Findings Of Fact The Petitioner is a wholly owned subsidiary of Florida Land Company which is, in turn, a wholly owned subsidiary of the Continental Group, Inc., a New York corporation. The parent developer companies are providing and will continue to provide the required financial backing. The Utility served 421 primarily residential customers at the end of 1979, the test year agreed to by the parties. This was the first rate proceeding involving the Utility since it was established in 1975. Service The Utility is providing satisfactory water and sewer service. There were no service complaints presented at the public hearing by the customers, nor were there any citations or corrective orders outstanding. Rate Base The Utility experienced rapid growth during the 1976 - 1979 period, increasing the number of customers served from 62 to 421. Therefore, year end rate base rather than average rate base should be utilized. 1/ The water and sewer rate bases are $155,920 and $179,360 respectively. These amounts are based on the computations detailed below and incorporate proposed Commission adjustments to which the utility stipulated. In addition, reductions to plant in service and construction work in progress (CWIP) were made by the Utility to reflect excess plant capacity which is of no benefit to current customers. The Utility replaced its reverse osmosis water treatment plant with a lime softening system in 1979. The new facility will be somewhat more expensive to operate but will improve water quality and fire flow (pressure). Because of the reverse osmosis water treatment plant retirement, the $3,615 in building and $34,541 in treatment plant assets remaining on the Utility books should be removed. This is a total adjustment to Utility Plant in Service of $38,156. A further reduction in both water and sewer rate base is needed to adjust the working capital allowance to the standard authorization, which is one-eighth of operation and maintenance expenses. The proper amounts to he authorized in these accounts are $5,338 water and $2,931 sewer. TEST YEAR PER UTILITY UTILITY ADJ. TEST ADJ. TO YEAR PER COMM. ADJ. & CORRECT. TO UTILITY ADJ. UTILITY TEST YEAR EXHIBIT BALANCE TEST YEAR $820376. $-551059. $269317. $-38156. $231161. 57866. -57866. 0. 0. 0. -18841. 17155. -1686. 0. -1686. -238419. 159526. -78893. 0. -78893. Water Rate Base Plant in Svc. C.W.I.P. Accum. Depr. C.I.A.C. Net of Amort. Working Capital Allowance 4755. 1421. 6176. -838. 5338. Income Tax Lag 0. 0. 0. 0. 0. Rate Base $625737. $-430823. $194914. $-38994. $155920. Sewer Rate Base UTILITY COMM. ADJ. TEST UTILITY ADJ. TEST & CORRECT. YEAR PER ADJ. TO YEAR PER TO UTILITY ADJ. UTILITY TEST YEAR EXHIBIT BALANCE TEST YEAR Plant in Svc. $591945. $-205690. $386255. $0. $386255. C.W.I.P. 77919. -77919. 0. 0. 0. Accum. Depr. -2815. 2551. -264. 0. -264. C.I.A.C. Net of Amort. -321611. 112049. -209562. 0. -209562. Working Capital Allowance 2558. 401. 2959. -28. 2931. Income Tax Lag 0. 0. 0. 0. 0. Rate Base $347996. $-168608. $179388. $-28. $179360. Operating Revenues The Utility is seeking water revenue of $41,429 and sewer revenue of $35,550. Computations and adjustments in support of these amounts along with test year expenses are detailed below. Because of the extraordinary expenses associated with replacement of the water treatment plant, it would not be appropriate to utilize test year data to determine operating costs. Therefore, a projected or pro forma operating expense of $42,789 removing replacement expenses is proper. A further adjustment to water operations is required to eliminate $1,987 of depreciation expense on contributed property as not authorized by current law. 2/ In addition, the useful life of various items of equipment should be increased to periods of 20 to 40 years. These extended depreciation periods are based on an engineering study which the Utility does not challenge. Finally, the requested revenue increase of $27,432 and the associated gross receipts tax of $686 are reversed to show test year operating results. The requested sewer revenue increase of $19,413 and gross receipts tax of $485 are also reversed on the sewer operating statement to show test year operating results. As with the water plant, depreciation on contributed sewer plant is disallowed, reducing depreciation by $5,261. Water Operating Statement UTILITY COMM. ADJ. TEST UTILITY ADJ. TEST & CORRECT. YEAR PER ADJ. TO YEAR PER TO UTILITY ADJ. UTILITY TEST YEAR EXHIBIT BALANCE TEST YEAR $ 14006. $ 27423. $ 41429. $-27423. $ 14006. 38039. 11368. 49407. -6678. 42789. 0. 0. 0. 0. 0. 6325. 3762. 10087. -5525. 4562. 0. 0. 0. 0. 0. 1979. 500. 2479. -686. 1793. 0. 0. 0. 0. 0. 0. 0. 0. 0. 0. Oper. Revenues Oper. Expenses Operation Maintenance Depreciation Amortization Taxes Other Than Income Other Expenses Income Taxes UTILITY COMM. ADJ. TEST UTILITY ADJ. TEST & CORRECT. YEAR PER ADJ. TO YEAR PER TO UTILITY ADJ. UTILITY TEST YEAR EXHIBIT BALANCE TEST YEAR Total Operating Expenses $46343. $15630. $61975. $-12889 $49084. Oper. Income -32337. 11793. -20544. -14534. -35078. Rate Base $ 825737. $ 194914. $ 155920. Rate of Return -5.17 pct. -16.54 pct. -22.50 pct. Oper. Sewer Operating Statement UTILITY COMM. ADJ. TEST UTILITY ADJ. TEST & CORRECT. YEAR PER ADJ. TO YEAR PER TO UTILITY ADJ. UTILITY TEST YEAR EXHIBIT BALANCE TEST YEAR Revenues $16137. $19413. $35550. $-19413. $16137. Oper. Expenses Operation 20462. 