The Issue The issue in this case is whether Respondents Paul Crum, Sr., and Paul Crum, Jr. (the "Crums"), are entitled to the Noticed General Permit issued by the Department of Environmental Protection ("Department") for the construction of a single- family residential dock and associated structures.
Findings Of Fact Background The Crums are the owners of the riparian property located at 15696 Shark Road West, Jacksonville, Florida. The Crum property is adjacent to Pumpkin Hill Creek, which lies within the Nassau River-St. Johns River Marshes Aquatic Preserve. Extending from the Crum property into Pumpkin Hill Creek is an existing wood dock approximately 90 feet long and four feet wide, with a platform near the landward end of the dock. Petitioner Brooks owns the property immediately adjacent to and north of the Crum property. Petitioner Brooks has a dock and boat lift. Petitioner Cole owns the property immediately adjacent to and southeast of the Crum property. The Cole property is located on a salt marsh and has no dock. Petitioner Jones lives approximately 3,200 feet north of the Crum property, on a tributary to Pumpkin Hill Creek. Petitioner Jones has fished Pumpkin Hill Creek and the surrounding waters for over 25 years. Noticed General Permits are a type of environmental resource permit granted by rule for those activities which have been determined to have minimal impacts to water resources. Florida Administrative Code Rule 62-341.427 grants by rule a general permit to construct a single family pier, along with boat lifts and terminal platforms, provided certain specific criteria are met. In August 2005, the Crums applied for a Noticed General Permit to extend their existing dock into deeper water. The Department issued a Notice of Determination of Qualification for Noticed General Permit, but later rescinded the authorization after Petitioner Brooks complained to the Department that the landward end of the existing dock is located only 21 feet from her property boundary and, therefore, did not comply with Florida Administrative Code Rule 18-21.004(3)(d), which requires that a dock be set back a minimum of 25 feet "inside the applicant's riparian rights lines." In November 2005, the Crums re-applied for a Noticed General Permit. Their revised plans called for removal of the existing dock and construction of a new dock extending approximately 255 feet out into Pumpkin Hill Creek. The proposed dock would be located a minimum of 25 feet inside the Crums' riparian rights lines. On December 6, 2005, the Department issued a Notice of Determination of Qualification for a Noticed General Permit for the revised dock, stating that the project satisfied the requirements of Florida Administrative Code Rule 62-341.427, as well as the conditions for authorization to perform activities on state-owned submerged lands set forth in Florida Administrative Code Rule 18-21 and for activities in an aquatic preserve under Florida Administrative Code Rule 18-20. In April 2006, Petitioners filed three petitions for hearing with the Department alleging that the proposed dock significantly impedes navigation by restricting access to a tidal creek and extends more waterward than necessary to access a water depth of (minus) -4 feet at mean low water, which is prohibited for docks in aquatic preserves under Florida Administrative Code Rule 18-20.005(3)(b)3. Petitioners attached to their petitions a copy of a bathymetric survey showing the elevations of the submerged lands in the vicinity of the proposed project. In response to the information contained in the survey, the Crums revised their plans to shorten the dock to its currently proposed length of 186.56 feet. A new Notice of Determination of Qualification for a Notice General Permit was then issued by the Department on October 16, 2006. The final dock project consists of: (a) removal of the existing wood dock; (b) construction of a four-foot wide, 186.56-foot long, single family residential dock consisting of an access pier, a 12-foot by 12-foot terminal platform, and a 14-foot by 20-foot open boat lift with catwalk (the “proposed dock”). The proposed dock will terminate where the water will be four feet deep at mean low water. Navigating in and Near the Tidal Creek To the south of the Crum property is a wide expanse of salt marsh. Within the salt marsh are unnamed tidal creeks. The mouth of one tidal creek that flows to Pumpkin Hill Creek is located approximately 90 feet south of the existing Crum dock. The tidal creek is shallow and is not navigable at or near low tide. Petitioner Jones owns an 18-foot flatboat which he sometimes keeps at his residence and sometimes at Petitioner Brooks' property. The boat draws about one foot of water. Petitioner Jones uses this boat to fish in the tidal creek located near the Crum property about ten times every month. No evidence was presented to show that Petitioner Brooks or Petitioner Cole ever navigate in or otherwise use this tidal creek. There are many other tidal creeks located in the marshes associated with Pumpkin Hill Creek. Petitioner Jones boats and fishes in most of them. Petitioner Jones said that, currently, he must wait two hours past low tide for the water depth to be sufficient for him to get into the tidal creek near the Crum property. His usual course to the creek lies just beyond the end of the existing Crum dock. He claims there is a channel there, but no channel is shown on the survey or in any of the parties' photographs. After the proposed dock is constructed, Petitioner Jones' usual course to the tidal will be obstructed. He contends that the new course he would have to take to the tidal creek will take him across shallower areas of Pumpkin Hill Creek so that he will have to wait two more hours (a total of four hours) after low tide to get into the creek. Therefore, Petitioner Jones' alleged injury is the reduction of the hours available to him to navigate in and out of the tidal creek for fishing. The existing Crum dock terminates on a broad mud flat which is exposed at mean low water. However, the bathymetric survey shows the mud flat is at a lower elevation near the end of the dock so water covers this area before it covers the rest of the mud flat. However, the bathymetric survey also shows the elevation of the bottom rising as one moves south from the existing dock. At the mouth of the tidal creek the elevation is 1.0 feet NGVD (National Geodetic Vertical Datum, an official, surveyed reference point). Because the tidal creek drains into the main body of Pumpkin Hill Creek, a reasonable inference can be made that the bottom elevations in the creek generally become higher (and the water depths decrease) as one moves up the creek toward dry land. Prop scars in the exposed bottom at the end of the existing dock indicate that boats have traveled over this area when the water was so shallow that the engine props were striking the bottom. Prop scarring can cause turbidity and damage to benthic organisms. The bathymetric survey indicates that mean high water in this area of Pumpkin Hill Creek is 3.03 feet NGVD, and the mean low water is -1.78 feet NGVD. The mean tidal fluctuation between mean low water and mean high water is thus 4.81 feet. Randall Armstrong, who was accepted as an expert in navigation and piloting, explained that in this area, where there are two daily tides, the water elevation will generally increase by 1/12 of the mean tidal fluctuation in the first hour after mean low water, another 2/12 of the fluctuation in the second, and 3/12 in the third hour. Applying this general rule to the tidal fluctuation here of 4.81 feet results in an estimated 1.2-foot increase in water elevation two hours after low tide and a 2.4-foot increase three hours after low tide. Based on the mean low water elevation of -1.78 feet NGVD, the water elevation would usually be about -0.6 foot NGVD two hours after low tide and 0.6 foot NGVD three hours after low tide. Therefore, the tidal creek (with a bottom elevation of 1.0 foot NGVD at the mouth) would usually be "dry" two hours after low tide and would usually have less than a foot of water three hours after low tide. That evidence contradicts Petitioner Jones' statement that he now navigates into the tidal creek two hours after low tide. That might occasionally be possible, but the bathymetric survey indicates the creek would usually be too shallow at that time. In fact, the evidence suggests that the tidal creek is only reliably navigable without causing prop scars to the bottom by using boats with very shallow draft and waiting until high tide (or shortly before or after) when the water depth at the mouth of the creek would be about two feet. It was Mr. Armstrong's opinion that the 1.0-foot NGVD elevation at the mouth of the tidal creek determines when and how long the tidal creek is navigable, and those times would not be affected by the proposed dock. He described the new course that a boater would use to navigate into the tidal creek after the proposed dock is built. He used the bathymetric survey to show that when the water is deep enough to navigate into the tidal creek, the water depth is also sufficient to navigate the new course. The proposed dock might, as Petitioner Jones alleges, cause boaters to traverse a longer section of the mudflat then they do currently. However, the more persuasive testimony supports the Crums' position that the navigability of the tidal creek is controlled by its shallowest point at the 1.0-foot NGVD elevation and that the proposed dock will not interfere with navigation of the tidal creek by requiring boaters to traverse shallower areas. Petitioner Jones testified that he regularly navigates his boat close to the existing Crum dock. The evidence does not indicate that the proposed dock would cause an unreasonable risk of collision for boaters using the new course to the tidal creek.
Recommendation Based on the foregoing findings of fact and conclusions of law, it is RECOMMENDED that the Secretary of the Florida Department of Environmental Protection enter a final order that grants Noticed General Permit No. 16-253057-002-EG to the Crums. DONE AND ENTERED this 22nd day of December, 2006, in Tallahassee, Leon County, Florida. S BRAM D. E. CANTER 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 22nd day of December, 2006.
The Issue Whether the finger pier portion of Respondent Raab's dock creates a navigational hazard. The resolution of that issue will determine whether the dock qualifies for an exemption from an environmental resource permit under Rule 40E-4.051(3)(b), Florida Administrative Code, and Section 403.813, Florida Statutes.
