buildings in the floodway are elevated on piles without the use of fill such that the lowest structural member of the first floor of the building is at an elevation at least one foot above the 100-year flood elevation; The area below the first floor of elevated buildings is left clear and unobstructed except for the piles or stairways; A permanent elevation monument is established on the property to be developed by a surveyor. The monument shall be adequate to establish land surface and minimum buildup elevations to the nearest 1/100 of a foot; No permanent fill or other obstructions are placed above the natural grade of the ground except for minor obstructions which are less than or equal to 100 square feet of the cross-sectional area of the floodway on any building or other similar structure provided that all such obstruction developed on any single parcel of land after the implementation date of this chapter is considered cumulatively; No activities are proposed which would result in the filling or conversion of wetlands. For any structure placed within a floodway which, because of its proposed design and method of construction, may, in the opinion of the district, result in obstruction of flows or increase in the water surface elevation of the 100-year flood, the district may require as a condition for issuance of a work of the district development permit that an engineer certify that such a structure will not obstruct flows or increase 100-year flood elevations. The following conditions shall apply to all works of the district development permits issued for development on lands subdivided after January 1, 1985: Clearing of land shall be limited [except as provided in (b) and (c) below] to that necessary to remove diseased vegetation, construct structures, associated water supply, wastewater disposal, and private driveway access facilities, and no construction, additions or reconstruction shall occur in the front 75 feet of an area immediately adjacent to a water. Clearing of vegetation within the front 75 feet immediately adjacent to a water shall be limited to that necessary to gain access or remove diseased vegetation. Harvest or regeneration of timber or agricultural crops shall not be limited provided the erosion of disturbed soils can be controlled through the use of appropriate best management practices, the seasonal scheduling of such activities will avoid work during times of high-flood hazard, and the 75 feet immediately adjacent to and including the normally recognized bank of a water is left in its natural state as a buffer strip. As to those lands subdivided prior to January 1, 1985, the governing board shall, in cases of extreme hardship, issue works of the district development permits with exceptions to the conditions listed in Rule 40B-4.3030(4)(a) through (c). The 75-foot setback in paragraphs (a) through (d) above shall be considered a minimum depth for an undisturbed buffer. The limitations on disturbance and clearing within the buffer as set out in paragraphs through (d) above shall apply, and any runoff through the buffer shall be maintained as unchannelized sheet flow. The actual depth of the setback and buffer for any land use other than single-family residential development, agriculture, or forestry shall be calculated in accordance with the methodology in: "Urban Hydrology for Small Watersheds", U.S. Department of Agriculture, Soil Conservation Service, Engineering Division, Technical Release 55, June 1986; and, "Buffer Zone Study for Suwannee River Water Management District", Dames and Moore, September 8, 1988, such that the post-development composite curve number for any one-acre area within the encroachment line does not exceed; a value of 46 for areas within the encroachment line with predominantly Class A soils; a value of 65 for areas within the encroachment line with predominantly Class B soils; a value of 77 for areas within the encroachment line with predominantly Class C soils; or a value of 82 for areas within the encroachment line with predominantly Class D soils. (emphasis supplied) Rule 40B-4.3040, Florida Administrative Code, reads as follows: Unlawful Use of Works of the District. It shall be unlawful to connect with, place a structure in or across, or otherwise cause development to occur in a work of the district without a works of the district development permit. The district may use any remedy available to it under Chapter 120 or 373, Florida Statutes, and Chapter 40B-1, Florida Administrative Code, to cause an unpermitted development to be removed or permitted. It shall be unlawful for any permitted use to violate the provisions of Chapter 373, Florida Statutes, or this chapter, or the limiting conditions of a works of the district development permit. The district may use any remedy available to it under Chapter 120 or 373, Florida Statutes, and Chapter 40B-1, Florida Administrative Code, to cause the unpermitted use to be removed or brought into compliance with Chapter 373, Florida Statutes, and this chapter. Damage to works of the district resulting from violations specified in Rule 40B-4.3040(1) and (2) above shall be repaired by the violator to the satisfaction of the district. In lieu of making repairs, the violator may deposit with the district a sufficient sum to insure such repair. Rule 40B-400.103(1)(h), Florida Administrative Code, reads as follows: (1) In order to obtain a standard general, individual, or conceptual approval permit under this chapter or chapter 40B-4, F.A.C., an applicant must provide reasonable assurance that the construction, alteration, operation, maintenance, removal or abandonment of a surface water management system: * * * (h) Will not cause adverse impacts to a work of the District established pursuant to s. 373.086. . . . Facts Based Upon the Evidence of Record History of the rules Mr. David Fisk is Assistant Director of the District. At the time of the hearing, he had been employed there for 26 and one-half years. He played a significant role in the rule adoption process of the rules that are the subject of this dispute. As part of that process, the District entered into a consulting contract with an engineering, planning, and consulting firm and consulted with the U.S. Corps of Engineers and the Federal Emergency Management Agency (FEMA), to conduct what are described as the FEMA flood studies. Additionally, the district commissioned an aerial photography consultant who provided a series of rectified ortho photographs of the entire floodplain of the rivers within the District, and a surveying subcontractor who provided vertical control and survey cross sections and hydrographic surveys of the rivers. The District also worked in conjunction with the United States Geological Survey to accumulate all of the hydrologic record available on flooding. The information was given to the U.S. Army Corps of Engineers who, operating under FEMA guidelines for conducting flood insurance rate studies, performed the analytical and computer modeling work to identify the flood plains and floodway boundaries. The District used the amassed knowledge of maps, cross sections and surveys that were developed as part of the FEMA flood studies as technical evidence or support for the adoption of the works of the district rules. Following a series of public workshops and public hearings in 1985, the rules were adopted and became effective in 1986. None of the rules were challenged in their proposed state. The District adopted the floodways of the Suwannee, Santa Fe, Alapaha, Aucilla, and Withlacoochee Rivers as works of the district. According to Mr. Fisk, the District adopted the rules pursuant to Section 373.086, Florida Statutes, which provided authority to the District to adopt district works and Section 373.085, Florida Statutes, which provided authority to regulate activities within those works. The Floodway Line Petitioner hired Mr. John Barnard, a professional civil engineer, with extensive environmental permitting experience, to look at the floodway and floodplain issues associated with Petitioner's site and project. Mr. Barnard conducted an engineering study entitled, "Floodplain Evaluation." It was Mr. Barnard's opinion that FEMA's determination of the floodway line was less than precise. Mr. Barnard used FEMA's data regarding the base flood elevation but manually changed the encroachment factor resulting in his placement of the floodway line in a different location than determined by FEMA. Mr. Barnard acknowledged that different engineers using different encroachment factors would reach different conclusions.1/ Respondent's expert in hydrology and hydraulic engineering, Brett Cunningham, noted that the definition of floodway in Rule 40B-4.1020(12), Florida Administrative Code, is essentially the same definition that used is in the FEMA regulations and which also is commonly used across the country in environmental rules and regulations. Mr. Barnard also acknowledged that the District's definition of "floodway", as found in Rule 40B-4.1020(12), Florida Administrative Code, is fairly commonly used by environmental regulatory agencies. Moreover, it was Mr. Cunningham's opinion that the Alapaha River is a stream or watercourse within the meaning of the rule and its floodway an accompanying land. In Mr. Cunningham's opinion, the FEMA flood insurance studies are widely used across the country for a variety of reasons and are typically relied upon by hydrologists and engineers to locate floodways. The definition of "works of the district" in Rule 40B-1020(30), Florida Administrative Code, is taken directly from the language found in Section 373.019(23), Florida Statutes. The statutory definition includes express references to streams and other watercourses, together with the appurtenant facilities and accompanying lands. Petitioner alleges that the phrase "will not cause adverse impact to a work of the SRWMD" as found in Rule 40B- 400.103(1)(h) is not clear because it does not identify what specific adverse impacts are being reviewed. While Petitioner's expert, Mr. Price, was not clear as to what the phrase means, Respondent's expert, Mr. Cunningham, understood the meaning of the phrase and noted that "adverse impact" is a phrase which is very commonplace in the rules and regulations of environmental agencies and is attributed a commonsense definition. The expert engineers differed in their opinions as to the meaning of the term "potential for reducing floodway conveyance" as used in Rule 40B-4.2030(4), Florida Administrative Code. According to Petitioner's expert engineer, Mr. Barnard, "potential for reducing floodway conveyance" is not a specific term that is open to interpretation as an engineer, and that he cannot quantify what constitutes "potential." Respondent's expert, Mr. Cunningham, understood the meaning of the phrase to be any increase in floodway conveyance. It was his opinion that there was nothing about that phrase to cause confusion. Rule 40B-4.3030, Florida Administrative Code, addresses conditions for issuance of works of the district development permits. Petitioner's expert Mr. Price testified that there is no quantification to what constitutes an "increase in soil erosion" as referenced in subsection (2) and linked the reference of soil erosion to a 100-year flood event referenced in the same subsection. Mr. Cunningham was of the opinion that there is no need to quantify an increase in soil erosion in the rule. He noted that soil erosion is used in a common sense manner and that attempting to put a numerical limit on it is not practical and "it's not something that's done anywhere throughout the country. It's just not something that lends itself to easy quantification like flood stages do". Mr. Cunningham's opinion that the words and phrases which Petitioner asserts are vague are words of common usage and understanding to persons in the field is the more persuasive testimony. This opinion is also consistent with statutory construction used by courts which will be addressed in the conclusions of law.