3208. 23670. -233. 23437. Maintenance 0. 0. 0. 0. 0. Depreciation 619. 9060. 9679. -5261. 4418. Amortization 0. 0. 0. 0. 0. Taxes Other Than Income 1747. 630. 2377. -485. 1892. Other Expenses 0. 0. 0. 0. 0. Income Taxes 0. 0. 0. 0. 0. Total Operating Expenses $22828. $12898. $35726. $-5979. $29747. Oper. Income $-6691. $6515. $-176. $-13434. $-13610. Rate Base $847996. $179388. $179360. Rate of Return -1.92 pct. -10. pct. -7.59 pct. Capitalization Debt $ 555,624. 60.96 percent Customer Deposits 6,195. .68 The capitalization of the Utility is as follows: Amount Percent to Total Common Equity 349,627. 38.36 $ 911,446. 100.00 percent Rate Design Both parties seek adoption of a base facility charge rate structure. This rate design provides a fixed charge to each customer served computed on that customer's share of fixed operating costs. The second element of the base facility charge represents the variable cost of water actually used. This rate design provides an equitable method of allocating service costs and has been adopted in virtually all recent water and sewer rate proceedings. The base facility charge should also be utilized where there is a temporary discontinuance of service. The Commission proposes a tariff revision incorporating a monthly standby charge equal to the base facility charge. Again, this method allocates the Utility's readiness to serve costs equitably among both active and temporarily inactive customers.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the petition of Sugar Mill Utility Company be granted in part, and that Petitioner be authorized to file new rates structured on the base facility charge concept, designed to generate gross water revenue of $41,429 annually, and gross sewer revenue of $35,550 annually, based on the number of customers served at the end of the test year. It is further RECOMMENDED that the Petitioner be permitted to retain interim revenues collected pursuant to Respondent's Order No. 9392, and that tie rate refunding bond requirement of said order be cancelled. DONE and ENTERED this 20th day of November, 1980, in Tallahassee, Leon County, Florida. R. T. CARPENTER, Hearing Officer Division of Administrative Hearings Room 101, Collins Building Tallahassee, Florida 32301 (904) 488-9675
The Issue The ultimate issue in this case is whether the South Florida Water Management District (SFWMD) should grant Environmental Resource Permit (ERP) Application No. 970509-10 for conceptual approval of a surface water management system serving a 167.9-acre commercial development in Broward County known as Pembroke Center and issue ERP No. 0600095-S-15 (Permit) to Arthur D. Weiss, Trustee (Weiss). The primary contested sub-issues involve the extent of use of offsite mitigation of the project's wetlands impacts through purchase of credits purchased from Florida Power and Light Company (FPL's) Everglades Mitigation Bank (EMB) 40 miles away in southern Dade County.
Findings Of Fact Some General Background on the Weiss Site The Weiss project site, which includes wetlands and open-water ditches, is located immediately east of Interstate Highway 75 in Broward County, south of Pines Boulevard, and north of the planned Pembroke Road fly-over of I-75. Before the drainage projects of the twentieth century, the Weiss site was a part of the Everglades having “ridge and slough" characteristics. The Atlantic Coastal Ridge extends along Florida's East Coast from Palm Beach County through Miami at a distance of some ten miles or so inland, then continues in a southwesterly direction, and ends in the vicinity of Homestead and Florida City. Before significant development of south Florida, the ridge acted as a dam to surface water flow, containing most of the interior waters of the Everglades. Lower elevations of the ridge, referred to as the “Transverse Glades,” allowed limited surface water to flow to the Atlantic Ocean, creating a southeasterly flow within the eastern portion of the Everglades. The "ridge and slough" provided a complex community structure, varying from the longest hydroperiod wetlands in the deepest sloughs to interspersed tree islands which provided habitat at or above the seasonal high water levels. In the deeper slough areas, vegetation would be predominantly floating and submerged. The deeper slough areas served to preserve aquatic organisms during periods of drought, allowing fish and other aquatic organisms to return to areas as they were re-hydrated. Progressing up the edges toward the ridge area, there would be emergent plants, such as Pontederia or pickerelweed, as well as some sawgrass. The ridges in the ridge and slough communities were primarily sawgrass. Before development, much of the ridge and slough communities was characterized by relatively long hydroperiods. Peat soils accumulated because the long hydroperiod inhibited aerobic respiration, resulting in an accumulation of partially decomposed organic matter/peat soils. Due to the peat soils, the sawgrass in the ridge and slough communities was relatively tall, thick, and lush. As drainage canals were constructed through these low-lying areas, the rate of drainage to the Atlantic Ocean increased, and the water regime changed. The South Broward