Findings Of Fact DEP has the authority to regulate the construction of docks in jurisdictional wetlands and other waters of the State of Florida and on state submerged lands under Chapters 253, 373, and 403, Florida Statutes, and Chapters 62-330 (which adopts Chapter 40E-4) and 18-21, Florida Administrative Code. The Association is a residential community located in Sewall's Point, Martin County, Florida. All lots within the community abut navigable channels which provide ingress and egress to the ICW. These channels converge so that there is only one channel that connects to the ICW. Most of the residents of the community have large vessels that routinely navigate the channels within the community. At the time of the formal hearing, many of the vessels owned by residents of the community had drafts of four feet and at least two had drafts of five feet. In 1997, Mr. Raab purchased a residence in the Association that is located very close to where the channel meets the ICW. Because of that location, practically all residents of the Association have to pass in front of Mr. Raab's property when going into or returning from the ICW. The property at issue is located at 22 Simara Street, Sewalls Point, Martin County, Florida. The dock at issue in this proceeding is subject to DEP's regulatory authority. When Mr. Raab purchased this property in 1997, there was an existing marginal dock parallel to the bulk-head. Mr. Raab subsequently sought and received approval from DEP to demolish the existing marginal dock and replace it with a virtually identical structure. The existence and configuration of the marginal dock is not at issue in this proceeding. Mr. Raab thereafter sought to modify his approved marginal dock by adding a finger pier which extended into the channel 36 feet so he could dock his vessel perpendicular to the bulkhead. Mr. Raab's plan also called for the construction of two pilings 12 feet from the end of the finger pier. Mr. Raab had, as of the time of the formal hearing, re-constructed the marginal dock and had constructed the finger pier. 3/ The two additional pilings had not been constructed at the time of the formal hearing. After reviewing the modified project, DEP determined that the project was exempt from the need for an environmental resource permit under Rule 40E-4.051(3)(b), Florida Administrative Code, and Section 403.813, Florida Statutes. DEP also authorized Mr. Raab to use state-owned submerged lands if necessary. The Association thereafter timely challenged DEP's determination that the finger pier portion of the project (and the two additional pilings) did not require an environmental resource permit. There was a conflict in the evidence as to the functional width of the channel in front of Mr. Raab's property. 4/ Mr. Holly testified on behalf of the Association that the functional width of the channel was 83 feet. Mr. Lidberg, testifying on behalf of Mr. Raab, testified that the functional width was 101 feet. This conflict is resolved by finding that the functional width of the channel in front of the Raab property is 101 feet. 5/ The prevailing winds in the area in front of Mr. Raabb's dock blow into the dock. The depth of the water in the channels is influenced by tides. The principal reason Mr. Raab wants the finger pier is so that he can moor his boat with the bow to the prevailing winds in times of high winds. At the time of the formal hearing, Mr. Raab owned a vessel with an overall length of 44 feet. There was a conflict in the evidence as to whether Mr. Raab's finger pier and the two pilings that have been authorized, but not constructed, constitute a hazard to navigation. 6/ Based on the totality of the evidence, it is found that these structures do not create a navigational hazard. 7/
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that DEP enter a final order dismissing the Association's challenge to the determination that Mr. Raab's project qualifies for an exemption from an environmental resource permit. DONE AND ENTERED this 1st day of March, 2000, in Tallahassee, Leon County, Florida. CLAUDE B. ARRINGTON 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 1st day of March, 2000.
Findings Of Fact Upon consideration of the oral and documentary evidence adduced at the hearing relating to the issue of jurisdiction, the following relevant facts are found: On or about March 28, 1979, respondents T.V. Rodriquez and Trafalgar Developers of Florida, Inc. filed with the Department of Environmental Regulation an application for a permit to conduct dredge and fill activities on a 2.3 acre area located within a 495 acre planned unit development in Orlando. The 2.3 acre tract is located in a cypress swamp area in the northeast portion of the development site. The application sought authority to excavate 2,000 cubic yards of material for the installation of a five foot diameter drainage culvert, and to backfill the installed pipe with 3,000 cubic yards of fill material. All of the construction activity was to be confined to the 2.3 acre tract which, as noted above, was a cypress swamp area interior to the project boundaries. While there were no other property owners immediately adjacent to the cypress swamp upon which the dredging and filling was to occur, the applicants did provide for notification purposes the names of two property owners which were the closest, although not adjacent, to the proposed project site. Neither the petitioners nor the intervenors in this proceeding were among the two names provided. The Department of Environmental Regulation reviewed the application and, on April 5, 1980, requested further infor- mation. Upon receipt of this information, an employee of DER, Jim Morgan, conducted a field inspection of the dredge and fill site on May 10, 1979. It was Mr. Morgan's conclusion that the proposed project would result in the elimination of approxi- mately three percent of the wetlands associated with the eastern boundary of the 495 acre development, and would not significantly impact the remaining portion of the wetland community. Mr. Morgan recommended that the application be approved, with two specific conditions. One condition pertained to the containment of turbidity at the project site if the site is inundated during construction. The other condition pertained to a proposed swale for outfall of a planned ditch system for the drainage of the 495 acre planned unit development. On May 18, 1979, the Department of Environmental Regulation issued Permit No. 48-18682-4E to respondents to excavate 2,000 cubic yards of material for the installation of a five foot diameter drainage culvert and to backfill the installed pipe with 3,000 cubic yards of fill material suitable for use as-a golf course foundation. The permit contained the specific conditions recommended by Mr. Morgan. Specific Condition Number 1 reads as follows: "(1) The drainage plan for this proposed 495 acre planned unit development will require the lowering of the water table via way of a planned ditch system, thus making development feasible. This ditch system will ultimately [sici discharge to an existing county canal via way of a proposed swale, which is exempt from this department's per- mitting pursuant to Chapter 17-4.04(10)(k). A swale conveys water only during and immediately after the advent of a storm. This installation must conform to this explicit definition, otherwise, additional dredge and fill permits will be required, including the entire development's drainage facility. Upon completion of the development, this department shall be notified and periodic inspections will be performed by the department's staff to determine if the outfall conforms with the definition of a swale." By letters to DER dated August 20, 1979, the petitioners herein stated that they had just been informed on August 17, 1979, of the issuance of the subject permit to the respondents. Their original letters to the DER, as well as their amended and restated petition, claim that, as owners of property located adjacent to the property upon which the drainage project would be conducted pursuant to the subject permit, they were entitled to notice prior to the issuance of the permit and that their substantial interest will be affected by the drainage project authorized by said permit. The petitioners Frances Bandy and Charles R. Bandy own Lot 14 in Golden Acres which is a considerable distance from the 2.3 acre tract upon which respondents are permitted to conduct dredging and filling activities. The petitioners Anna and Lee Rowe and Fay M. Handy own Lots 20 and 21 in Golden Acres, as well as a five acre lake. These lots and lake are even further from the permitted dredge and fill site. None of the petitioners own property which is adjacent to the permitted 2.3 acre site. Betty J. Hardy, Wayne Hardy and Vista Landscaping Inc. moved to intervene in this proceeding by motion dated March 5, 1980. An amended motion to intervene was filed on March 17, 1980, adding Julian T. Hardy as a named party intervenor. The intervenors own and have a business interest in property located a considerable distance south of the permitted 2.3 acres. The intervenors conduct a wholesale nursery business on their property. Their complaint lies with the effect that the proposed drainage of the entire 495 acre development and the alleged drainage ditch located on property contiguous to their property will have on their property and business interests. As of the time of the hearing on March 18, 1980, construction pursuant to the permit issued on May 18, 1979, was approximately ninety-five percent (95 percent) complete.
Recommendation Based upon the findings of fact and conclusions of law recited herein, it is RECOMMENDED that the petitioners request for an administrative hearing pursuant to Section 120.57(1) be dismissed, with prejudice, for lack of jurisdiction. Respectfully submitted and entered this 22nd day of April, 1980, in Tallahassee, Florida. DIANE D. TREMOR Hearing Officer Division of Administrative Hearings 101 Collins Building Tallahassee, Florida 32301 (904) 488-9675 COPIES FURNISHED: Cleatous J. Simmons Lowndes, Drosdick and Doster Post Office Box 2809 Orlando, Florida 32802 Roger D. Schwenke Carlton, Fields, Ward, Emmanual, Smith and Cutler, P.A. Post Office Box 3239 Tampa, Florida 33601 Stanley J. Niego Office of General Counsel Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32301 Honorable Jacob Varn Secretary, Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32301
The Issue Issues presented here concerned the entitlement of Respondent, Russell D. Horn, Sr., to be granted an environmental permit by Respondent, Department of Environmental Regulation, to build a boat stall on an existing dock in Putnam County, Florida. The boat stall's dimensions are ten feet wide by twenty feet deep and the construction would be on the St. Johns River.