Florida Laws (15) 120.52120.536120.54120.56120.57120.595120.68373.019373.044373.085373.086373.113373.171403.814704.01
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FRANCELL FREI vs CITY OF DELTONA AND ST. JOHNS RIVER WATER MANAGEMENT DISTRICT, 04-002404 (2004)
Division of Administrative Hearings, Florida Filed:Deltona, Florida Jul. 12, 2004 Number: 04-002404 Latest Update: Feb. 14, 2006

The Issue The issue is whether the applicant for an Environmental Resource Permit ("ERP"), the City of Deltona ("City" or "Applicant"), has provided reasonable assurance that the system proposed complies with the water quantity, environmental, and water quality criteria of the St. Johns River Water Management District's ("District") ERP regulations set forth in Florida Administrative Code Chapter 40C-4, and the Applicant's Handbook: Management and Storage of Surface Waters (2005).

Findings Of Fact The District is a special taxing district created by Chapter 373, Florida Statutes, charged with the duty to prevent harm to the water resources of the District, and to administer and enforce Chapter 373, Florida Statutes, and the rules promulgated thereunder. The City of Deltona is a municipal government established under the provisions of Chapter 165, Florida Statutes. The Lake Theresa Basin is comprised primarily of a system of interconnected lakes extending from Lake Macy in the City of Lake Helen to the Butler Chain of Lakes (Lake Butler and Lake Doyle). The Lake Theresa Basin is land-locked and does not have a natural outfall to Lake Monroe and the St. Johns River. In 2003, after an extended period of above-normal rainfall in the Deltona area, the lakes within the land-locked Lake Theresa Basin staged to extremely high elevations that resulted in standing water in residential yards, and rendered some septic systems inoperable. Lake levels within the Lake Theresa Basin continued to rise and were in danger of rising above the finished floor elevations of some residences within the basin. On March 25, 2003, the District issued an Emergency Order (F.O.R. No. 2003-38) authorizing the construction and short-term operation of the Lake Doyle and Lake Bethel Emergency Overflow Interconnection. Since wetland and surface water impacts would occur, the Emergency Order required the City of Deltona to obtain an ERP for the system. The project area is 4.1 acres, and the system consists of a variable water structure on the west shore of Lake Doyle connected to a series of pipes, swales, water control structures, and wetland systems which outfall to a finger canal of Lake Bethel, with ultimate discharge to Lake Monroe and the St. Johns River. The first segment of the system extends downstream from the weir structure on the west shore of Lake Doyle via a pipe entrenched in the upland berm of the Sheryl Drive right-of-way. The pipe passes under Doyle Road and through xeric pine-oak uplands to the northeast shore of a large (approximately 15 acres) deepwater marsh. Water flows south through the deepwater marsh where it outfalls through four pipes at Ledford Drive. Two of the four pipes are overflow structures, controlled by canal gates. The pipes at Ledford Drive discharge into a ditch and into a large (greater than 20 acres) shallow bay swamp. The south end of the bay swamp is defined (and somewhat impounded) by a 19th Century railroad grade. Water flows through the bay swamp where it outfalls through five pipes at the railroad grade. Three of the five pipes are overflow structures, controlled by channel boards. The pipes at the railroad grade discharge to a 1500-foot long finger canal that was dug some time during the period 1940-1972 from the north central shore of Lake Bethel. The overflow interconnection system has three locations whereby the system can be shut down: 1) Lake Doyle--a control weir, controlled by three sluice gates; 2) Ledford Drive--two thirty-inch reinforced concrete pipes, controlled by canal gates; and 3) railroad grade--three thirty-inch reinforced concrete pipes, controlled by channel boards (collectively referred to as "Overflow Structures"). The Overflow Structures are designed to carry the discharge of water from Lake Doyle to Lake Bethel. With the Overflow Structures closed the system returns to pre-construction characteristics, meaning there will be no increase or decrease in the quantity or quality of water throughout the path of the system as a result of the project. An unequivocal condition of the permit is that the system would operate with all of the Overflow Structures closed. As an added assurance, the City proposes to place a brick and mortar plug in the Lake Doyle weir structure outfall pipe to prevent any discharge from the weir. The City has submitted to the District preliminary plans for a future phase in which the system would be modified for the purpose of alleviating high water levels within the Lake Theresa Basin when the water level in Lake Doyle rises above an elevation of 24.5 feet. The District shall require a separate permit application to be submitted for such future plans. Petitioner, Barbara Ash, has lived on Lake Theresa for 19 years. Ms. Ash lives upstream from the area of the weir that will be plugged in accordance with the ERP. She does not trust either the City of Deltona to comply with or the District to enforce the conditions of the ERP applied for by the City. Petitioner, Barbara Ash, also served as the qualified representative for Petitioners, Francell Frei, Bernard J. and Virginia Patterson, and Ted and Carol Sullivan. Ms. Ash represented that Ms. Frei has lived on Lake Theresa for 12 years, and both the Pattersons and the Sullivans live on Lake Louise, which is within the area of concern in this proceeding. Petitioner, Diana Bauer, has lived on Lake Theresa since February 2004. She fears that the lake will become too dry if the system is allowed to flow. She also believes the wildlife will be adversely affected if the water levels are too low since many species need a swampy or wet environment to thrive. She fears her property value will decrease as a result of the approval of the ERP. She also does not trust either the City to comply with or the District to enforce the conditions of the ERP. Petitioner, Howard Ehmer, lives two to three hundred yards down Lake Theresa from Ms. Bauer. He is concerned about the lake bed being too dry and attracting people on all terrain vehicles who enjoy driving around the lake bottom. He is concerned about his property value decreasing if the lake bed is dry. Further, when the lake level is too low, people cannot enjoy water skiing, boating, and fishing on Lake Theresa. Petitioner, Phillip Lott, a Florida native, has also owned and lived on property abutting Lake Theresa since 1995. Mr. Lott has a Ph.D. in plant ecology, and M.P.A. in coastal zone studies, an M.B.A. in international business, and a B.S. in environmental resource management and planning. Mr. Lott has been well acquainted with the water levels on Lake Theresa for many years. Based upon his personal observations of the lake systems in the Deltona area over the years, Mr. Lott has seen levels fluctuate greatly based upon periods of heavy and light rainfall. Mr. Lott is concerned that the District will permit the City to open the weir to let water flow through the system and cause flooding in some areas and low water levels in other areas. He fears that the District will allow the water to flow and upset the environmental balance, but he admits that this ERP application is for a closed system that will not allow the water to flow as he fears. Mr. Lott similarly does not trust the City to comply with and the District to enforce the conditions of the ERP. Petitioners, James E. and Alicia M. Peake, who were represented by Steven L. Spratt at hearing as their qualified representative, live on Lake Louise, which is interconnected with the Lake Theresa basin. The Peakes are concerned that if the level of Lake Louise drops below 21 feet, nine inches, they will not be able to use the boat launch ramps on the lake. Petitioner, Steven L. Spratt, also lives on Lake Louise, and is concerned about the water levels becoming so low that he cannot use the boat launch on the lake. He has lived on the lake since 2000, and remembers when the water level was extremely low. He fears that approval of the ERP in this case will result in low levels of water once again. Petitioner, Gloria Benoit, has live on Lake Theresa for two years. She also enjoys watching recreational activities on the lake, and feels that approval of the ERP will devalue her lakefront property. Ms. Benoit appeared at the first day of the hearing, but offered no testimony on her behalf. J. Christy Wilson, Esquire, appeared prior to the final hearing as counsel of record for Petitioners, Steven E. Larimer, Kathleen Larimer, and Helen Rose Farrow. Neither Ms. Wilson nor any of the three Petitioners she represented appeared at any time during the hearing, filed any pleadings seeking to excuse themselves from appearing at the final hearing, or offered any evidence, testimony, pre- or post- hearing submittals. Petitioner, Gary Jensen, did not appear at hearing, did not file any pleadings or papers seeking to be excused from appearing at the final hearing, and did not offer any evidence, testimony, pre- or post-hearing submittals. Both the City and the District recognize that areas downstream from the project site, such as Stone Island and Sanford, have experienced flooding in the past in time of high amounts of rainfall. The system proposed by the City for this ERP will operate with the overflow structures closed and a brick and mortar plug in the outfall pipe to prevent water flow from Lake Doyle to Lake Bethel. So long as the overflow structures are closed, the system will mimic pre-construction flow patterns, with no increase in volume flowing downstream. The District has considered the environment in its proposed approval of the ERP. The area abutting the project is little urbanized and provides good aquatic and emergent marsh habitat. With the exception of the western shore area of the deepwater marsh ("west marsh area"), the bay swamp and remaining deepwater marsh area have good ecological value. In the 1940's, the west marsh area was incorporated into the drainage system of a poultry farm that occupied the site. This area apparently suffered increased nutrient influxes and sedimentation that contributed to a proliferation of floating mats of aquatic plants and organic debris. These tussocks reduced the deepwater marsh's open water and diminished the historical marsh habitat. Water under the tussocks is typically anoxic owing to total shading by tussocks and reduced water circulation. Thick, soft, anaerobic muck has accumulated under the matted vegetation. Exotic shrubs (primrose willow Ludwigia peruvania) and other plants (cattails Typha spp.) dominate the tussocks. The construction of the project, from the 2003 Emergency Order, resulted in adverse impacts to 1.3 acres of wetlands having moderately high- to high ecological value and 0.2 acres of other surface waters. The 0.2 acre impact to other surface waters was to the lake bottom and the shoreline of Lake Doyle where the weir structure was installed. The 0.3 acres of wetland impacts occurred at the upper end of the deepwater marsh where the pipe was installed. The largest wetland impact (1.0 acre) was to the bay swamp. The bay swamp is a shallow body dominated by low hummocks and pools connected inefficiently by shallow braided channels and one acre is filled with a 1-2 foot layer of sediment following swamp channelization. Disturbance plants (e.g., primrose willow, Ludwigia peruvania, and elderberry Sambucus Canadensis) now colonize the sediment plume. Pursuant to the District's elimination and reduction criteria, the applicant must implement practicable design modifications, which would reduce or eliminate adverse impacts to wetlands and other surface waters. A proposed modification, which is not technically capable of being done, is not economically viable, or which adversely affects public safety through endangerment of lives or property is not considered "practicable." The City reduced and/or eliminated the impacts to the lake bottom and shoreline of Lake Doyle and deepwater marsh, to the extent practicable. The impacts were the minimum necessary to install the weir structure and pipe for the system; the weir structure and pipe were carefully installed on the edges of the wetland and surface water systems, resulting in a minimum amount of grading and disturbance. To compensate for the loss of 1.3 acres of wetlands and 0.2 acres of other surface waters, the City proposes to preserve a total of 27.5 acres of wetlands, bay swamp, marsh, and contiguous uplands. Included in this 27.5 acres are 6.4 acres of the west marsh, which are to be restored. The parties stipulated that the mitigation plan would adequately compensate for losses of ecological function (e.g. wildlife habitat and biodiversity, etc.) resulting from the project. Water quality is a concern for the District. Lake Monroe is included on the Florida Department of Environmental Protection's verified list of impaired water bodies for nitrogen, phosphorous, and dissolved oxygen. Water quality data for Lake Monroe indicate the lake has experienced high levels of nitrogen and phosphorous and low levels of dissolved oxygen. Prior to construction of the project, there was no natural outfall from the Lake Theresa Basin to Lake Monroe and therefore no contribution from this basin to nitrogen and phosphorous loadings to Lake Monroe. Lake Colby, Three Island Lakes (a/k/a Lake Sixma), and the Savannah are surface waters within the Lake Theresa Basin for which minimum levels have been adopted pursuant to Florida Administrative Code Chapter 40C-8. The system will operate with the overflow structures closed and a brick and mortar plug in the outfall pipe to prevent water flow from Lake Doyle to Lake Bethel, resulting in no outfall from the Theresa Basin to Lake Monroe. Minimum flows established for surface waters within the Lake Theresa Basin will not be adversely impacted. Under the first part of the secondary impact test, the City must provide reasonable assurance that the secondary impacts from construction, alteration, and intended or reasonable expected use of the project will not adversely affect the functions of adjacent wetlands or surface waters. The system is designed as a low intensity project. As proposed, little activity and maintenance are expected in the project site area. The reasonably expected use of the system will not cause adverse impacts to the functions of the wetlands and other surface waters. None of the wetland areas adjacent to uplands are used by listed species for nesting or denning. In its pre-construction state, the project area did not cause or contribute to state water quality violations. Under the second part of the secondary impact test, the City must provide reasonable assurance that the construction, alteration, and intended or reasonably expected uses of the system will not adversely affect the ecological value of the uplands to aquatic or wetland dependent species for enabling existing nesting or denning by these species. There are no listed threatened or endangered species within the project site area. Under the third part of the secondary impact test, and as part of the public interest test, the District must consider any other relevant activities that are closely linked and causally related to any proposed dredging or filling which will cause impacts to significant historical and archaeological resources. When making this determination, the District is required, by rule, to consult with the Division of Historical Resources. The Division of Historical Resources indicated that no historical or archaeological resources are likely present on the site. No impacts to significant historical and archaeological resources are expected. Under the fourth part of the secondary impact test, the City must demonstrate that certain additional activities and future phases of a project will not result in adverse impacts to the functions of wetlands or water quality violations. The City has submitted to the District preliminary plans for a future phase in which the system would be modified for the purpose of alleviating high water levels within the Lake Theresa Basin when the level in Lake Doyle rises above an elevation of 24.5 feet. Based upon the plans and calculations submitted, the proposed future phase, without additional measures, could result in minor increases in the loadings of nitrogen and phosphorous to Lake Monroe. Lake Monroe is included on the Florida Department of Environmental Protection's verified list of impaired water bodies due to water quality data indicating the lake has experienced high levels of nitrogen and phosphorous, and low levels of dissolved oxygen. Under this potential future phase, there would be an outfall from the Lake Theresa Basin to Lake Monroe. To address the impact on water quality of this potential future phase, the City has submitted a loading reduction plan for nitrogen, phosphorous, and dissolved oxygen. The plan includes compensating treatment to fully offset the potential increased nutrient loadings to Lake Monroe. Specifically, the loading reduction plan includes: Construction and operation of compensating treatment systems to fully offset anticipated increased nutrient loadings to Lake Monroe. Weekly water quality monitoring of the discharge from Lake Doyle for total phosphorous and total nitrogen. A requirement that the overflow structure be closed if the total phosphorous level reaches 0.18 mg/l or higher or the total nitrogen level reaches 1.2 mg/l or higher in any given week and will remain closed until levels fall below those limits. The implementation of these water quality mitigation measures will result in a net improvement of the water quality in Lake Monroe for nitrogen, phosphorous, or dissolved oxygen. The future phase was conceptually evaluated by the District for impacts to wetland functions. The future phase as proposed could result in adverse impacts to wetland functions. Operation of the system with the overflow structures open could impact the bay swamp and deepwater marsh. The City has demonstrated that any adverse impacts could be offset through mitigation. Based upon the information provided by the City and general engineering principles, the system is capable of functioning as proposed. The City of Deltona will be responsible for the operation, maintenance, and repair of the surface waster management system. A local government is an acceptable operation and maintenance entity under District rules. The public interest test has seven criteria. The public interest test requires the District to evaluate only those parts of the project actually located in, on, or over surface waters or wetlands, to determine whether a factor is positive, neutral, or negative, and then to balance these factors against each other. The seven factors are as follows: the public health, safety, or welfare of others; conservation of fish and wildlife and their habitats; fishing, recreational value, and marine productivity; temporary or permanent nature; 5) navigation, water flow, erosion, and shoaling; 6) the current condition and relative value of functions; and 7) historical and archaeological resources. There are no identified environmental hazards or improvements to public health and safety. The District does not consider impacts to property values. To offset any adverse impacts to fish and wildlife and their habitats, the City has proposed mitigation. The areas of the project in, on, or over wetlands do not provide recreational opportunities. Construction and operation of the project located in, on, or over wetlands will be permanent in nature. Construction and operation of the project located in, on, or over wetlands will not cause shoaling, and does not provide navigational opportunities. The mitigation will offset the relative value of functions performed by areas affected by the proposed project. No historical or archaeological resources are likely on the site of the project. The mitigation of the project is located within the same drainage basin as the project and offsets the adverse impacts. The project is not expected to cause unacceptable cumulative impacts.