Drainage District (SBDD) S-3 Basin was issued SFWMD Permit No. 06-00095-S on February 10, 1977, to construct a regional water management system to serve 5,500 acres of agricultural, recreational, residential, and undeveloped lands. SBDD's S-3 Basin includes an internal canal system and two 45,000 gallons per minute pumps discharging into C-9 canal. Both SFWMD's Western C-9 Basin and the Weiss site are within SBDD's S-3 Basin. An east-west SBDD canal approximately bisects the Weiss site. Also receiving water from Century Village, a development of some 9,000 town homes and condominiums, this canal leads to the SBDD's main north-south canal, which leads to the pump station approximately four miles to the south, which drains the entire S-3. East of the Weiss site has become very urbanized, with a nursery, a small office building, warehouses, shopping centers, Century Village, and the City of Miramar Sewage Treatment Plant. The land to the south of the site is undeveloped but is designated and zoned planned industrial. The Weiss project site subject to this permit proceeding is part of a larger Weiss parcel that received a permit in 1988 for construction and operation of a 375-acre cattle ranch. As a result of that permit, ditches and dikes were constructed to interconnect with the backbone surface water management system operated by the SBDD. The Weiss site now consists of these previous agricultural drainage ditches and flood control canals. The onsite wetlands have been degraded by drainage by these ditches and canals, by being actively mowed for cattle pasture, and by invasion of melaleuca, an undesirable invasive exotic species which dominates in the areas not regularly mowed for cattle pasture. Modification Application On May 9, 1997, R.J. Pines Corporation, on behalf of Weiss, submitted Application No. 970509-10 for modification of Permit No. 06-00095-S, to construct a surface water management system to serve 213 acres of residential and commercial development. SFWMD submitted Requests for Additional Information (RAIs) on June 6, 1997, February 6, 1998, February 27, 1998, May 1, 1998, April 15, 1999, June 16, 1999, April 14, 2000, August 24, 2000, October 6, 2000, and February 22, 2001. Responses to the RAI's were received on January 29, 1998, March 30, 1998, April 1, 1998, March 17, 1999, May 13, 1999, May 14, 1999, May 18, 1999, July 28, 2000, September 7, 2000, January 18, 2001, and March 2, 2001. During approximately four years of application review (including RAIs and responses), changes were made to the original application. The overall size of the project was decreased, and various mitigation options were explored. From early on in the process, offsite mitigation was proposed. Various possibilities for offsite mitigation were explored. Some were within SFWMD's Western C-9 Basin; others were outside but relatively close to the Western C-9 Basin. One 86-acre parcel within the Western C-9 Basin known as the "Capeletti" parcel was rejected for having a less-than-ideal operational entity (as well as for being costly); yet, the majority of the Capeletti parcel has been sold to private parties for mitigation projects, and 14 acres remain available for purchase for mitigation. Eventually, all offsite mitigation possibilities were rejected for various reasons except for one--FPL's Everglades Mitigation Bank (EMB), 40 miles to the south in southern Dade County. Ultimately, Weiss decided to purchase wetlands mitigation credits at the EMB for use as offsite mitigation. Different combinations of onsite mitigation and EMB credits were then proposed and considered. At the conclusion of this phase of the application process, the total size of the proposed project was reduced to 167.9 acres. Of the total project, approximately 149 acres were jurisdictional wetlands; the rest was open water ditches and canals. Ultimately, Weiss proposed to preserve and enhance 24.4 acres onsite as partial mitigation; the balance of the proposed mitigation consisted of 50.25 wetlands credits at FPL's EMB, which Weiss agreed to purchase from FPL. On April 25, 2001, SFWMD issued a notice of intent to issue the Staff Report recommending conceptual approval of the ultimately proposed surface water management system to serve the 167.9 acre commercial development known as Pembroke Center, Application No. 970509-10, ERP Permit No. 06-00095-S- 15. Existing Onsite Wetlands There are three classes of wetlands at the Weiss project site: sawgrass prairie; marsh wetlands; and remnant tree islands. The dominant wetland type is the sawgrass prairie. Sawgrass dominates in these areas, but some other wetland species like sedges and rushes and other grasses are mixed in. Marsh wetlands occur in places where elevations are somewhat (just inches) lower. Here are found wetland marsh species such as pickerelweed, duck potato and possibly spike rush (Eleocharis species). Small bay trees exist on the remnant tree islands, as well as wax myrtle. The soils on the Weiss site have retained their hydric characteristics; muck soils exist throughout the site. The soils have enough muck to stay saturated and allow wetland vegetation to grow on the site. But the site has been impacted by drainage and use as a cattle pasture. The vegetation is impacted to varying degrees by cattle grazing. The more