Findings Of Fact On July 13, 1981, Russell D. Horn, Sr., who has a residence in Putnam County, Florida, bade application to the State of Florida, Department of Environmental Regulation, for the necessary permits to construct a boat stall ten feet wide by twenty feet deep at the site of an existing dock. A copy of the application may be found as Respondent Horn's Exhibit No. 2 admitted into evidence. The dock where Horn applied to build the boat slip is found in the St. Johns River, a navigable water body and waters of the State of Florida in Putnam County, Florida. The application form which was executed by Horn required him to indicate the name of adjacent property owners to the property at which the dock site was located, both upland and adjacent to the uplands. See Rule 17- 4.28(11)(c), Florida Administrative Code. To accomplish this task, the applicant utilized a sketch which he had been provided when he purchased his homesite in the area and indicated to the Department that the adjoining landowners were Milton Kilis and Robert Michal. In fact, Robert Michal was not an adjacent landowner. The adjacent landowner, Milton G. Kilis, wrote to advise the Department that he had no objection to the construction of the boat slip. This correspondence was dated September 11, 1981. A copy of that correspondence may be found as Respondent Department's Exhibit No. 3 admitted into evidence. After reviewing the initial application, additional information was requested by a document entitled "Completeness Summary" which was addressed from the Department to the Applicant Horn. A copy of this "Completeness Summary" requesting additional information may be found as Department's Exhibit No. 1 admitted into evidence. Through this summary, Horn was requested to provide written authorization from the dock owners. It was also requested that Respondent provide an affidavit of ownership of the upland property adjacent to the dock site. Horn received permission to construct from Frank Scussell and William A. Reaves, persons he understood to be the dock owners. See Respondent Horn's Exhibit No. 3 admitted into evidence. Horn misunderstood the question related to ownership of upland property and provided a mortgage deed with its attendant description of his home site property in Putnam County, which is at a different location from that of the upland property adjacent to the dock. A copy of that deed and other matters may be found as Respondent Horn's Exhibit No. 4 admitted into evidence. Department of Environmental Regulation reviewing authorities wrote on the "Completeness Summary" form, Respondent Department's Exhibit No. 1, indicating that the task of seeking written authorization from the dock owners had been achieved and that the affidavit of ownership of upland property owners was satisfactory. In fact, all adjacent property owners had not been notified of the pendency of the application request through the process of Horn's advising the Respondent agency of the names of all adjacent property owners to the uplands and the affidavit of ownership of the upland property owner at the dock site was not filed. During the review process, permission was given by the Department of the Army, Corps of Engineers, for the construction of the boat slip. A copy of this permission, by letter dated August 31, 1981, is Respondent Department's Exhibit No. 2, admitted into evidence. The Department of Environmental Regulation reviewed the permit application and prepared an application appraisal, which may be found as Respondent Department's Exhibit No. 5 admitted into evidence. The findings made by that application appraisal related to application review are found to be accurate. In particular the permit application appraisal indicated that the boat slip would be located at the waterward end of the existing dock structure, which existing dock structure accommodated four boats. The appraisal found that the project was located in South Putnam County in the town of Georgetown on the St. Johns River. The permit appraisal found that the project site would be located in the littoral zone of the river about one hundred feet waterward of the mean high water line. No littoral growth was seen at the depth of the proposed construction. Tapegrass, Mexican waterlily and cattail were present near the shore. Several large hardwood swamp trees were present at the shoreline. The project was found to be located in a Water Class III and adjacent waters were Class III according to the appraisal, no significant immediate or long-term adverse environmental impacts were to be expected to occur due to the completion of the boat slip. Horn was subsequently given a construction permit to add the boat stall to the existing dock. A copy of that permit may be found as Respondent Department's Exhibit No. 6 admitted into evidence. The only specific conditions related to that matter pertain to the necessity for the utilization of turbidity curtains throughout the project for purposes of containing the turbidity that might exceed State water quality standards, The permit was issued on September 22, 1981. After receiving the permit, sometime around October 20, 1981, Horn purchased the necessary lumber to construct the stall and on October 24, 1981, went to the dock site to begin the installation of pilings related to the construction of the boat stall. While placing the pilings on October 24, 1981, an adjoining property owner and Petitioner in this cause, Marshall Wolfe, stood on his dock, that is, Wolfe's dock, and hailed to Horn to stop building. Horn did not know Wolfe before that time and did not know that Wolfe, not Michal, was the adjacent property owner on that side of the dock. On October 28, 1981, Marshall Wolfe and his wife, Ann Wolfe, wrote to the Department in the person of G. Doug Dutton, Subdistrict Manager, and indicated that they were opposed to the issuance of the permit, which is under the number of the permit issued to Respondent, and requested a hearing on the question of the issuance. A copy of that correspondence may be found as Department's Exhibit No. 7 admitted into evidence. On the same date, October 28, 1981, Horn was contacted by the Department of Environmental Regulation and advised of the Wolfe complaint and Horn was told that he would receive a cease and desist order from the Department of Environmental Regulation. On October 30, 1981, Horn returned to the construction site and found four of his neighbors finishing the construction of the stall. In fact, the neighbors did conclude the construction and the boat slip remains in place. A cease and desist letter was mailed on November 2, 1981; however, this letter was not received by Horn immediately. Horn did subsequently learn of the contents of the letter some time in November or December, 1981. A copy of the cease and desist letter may be found as Respondent Department's Exhibit No. 8 admitted into evidence. On December 13, 1981, an attempt was made at the instigation of Department officials for the Petitioners and Respondent Horn to resolve the controversy. This effort was unsuccessful. As a consequence, a formal hearing was necessary in keeping with the request of the Department that the Division of Administrative Hearings conduct a Subsection 120.57(1), Florida Statutes, formal hearing. This request had been made on November 12, 1981, and an initial hearings had been scheduled for February 11, 1982, following consultation between the various parties and the Hearing Officer. At the initial hearing session on February 11, 1982, which was to be held in Palatka, Florida, counsel for Department indicated that the upland property was not owned by Horn and that easement rights to that property were unclear. In view of this fact the hearing was continued until the ostensible upland property owner could be notified of the pendency of the issuance of an environmental permit and be allowed to participate. Notification was subsequently provided by an Intent to Issue Statement, a copy of which may be found as Respondent Department's Exhibit No. 9 admitted into evidence. This notification was through the Department at the instigation of the Hearing Officer. The date of notification was February 12, 1982. An order was entered on March 17, 1982, which allowed the intervention of St. Johns Crescent Lakesites, Inc. into the proceedings and that party, in the person of its counsel, Lauren E. Merriam, III, Esquire, participated in the April 15, 1982 hearing. St. Johns Crescent Lakesites, Inc. is the owner of the upland property adjacent to the dock in which Horn had constructed the boat slip. No indication was given that any easement rights were ever granted by that corporation to grant access to the boat slip from the adjacent property. The overall dock area, in terms of square feet, is between 500 and 1000 square feet. Other than the permit application made by Horn, no other permission has been received by the Department to construct the other features of the dock. A further appraisal of the project site subsequent to the September 18, 1981, appraisal has been made. That appraisal was made by the field inspector for the Department. This appraisal by Melvin Rechtor agrees with the project appraisal made by the first field inspector, John Hendricks. The testimony of Melvin Rechtor on environmental impacts of the project are accepted as accurate. Rechtor's testimony established that the project would have an insignificant impact on water quality considerations and would not adversely affect the species or the conservation of fish, marine and wildlife or other natural resources. Rechtor's testimony established that there would be no unreasonable interference with waterward access of adjacent property owners. Rechtor's testimony also established that there would be no navigational hazard nor interference with fishing and swimming by persons using the river.
The Issue Whether Petitioner's application for an environmental resource permit to remove two canal plugs in the Cahill canal system should be granted or denied.
Findings Of Fact The proposed project On March 19, 1998, Petitioner Cahill submitted a permit application to the Department to remove two canal plugs in the Cahill Pines and Palms subdivision on Big Pine key. A backhoe would be used to dredge and lower the plugs to a depth of minus five feet mean low water (-5 ft. MLW) for the purpose of providing boating access to the properties now isolated from open water. The Cahill canal system is located within class III waters of the state which open into Pine Channel, a natural waterbody designated as Outstanding Florida Waters (OFW). In 1991 and 1995 Petitioner Cahill submitted permit applications to the Department to remove the same two canal plugs. Those applications were initially denied and the denials were litigated in formal administrative hearings. Those hearings resulted in Department final orders denying both applications.3 Background4 In July, 1991, the Department received a permit application requesting the removal of two canal plugs down to a depth of minus five-and-a-half feet NGVD. A formal administrative hearing was conducted on March 3 and 4, 1994, in Key West, Florida, before Stuart M. Lerner, a duly designated Hearing Officer (now Administrative Law Judge) of the Division of Administrative Hearings. That initial permit application denial was based upon water quality considerations and the project's failure to meet the public interest test. On May 17, 1995, Petitioner submitted a permit application to the Department which was denied. The basis for the permit denial was that the project was substantially similar to the previously litigated project. On April 23, 1996, a second formal administrative hearing was held in Key West, Florida, before Administrative Law Judge Susan B. Kirkland. Judge Kirkland found that the 1995 permit application did not address the issues raised by the Department in the first administrative hearing. Judge Kirkland also concluded that the 1995 application should be denied on the basis of res judicata. The Department entered a Final Order on September 12, 1996, concluding that the doctrine of res judicata applied to support the denial of Petitioner's 1995 application. New facts/changed conditions In all material aspects, the proposed dredging activity in the current permit application is identical to the previously proposed dredging activity. Petitioner Cahill seeks to lower the two canal plugs to allow boat access. The documents submitted in support of the current application do not propose any significant changes to what was proposed in the two prior applications. Petitioner Cahill provided copies of provisions of the Monroe County Comprehensive Plan, the Florida Keys National Marine Sanctuary Management Plan and two Monroe County Ordinances, in support of the current permit application. This information does not constitute new facts or changed conditions sufficient to characterize the proposed project as substantially different from the previously denied applications. Petitioner Cahill provided a list of "enhancements" in the current permit application seeking to provide reasonable assurance for issuance of an environmental resource permit. These proposed "enhancements" are not binding on the Petitioner Cahill's members and do not constitute such new facts or changed conditions as to make the project substantially different from the previously denied applications. The differences between the current application and the two previously denied applications are primarily cosmetic differences. The substance of the matter is unchanged in any material detail.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that a final order be issued in this case denying Petitioner's pending application for an environmental resource permit. DONE AND ENTERED this 15th day of March, 1999, in Tallahassee, Leon County, Florida. MICHAEL M. PARRISH 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 15th day of March, 1998.