Recommendation Based upon the Findings of Fact and Conclusions of Law, it is RECOMMENDED that a Final Order be entered granting the City of Deltona's application for an environmental resource permit with the conditions set forth in the Technical Staff Report, and dismissing the Petitions for Formal Administrative Hearing filed by Gary Jensen in Case No. 04-2405, and by Steven E. Larimer, Kathleen Larimer, and Helen Rose Farrow in Case No. 04-3048. DONE AND ENTERED this 27th day of May, 2005, in Tallahassee, Leon County, Florida. S ROBERT S. COHEN 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 27th day of May, 2005. COPIES FURNISHED: George Trovato, Esquire City of Deltona 2345 Providence Boulevard Deltona, Florida 32725 Diana E. Bauer 1324 Tartan Avenue Deltona, Florida 32738 Barbara Ash, Qualified Representative 943 South Dean Circle Deltona, Florida 32738-6801 Phillip Lott 948 North Watt Circle Deltona, Florida Howard Ehmer Nina Ehmer 32738-7919 1081 Anza Court Deltona, Florida 32738 Francell Frei 1080 Peak Circle Deltona, Florida 32738 Bernard T. Patterson Virginia T. Patterson 2518 Sheffield Drive Deltona, Florida 32738 Kealey A. West, Esquire St. Johns River Water Management District 4049 Reid Street Palatka, Florida 32177 J. Christy Wilson, Esquire Wilson, Garber & Small, P.A. 437 North Magnolia Avenue Orlando, Florida 32801 Gloria Benoit 1300 Tartan Avenue Deltona, Florida 32738 Gary Jensen 1298 Tartan Avenue Deltona, Florida 32738 James E. Peake Alicia M. Peake 2442 Weatherford Drive Deltona, Florida 32738 Steven L. Spratt 2492 Weatherford Drive Deltona, Florida 32738 Ted Sullivan 1489 Timbercrest Drive Deltona, Florida 32738 Kirby Green, Executive Director St. Johns River Water Management District 4049 Reid Street Palatka, Florida 32177

Florida Laws (3) 120.569120.57373.086 Florida Administrative Code (6) 40C-4.30140C-4.30240C-4.33140C-4.75162-302.30062-4.242
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FORT LAUDERDALE COUNTRY CLUB vs. CENTRAL AND SOUTH FLORIDA FLOOD CONTROL DISTRICT, 75-001917 (1975)
Division of Administrative Hearings, Florida Number: 75-001917 Latest Update: Mar. 21, 1977