highly-disturbed portions of the site, such as those adjacent to ditches, contain dense stands of melaleuca. Were it not for grazing and regular mowing, melaleuca would spread and probably out-compete the wetland vegetation. While it once had a long hydroperiod, the Weiss property's hydroperiod is currently diminished. The depth of the hydroperiod has been most significantly altered by the pump stations operated by SBDD. Today, the depth and duration of the hydroperiod on the Weiss site has been diminished. Proposed Onsite Mitigation Weiss's proposed onsite mitigation consists of preservation and enhancement of 24.4 acres of wetlands. Muck and peat topsoil will be removed, lower soils will be excavated to achieve optimal elevations, and the topsoil will be replaced. By generally lowering elevations, a regular and deeper hydroperiod will be achieved; by choosing different elevations, different types of wetland habitats (cypress stands, marsh, and tree islands) will be produced; by replacing the topsoil, wetland plant species will be able to grow and thrive in the mitigation area. Exotic plants will be removed and minimized through ongoing management of the mitigation area. Water quality will improve when the cows are removed. EMB The EMB is a 13,455-acre wetland preservation, enhancement and restoration project consisting of herbaceous freshwater wetlands with tree islands, saltwater marsh with tree islands, mangrove wetlands with tree islands, and riverine depressional ecological communities. The EMB was undertaken to provide mitigation to offset adverse impacts to wetlands and other surface waters, and is being undertaken in phases. Phase I of the EMB consists of 4,212 acres of the overall project. FPL’s EMB has been permitted under Section 373.4136, Florida Statutes, with a mitigation service area for non- linear projects covering Miami-Dade, Broward, and the southern portion of Palm Beach County south of Southern Boulevard. The Florida Department of Environmental Protection (DEP) issued permits numbered 132622449 and 132637449 in 1996 authorizing the establishment, construction, and operation of the EMB. The U.S. Army Corps of Engineers, U.S. Environmental Protection Agency, and U.S. Fish and Wildlife Service issued a mitigation banking instrument authorizing the establishment, construction, and operation of the EMB in 1998. The U.S. Army Corps of Engineers also issued Permit No. 199500155(IP-GS) authorizing the EMB. The EMB is in full compliance with these state and federal permits and the federal mitigation banking instrument. The EMB has 50.25 mitigation credits available on its mitigation bank ledger to be used to offset wetland impacts on the Weiss property. The 50.25 credits equate to approximately 500 acres of EMB sawgrass, marsh, and tree islands. The EMB Phase 1 is part of the marl prairie of the Southeastern Saline Everglades. The characteristics of Phase 1 of the EMB have not changed substantially from its historic condition. (The EMB's original hydroperiod would have been somewhat longer, but efforts are being made to lengthen the hydroperiod as part of the EMB mitigation project.) The EMB Phase 1 is characterized by sawgrass- dominated marl soils, interspersed with depressional areas where peat soils typically occur. Plants in the marl areas are dominated primarily by sawgrass that is relatively short and sparse compared to a "ridge and slough" area, with other emergent and occasional floating plants in low ponded areas, and thicker sawgrass and tree islands in the areas of peat soils in low areas. The predominance of marl in the EMB results from a historical hydroperiod (generally between one and a half and five months) that is shorter than in a "ridge and slough." The shorter hydroperiod prevents the formation of peat soils through exposure to the air, allowing bacteria to break down the organic matter that is typical of peat soils. Marl forms on the soil when photosynthesis of algae during daylight hours pulls carbon dioxide out of the water and raises the water's pH to the point where calcium carbonate starts to come out of solution. Compared to the structurally more complex peat-based wetland community of the "ridge and slough," the marl prairie of the EMB Phase 1 is a relatively simple community. The ridge and slough community's areas of deep water, marshes, and uplands supported a variety of aquatic organisms and wildlife in a manner that is distinct from that provided in the marl prairie of the EMB Phase 1. Marl prairie is not as conducive to rookeries as ridge and slough communities because the tree islands in marl prairies afford less protection from predation than is characteristic of the ridge and slough communities. Despite these differences, the wetlands in the EMB are similar in many ways to the historic wetlands on the Weiss property. In addition, due to its size and location in relation to other undeveloped land, the EMB retains characteristics that appear to have been lost to the Weiss property, which is relatively isolated by surrounding development and urbanization. The EMB is surrounded by public lands acquired for conservation and preservation including the Biscayne National Park, Everglades National Park, and the District's Southern Glades property. The EMB provides valuable habitat for a number of threatened