Recommendation Based upon the above findings of fact and conclusions of law it is recommended that the permit requested be issued in accordance with the recommendations and special provisions set forth in the staff report (attached thereto). Respectfully submitted this 3rd day of November, 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 3rd day of November, 1975. COPIES FURNISHED: Thomas C. Garwood, Jr., Esquire Post Office Box 231 Orlando, Florida 32802 John Wheeler, Esquire Post Office Box V West Palm Beach, Florida
Findings Of Fact Petitioners filed separate, although virtually identical, applications with the Department in February, 1983 to construct separate catwalks from their properties, with platforms at the end of each catwalk. The dimensions of each catwalk were to be three feet by 350 feet, and the platform dimensions were to be six feet by twelve feet. This construction was to take place through a marsh and mangrove wetland and tidal creek known as Andrews Creek. Petitioner's properties adjoin and are in the interior of the creek. Intervenor's property is located at the mouth of Andrews Creek where it intersects a canal, and borders that area of the creek through which Petitioners proposed to construct their catwalks and platforms. On March 9, 1983 the Department notified Petitioners that a permit would be required for their project pursuant to Chapters 253 and 403, F.S., that their applications were incomplete, and that approval from the Department of Natural Resources in the form of a "consent of use of state-owned land" might be required. Petitioners provided additional information in support of their application, but were again notified on April 5, 1983 that Department of Natural Resources consent or approval was necessary in order to complete their application file. The Department prepared a permit application appraisal report on June 13, 1983 without the benefit of an on-site inspection for these applications. The appraisal was based upon written materials submitted by Petitioners in their applications. The appraisal recommended approval, noting that a single joint access facility would be preferable to the dual catwalk and platform configuration proposed by Petitioners As a result of this appraisal, the Department notified the Department of Natural Resources on July 1, 1983 that it intended to issue permits to the Petitioners but that it needed a response from the Department of Natural Resources concerning consent of use or approval pursuant to Section 253.77, F.S. Final action on Petitioners' applications could not take place until the Department received a reply from the Department of Natural Resources. Petitioners received a copy of this notice which was sent from the Department to the Department of Natural Resources. Petitioner was again notified on August 29, 1983 that consent or approval from the Department of Natural Resources was required before the Department's approval could be given. The August 29 letter also stated that Petitioners would have to obtain a letter of authorization and affidavit of ownership from any property owner, other than Petitioners themselves, whose property would be crossed by their construction. In response, Petitioners submitted to the Department an approval they received from the local homeowner's association, but this approval was not issued in compliance with the association's by-laws, and was therefore not a valid authorization and consent to the use of whatever interest the association has in Andrews Creek. On December 5, 1933 Petitioners notified the Department that they were amending their applications to eliminate the platforms at the end of their respective catwalks. On or about January 3, 1984 the Department of Natural Resources suggested to the Department that public notice of this project be given due to the type and location of the project. The Department notified Petitioners on January 26, 1984 that since numerous property owners might be affected by their project, a public notice would have to be published. In response to such publication, the Department received letters from other property owners on Andrews Creek which both opposed and supported Petitioners' project. At about the same time, the Department learned that Petitioners had already constructed their catwalks, with one large platform joining the ends of both catwalks. This construction took place despite the lack of either a permit from the Department or consent/approval from the Department of Natural Resources. Petitioners' applications indicate the use of six inch pilings and a portable jet pump with a one inch jet nozzle in the construction of their project. The Department performed a field inspection of the site and issued a permit application appraisal report dated May 3, 1984 which recommended denial of the permit applications while also confirming that the project had already been constructed. Denial was recommended since the dimensions of the actual construction exceeded the project dimensions described in the applications, considerable clearing of mangroves had taken place although the applications stated no such clearing would be required, and the adverse impact on water quality, marine productivity and other environmental factors the two catwalks were found to terminate with a large platform thirty-eight feet long by ten feet wide, with Zembillas' catwalk being 417.5 feet in length and Starzak's being 398 feet long. The combined project has a total square footage of approximately 3700 square feet, with each catwalk exceeding the permit exemption dimensions of 1000 square feet. Andrews Creek has been designated a conservation area and therefore the clearing and resulting damage to the mangrove community resulting from this project is particularly significant. As part of a permitting action in 1972 the State of Florida, through he Board of Trustees of the Internal Improvement Trust Fund, negotiated with Lindrick Corporation, the developer of the residential area surrounding Andrews Creek, to preserve certain areas from development. The Board of Trustees issued a permit to Lindrick Corporation "to perform certain works in the navigable waters of the State of Florida" which allowed half of Andrews Creek to be filled and which preserved the other half that remains today as a conservation area. The conservation area was to be protected from development. Thereafter, the Lindrick Corporation entered into an agreement with the homeowner's association whereby association approval would be required for development in the conservation area. Petitioners' project, as constructed, shades a larger area than it would have if built in accordance with their applications. Shading of wetlands can reduce dissolved oxygen levels of a wetland and thereby reduce the area's productivity. Although Petitioners offered a laboratory report showing exceedingly high dissolved oxygen levels in Andrews Creek, it appears that the sampling technique used resulted in the aeration of the sample which therefore did not reflect the true level of dissolved oxygen. Intervenor testified that he purchased his property because of the designation of Andrews Creek as a conservation area, and the resulting privacy of such a natural habitat. Petitioners' construction has obstructed Intervenor's view of the water and wetlands area of Andrews Creek, and infringes on this privacy due to the close proximity of Petitioners' platform to Intervenor's property. The catwalk is twelve to fourteen feet from the boundary of Intervenor's property. The portion of Andrews Creek crossed by Petitioners' project is navigable according to testimony presented, and as recognized in 1972 when a dredging permit was issued to the developer, Lindrick Corporation. The portion in question includes the original tidal creek, which is a tributary of the Gulf of Mexico via an excavated channel. Navigability of the creek has been adversely affected by this project. There would be a significant, adverse, cumulative effect on Andrews Creek if other surrounding property owners decided to construct docks similar to Petitioners' since this would involve additional clearing of mangroves, a reduction of dissolved oxygen in the water due to extensive shading, and the further elimination of the creek's navigability. There are eighteen (18) property owners on Andrews Creek, including Petitioners and the Intervenor, and there is a reasonable likelihood that other homeowners will apply for permits to construct similar docks.
Recommendation Based upon the foregoing findings of fact and conclusions of law it is recommended that: Petitioners permit applications be DENIED. Petitioners shall have forty-five (45) days from rendition of the Final Order in this case to remove their dock, consisting of catwalks, a connecting platform and support pilings. DONE and ENTERED this 1st day of April, 1985 at Tallahassee, Florida. DONALD D. CONN Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 1st day of April, 1987. COPIES FURNISHED: Charles G. Stephens, Esquire Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32301 Nicholas M. Zembillas 2001 Dewey Drive New Port Richey, Florida 33552 Martha Harrell Hall Esquire Post Office Drawer 190 Tallahassee, Florida 32301 W. L. Starzak 2003 Dewey Drive New Port Richey, Florida 33552 Victoria J. Tschinkel, Secretary Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32301
The Issue The issue is whether Respondent Crestwood Lakes Associates provided reasonable assurance that a modification to a conceptual surface water management permit complies with the permit criteria contained in statutes and rules.