Findings Of Fact The subject applications requests a permit from the Central and Southern Florida Flood Control District for the irrigation of 280 acres of golf courses. The public notice of hearing appearing in The Fort Lauderdale News, Fort Lauderdale, Florida, which noticed the permit applications submitted on behalf of the Fort Lauderdale Country Club, were received into evidence without objection. Mr. Carnahan, as representative for the applicant and Mr. Walker, on behalf of the Central and Southern Florida Flood. Control District stipulated to the introduction of the applications and the staff report of the Central and Southern Florida Flood Control District, without objection. It was further stipulated that the matters as contained in the applications and staff report could be utilized as a basis for findings of fact and recommended order, without the necessity of putting on testimony in behalf of - the applicant or the staff. Pursuant to that stipulation, oral testimony was not presented by the parties. The amount of water requested by the applicant in application number 21938 is 26 million gallons per year and the amount requested in application number 21939 is 264 million gallons per year. The staff report recommended an annual allocation in the amount of 14.4 inches which is equivalent to 336 acre/feet or 109.4 million gallons a year for approval. Mr. David Carnahan, P.E., representing the applicant, did not offer any further evidence beyond the application and staff report in support of the requests for permits. Specifically, Mr. Nagendra Khanal, Hydrology Division, Resource Planning, Central and Southern Florida Flood Control District, recommended the following, through his staff report: Allocation of 14.4 inches which is equivalent to 336.0 acre/feet or 109.4 million gallons per year. The following special provisions are recommended: Approval of maximum pumpage not to exceed 5.5 inches which is equivalent to 128.3 acre/feet or 41.8 million gallons per month. Diversions of water in this amount are subject to availability of surplus water in the basin, consistent with and subject to specific basin rules including minimum flows and levels, all as determined by the District. The existing five 12 inch wells with the total installed capacity of 3,020 gpm. The term of allocation is until October, 1977. The applicant shall install a measuring device. Pumpage records from the wells shall be submitted to the District at the end of each irrigation season. There were no persons at the hearing who wished to act as intervenors in the capacity of proponents or opponents of the applications, nor were there any members of the general public, not party to the proceedings, who wished to comment on the applications.

Recommendation Based upon the above findings of fact and conclusions of law, it is recommended that the permits requested be issued in accordance with the recommendations set forth in the staff report (attached thereto). Respectfully submitted this 31st day of October, 1975, in Tallahassee, Florida. CHARLES C. ADAMS 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 October, 1975. COPIES FURNISHED: Mr. David Carnahan 1350 South Pompano Parkway Pompano Beach, Florida 33020 Stephen Walker, Esquire Post Office Box V West Palm Beach, Florida 33402 Fort Lauderdale Country Club 415 Country Club Circle Fort Lauderdale, Florida

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PHILLIP LOTT vs CITY OF DELTONA AND ST. JOHNS RIVER WATER MANAGEMENT DISTRICT, 04-002406 (2004)
Division of Administrative Hearings, Florida Filed:Deltona, Florida Jul. 12, 2004 Number: 04-002406 Latest Update: Jul. 25, 2005

The Issue The issue is whether the applicant for an Environmental Resource Permit ("ERP"), the City of Deltona ("City" or "Applicant"), has provided reasonable assurance that the system proposed complies with the water quantity, environmental, and water quality criteria of the St. Johns River Water Management District's ("District") ERP regulations set forth in Florida Administrative Code Chapter 40C-4, and the Applicant's Handbook: Management and Storage of Surface Waters (2005).