or endangered species. The EMB also provides foraging, resting, and roosting opportunities for numerous wading birds including little blue herons, snowy egrets, white ibis, great blue herons, and great egrets. Because of the way it provides base flow and detrital export to Biscayne Bay, its connection and relationship to surrounding publicly-owned lands, and its integration into the Everglades Restoration Project, the EMB significantly contributes to a regional integrated ecological network. For example, the EMB can assist other key resources such as the Everglades National Park and provide habitat to some larger top-order consumers that historically also would have used the Weiss property--such as deer, bobcats, panthers, and even bear--something onsite mitigation cannot do. Application of SFWMD Policies and Interpretations Wetland protection is one of three major components of the ERP Program. The intent of the wetlands protection criteria in the ERP Program is to ensure no net loss of wetland function. In other words, SFWMD determines what functions are provided by the wetlands to be developed, which wetland-dependent wildlife benefits from those functions; then taking any proposed mitigation into consideration, SFWMD attempts to ensure that those functions are not diminished. Reduction and Elimination of Wetlands Impacts SFWMD's BOR 4.2.1. provides that design modifications to reduce or eliminate adverse impacts must be explored. After implementation of practicable design modifications, any adverse impacts must be offset by mitigation. In this case, Weiss ultimately proposed to preserve and enhance 24.4 acres of onsite wetlands. This was a modification of earlier proposals for 11 acres of onsite mitigation and then for all offsite mitigation. The evidence did not prove that there were no other practicable design modifications to reduce impacts to wetland functions. However, SFWMD does not necessarily require that all wetland impacts be reduced or eliminated when wetlands are of low quality and the proposed mitigation will provide greater long-term ecological value than the area of wetland to be adversely affected. See BOR 4.2.1.2(a). BOR 4.2.2.3 balances five factors to determine the functional value of wetlands: condition; hydrologic connection; uniqueness; location; and fish and wildlife utilization. The condition of the Weiss site's wetlands is low because past alterations in hydrology have been deleterious. Due to the ditches and canals, not much water quality treatment of the site's runoff occurs onsite. In addition, the Weiss site contains exotic vegetation, which would overrun the wetlands without regular mowing. Even the County's experts agree that the condition is at the high end of low. In evaluating hydrologic connection, SFWMD considers the following parameters: (1) benefits to offsite water resources through detrital export; (2) base flow maintenance; (3) water quality enhancement; and (4) nursery habitat. The Weiss property does not have much opportunity for detrital export, as it is not a saltwater system. The site does not maintain base flow, which is controlled by SBDD's pump station. Since little onsite water quality treatment occurs, neither onsite nor offsite water quality is enhanced; to the contrary, use of the wetlands as cow pasture would tend to reduce water quality both onsite and offsite. (Much greater reductions would be expected if the property were being used as a feed lot instead of for pasture.) There is not much opportunity for nursery habitat. In consideration of these parameters, the hydrologic connection is at least low; and some of the parameters are negative. The County contends that the ditches and canals on the Weiss site provide nursery habitat and serve as refugia for aquatic species in times of drought. However, the ditches and canals themselves are not jurisdictional wetlands. There are some depressions in the wetlands that might stay wet during some drought conditions, but the evidence did not suggest that these areas would serve as significant nursery habitat or refugia. SFWMD measures the uniqueness of wetlands by determining whether the wetland type is underrepresented in the basin or watershed--in other words, the relative rarity of the wetlands. The Weiss wetlands are not unique because drained wetlands converted to a cow pasture are not underrepresented in Broward County. While noting that cow pasture is decreasing in Broward County, even the County's expert agreed that the Weiss wetlands are not unique. As the County points out, the Weiss wetlands have some opportunity to interact with the other water resources in this basin, particularly the other mitigation sites. The County owns conservation easements on mitigation sites in the vicinity and has attempted to work with SFWMD and developers to group mitigation projects near each other to achieve greater benefits. Nonetheless, the opportunity for interaction is limited due to the surrounding development, which includes Interstate Highway 75 and other barriers to land animals. As a result, the parties agree that the location is in the low-to-moderate range. Fish and wildlife utilization of the Weiss wetlands is low. A wetland typically provides the following functions or benefits to wildlife: resting; feeding; breeding; and nesting or