Findings Of Fact Background This case involves a 900-acre parcel in the Loxahatchee Slough, west of the Florida Turnpike in Palm Beach County (County). Although the property occupies part of a slough, all of the wetlands in this case are isolated wetlands. Respondent Crestwood Lakes Associates (Applicant) owns the south 503 acres, Petitioner owns the north 287 acres, and the Village of Royal Palm Beach (Village) owns the remaining 115 acres, which abut the southwest boundary of the north parcel. The acreages do not total 900 acres because the numbers are approximate. The 900-acre parcel is generally bounded on the south by Okeechobee Boulevard and the north and east by the M-1 canal. The west boundary of the south part of the parcel adjoins a residential development known as Loxahatchee Groves, and the 115-acre parcel adjoins a County-owned preserve of at least 600 acres. Applicant’s land is undeveloped except for some landclearing. Petitioner’s land is partly developed, mostly in the south next to the boundary with Applicant’s land. The Village's 115 acres are a preserve, divided equally between wetlands and uplands. On February 11, 1988, Respondent South Florida Water Management District (District) issued surface water management (SWM) permit No. 50-00618-S-02 to Royal Palm Homes, Inc. for conceptual approval of a SWM system serving a residential development on the 900-acre parcel (1988 Permit). References to the Original Developer shall include Royal Palm Homes, Inc., its agents, lenders, and assigns, except for Petitioner and Applicant. The permitted development, which was known as the Royal Palm Homes PUD, comprises single-family and multifamily residences, wetland preserve areas, two 18-hole golf courses, and a park area. On August 3, 1994, Applicant filed SWM application number 940803-6 to modify the 1988 Permit to show the change in ownership and obtain conceptual approval of a modification to the permitted SWM system. The application was not complete when the new Environmental Resource Permit (ERP) rules replaced the old Management and Storage of Surface Water (MSSW) permit rules. On May 24, 1996, the District transmitted the staff report, which proposed the issuance of a permit modification. On June 13, 1996, the District approved the issuance of the proposed permit modification. On the same date, Petitioner filed its petition challenging the proposed agency action. Permits The first relevant SWM permit for the 900-acre parcel involved a larger parcel that includes the 900-acre parcel. On September 14, 1978, the District issued a two-page permit authorizing the “construction of a water management system serving 2073 acres of residential lands by waterways discharging into canal C-51.” This 1978 permit, which is identified as number 50-00618-S, contains a special condition calling for a minimum finished floor elevation of 18.0 feet National Geodetic Vertical Datum (NGVD). The next permit is the 1988 Permit, which is a substantial modification to the 1978 permit. The 1988 Permit covers only the previously described 900 acres and, as modified, currently remains in effect. The 1988 Permit requires the preservation of two large wetlands in the north parcel, just north of the 115-acre preserve; one wetland is about 30 acres and the other is about ten acres. The 1988 Permit requires the preservation of no other wetlands in the north parcel, but, in addition to the wetlands in the 115-acre preserve, the 1988 Permit requires the preservation of several much smaller wetlands in the south parcel. The staff report for the 1988 Permit divides into three basins the drainage area for the 900-acre parcel: a north basin of 98.9 acres, a central basin of 525.7 acres, and a south basin of 270.8 acres. The staff report states that basin runoff will pass through a system of inlets and culverts into a series of interconnected lakes, from which, through control structures, the runoff will pass into the M-1 canal and eventually into the C-51 canal. The staff report notes that the control elevations will be 17.25 feet NGVD for the north basin, 17.55 feet NGVD for the central basin, and 17.75 feet NGVD for the south basin. Under the discussion of environmental impacts, the staff report observes that the 1978 permit proposed for protection only 30 acres of wetlands among the 281 acres of isolated wetlands on the site. The staff report notes that “extensive” melaleuca invasion has taken place since the 1978 permit and only 160 acres of wetlands remain in “relatively good” condition, with much of this subject to melaleuca encroachment. Due to the “extensive seed source” and “seasonal drying of the wetlands,” the staff report predicts eventual melaleuca dominance of the “entire site.” The staff report asserts that the proposed development plan includes the protection of about 100 acres of the “best quality wetlands,” plus eight acres of wetlands created in conjunction with the golf courses and 15 acres of wetlands created as littoral zones in conjunction with the lakes to be constructed. The staff report calls a program “to eradicate all melaleuca from the site” “[t]he major environmental feature” of the proposed development plan. But this major environmental feature of the 1988 Permit is presently in jeopardy. One major component of the present case is that, following the conveyances of the three parcels by the Original Developer, the District has evidently concluded that no one is responsible to perform certain obligations under the 1988 Permit and no remedies are available for the nonperformance of these obligations. It appears that these conclusions are largely driven by the vagueness of the plan to eradicate the melaleuca. This plan is called the "Melaleuca Eradication Plan." The Melaleuca Eradication Plan is incorporated into the 1988 Permit. The Melaleuca Eradication Plan, which is dated December 11, 1987, recounts that the Original Developer and regulatory bodies agreed that the melaleuca should be “eradicated and a program for this should be developed and included as a part of the permit application.” The plan states that the eradication plan will cover the entire 900- acre site with the Original Developer performing the “initial . . . program” on the entire site, including the 115-acre preserve to be deeded to the Village. The Melaleuca Eradication Plan calls for the Original Developer to create a bonded authority to conduct the “ten-year melaleuca eradication program.” The program is phased to coincide with the projected 10-year buildout of the 3000-unit parcel. The Melaleuca Eradication Plan describes in detail the three phases of the program and exactly how the Original Developer will proceed to remove the melaleuca and restore wetlands by planting native wetland species in disturbed areas. The plan promises a yearly inspection followed by hand-removal of any seedlings discovered on the site. This last phase will terminate ten years after commencement of the first phase. A “Wetlands Monitoring/Maintenance Program” is also incorporated into the 1988 Permit. The Wetlands Monitoring/Maintenance Program, which is dated December 8, 1987, states that Dr. Dwight Goforth performed a wetlands survey of the 900-acre site in 1985 and divided wetlands into three categories based on their quality. The Wetlands Monitoring/Maintenance promises the preservation of 112.71 acres of wetlands comprising 98.81 acres of “large wetlands totally preserved” and nine wetlands totaling 13.9 acres that will be “partially preserved.” Also, the program will create golf course wetlands of 6.93 acres and littoral-zone wetlands around the lakes of 15 acres. Thus, the program summarizes, the “total wetland acreage preserved, enhanced and created will [be] 134.64 acres.” The Wetlands Monitoring/Maintenance Program describes a three-year monitoring program using transects to assist in the vegetative mapping of the site. The program also promises semiannual observations of birds, small rodents, and larger mammals using the wetlands and adjacent preserved uplands, as well as semiannual sampling for fish, macroinvertebrates, and amphibians. The Wetlands Monitoring/Maintenance Program outlines a plan to remove melaleuca and control algae buildup in the lakes. The program promises to contain algae through the use of “biological controls” and, when needed, hand-raking. The program also assures that the Original Developer will use a “conservative fertilization program” for the golf course and landscaped areas to reduce eutrophication in the created lakes. On February 18, 1988, the District issued its conceptual approval of the 1988 Permit. Among the special conditions of the 1988 Permit are Special Condition 15, which requires wetland monitoring and maintenance in accordance with the Wetlands Monitoring/Maintenance Program, and Special Condition 16, which requires melaleuca removal in accordance with the Melaleuca Eradication Plan. Also, Special Condition 17 requires low berms around protected or created wetlands, including littoral zones, to protect against sheetflow runoff from the golf course or other areas of intense development. The references in the preceding paragraphs to the responsibilities of the "Original Developer" imply greater clarity than is present in the Melaleuca Eradication Plan or Wetlands Monitoring/Maintenance Program. The passive voice predominates in both these documents, so it is sometimes difficult to determine on whom a particular responsibility falls. The Melaleuca Eradication Plan states clearly that "[the Original Developer] will conduct the initial melaleuca eradication on the entire site including the dedicated park area [i.e., the 115 acres]." The next sentence of the plan contemplates the conveyance of the 115 acres to the County. But, after these clear provisions, the Melaleuca Eradication Plan lapses into the passive voice almost invariably. The next two sentences read, "A bonded authority will be created to conduct the ten-year melaleuca eradication program" and "The eradication program will be carried out through a bonded agreement with the [Original] Developer to remove the melaleuca . . .." Alluding to the several phases of melaleuca eradication, the plan states only "[t]he eradication program will be completed in stages " Only two other sentences establishing responsibility for melaleuca eradication identify the responsible party. The end of the plan states that the "bonded authority responsible for initial eradication clearance will likewise provide a yearly inspection." One of the final sentences of the plan adds: "the bonding authority's crew will hand remove entire seedlings found on site." The Wetlands Monitoring/Maintenance Program is similar except that it does not once name the entity responsible for the monitoring and maintenance duties or hiring the firm or individual to conduct the actual work. The two special conditions incorporating these two documents likewise are in the passive voice, implying only that the responsibility belongs to the Original Developer. Given the vagueness of the melaleuca-eradication and wetlands-maintenance documents, it is not surprising that they fail entirely to address the issue whether these responsibilities run with the land, remain the responsibility of the Original Developer, or, for the eradication of melaleuca, remain the duty of the "bonded authority," if the Original Developer ever created such an entity, which appears highly doubtful. The documents likewise do not disclose the penalties for noncompliance. On June 16, 1988, the District issued a modification to the 1988 Permit for the construction and operation of a 110.9-acre residential development in Phase I, which occupies the central basin. On October 1, 1988, the United States Army Corps of Engineers (Army Corps) issued the Original Developer a permit to destroy 164 acres of wetlands on the 900-acre parcel. Special conditions of the 1988 Army Corps permit require the preservation of "115 acres of high quality wetlands," the creation of 18 acres of wetlands and 15 acres of littoral shelf, and the implementation of a "Melaleuca Eradication Program," which is the same program as is incorporated in the 1988 Permit. The 1988 Army Corps permit contains an attachment dated October 24, 1987. This attachment identifies the protected wetlands as the two large wetlands in the north parcel totaling about 40 acres, 58 acres in the 115-acre preserve, and 53.5 acres in the south parcel. The 1988 Army Corps permit protects several wetlands in the south parcel, including wetland numbers 14 (3.04 acres), 16 (1.6 acres), 23 (0.53 acres), 30 (2.6 acres), 44 (0.8 acres), 29 (1.08 acres), and 46 (3.0 acres). These wetlands, which total 12.65 acres, are seven of the nine wetlands partially preserved in the 1988 Permit, although some of the acreages vary from those preserved