Findings Of Fact The District is a special taxing district created by Chapter 373, Florida Statutes, charged with the duty to prevent harm to the water resources of the District, and to administer and enforce Chapter 373, Florida Statutes, and the rules promulgated thereunder. The City of Deltona is a municipal government established under the provisions of Chapter 165, Florida Statutes. The Lake Theresa Basin is comprised primarily of a system of interconnected lakes extending from Lake Macy in the City of Lake Helen to the Butler Chain of Lakes (Lake Butler and Lake Doyle). The Lake Theresa Basin is land-locked and does not have a natural outfall to Lake Monroe and the St. Johns River. In 2003, after an extended period of above-normal rainfall in the Deltona area, the lakes within the land-locked Lake Theresa Basin staged to extremely high elevations that resulted in standing water in residential yards, and rendered some septic systems inoperable. Lake levels within the Lake Theresa Basin continued to rise and were in danger of rising above the finished floor elevations of some residences within the basin. On March 25, 2003, the District issued an Emergency Order (F.O.R. No. 2003-38) authorizing the construction and short-term operation of the Lake Doyle and Lake Bethel Emergency Overflow Interconnection. Since wetland and surface water impacts would occur, the Emergency Order required the City of Deltona to obtain an ERP for the system. The project area is 4.1 acres, and the system consists of a variable water structure on the west shore of Lake Doyle connected to a series of pipes, swales, water control structures, and wetland systems which outfall to a finger canal of Lake Bethel, with ultimate discharge to Lake Monroe and the St. Johns River. The first segment of the system extends downstream from the weir structure on the west shore of Lake Doyle via a pipe entrenched in the upland berm of the Sheryl Drive right-of-way. The pipe passes under Doyle Road and through xeric pine-oak uplands to the northeast shore of a large (approximately 15 acres) deepwater marsh. Water flows south through the deepwater marsh where it outfalls through four pipes at Ledford Drive. Two of the four pipes are overflow structures, controlled by canal gates. The pipes at Ledford Drive discharge into a ditch and into a large (greater than 20 acres) shallow bay swamp. The south end of the bay swamp is defined (and somewhat impounded) by a 19th Century railroad grade. Water flows through the bay swamp where it outfalls through five pipes at the railroad grade. Three of the five pipes are overflow structures, controlled by channel boards. The pipes at the railroad grade discharge to a 1500-foot long finger canal that was dug some time during the period 1940-1972 from the north central shore of Lake Bethel. The overflow interconnection system has three locations whereby the system can be shut down: 1) Lake Doyle--a control weir, controlled by three sluice gates; 2) Ledford Drive--two thirty-inch reinforced concrete pipes, controlled by canal gates; and 3) railroad grade--three thirty-inch reinforced concrete pipes, controlled by channel boards (collectively referred to as "Overflow Structures"). The Overflow Structures are designed to carry the discharge of water from Lake Doyle to Lake Bethel. With the Overflow Structures closed the system returns to pre-construction characteristics, meaning there will be no increase or decrease in the quantity or quality of water throughout the path of the system as a result of the project. An unequivocal condition of the permit is that the system would operate with all of the Overflow Structures closed. As an added assurance, the City proposes to place a brick and mortar plug in the Lake Doyle weir structure outfall pipe to prevent any discharge from the weir. The City has submitted to the District preliminary plans for a future phase in which the system would be modified for the purpose of alleviating high water levels within the Lake Theresa Basin when the water level in Lake Doyle rises above an elevation of 24.5 feet. The District shall require a separate permit application to be submitted for such future plans. Petitioner, Barbara Ash, has lived on Lake Theresa for 19 years. Ms. Ash lives upstream from the area of the weir that will be plugged in accordance with the ERP. She does not trust either the City of Deltona to comply with or the District to enforce the conditions of the ERP applied for by the City. Petitioner, Barbara Ash, also served as the qualified representative for Petitioners, Francell Frei, Bernard J. and Virginia Patterson, and Ted and Carol Sullivan. Ms. Ash represented that Ms. Frei has lived on Lake Theresa for 12 years, and both the Pattersons and the Sullivans live on Lake Louise, which is within the area of concern in this proceeding. Petitioner, Diana Bauer, has lived on Lake Theresa since February 2004. She fears that the lake will become too dry if the system is allowed to flow. She also believes the wildlife will be adversely affected if the water levels are too low since many species need a swampy or wet environment to thrive. She fears her property value will decrease as a result of the approval of the ERP. She also does not trust either the City to comply with or the District to enforce the conditions of the ERP. Petitioner, Howard Ehmer, lives two to three hundred yards down Lake Theresa from Ms. Bauer. He is concerned about the lake bed being too dry and attracting people on all terrain vehicles who enjoy driving around the lake bottom. He is concerned about his property value decreasing if the lake bed is dry. Further, when the lake level is too low, people cannot enjoy water skiing, boating, and fishing on Lake Theresa. Petitioner, Phillip Lott, a Florida native, has also owned and lived on property abutting Lake Theresa since 1995. Mr. Lott has a Ph.D. in plant ecology, and M.P.A. in coastal zone studies, an M.B.A. in international business, and a B.S. in environmental resource management and planning. Mr. Lott has been well acquainted with the water levels on Lake Theresa for many years. Based upon his personal observations of the lake systems in the Deltona area over the years, Mr. Lott has seen levels fluctuate greatly based upon periods of heavy and light rainfall. Mr. Lott is concerned that the District will permit the City to open the weir to let water flow through the system and cause flooding in some areas and low water levels in other areas. He fears that the District will allow the water to flow and upset the environmental balance, but he admits that this ERP application is for a closed system that will not allow the water to flow as he fears. Mr. Lott similarly does not trust the City to comply with and the District to enforce the conditions of the ERP. Petitioners, James E. and Alicia M. Peake, who were represented by Steven L. Spratt at hearing as their qualified representative, live on Lake Louise, which is interconnected with the Lake Theresa basin. The Peakes are concerned that if the level of Lake Louise drops below 21 feet, nine inches, they will not be able to use the boat launch ramps on the lake. Petitioner, Steven L. Spratt, also lives on Lake Louise, and is concerned about the water levels becoming so low that he cannot use the boat launch on the lake. He has lived on the lake since 2000, and remembers when the water level was extremely low. He fears that approval of the ERP in this case will result in low levels of water once again. Petitioner, Gloria Benoit, has live on Lake Theresa for two years. She also enjoys watching recreational activities on the lake, and feels that approval of the ERP will devalue her lakefront property. Ms. Benoit appeared at the first day of the hearing, but offered no testimony on her behalf. J. Christy Wilson, Esquire, appeared prior to the final hearing as counsel of record for Petitioners, Steven E. Larimer, Kathleen Larimer, and Helen Rose Farrow. Neither Ms. Wilson nor any of the three Petitioners she represented appeared at any time during the hearing, filed any pleadings seeking to excuse themselves from appearing at the final hearing, or offered any evidence, testimony, pre- or post- hearing submittals. Petitioner, Gary Jensen, did not appear at hearing, did not file any pleadings or papers seeking to be excused from appearing at the final hearing, and did not offer any evidence, testimony, pre- or post-hearing submittals. Both the City and the District recognize that areas downstream from the project site, such as Stone Island and Sanford, have experienced flooding in the past in time of high amounts of rainfall. The system proposed by the City for this ERP will operate with the overflow structures closed and a brick and mortar plug in the outfall pipe to prevent water flow from Lake Doyle to Lake Bethel. So long as the overflow structures are closed, the system will mimic pre-construction flow patterns, with no increase in volume flowing downstream. The District has considered the environment in its proposed approval of the ERP. The area abutting the project is little urbanized and provides good aquatic and emergent marsh habitat. With the exception of the western shore area of the deepwater marsh ("west marsh area"), the bay swamp and remaining deepwater marsh area have good ecological value. In the 1940's, the west marsh area was incorporated into the drainage system of a poultry farm that occupied the site. This area apparently suffered increased nutrient influxes and sedimentation that contributed to a proliferation of floating mats of aquatic plants and organic debris. These tussocks reduced the deepwater marsh's open water and diminished the historical marsh habitat. Water under the tussocks is typically anoxic owing to total shading by tussocks and reduced water circulation. Thick, soft, anaerobic muck has accumulated under the matted vegetation. Exotic shrubs (primrose willow Ludwigia peruvania) and other plants (cattails Typha spp.) dominate the tussocks. The construction of the project, from the 2003 Emergency Order, resulted in adverse impacts to 1.3 acres of wetlands having moderately high- to high ecological value and 0.2 acres of other surface waters. The 0.2 acre impact to other surface waters was to the lake bottom and the shoreline of Lake Doyle where the weir structure was installed. The 0.3 acres of wetland impacts occurred at the upper end of the deepwater marsh where the pipe was installed. The largest wetland impact (1.0 acre) was to the bay swamp. The bay swamp is a shallow body dominated by low hummocks and pools connected inefficiently by shallow braided channels and one acre is filled with a 1-2 foot layer of sediment following swamp channelization. Disturbance plants (e.g., primrose willow, Ludwigia peruvania, and elderberry Sambucus Canadensis) now colonize the sediment plume. Pursuant to the District's elimination and reduction criteria, the applicant must implement practicable design modifications, which would reduce or eliminate adverse impacts to wetlands and other surface waters. A proposed modification, which is not technically capable of being done, is not economically viable, or which adversely affects public safety through endangerment of lives or property is not considered "practicable." The City reduced and/or eliminated the impacts to the lake bottom and shoreline of Lake Doyle and deepwater marsh, to the extent practicable. The impacts were the minimum necessary to install the weir structure and pipe for the system; the weir structure and pipe were carefully installed on the edges of the wetland and surface water systems, resulting in a minimum amount of grading and disturbance. To compensate for the loss of 1.3 acres of wetlands and 0.2 acres of other surface waters, the City proposes to preserve a total of 27.5 acres of wetlands, bay swamp, marsh, and contiguous uplands. Included in this 27.5 acres are 6.4 acres of the west marsh, which are to be restored. The parties stipulated that the mitigation plan would adequately compensate for losses of ecological function (e.g. wildlife habitat and biodiversity, etc.) resulting from the project. Water quality is a concern for the District. Lake Monroe is included on the Florida Department of Environmental Protection's verified list of impaired water bodies for nitrogen, phosphorous, and dissolved oxygen. Water quality data for Lake Monroe indicate the lake has experienced high levels of nitrogen and phosphorous and low levels of dissolved oxygen. Prior to construction of the project, there was no natural outfall from the Lake Theresa Basin to Lake Monroe and therefore no contribution from this basin to nitrogen and phosphorous loadings to Lake Monroe. Lake Colby, Three Island Lakes (a/k/a Lake Sixma), and the Savannah are surface waters within the Lake Theresa Basin for which minimum levels have been adopted pursuant to Florida Administrative Code Chapter 40C-8. The system will operate with the overflow structures closed and a brick and mortar plug in the outfall pipe to prevent water flow from Lake Doyle to Lake Bethel, resulting in no outfall from the Theresa Basin to Lake Monroe. Minimum flows established for surface waters within the Lake Theresa Basin will not be adversely impacted. Under the first part of the secondary impact test, the City must provide reasonable assurance that the secondary impacts from construction, alteration, and intended or reasonable expected use of the project will not adversely affect the functions of adjacent wetlands or surface waters. The system is designed as a low intensity project. As proposed, little activity and maintenance are expected in the project site area. The reasonably expected use of the system will not cause adverse impacts to the functions of the wetlands and other surface waters. None of the wetland areas adjacent to uplands are used by listed species for nesting or denning. In its pre-construction state, the project area did not cause or contribute to state water quality violations. Under the second part of the secondary impact test, the City must provide reasonable assurance that the construction, alteration, and intended or reasonably expected uses of the system will not adversely affect the ecological value of the uplands to aquatic or wetland dependent species for enabling existing nesting or denning by these species. There are no listed threatened or endangered species within the project site area. Under the third part of the secondary impact test, and as part of the public interest test, the District must consider any other relevant activities that are closely linked and causally related to any proposed dredging or filling which will cause impacts to significant historical and archaeological resources. When making this determination, the District is required, by rule, to consult with the Division of Historical Resources. The Division of Historical Resources indicated that no historical or archaeological resources are likely present on the site. No impacts to significant historical and archaeological resources are expected. Under the fourth part of the secondary impact test, the City must demonstrate that certain additional activities and future phases of a project will not result in adverse impacts to the functions of wetlands or water quality violations. The City has submitted to the District preliminary plans for a future phase in which the system would be modified for the purpose of alleviating high water levels within the Lake Theresa Basin when the level in Lake Doyle rises above an elevation of 24.5 feet. Based upon the plans and calculations submitted, the proposed future phase, without additional measures, could result in minor increases in the loadings of nitrogen and phosphorous to Lake Monroe. Lake Monroe is included on the Florida Department of Environmental Protection's verified list of impaired water bodies due to water quality data indicating the lake has experienced high levels of nitrogen and phosphorous, and low levels of dissolved oxygen. Under this potential future phase, there would be an outfall from the Lake Theresa Basin to Lake Monroe. To address the impact on water quality of this potential future phase, the City has submitted a loading reduction plan for nitrogen, phosphorous, and dissolved oxygen. The plan includes compensating treatment to fully offset the potential increased nutrient loadings to Lake Monroe. Specifically, the loading reduction plan includes: Construction and operation of compensating treatment systems to fully offset anticipated increased nutrient loadings to Lake Monroe. Weekly water quality monitoring of the discharge from Lake Doyle for total phosphorous and total nitrogen. A requirement that the overflow structure be closed if the total phosphorous level reaches 0.18 mg/l or higher or the total nitrogen level reaches 1.2 mg/l or higher in any given week and will remain closed until levels fall below those limits. The implementation of these water quality mitigation measures will result in a net improvement of the water quality in Lake Monroe for nitrogen, phosphorous, or dissolved oxygen. The future phase was conceptually evaluated by the District for impacts to wetland functions. The future phase as proposed could result in adverse impacts to wetland functions. Operation of the system with the overflow structures open could impact the bay swamp and deepwater marsh. The City has demonstrated that any adverse impacts could be offset through mitigation. Based upon the information provided by the City and general engineering principles, the system is capable of functioning as proposed. The City of Deltona will be responsible for the operation, maintenance, and repair of the surface waster management system. A local government is an acceptable operation and maintenance entity under District rules. The public interest test has seven criteria. The public interest test requires the District to evaluate only those parts of the project actually located in, on, or over surface waters or wetlands, to determine whether a factor is positive, neutral, or negative, and then to balance these factors against each other. The seven factors are as follows: the public health, safety, or welfare of others; conservation of fish and wildlife and their habitats; fishing, recreational value, and marine productivity; temporary or permanent nature; 5) navigation, water flow, erosion, and shoaling; 6) the current condition and relative value of functions; and 7) historical and archaeological resources. There are no identified environmental hazards or improvements to public health and safety. The District does not consider impacts to property values. To offset any adverse impacts to fish and wildlife and their habitats, the City has proposed mitigation. The areas of the project in, on, or over wetlands do not provide recreational opportunities. Construction and operation of the project located in, on, or over wetlands will be permanent in nature. Construction and operation of the project located in, on, or over wetlands will not cause shoaling, and does not provide navigational opportunities. The mitigation will offset the relative value of functions performed by areas affected by the proposed project. No historical or archaeological resources are likely on the site of the project. The mitigation of the project is located within the same drainage basin as the project and offsets the adverse impacts. The project is not expected to cause unacceptable cumulative impacts.