denning, particularly by listed species. Due to reduced hydrology and the presence of exotic species, the Weiss wetlands cannot provide this entire suite of functions; instead, it only provides resting and limited foraging for wading birds. SFWMD's determination as to fish and wildlife utilization of the site was based on personal site visits by SFWMD staff and in-house knowledge of the Western C-9 Basin. During the site visits, wading birds were not seen foraging onsite, and there was little evidence of successful foraging or actual use of the Weiss site by wading birds. Even if wading birds attempted to use the site for foraging and were successful to an extent, no witnesses testified to abundant food sources. Most saw no crayfish, a good food source, or any signs of crayfish, such as "chimneys" of tunnels leading into the water table. Several witnesses questioned whether there was enough relatively soft soil over many portions of the site to allow for tunnels into the water table. One Broward County witness testified to seeing limited evidence of crayfish at the site. But overall the evidence was persuasive that the site probably does not have enough food to make it worthwhile foraging for large numbers of birds. Ironically, most foraging on the site would be expected to occur in ditches not actually part of the jurisdictional wetlands. The evidence suggested that relatively little foraging would be expected to occur in the wetlands themselves. In addition, the wetlands would be less suitable for foraging if the cattle pastures were not grazed and mowed on a regular basis. Broward County criticizes SFWMD for not conducting lengthy wildlife surveys and for not visiting the site during the dry season when wading birds might be more likely to use the site for foraging. But SFWMD's review for fish and wildlife utilization on the Weiss site was consistent with the customary review conducted in nearly all ERP applications. A wildlife survey was not necessary to analyze the fish and wildlife utilization of the Weiss wetlands. It should be noted that SFWMD does not use the Wetland Rapid Assessment Procedure (WRAP), the Wetland Benefit Index (WBI), or the Wetland Quality Index (WQI) indices to determine the functional value of wetlands. There was some evidence that the overall quality of the Weiss wetlands could have been rated as high as moderate using some of these methods. But these methods do not necessarily attempt to make the same determination required under BOR 4.2.2.3. In addition, while these methods purport to objectively quantify wetlands evaluations, the evidence was that they are not easily understood or uniformly applied; as a result, they do not eliminate subjectivity and possible manipulation. Giving deference to SFWMD's interpretation of the parameters of BOR 4.2.2.3, it is found that SFWMD correctly assessed the function of the Weiss wetlands as being low. The proposed onsite mitigation clearly would improve the ecological value of the currently low-functioning wetlands on those 24.4 acres. In particular, better foraging opportunities for wading birds as well as other wetland- dependent species will be made available there for a greater portion of the year. However, the evidence also was clear that preservation and enhancement of the 24.4 acres would not replace the wetland function of the entire 149 acres of impacted wetlands. The proposed offsite mitigation through purchase of 50.25 credits at the EMB will be an additional improvement in ecological value over the existing wetlands on the Weiss site. The EMB is managed for exotic species control, has a greater opportunity for wildlife utilization, and has offsite hydrologic connections, both in receiving waters and downstream. Taken together, the proposed onsite and offsite mitigation would be an improvement in ecological value from the current, low-functioning wetlands on the Weiss site. Offsite Mitigation Provides Greater Improvement In Long-Term Ecological Value Than Onsite Mitigation (BOR 4.3.1.2) Due to its location, size, and prospects of effective long-term management, mitigation at the EMB probably has higher likelihood of success than mitigation on the Weiss site. But the evidence was clear that onsite mitigation also has good likelihood of success, comparable to mitigation at the EMB. Onsite mitigation will provide better forage habitat for some of the wading birds than the Weiss wetlands do today, but it is limited by size and location and will never be able to provide all of the functions that the Weiss wetland provided historically. It will provide some forage habitat for wading birds, but not for some of the larger consumers that historically used the site, such as deer, bobcats, panther and bear. No matter how perfect onsite mitigation is, its function still is limited. By comparison, mitigation at the EMB has greater opportunity for improvement and ecological value than mitigation at the Weiss site. The EMB is connected to other water resources, and it is not limited by lack of size or location. For this reason, the purchase of 50.25 credits at EMB has an opportunity to result in greater improvement in ecological value than just onsite mitigation. Unacceptable Cumulative Impacts (BOR 4.2.8) In this case, Robert Robbins conducted SFWMD's cumulative impacts analysis; Weiss