in the 1988 Permit. Unlike the District's permits (except for the subject proposed permit modification), the 1988 Army Corps permit addresses conveyances by the developer. The 1988 Army Corps permit states: "If you sell the property associated with this permit, you must obtain the signature of the new owner in the space provided and forward a copy of the permit to this office to validate the transfer of this authorization." Below the signature line of the 1988 Army Corps permit is language stating: When the structures or work authorized by this permit are still in existence at the time the property is transferred, the terms and conditions of this permit will continue to be binding on the new owner(s) of the property. To validate the transfer of this permit and the associated liabilities associated with compliance with its terms and conditions, have the transferee sign and date below. On March 1, 1989, the Original Developer conveyed the 115-acre preserve to the Village, which later leased the preserve to the County. The Original Developer had not eradicated the melaleuca at the time of the conveyance, nor has anyone since done so. On August 17, 1990, water elevations in the wetlands in Phase I reached 19.4 feet NGVD, washing out construction pads, roads, and in-ground utilities. On September 7, 1990, the District issued a stop-work request because the SWM system was not working as required. On September 28, 1990, the District approved interim measures to preserve the wetland hydroperiod and allow for wetland overflow. These measures include berming the residential areas in Phase I/Plat I adjacent to wetlands. On June 13, 1991, the District approved additional modifications to the 1988 Permit and the construction and operations permit for Phase I and issued a conceptual approval for works in the north and central basins. The revisions to the conceptual approval include adding two control structures to the north wetland that connect to the water management system in the north basin and adding a berm around the smaller of the two preserved wetlands in the north parcel. The construction approval was for a perimeter berm along the south wetland and park areas. On June 24, 1992, the District issued a staff report recommending issuance of another modification of the 1988 Permit for the conceptual approval of a SWM system to serve the 900-acre parcel and approval of construction and operation of a SWM system to isolate and control the existing onsite wetlands and revise the control structure for the central basin. The staff report explains that this modification proposes berming the wetlands to the 100-year, three-day peak elevation. The staff report notes that the wetlands basin consists of 295.18 acres of wetlands, including 155.85 acres of “wetlands/uplands.” The staff report notes that the north basin contains 107.41 acres of “good quality wet prairie wetlands” with “minimal” melaleuca encroachment. The staff report restates that the purpose of the modification is to berm all of the wetlands and uplands not planned for development. Special Condition 19 requires the Original Developer to dedicate as conservation and common areas in deed restrictions the “wetland preservation/mitigation areas, upland buffer zones, and/or upland preservation areas," so that these areas are the “perpetual responsibility” of a named property owners’ association. Special Condition 22 states that “a wetland monitoring and maintenance program” and “a melaleuca eradication program” “shall be implemented,” but the condition does not expressly state by whom. Special Condition 22 requires that the work implementing these programs conform to these “approved environmental programs as outlined in the [1988 Permit].” Special Condition 25 provides that, on submittal of an application for construction approval in the south basin (Phase II), the "permittee shall submit a detailed wetland construction mitigation, monitoring and maintenance plan.” In evaluating the plan for approval, the District shall apply the “environmental criteria in effect at the time of construction permit application.” Although the approval of the District is not attached to the staff report, the District approved the June 24, 1992, staff report and proposed permit. The 1992 permit modification did not address the issue of who was responsible for melaleuca eradication after the sale of the property. On November 10, 1993, the staff report accompanying another request for a permit modification restates the special conditions of earlier permit modifications. Special Condition 23 restates the requirement that a melaleuca eradication program “shall be implemented,” again not stating by whom. Special Condition 23 now requires the completion of the melaleuca eradication program by February 25, 1994. The omission of a referenced exhibit to the permit from the exhibit filed in this case prevents a determination that this is the same as the Melaleuca Eradication Plan incorporated in the 1988 Permit and restated in the 1992 modification, although it probably is. In any event, Special Condition 23 concludes in another sentence lacking a stated or implied subject: “Maintenance of the preserved wetlands and berm planting areas shall be conducted in perpetuity to ensure that the conservation areas are maintained free from exotic vegetation (Brazilian pepper, Australian pine and melaleuca) . . ..” Although the record does not contain the written approval of the District to the staff report, the District approved the staff report dated November 10, 1993. On November 12, 1993, the Original Developer conveyed by special warranty deed the north to Petitioner. The deed is subject only to "easements, declarations, restrictions and reservations of record . . .." The record does not provide recording information for the deed. The Original Developer probably conveyed the south parcel to Applicant in the same fashion and at the same approximate time. Almost five months later, on March 29, 1994, the Army Corps issued another permit for the 900-acre parcel. Although the Original Developer had conveyed at least the north parcel, the Army Corps issued the 1994 permit to the Original Developer. The 1994 Army Corps permit authorizes the destruction of 158 acres. The general conditions governing transfers are the same as those in the 1988 Army Corps permit. The special conditions of the 1994 Army Corps permit require the permittee to preserve and enhance only 110 acres of high quality wetlands, instead of preserving 115 acres of such wetlands, as was required in the 1988 Army Corps permit. The 1994 Army Corps permit drops the requirement of creating eight acres of wetlands and 15 acres of littoral zone, as was required in the 1988 Army Corps permit, but requires the preservation of what appears to be the 39.5-acre preserve that is proposed by Applicant in the subject permit modification, as described below. Special Condition 3 of the 1994 Army Corps permit adds that all preserved areas "will be maintained in perpetuity free of Melaleuca. The permittee agrees to develop a bonded Melaleuca eradication program for the entire 906 acres. Copies of the bonded agreement will be provided to this office for approval before development can commence." The next permit activity affecting the 900-acre parcel is the subject application filed by Applicant on August 3, 1994, for its 503-acre parcel. On May 24, 1996, the District issued a staff report for conceptual approval of a SWM system proposed by Applicant for its 503-acre parcel. On June 13, 1996, the District issued an addendum to the staff report that contains another special condition that is not especially relevant to this case. In the background section, the staff report mentions the flooding of Phase I of the north parcel and states that the District had “assumed the adjacent wetlands would flow away from the development.” The staff report outlines the modifications implemented to eliminate the flooding; these modifications include connecting the M-1 canal, through inlets, with several wetlands located in the north and central basins. According to the staff report, Petitioner’s north parcel, which totals 287.34 acres, includes the Phase I/Plat 1 area, north basin, and part of central basin south of Phase I. Describing Applicant’s proposal, the staff report states that a preserve of 39.5 acres will be located in the northwest corner of the south parcel, adjoining the east boundary of the 115-acre parcel. The staff report states that the 39.5-acre preserve will sheetflow through cuts in the berm to wetlands in the 115-acre preserve. The 115-acre preserve is connected to the SWM system permitted on November 10, 1993, to eliminate flooding from these wetlands, whose control elevation is 19 feet NGVD. The staff report describes the south parcel as “dominated by flatwood habitat,” within which are stands of Australian pine and other exotic plant species that have recently been spreading across the site. The onsite wetlands are 4.93 acres of wet prairies, 18.4 acres of pond cypress strands, 1.56 acres of isolated marsh, 3.5 acres of cypress mixed with pine flatwood, and 163.91 acres of melaleuca. The staff report finds that only the 4.93 acres of wet prairies and 18.4 acres of cypress are in good condition, but melaleuca has become established in many of the wet prairies. The 1.56 acres of freshwater marshes and 163.91 acres of melaleuca are in poor condition. The 3.5 acres of cypress mixed with pine flatwoods are in fair condition. As for listed species, the staff report mentions only the possibility that herons might forage onsite during periods of standing water. Summarizing the impact of the proposed project on wetlands preservation, the staff report endorses the hydrologic reconnection of the 39.5-acre wetland/upland site with the 115-acre wetland. The staff report notes that water levels in the 115-acre preserve, which has been bermed to 21 feet NGVD, have stabilized at 19 feet NGVD. The staff report asserts that the “proposed wetland impacts (183.54 acres) were previously permitted under the conceptual permit application” for the original 1988 Permit. The staff report adds that this modification is to “change a portion of the original mitigation requirements . . . and includes impacts to a 6.78 acre wetland area that was previously permitted to be preserved.” But the staff report does not recommend the preservation of this wetland “[d]ue to the reduced hydrology and proximity to the proposed upland development” and the mitigation and compensation provided by the 39.5-acre preservation area. The staff report states that 8.76 acres of the 39.5- acre preserve are wetlands, and the remainder are uplands. As for the 8.76 acres of wetlands, the staff report lists 0.67 acres of mixed cypress and pine flatwoods, 4.93 acres of wet prairies, and 3.16 acres of cypress. Applicant would also restore 4.95 acres of pine flatwoods. As for the 183.54 acres of wetlands to be destroyed, the staff report lists 2.83 acres of mixed cypress and pine flatwoods in fair condition, 15.24 acres of cypress in fair condition, 1.56 acres of freshwater marshes in poor condition, and 163.91 acres of melaleuca in poor condition. Addressing the mitigation and monitoring elements of the current proposal, the staff report states that the modification would eliminate the creation of 15 acres of littoral wetlands around SWM lakes and 7.99 acres of marshes in golf courses in return for the creation of the 39.5-acre preservation area. The staff report assures that Applicant will perpetually manage and maintain the 115-acre preserve. Conceding that the 1988 Permit also required long-term maintenance of the 115-acre parcel, the staff report notes that the initial eradication effort was never completed. The staff report mentions an “access agreement” giving Applicant the authority to enter the 115-acre preserve for mitigation and monitoring, but “anticipat[es]” that Applicant will submit an application for another permit modification, on behalf of the two governmental entities, so that Applicant can “assume future maintenance responsibilities for this area.” As is clarified by the maintenance and monitoring plan, which is part of the proposed permit, Applicant's expectation is that the County and Village, not Applicant, will assume future maintenance responsibilities for the 115-acre preserve. The staff report concludes that the District should issue the permit subject to various conditions. Special Condition 1 is that the minimum building floor elevation is 20 feet NGVD. Special Condition 16 requires the implementation of a wetland mitigation program and requires Applicant to create 4.95 acres of marsh; restore 3.16 acres of cypress, 4.93 acres of marsh, and 0.67 acres of mixed forest; and protect 25.79 acres of uplands. Special Condition 