Recommendation Based upon the Findings of Fact and Conclusions of Law, it is RECOMMENDED that a Final Order be entered granting the City of Deltona's application for an environmental resource permit with the conditions set forth in the Technical Staff Report, and dismissing the Petitions for Formal Administrative Hearing filed by Gary Jensen in Case No. 04-2405, and by Steven E. Larimer, Kathleen Larimer, and Helen Rose Farrow in Case No. 04-3048. DONE AND ENTERED this 27th day of May, 2005, in Tallahassee, Leon County, Florida. S ROBERT S. COHEN 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 27th day of May, 2005. COPIES FURNISHED: George Trovato, Esquire City of Deltona 2345 Providence Boulevard Deltona, Florida 32725 Diana E. Bauer 1324 Tartan Avenue Deltona, Florida 32738 Barbara Ash, Qualified Representative 943 South Dean Circle Deltona, Florida 32738-6801 Phillip Lott 948 North Watt Circle Deltona, Florida Howard Ehmer Nina Ehmer 32738-7919 1081 Anza Court Deltona, Florida 32738 Francell Frei 1080 Peak Circle Deltona, Florida 32738 Bernard T. Patterson Virginia T. Patterson 2518 Sheffield Drive Deltona, Florida 32738 Kealey A. West, Esquire St. Johns River Water Management District 4049 Reid Street Palatka, Florida 32177 J. Christy Wilson, Esquire Wilson, Garber & Small, P.A. 437 North Magnolia Avenue Orlando, Florida 32801 Gloria Benoit 1300 Tartan Avenue Deltona, Florida 32738 Gary Jensen 1298 Tartan Avenue Deltona, Florida 32738 James E. Peake Alicia M. Peake 2442 Weatherford Drive Deltona, Florida 32738 Steven L. Spratt 2492 Weatherford Drive Deltona, Florida 32738 Ted Sullivan 1489 Timbercrest Drive Deltona, Florida 32738 Kirby Green, Executive Director St. Johns River Water Management District 4049 Reid Street Palatka, Florida 32177

Florida Laws (3) 120.569120.57373.086 Florida Administrative Code (6) 40C-4.30140C-4.30240C-4.33140C-4.75162-302.30062-4.242
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TAMARAC UTILITIES, INC. vs. CENTRAL AND SOUTH FLORIDA FLOOD CONTROL DISTRICT, 76-000409 (1976)
Division of Administrative Hearings, Florida Number: 76-000409 Latest Update: Jun. 21, 1991

Findings Of Fact By application number 21312, the applicant seeks a ten year water use permit for a total annual diversion of 3,831 million gallons to provide water and sewer services to an area containing approximately 7,300 acres. In September of 1969, the Florida Public Service Commission granted the applicant certificates of convenience and necessity. The existing facilities of the applicant include nine wells and an average capacity of 700 gallons per minute each. Based upon historical data and taking into accourt the reduction of construction in the service area, the projected 1984 water demand is 375 gallons per day per unit. This is equivalent to an average of 150 gallons per day per person, using a figure of 2.5 persons per living unit. The ultimate estimated population is to be 70,000 to 80,000 people with 28,000 to 32,000 living units. Based upon the average capacities of the wells, in order to meet the projected demand a total number of 22 or 23 wells will be required. This includes the nine existing wells, eleven proposed wells with the same 700 gallon per minute average and a fifteen percent standby capability of two or three additional wells. Rather than the total number of wells utilized -- 22 or 23, -- what is important is the total gallon per minute capacity of 15,400. An allocation based on this data would be equal to the applicant's requested annual maximum diversion of 3,831 million gallons and a daily maximum diversion of 18.37 million gallons. The requested diversion presents no threat of salt water intrusion. The proposed well sites will create no adverse impact upon the Fort Lauderdale well fields. While there is evidence of recharge to the aquifer from runoff waters, there is insufficient data to determine the exact amount which will be returned. For this reason, the staff report's water budget calculations are conservative.

Recommendation Based upon the above findings of fact and conclusions of law, it is recommended that a ten year permit be issued to the applicant for a maximum annual diversion of 3,831 million gallons; a maximum daily diversion of 18.37 million gallons and a maximum installed field capacity of 15,400 gallons per minute, utilizing 22 or 23 wells with a capacity of 700 gallons per minute each. It is further recommended that the applicant be subject to the conditions set forth on page 5 of the staff report (Exhibit 8) concerning the submission of monthly reports of daily pumpage and actual connections or population served, conformance with health department standards of the water quality of all wells, and the installation and maintenance of an observation well and monthly reports of the data obtained therefrom. Respectively submitted and entered this 10th day of May, 1976, in Tallahassee, Florida. DIANE D. TREMOR Hearing Officer Division of Administrative Hearings Room 530, Carlton Building Tallahassee, Florida 32304 COPIES FURNISHED: Mr. John R. Maloy Executive Director Central and Southern Florida Flood Control District P.O. Box V West Palm Beach, Florida 33402 Mr. Edward B. Deutsch 350 Southern Federal Building 400 North State Road 7 Margate, Florida 33063 Mr. John Wheeler P.O. Box V West Palm Beach, Florida 33402 Attorney for the Central and Southern Florida Flood Control District

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DEPARTMENT OF ENVIRONMENTAL REGULATION vs. COMMUNITIES FINANCIAL CORPORATION, ET AL., 79-001560 (1979)
Division of Administrative Hearings, Florida Number: 79-001560 Latest Update: May 14, 1980