and FPL relied on Robbins's analysis. In conducting his analysis, Robbins relied on his knowledge of the Western C-9 Basin, his staff's knowledge of the Basin, aerial pictures of the Western C-9 Basin, and County Exhibits 97 and 98. Robbins also interpreted and applied SFWMD's statutes, rules, and BOR 4.2.8. His interpretations were guided by the "Cumulative Impacts White Paper" ("White Paper"), a memorandum authored by representatives of Florida’s Water Management Districts, including Robbins. Since other rules and regulations require that all wetland impacts be fully mitigated, the cumulative impact analysis only applies when an applicant proposes mitigation outside of a drainage basin. In the context of impacts to wetland functions, SFWMD's cumulative impacts analysis presumes that a particular basin (in this case the Western C-9 Basin) can only tolerate so much loss of wetland function before there is a significant adverse impact on the basin overall; if cumulative impacts reach that point, they are considered unacceptable. The "White Paper" analogizes such a cumulative impact to "the straw that breaks the camel's back." If cumulative impacts of a proposed project would be unacceptable, they would have to be reduced so that impacts would be equitably distributed among the applicant and prospective developers, and there would not be a significant adverse or unacceptable cumulative impact when the basin is fully developed. The cumulative impact analysis presumes that development will continue to the extent that land use and planning and zoning allow such development to continue. It also presumes that how SFWMD permits a development today will set the precedent for like applicants in the future. SFWMD's cumulative impacts analysis does not focus on how much wetland acreage is leaving the basin; rather, it is concerned with the wetland functions that are being lost. In this case, the only functions being lost at the Weiss site are opportunities for resting and limited foraging for wading birds. Neither the statutes, rules, BOR 4.2.8., nor the White Paper further defines unacceptable or significant adverse cumulative impact on wetland functions. Robbins interpreted the terms in the context of this case as being a cumulative impact that would place the wading bird population in a basin in jeopardy of collapse. Collapse would occur when the population no longer is sustainable. Collapse could lead to extirpation of the population from the Basin. In this case, 124.9 acres of low-functioning wetlands will be impacted, and 24.4 acres of higher- functioning mitigation will remain in the basin. The evidence was that the 24.4 of higher-functioning mitigation onsite would not offset all of the feeding and resting functions lost to the Western C-9 Basin by 124.9 acres of impacts. But Robbins expressed the opinion that there would not be a significant adverse impact to the wading bird population which relies on the feeding and resting functions within the Western C-9 Basin if the relatively few remaining wetlands in the Western C-9 Basin are developed in a fashion similar to the Weiss proposal because the wading bird population that utilizes the basin would not be placed in jeopardy. However, the evidence was clear that Robbins viewed 25% in-basin mitigation as the minimum required to avoid unacceptable cumulative impacts and that Robbins based his opinion on an assumption that, under Weiss's mitigation proposal, 25% of the total wetland mitigation required to offset impacts to wetland functions would remain within the Western C-9 Basin. But the evidence also is clear that Robbins's assumption was incorrect. Robbins began to explain his assumption by referencing an earlier proposal by Weiss to mitigate entirely offsite through purchase of 67 credits at the EMB. Robbins testified that he accepted 67 EMB credits as enough to offset wetland impacts. However, in applying his cumulative impacts analysis, Robbins rejected the proposal for all mitigation to be offsite at the EMB; instead, Robbins and SFWMD decided to let Weiss use 75% of the 67 EMB credits but required the balance of the "credit-equivalents" of mitigation to occur onsite. Eventually, Weiss made the proposal eventually accepted by Robbins and SFWMD: 149 acres of impact; 24.4 acres of mitigation onsite; and 50.25 credits of mitigation at the EMB. In further explanation, Robbins later responded to the following questions: THE COURT: So the 24 acres of on-site you said that is equivalent of about 48 credits? THE WITNESS: No, 12. The on-site is the ecological value of about half a credit, so it takes twice as much on-site mitigation to offset one acre of impact as it would take in the bank. THE COURT: So 12 of the 67 leaving 55? THE WITNESS: No, that mixes up apples and oranges. If I can back up, from the starting point of 67 credits that were being proposed, and I said 75 percent of that they could do, 75 percent of 67 is 50.25 credits and that's where the 50.25 comes from and that offsets about 100 acres of impact and that leaves about 24 and half acres of impact to be mitigated and that is the 24.4 acres on-site. (TR454, L25 – TR455, L21 [Robbins]). As the County states in its PRO, Robbins himself "was mixing apples and oranges, by switching between credits and acres, and by subtracting the