17 sets performance criteria for the mitigation areas in terms of percentage and length of survival of vegetation. Special Condition 17 supplies completion dates for monitoring reports. Special Condition 21 addresses listed species. Noting that listed species have been seen onsite or the site contains suitable habitat for such species, Special Condition 21 requires Applicant to coordinate with the Florida Game and Fresh Water Fish Commission or the U. S. Fish and Wildlife Service for guidance, recommendations, or permits to avoid impacts to such species. The monitoring and maintenance plan does not address direct and contingent liabilities for maintenance and generally is a poor candidate for enforcement. In addition to the vagueness of the passive voice, the plan is, at times, simply unreadable, as, for example, when it concludes boldly, but enigmatically: The site as a whole is evolving hydrologic trends which permits successional seres development toward communities with shorter hydroperiods and ultimately, toward more upland transitional and/or exotic species dominance of historically wetland habitats. Long-term prospectives infer that successional deflection has become a severe detriment for natural environmental control to alter the present scenario. Active management coupled with graduated balanced in hydrologic restoration and created habitat elements will become the processes engineered to obtain an infusion of probabilities fashioned to inscribe a regenerative adaptation to the present site condition while fostering in situ processes, to optimize derived functions, for the maintenance of both habitat and wildlife over the long-term existence of the Preserve. (Sic.) Water Quality Impacts Petitioner does not contend in its proposed recommended order that the proposed project fails to meet applicable requirements regarding water quality. Applicant has provided reasonable assurance that the proposed permit modification would not violate State water quality standards. Flooding Petitioner contends in its proposed recommended order that the proposed permit modification would not meet applicable requirements regarding water quantity and flooding. However, Applicant has provided reasonable assurance that the project would not violate these requirements. There are several aspects to a SWM system. Undeveloped land stores and conveys rainfall through soil and surface storage. An artificial SWM system alters the undeveloped land’s storage capacity by the addition of a storage and drainage system, such as, in this case, conveying water through the soil into storm drains and then to lakes to store surface runoff prior to release, through an outfall structure, into a receiving body of water--in this case, the M-1 canal. The SWM system hastens the conveyance of stormwater runoff offsite. The control elevation of a SWM system is the height at which water in the lakes will flow through the outfall structure into the receiving body of water. Except during the dry season, the control elevation tends to establish not only the water level of the SWM lakes, but also of the nearby water table. The hastening of drainage offsite with the establishment of control elevations produce the drawdown effect of SWM systems. As to flooding, the basic underlying dispute between Petitioner and Respondents is whether to use the pre- or post- development depth to water table. In determining whether an applicant has provided reasonable assurance as to the impact of a proposed development on wetlands, one would project the effect of any post-development drawdown on the wetlands themselves and their functions and inhabitants. It would be illogical not to do the same in determining whether an applicant has provided reasonable assurance as to the impact of a proposed development on flooding. Pre-development, the average depth to water table on Applicant’s property is as little as two feet. Post- development, the average depth to water table on Applicant’s property will be five feet, which is the difference between the control elevation of 14 feet NGVD and ground elevation of 19 feet NGVD. Petitioner’s evidence concerning flooding is flawed because its expert witness based his calculations on an average depth to water table of two feet on Applicant’s property. He did not adjust for the considerable drawdown effect of the SWM system. The District table allows for no more than four feet between the water table and ground, so there is an added margin of safety in the ensuing flooding calculations. Another important factor in the flooding calculations is the soil type in terms of permeability. The District properly characterized the prevailing soils as flatwoods, and the soils onsite are in the category of “good drainage.” Applicant’s suggestion that flooding calculations use the post-development soils is rejected. Post-development depths to water table are used because they can be calculated to predict post-development conditions accurately. Applicant produced no proof that it would replace such massive amounts of soil from the site with more permeable soils so as to justify reclassifying the soil type. The District's flooding calculations probably overstate the risk of flooding in the three-day, 100-year design storm because they ignore lake bank storage, which is the additional amount of water that a lake can store in its sloped banks above the typical water elevation. The District could have relied on the effect of lake bank storage for additional assurance that the proposed project will not result in flooding. The proposed project contains a large number of long, narrow lakes, which will thus have a relatively high percentage of lake banks to lake area. Additionally, the District has raised the minimum floor elevation at this site by two feet over 18 years. Whatever other effects may follow from this trend, the higher floor elevation offers additional protection to onsite improvements. The flooding of Petitioner’s property seven years ago understandably is a matter of concern to Petitioner. Applicant proposes to change the configuration of drainage basins, but the District has adequately addressed the drainage issue, and this is not the first time in the 20-year permitting history of this property that the District has approved a reconfiguration of basins. Also, in the 1988 Permit, the District incorrectly projected the direction of runoff under certain conditions. However, the flooding was partly due to inadequate road- drainage facilities. Following the flooding, the Original Developer enlarged these features and bermed the flooding wetlands, so as to eliminate the flooding of developed areas due to design storm events. On balance, Applicant has proved that the proposed permit modification would not adversely affect flooding or water quantity. Environmental Impacts A. Wetlands Petitioner contends in its proposed recommended order that the proposed permit modification would not meet applicable requirements regarding environmental impacts to wetlands. Applicant has failed to provide reasonable assurance that the proposed work would not violate these requirements. There are two major deficiencies in the District's analysis of wetland impacts and mitigation or compensation. First, the proposed permit modification includes mitigation or compensation in the form of melaleuca removal. But prior permits have already required the same work, no one has ever done the work, and the District does not know if these permit requirements are still enforceable. Second, the proposed permit modification ignores 13.9 acres of preserved wetlands in the 1988 Permit, allowing their destruction without mitigation or compensation. The permitting process requires the District to balance the impacts of development and mitigation or compensation on the natural resources under the District's jurisdiction. Balancing these impacts in issuing the 1988 Permit, the District required the complete eradication of melaleuca in return for permitting the residential, institutional, and recreational development proposed by the Original Developer. District staff, not the Original Developer or Petitioner, called the Melaleuca Eradication Plan “the major environmental feature” of the development plan approved by the 1988 Permit. The major environmental feature of the 1988 Permit clearly justified significant development impacts on natural resources. To justify additional development impacts on natural resources, the District now proposes to count again another developer’s promise to eradicate the melaleuca. The District claims that the term of the original melaleuca protection plan was only ten years, not perpetual as is presently proposed. However, the District's claim ignores Special Condition 23 in the 1993 permit modification. This condition set a deadline of February 25, 1994, for the eradication of melaleuca and made perpetual the requirement that one or more of the potentially responsible parties--the Original Developer, Petitioner, Applicant, the bonded authority, the property owners' association, or transferees-- maintain the wetlands free of melaleuca and other exotics. Unfortunately, this “major environmental feature” of the 1988 Permit, as well as subsequent permit modifications, was so poorly drafted as to leave potentially responsible parties unsure of their legal obligations. The District tacitly suggests that it cannot enforce the obligations imposed by the 1988 Permits and later modifications for the eradication of melaleuca. But there is presently no reason for the District to resort again to permitting without first reviewing carefully its enforcement options. The District should first determine whether anyone will voluntarily assume these obligations. As a business consideration, Petitioner may choose to eradicate the melaleuca from the north parcel and 115-acre preserve to prevent Applicant from providing this service and claiming that it should receive compensation credit against additional environmental impacts permitted by a modification of the 1988 Permit. Maybe the County or Village has already budgeted funds for this work. If no party offers to perform the necessary work, the District must next determine its legal rights and the legal obligations of these parties. Depending on the results of this research, the District may need to consider litigation and the cessation of the issuance of construction and operation permits on the 900-acre parcel or either the north or south parcel. At this point, the District should discuss joint litigation or permit revocation with the Army Corps, whose 1994 permit requires the permittee to develop a bonded melaleuca-eradication program and apparently imposes on the permittee the responsibility to maintain all preserved areas free of melaleuca. Only after having exhausted these options may the District legitimately conclude that melaleuca eradication on any part of the 900 acres represents fair compensation for the development impacts on jurisdictional natural resources. The second major problem as to wetlands impacts concerns the calculation of wetlands acreages to be destroyed by the proposed permit. The 1988 Permit expressly incorporates the Wetlands Monitoring/Maintenance Program. This program, as an operative part of the 1988 Permit, represents that the developer will “partially preserve. . .” nine wetlands totaling 13.9 acres. The partial preservation of wetlands does not mean that a five-acre wetland will remain a five-acre wetland, except that its function will be impaired. Partial preservation means that, for instance, two acres of a five- acre wetland will be preserved. It is impossible for the District to have required mitigation to offset the destruction of these 13.9 acres of wetlands because the District denies that the 1988 Permit required the partial preservation of these nine wetlands. As noted below, neither the District nor Applicant can identify all of the wetlands that make up the 13.9 acres. Rather than account for these wetlands that were to have been partially preserved, the District instead contends that this undertaking by the Original Developer was ineffective or nonbinding because it was overriden by contrary statements in the staff report. Not so. The specific provisions delineating the preserved wetlands area in the Wetlands Monitoring/Maintenance Program, which was prepared by the Original Developer, override more general statements contained in the staff report accompanying the permit. There is not necessarily a conflict between the staff report and the Wetlands Monitoring/Maintenance Program. The staff report states that the plan “includes the protection of approximately 100 acres of the best quality wetlands,” together with the creation of eight acres of golf course wetlands and 15 acres of lake littoral zones. The plan “includes” these wetlands among those preserved or created; the word suggests that the list is not exhaustive, but only illustrative. Alternatively, if the list were exhaustive, the preservation of “approximately” 100 acres reasonably encompasses the 112.71 acres of partially or totally preserved wetlands cited in the Wetlands Monitoring/Maintenance Program. More to the point, on October 26, 1987, Donald Wisdom, the engineer handling the 1988 Permit, prepared a memorandum for the file stating that the total acreage of wetlands to be preserved or created was 134.45. This figure represents an insignificant deviation of 0.19 acres from the total listed in the Wetlands Monitoring/Maintenance Program, which was dated six weeks later, on December 8, 1987. In the October 26 memorandum, Mr. Wisdom describes the preserved wetlands as 111.46 acres of A- and B-quality wetlands. This is 1.25 acres less than the acreage in the Wetlands Monitoring/Maintenance Program. These small discrepancies were eliminated by November 18, 1987, when Mr. Wisdom wrote a memorandum noting that the program called for the total preservation of 98.81 acres and partial preservation of 13.9 acres. Adding the created wetlands, the new total for preserved or created wetlands was 134.64 acres. A month later, a District employee wrote a memorandum to the file, expressing his “main concern” that the proposed development would protect only 99 acres of wetlands. It is unclear why the employee mentioned only the 98.81 acres slated for preservation. Perhaps he was confused or mistaken. But the misgivings of a single employee do not constitute the rejection by the District of a developer's proposal to preserve nearly 14 acres of high-quality wetlands. The staff report for the 1988 Permit notes that the 900-acre site contained about 281 acres of wetlands. If the 1988 Permit required the preservation, as an entire wetland or part of a larger wetland, of 112 acres of wetlands, then the 1988 Permit allowed the destruction of 169 acres, which is consistent with the 164 and 158 acres allowed to be destroyed by the 1988 and 1994 Army Corps permits. However, by the 1996 permit modification, the staff report refers, without explanation or justification, to the permitted destruction of 183.54 acres of wetlands--evidently adding the 13.9 acres to the 169 acres previously permitted to be destroyed. Tab 13 of the Wisdom bluebook identifies the nine wetlands constituting the 13.9 acres, which are entirely in Applicant's south parcel. Except for three, all of these wetlands were characterized as A-quality, meaning that they are in good to excellent condition and “have not been stressed significantly from the biological viewpoint.” B-quality wetlands are in disturbed condition and “are in various stages of biological stress caused primarily by a lowered water table and/or melaleuca invasion.” C-quality wetlands are highly disturbed and “are substantially degraded biologically.” The 13.9 acres of wetlands comprise wetland numbers 23 (0.5 acres), 46 (0.4 acres), 44 (0.6 acres), 37 (0.4 acres), 29 (1.1 acres), 20 [sometimes misreported as 21] (3.9 acres), 30 (2.6 acres), 16 (1.5 acres), and 14 (2.9 acres). Wetland numbers 46 and 29 are B-quality, and wetland number 20 is C-quality. The wetlands shown in District Exhibit 4 and Applicant Exhibit 3 inaccurately portray the wetlands constituting the missing 13.9 acres. A internal memorandum to the file notwithstanding, the District predicated the 1988 Permit in part on the preservation of 112.71 acres of functioning wetlands, including the 13.9 acres that the District now disclaims. The mitigation and compensation required of Applicant in the present case ignored the destruction of these wetlands. The District's analysis of mitigation and compensation in this case was fatally flawed by these two deficiencies. But more deficiencies exist in the District's analysis of wetland impacts. The District relied on faulty data in reviewing Applicant's request for a permit modification. Undercounting the extent of wetlands by at least 21 acres and their condition by an indeterminable amount, Applicant presented to the District a materially inaccurate picture of the wetland resources on the south parcel. Despite disclaimers to the contrary, the District relied on this inaccurate data in reviewing Applicant's request for a permit modification. There are possible problems with 39.5-acre preserve offered by Applicant. This parcel contains less than nine acres of wetlands, including two wetlands that Applicant may already be required to preserve under the 1994 Army Corps permit. At the same time, Applicant's proposal may include the destruction of a third wetland that is to be preserved under the 1994 Army Corps permit. The best rendering in the record of the 1994 Army Corps permit may be Applicant Exhibit 4, which shows eight large wetland areas to be “preserved/enhanced/created.” Two of these are the 10- and 30-acre wetlands on Petitioner’s property, which were preserved in the 1988 Permit. Three of the eight wetlands are in the 115-acre preserve; these were also preserved in the 1988 Permit. The remaining three wetlands to be preserved, enhanced, or created under the 1994 Army Corps permit are in the north end of Applicant’s property. It is difficult to estimate acreage given the scale of the drawing, but the two westerly wetlands are about 4-5 acres each and the easterly wetland is 3-3.5 acres. Subtracting the total preserved acreage of 110 from the acreage identified in the preceding paragraph, the total acreage of these remaining three wetlands is about 12. The two westerly wetlands are in the 39.5-acre preserve that Applicant offers as mitigation in the present case. According to Applicant Exhibit 6, the easterly wetland, or at least the most valuable part of it--the center--is slated for destruction if the District grants the subject permit modification. The proposed destruction of the third wetland is a matter of greater interest to the Army Corps than to the District, but the offer to preserve the other two wetlands really does not provide anything in return for the permitted development impacts because these two wetlands are already preserved under the 1994 Army Corps permit. As the District and Applicant contend, golf course marshes and littoral zones are typically of little environmental importance. Although the 1988 Permit addresses some of these problems, although without supplying any performance standards, golf courses themselves are often conduits of fertilizers and pesticides into the groundwater and nearby surface water. The District and Applicant justifiably question the value of the golf courses approved in the 1988 Permit as wildlife corridors. It is unclear what wildlife would use the corridor, which is surrounded by residential development and bounded by Okeechobee Boulevard. Other factors also militate in favor of Applicant's proposal. But, as the record presently stands, there is no way to find that Applicant has provided reasonable assurance that the proposed development and related mitigation and compensation, as described in the subject permit modification, meet the applicable criteria. The District substantially undervalued the environmental impacts of the proposed modification while substantially overvaluing the environmental impacts of Applicant's proposed contributions in the form of mitigation and compensation. To find adequate assurance as to wetland impacts in these circumstances, where the District did not perform an informed balancing of various impacts in a large-scale development, would permit the District to transform the unavoidably imprecise task of balancing wetland impacts into an act of pure, unreviewable discretion. Listed Species The only relevant listed species onsite is the gopher tortoise, which is a species of special concern. Gopher tortoises use the site to an undetermined extent. Applicant's suggestion that someone brought the tortoises to the site is rejected as improbable. However, due to the resolution of the wetlands issue, it is unnecessary to determine whether Applicant provided reasonable assurance as to the value of functions provided to wildlife and listed species by wetlands. Procedural Issues A. Standing Petitioner has standing due most obviously to flooding considerations. Additionally, the SWM system permitted in 1988 is for the entire 900-acre parcel, of which Petitioner’s parcel is a part. Applicability of ERP Rules The proposed permit modification would substantially affect water resources. The proposed permit modification would substantially increase the adverse effect on water resources. Requirement to Delineate Wetlands Due to the resolution of the wetlands issue, it is unnecessary to determine whether Applicant met applicable requirements concerning the delineation of wetlands. Improper Purpose Petitioner did not challenge the proposed permit modification for an improper purpose. Relevant Provisions of Basis of Review The District revised its Basis of Review after the adoption of ERP rules. Although the order concludes that the District should have applied the ERP rules, and thus the ERP Basis of Review, the order shall discuss both versions of the Basis of Review because the District ignored numerous provisions of both documents in approving Applicant's request for a permit modification. Section 4.6 MSSW Basis of Review requires the District to consider "actual impact" to the site by "considering the existing natural system as altered by the proposed project[,]" including "positive and negative environmental impacts." Section 4.6 requires the District to "balance" these impacts "to achieve a reasonable degree of protection for significant environmental features consistent with the overall protection of the water resources of the District." The proposed permit modification fails to comply with several provisions of Appendix 7 of the MSSW Basis of Review, such as Sections 4.2 requiring a detailed description of the isolated wetlands to be destroyed; 5.1.1(d) favoring the protection of isolated wetlands over their destruction, mitigation, and compensation, which are considered "only when there are no feasible project design alternatives"; and 5.1.6 prohibiting the alteration of water tables so as to affect adversely isolated wetlands. The proposed permit modification also violates various provisions of the ERP Basis of Review. Section 4.0 of the ERP Basis of Review sets the goal of permitting to be "no net loss in wetland . . . functions." Sections 4.2 and following generally require balancing. Section 4.2.1 predicates District approval on a showing that the SWM system does not cause a "net adverse impact on wetland functions . . . which is not offset by mitigation." The ERP provisions first require that the District "explore" with an applicant the minimization of impacts prior to considering mitigation. Section 4.2.2.4(c) specifically imposes monitoring requirements for SWM systems that "could have the effect of altering water levels in wetlands." Sections 4.3.2.2 and following discuss mitigation ratios under the ERP Basis of Review. If the District can explicate a policy to count as mitigation wetlands acreage already preserved under Army Corps permits, the ratios in this case might warrant further consideration, assuming Applicant resubmits an application for permit modification. But it would be premature to consider the ratios on the present record for several reasons. The District has not proved such a policy. If such a policy counts such wetland acreage, on the theory that the District protects function and the Army Corps protects merely the wetland, the record is insufficiently developed as to the functions of the wetlands proposed for protection, as well as the functions of the 13.9 acres of wetlands proposed for destruction. Also, the District has not sufficiently explored project minimization, as is now required under the ERP Basis of Review.
Recommendation It is RECOMMENDED that the District enter a final order denying Applicant's request for a permit modification. ENTERED in Tallahassee, Florida, on June 13, 1997. ROBERT E. MEALE Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (904) 488-9675 SUNCOM 278-9675 Fax Filing (904) 921-6847 Filed with the Clerk of the Division of Administrative Hearings on June 13, 1997. COPIES FURNISHED: Jeffrey D. Kneen John F. Mariani J. Barry Curtain Levy Kneen 1400 Centrepark Boulevard, Suite 1000 West Palm Beach, Florida 33401 Ronald K. Kolins Thomas A. Sheehan, III Moyle Flanigan Post Office Box 3888 West Palm Beach, Florida 33402 John J. Fumero Marcy I. LaHart Office of Counsel South Florida Water Management District 3301 Gun Club Road West Palm Beach, Florida 33406 Samuel E. Poole, III Executive Director Post Office Box 24680 West Palm Beach, Florida 33416