Findings Of Fact Respondent Communities Financial Corporation is a Florida corporation engaged in the subdivision and sale of real property. In 1971 CFC purchased approximately twenty-two sections, or 22 square miles, of real property ("the land") in Township 34 South, Range 33 East, Okeechobee County, Florida, which it proposed to sell as individual one-and-one-quarter (1-1/4) acre lots. The subsequent development of that land is the subject of this proceeding. Respondent Coquina Water Management District ("Coquina") was organized pursuant to Chapter 298, Florida Statutes, by judgment of the Circuit Court for Okeechobee County, Florida to perform drainage activities on the land. The land which CFC purchased in 1971 was originally platted in 1912 in a grid system with roads, drainage canals, and ditches. Extensive drainage was required for use of the land because it was very flat and had a high water table. Approximately one-half of the land was subject to flooding. After it was originally platted it was utilized for cattle ranching with drainage ditches connecting the low areas to encourage runoff. Ten-acre tracts surrounded by dikes and two to three foot deep ditches were used for tomato farming. Such agricultural ditching covered approximately 15 square miles of the property. At one time a hotel was situated on a portion of the property. North-South and East-West roads and a 5,000-foot airstrip were constructed across the property. The East-West road along the South boundary of the property, which is now a state road, has an adjacent drainage ditch which received ranchland water runoff from property east of the land. In 1971 and 1972 CFC registered the platted lots for sale with the Division of Florida Land Sales and Condominiums ("Land Sales") of the State of Florida Department of Business Regulation. In the normal course of compiling the documentation to be submitted for registration, CFC contacted several state regulatory agencies to determine whether such agencies required CFC to obtain permits for development of the property. CFC provided those agencies copies of its drainage plans, which included roads, swales, canals, and control structures. The State of Florida Department of Natural Resources ("DNR") stated that the construction of improvements as planned in the development would not be subject to that agency's jurisdiction for purposes of a dredge and/or fill permit. The State of Florida Department of Pollution Control ("DPC"), predecessor of DER, first stated in a letter of October 4, 1971, to Mr. Moseley Collins, who submitted a "plan of reclamation to DPC, that it had no regulatory responsibilities over the project: In response to your request for comments this Department has conducted a preliminary review of the proposed plan. We have no basic objections to the overall plan of development and believe it could be platted as shown. Specific details as to drainage techniques will be reviewed at a latter [sic] date. It is brought to you [sic] attention that although we have no regulatory responsibili- ties in this area we will welcome the opportunity to review cross sections and details at a latter [sic] date. We thank you for the opportunity to review a project of this magnitude at an early date. [Emphasis added.] The DPC, in a letter of March 30, 1972, to Collins, also observed that: This Department has conducted a review of the revised plan for the subject project and endorse the approach that you are contemplating in developing these areas. I have coordinated with other agencies and organizations and they concur with the approach. We would like to review the project at a future date to deter- mine the method of construction of the swales or greenways to move the water from one lake to another through the complete watershed area. You and your client are to be commended on this approach. From the preliminary layout you can see the possibilities for the potential develop- ment of an area for residential usage that will retain a large percentage of the natural resources and minimize the downstream effect on the overall watershed. Please advise when you want to review the project in greater detail. [Emphasis added.] In connection with the registration of the development, CFC submitted to Land Sales the above-referenced letters from DNR and DPC, detailed evidence of the proposed plan of development, and a public offering statement for use in solicitation of lot sales from the general public. Each offering statement contains several statements to the effect that "this is not a homesite subdivision." Land Sales approved use of the offering statement. In using it to solicit sales, CFC committed to the purchasers that it would complete the required road and drainage improvements by December 31, 1979. CFC commenced sales of lots in the development in 1971. The Agreements for Deed approved by Land Sales and subsequently entered into by CFC with lot purchasers required CFC to deliver improved lots by December 31, 1979. Most of the land sales were made between 1971 and 1973. (6,412 lots were sold and 1,146 were conveyed by June 23, 1977.) Approximately eighty percent of the lots have been sold to date. Up to one-half of the approximately nine thousand lot purchasers hold legal title to their lots pursuant to deeds issued to them by CFC upon full payment. CFC began construction of the promised improvements, consisting of roads and drainage, in 1972. At the present time approximately $1,000,000 of improvements have been completed and approximately $750,000 remain to be completed. In 1973 or 1974, CFC and Coquina submitted plans for the surface water management system which CFC proposed to construct for the property to the South Florida Water Management District ("SFWMD"). The initial plan of development called for the construction of a road and canal system. At the request of SFWMD, the plan was subsequently changed to a road and swale system, and the configuration of one of the control structures was changed. The design changes resulted in more water retention on the property and the preservation of sensitive areas. After several years of analysis and review of the design plan, inspection of the project site, and a public hearing, SFWMD granted conceptual approval for the surface water management system to be constructed by CFC in 1977. The conceptual approval was partially based on the SFWMD staff's assessment than pollutant loadings from the property after development would be less than existing loadings, and that adverse water quality impacts as a result of the proposed development were unlikely. The 1977 SFWMD conceptual approval of the drainage plan for the development was followed by the issuance of a construction permit for the westernmost seven sections on March 15, 1979. Throughout this period construction was continuing. The drainage system as approved consists of grassed lot, roadside, and collector "swales" together with a retention area comprised of natural wetlands in the area of the property known as Ash Slough. The volume of water leaving the property after development will be the same as that leaving the property before development. The drainage conveyances are designed with gradually sloping sides, vary to widths of over 100 feet for the larger collector conveyances, and have depths varying from 2 feet for the "lateral" swales to 3 feet for the larger collector swales. The groundwater table in the area of the project site varies from zero to approximately 30 inches below ground surface. The swales were designed at the request of SFWMD in lieu of the canals proposed within the same easements in the original drainage plan for the development. It appears from the evidence that these drainage conveyances are designed so as to contain contiguous areas of standing or flowing water only following the occurrence of rainfall or flooding. Although some testimony indicated that these conveyances contained contiguous areas of standing water, these observations were made either at isolated times during the progress of construction or soon after a major hurricane passed through the area. Since the purpose of the "swales" is to facilitate drainage from the property, it would appear necessary from an engineering viewpoint to allow some period of time after construction of the swales for them to stabilize to make a valid determination that they will not function as designed. Accordingly, it would not appear unusual that the swales contain areas of standing water until they have been given ample opportunity to stabilize. On the basis of the record in this proceeding, a determination simply cannot be made at this point in time that the swales will not function as designed. Following DPC's initial determination of no jurisdiction in 1971 and 1972, it and DER, its successor agency, were not involved with the project until 1974, when DPC received an inquiry concerning land sales matters from the U.S. Department of Housing and Urban Development. In 1975, a DER staff member conducted a critical review of the Project and filed an internal memorandum faulting the project on the same essential grounds that are the basis for the Notice of Violation issued June 1, 1979. DER representatives participated in various SFWMD meetings from 1975 to 1977 when the conceptual approval of the drainage plan for the project was discussed. During this period, SFWMD forwarded copies of various materials dealing with the project to DER. Further, a DER representative attended the public hearing on September 8, 1977, when the conceptual approval of the project was granted by SFWMD. Respondents' first indication of DER's renewed interest in the development was a letter from DER Subdistrict Manager Warren Strahm to Robert Birenbaum on June 23, 1977. This letter stated, in part, that: The above referenced application/staff report has been supplied to this office by the South Florida Water Management District (SFWMD). It has been determined that your project is subject to Chapters 403 and/or 253, Florida Statutes. A review of drainage plans by our staff indicates the referenced project will comply with Chapter 403, Florida Statutes permit requirements for pollutant discharge. Since these plans have been incorporated into the SFWMD permit, no discharge permit or monitoring in addition to SFWMD permit requirement will be required by the Department at this time. It appears, however, that the referenced project may fall within the permitting requirements set forth in Chapter 17-4, Florida Administrative Code. Pursuant to F.A.C. 17-4.28(2) should any excavation take place in submerged lands or within the transitional zone of submerged lands, dredge and fill permits will be required by this Department prior to commencement of said activi- ties. [Emphasis added.] Please contact Mr. Roger G. Gallop, at the Fort Pierce Branch Office, telephone (305) 464-8525, at your convenience in order to discuss the need for a construction dredge and fill permit. Thank you for your cooperation. Three months later, in a letter from James Brindell to Coquina, Respondents were notified that: A review, by this agency, of the plans associated with your Surface Water Management Permit Applica- tion No. 02187-A indicates that permits will be required from the Department of Environmental Regulation pursuant to Chapter 403 and/or Chapter 253, Florida Statutes for the construction con- templated. Specifically, permits will be required for the construction and operation of discharge structures as well as for any dredging and/or filling in the waters of the state including the submerged lands and transitional zone of these submerged lands. Additionally, certification pursuant to section 401 of F.L. 92-500 may be required. Formal or conceptual appova1 of your project by the South Florida Water Management District does not imply that your project will satisfy the requirements of this agency. Please contact Mr. Warren G. Strahm, Subdistrict Manager, 3301 Gun Club Road, West Palm Beach, phone 305/689-5800, at your earliest convenience concerning application for these permits. (Emphasis added). This letter was followed one-and-one-half months later by a "Letter of Notice" from DER advising Respondents that DER had reason to believe the project was in violation of Chapter 403, Florida Statutes, and requesting CFC to cease any further work. Throughout this series of correspondence, CFC and Coquina maintained that DER did not have permit jurisdiction. This position was reasserted in a letter of November 1, 1977, from Emerson Allsworth, counsel for Coquina, to DER. During this period, numerous meetings were held involving representatives of Respondents and DER in which Respondents were urged by DER to apply for permits. Respondents failed to do so, and, on June 1, 1979, DER issued its Notice of Violation. Natural drainage from the property occurs southwestward into an area known as Ash Slough; southward from the central portion of the property into Gore Slough; and from the northeast section of the property into Company Slough. The headwaters of both Ash Slough and Gore Slough originate on the project site and periodically extend off Respondents' property to the south to join the waters of Chandler Slough. Chandler Slough, in turn, eventually empties into Lake Okeechobee 11 to 15 miles from the property. Company Slough also extends off the project site eastward onto the lands of others. There is, however, insufficient evidence in this record from which to conclude that Company Slough regularly exchanges flow with any other body of water. A "slough", as that term is used in the context of this proceeding, is a surface conveyance pathway for waters whose lateral boundaries are not as well-defined as a stream bed, and whose rate of flow is relatively slow. Due to the flat topography of the project site, Ash, Gore and Company Sloughs have imprecise boundaries, and their rates of flow appear to range at various times from very slow to nonexistent. By Cease and Desist Order dated March 28, 1978, the United States Army Corps of Engineers required Respondents to halt any further work then being conducted on the project, asserting that work in progress at that time was being conducted in waters of the United States, including adjacent wetlands, without first having acquired a permit from the Corps of Engineers. This Order provided, in part, that: Section 301(a) of the [Federal Water Pollution Control Act Amendments of 1972] makes it unlawful to discharge dredged or fill material into waters of the United States unless author- ized by a Section 404 permit issued by the Secretary of the Army acting through the Chief of Engineers. Section 10 of the River and Harbor Act of 1899 prohibits the excavation or depositing of material or erecting any struc- tures in navigable waters of the United States unless authorized by a Department of the Army permit. The work referred to in the paragraph above is deemed to have occurred in waters subject to these statutory requirements without the requisite permits and is considered unlaw- ful by this office. Prior to 25 July, the Corps of Engineers limited the requirement for Section 404 type permits to areas either below the mean high water line in tidal areas or below the ordinary high water line of rivers and streams which either now sup- port, had supported, or were capable of supporting interstate commerce. However, on 25 July 1975, the regulatory juris- diction of the District was expanded to all waters of the United States and adjacent wetlands. [Emphasis add.] Subsequently, however, by memorandum dated May 17, 1978, the United States Army Corps of Engineers determined that it did not have jurisdiction over Respondent's activities for the following reasons: In the northeast and eastern portion of the tract the flagponds and saw grass prairies are isolated with no discernible drainage sloughs or patterns. The other area of concern, in the south west sector, contains isolated ponds and an old man-made drainage canal that comprises shallow, intermittent potholes above the natural headwaters of Ash and Gore Sloughs. There was no recognizable flow in any part of the canal and the point at which average annual flow appear to be 5 c.f.s. or greater is located to the south a considerable distance from the subject tract. The project, as proposed, will not destroy or threaten any endangered species or their habitat nor adversely impact water quality of the ultimate receiving waters in Kissimmee River and Lake Okeechobee. In 1971, the Soil Conservation Service of the United States Department of Agriculture classified Ash and Gore Sloughs, as well as Fish Slough, to which Company Slough is alleged by DER to connect, as "intermittent". This determination is supported by hydrological data compiled by the South Florida Water Management District which shows no net flow in Chandler Slough for as many as six months in 1975 and four months in 1976. In the South Florida Water Management District report concerning flow patterns in Chandler Slough, it was pointed out that: The climate in this portion of Florida is subtropical with warm summers and moderate winters. Rainfall is seasonal with about 75 percent of the total occur- ring in a well-defined wet season, from May to October. This distribution of rainfall results in considerable surface water flow during part of the year. During the late winter and early spring many of the creeks and sloughs, such as Chandler Slough, become completely dry. [Emphasis added.] In addition, testimony in the record in this proceeding establishes that on at least one occasion during the time in which construction on the property was being conducted, Company Slough was completely dry. There is no data in the record quantifying the annual flow of water from Ash and Gore Sloughs into Chandler Slough. Further, there is no evidence concerning the periodicity of any such water exchanges between Ash and Gore Sloughs and Chandler Slough. As indicated above, the evidence establishes that Chandler Slough, which is the larger collector slough into which both Ash and Gore sloughs allegedly discharge, periodically becomes "completely dry." DER witnesses testified that they had observed contiguous areas of standing water in Ash, Gore and Company Sloughs during visits to the site, and had also determined the existence of an exchange of waters between Ash, Gore and Company Sloughs with other sloughs connecting to Chandler Slough by analyzing aerial photographs. However, those aerial photographs were not made a part of the record in this proceeding. Additionally, the relatively few visits to the site by these witnesses, in the absence of validly derived data establishing pertinent flow rates, is insufficient to establish "normal" conditions in the area. This is especially true in light of the aforementioned countervailing determinations based upon data compiled by the United States Army Corps of Engineers, the United States Department of Agriculture and the South Florida Water Management District. The evidence shows that some of the types of vegetation listed in DER's vegetation indices by which DER determines whether areas are "submerged lands" or "transitional zones" of submerged lands have been found on the project site. Among the types of vegetation observed in and around Ash, Gore and Company Sloughs are maidencane, water willow, pickerelweed, button bush, saw grass and St. John's wort. Although these species were detected in some locations by visual observation, apparently no attempt was made to quantify these plants vis-a-vis other vegetative types, nor were any physical measurements made to locate their boundaries. In a report dated August 26, 1977, the SFWMD attempted to identify the acreage, but not boundaries, of wetlands on the development site. The findings of that report show that approximately 2,014 of 14,080 acres, or 14.3 percent of the total site, contains wetlands vegetation. The report also indicates that the wetlands vegetation is scattered in different locations over the site, with the median occurrence being 68 acres per 640-acre section. DER presented quantified evidence showing turbidity readings in the Ash Slough area of the development during the construction of swales in August, 1979, of 325 Jackson Units and November and December, 1979, of 155 and 176 Jackson Units, respectively. It should be noted that these readings were performed after the filing of the Notice of Violation herein. Although samples of August 6, 1979, were taken without a background sample in Ash Slough, the evidence establishes that background readings in Ash Slough were less than 25 Jackson Units. The evidence clearly establishes that DER's water quality sampling and analysis were conducted in accordance with applicable requirements of Chapter 17, Florida Administrative Code. The evidence establishes that these readings are attributable to construction of swales and control structures and would not be expected to continue after completion of construction. There is no evidence to show the duration of the discharges resulting in these turbidity readings, nor is there any showing of actual damage to animal, plant or aquatic life. Petitioner and Respondent have submitted proposed findings of fact in this proceeding. To the extent that those findings of fact are not adopted in this Recommended Order, they have been specifically rejected as being either irrelevant to the issues in this cause, or as not having been supported by the evidence.

Florida Laws (12) 120.57380.06380.12403.031403.061403.062403.087403.088403.121403.161403.803403.813
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ROBERT E. LEE vs. CENTRAL AND SOUTH FLORIDA FLOOD CONTROL DISTRICT, 75-001915 (1975)
Division of Administrative Hearings, Florida Number: 75-001915 Latest Update: Mar. 21, 1977

Findings Of Fact The subject application requests a permit from the Central and Southern Florida Flood Control District for the agricultural irrigation of 640 acres of grass-clover mixture, of which approximately 320 are planted annually to small grains and annual rye grass. The public notice of hearing appearing in The Orlando Sentinel Star, Orlando, Florida, and The Evening Herald, Sanford, Florida, which noticed the permit application submitted on behalf of Robert E. Lee, were received into evidence without objection. (A copy of The Orlando Sentinel Star exhibit, public notice of hearing, is attached to this report, because the original of the exhibit is contained with the report on docket no. 61, application 21423.) Mr. Lee and Mr. Wheeler on behalf of the Central and Southern Florida Flood Control District stipulated to the introduction of the application and the staff report of the Central and Southern Florida Flood Control District, without objection. It was further stipulated that the matters as contained in the application and staff report could be utilized as a basis for findings of fact and recommended order, without the necessity of putting on testimony in behalf of the applicant or the staff. Pursuant to that stipulation, oral testimony was not presented by the parties. The amount of water requested by the application is 398.9 acre/feet per year. The staff report recommended approval of 398.9 acre/feet per year, as requested by the applicant, based on the applicant's supplemental water use request. Mr. Lee did not offer any further evidence beyond the application and staff report, in support of the request for permit. The recommendation as contained in the staff report prepared by Mr. Nagendra Khanal, Hydrology Division, Resource Planning Department, Central and Southern Florida Flood Control District, was that the application #25642 for annual allocation of 398.9 acre/feet per year for purposes as applied for was acceptable. However, Mr. Khanal indicated that the permit should be subject to the following conditions: Recommendation of maximum monthly pumpage not to exceed 180.17 acre/feet or 4.70 inches/month. Pumpage in this amount is subject to availability of surplus water in the basin, consistent with and subject to specific basin rules including minimum flows and levels, all as determined by the District. Existing well and 10 inch deep well turbine pump with an installed capacity of 3,000 gpm be approved. This permit shall expire on October 15, 1978. The applicant shall install a measuring device on the well. Pumpage records shall be submitted to the District at the end of each irrigation season. There were no persons at the hearing who wished to act as intervenors in the capacity of proponents or opponents of the application, nor were there any members of the general public, not party to the proceedings, who wished to comment on the application.

Florida Laws (1) 180.17
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MARTIN COUNTY AND SOUTH FLORIDA WATER MANAGEMENT DISTRICT vs. PAL-MAR WATER MANAGEMENT DISTRICT, 78-000312 (1978)
Division of Administrative Hearings, Florida Number: 78-000312 Latest Update: May 21, 1979

Findings Of Fact Pal-Mar has filed application No. 29454 pursuant to Chapter 373, Florida Statutes, requesting approval for a surface water management system known as Phase III of Pal-Mar Water Management District, to serve approximately 3,600 acres of residential land in Martin County, Florida. The project discharges to C-44, the St. Lucie canal. SFWMD's staff report recommends approval be granted for the proposed water management system based on considerations of water quality, rates of discharge, environmental impact and flood protection. Approval is subject to certain conditions which are not material to the instant cause. As background material to the staff report, the staff makes reference to the U.S. Army Corps of Engineers report entitled "Survey-Review Report of Central and Southern Florida Flood Control Project, Martin County," dated September 22, 1967. The Corps of Engineers' report was not used in the decision-making process but rather was included in the staff report to provide a comprehensive overview. Whether the Corps of Engineers' plans were ever implemented would not affect the recommendations of the staff. The land in question is currently zoned "IZ" (interim zoning) according to Martin County's zoning regulations. In this category, if the neighborhood is predominantly one classification of usage, then the zoning director is to be governed by the regulations for that class of usage in determining the standard zoning regulations to be applied to the interim zoning district. If no trend of development has been established in the neighborhood, the minimum standards of the R2 single family zoning district are to be complied with. Rule 16K-4.035, Florida Administrative Code, entitled Basis of Review of Applications for Construction of Works, provides in Section (2) that all applications such as the instant one shall be reviewed in accordance with the provisions of the district's "Basis Of Review For Construction Of Surface Water Management Systems Serving Projects With Two Or More Acres Of Impervious Area Within The South Florida Water Management District - December, 1977." The Basis of Review provides in Part VI that before an application will be considered for the issuance of a permit, the proposed land use must be "compatible with the applicable zoning for the area." The evidence indicates that the land in question has a history of agricultural use. However, the evidence also discloses that far from being a trend towards agricultural use there is a trend away from it. A major portion of the neighboring lands will be devoted to Phases I, II, IV and V, of the Pal-Mar Water Management District. According to Florida Land Sales Board registrations, the land in question is subdivided into one-half acre, one acre, 1.4 acre and two acre lots. The average project density is one lot per acre. In addition, there is some mobile home usage within neighboring areas. If there is a trend, it is toward R2 zoning type usage. SFWMD's staff concluded that the proposed land use was compatible with the applicable zoning for the area. Martin County has failed to establish that such compatibility does not exist. In the Redraft of Order Permitting Change of Plan of Reclamation and Change of Name dated November 4, 1969, the Honorable C. Pfeiffer Trowbridge, Circuit Court Judge of the Nineteenth Judicial Circuit in and for Martin County, observes that the Petitioner in that case (herein Pal-Mar) "permanently and irrevocably withdrew its application to drain into the St. Lucie canal thereby removing all reasons for objections" to the proceedings in Circuit Court. However, there is no evidence to indicate that there exists a prohibition against drainage into the St. Lucie canal or that Judge Trowbridge's order is intended to preclude approval of Pal-Mar's present application.

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