product of one denominator (75 percent of 67 credits) from a smaller denominator (62.45 credits), he apparently assumed that the resulting product (24.4 acres [or 12.2 credits]) was 25 percent of the denominator (124.9 acres), when it was only 19.5 percent." (County's PRO, p. 8) While the County's math terminology may not be correct, it does appear that Robbins indeed "mixed apples and oranges" by confusing two earlier Weiss mitigation proposals. An earlier SFWMD RAI, dated June 16, 1999, referenced an "overall requirement for 67 credits of wetland mitigation for the 135 acres of proposed wetland impact." Weiss's subsequent application amendment dated March 2, 2001, stated that the wetlands impact would be 124.9 acres, and that the total mitigation credits for the project would be 62.45 mitigation credits. (Exh. 2G, p. 2; Exh. 3L, p. 2). In his analysis, Robbins appear to have taken the number of mitigation credits from the first proposal and the acreage of wetland impacts from second. Under both the proposal referenced in the SFWMD RAI, dated June 16, 1999, and Weiss's subsequent application amendment dated March 2, 2001, EMB mitigation credits were assigned to the wetland impacts of the project on a 0.5:1 ratio; in other words, one EMB credit (which represented ten acres of the EMB Phase 1) offsets the impacts of two acres of wetlands lost through impact. As a result, 50.25 EMB credits offset 100.5 acres of wetlands lost through impact. In addition, each acre of onsite mitigation counted as half an EMB credit and would offset one acre of wetlands lost through impact. As a result, the 24.4 acres of onsite mitigation was the equivalent of 12.2 EMB credits of mitigation and offset 24.4 acres of wetlands lost through impact. As the County asserts, using these numbers, whether credits of impact and offset or acres of impact and offset are compared, only 19.5% of the proposed mitigation appears to be occurring onsite and in-basin. Expressed another way, 62.45 EMB credit equivalents was found by Robbins to be necessary to offset impacts to wetland functions from the Weiss project. To achieve the 25% in-basin mitigation found by Robbins to be the minimum, 15.61 EMB credit equivalents would have to remain in-basin, according to Robbins. Yet under the Weiss's current proposal, only 12.2 EMB credit equivalents remain in-basin (in this case, onsite). To meet the minimum requirement testified to by Robbins, Weiss would have to increase onsite mitigation by approximately 6.8 acres or otherwise increase in-basin mitigation. It should be noted in this regard that the "White Paper" would count as in-basin mitigation "outside the impact basin, but close enough to the impact basin that certain functions 'spill over' and offset impacts in the impact basin to an acceptable level." The County also disputed Robbins's opinion that 25% in-basin mitigation was the minimum required to avoid unacceptable cumulative impacts. The County contended that the percentage of in-basin mitigation would have to be much higher to avoid unacceptable cumulative impacts, at least 50%. In part, the County based its position on the regulatory history in the Western C-9 Basin. The evidence was that approximately 33% of project wetlands remained after development in the County's portion of the Western C-9 Basin and that approximately 85% of the wetland functions remained onsite after mitigation. Robbins explained adequately why 25% in-basin mitigation is enough under current circumstances. The Western C-9 Basin is now largely urbanized and developed with limited potential for new development. The Basin has approximately 4,500-5,000 acres of already preserved, relatively highly functioning wetlands. There remains approximately 250 to 450 (worst case scenario) acres of somewhat degraded wetlands that are yet to be developed. Robbins testimony is accepted that, if at least 25% of mitigation for wetland impacts from future development remains in the Western C-9, adverse cumulative impacts can be avoided. The County also questions the assumption that all 4,500-5,000 acres of relatively highly functioning wetlands in the Western C-9 Basin will be preserved to provide for resting and foraging for wading birds. In support of its position, the County presented evidence that consideration is being given to using the Buffer Strip to the east of U.S. Highway 27 for conveyance and using the Water Preserve Area (WPA) to the west of U.S. Highway 27 for impounding and stacking water up to four feet high for water management purposes, without regard for wildlife or wetland functions. However, Robbins believes, logically, that even if the decision-making authorities (SFWMD, DEP, and the United States Army Corps of Engineers) were inclined to use wetlands to impound water for storage purposes, they would try not to sacrifice highly- functioning wetlands for this purpose, if at all possible. He pointed out that, also militating against use of highly- functioning wetlands in such a way, the relatively high east- to-west transmissivity of groundwater in western Broward County would limit the amount of water that could be "stacked" in the area for any significant length of time. He pointed out that some wetlands in western Broward County have been rejected for use to impound and store water for these reasons. Robbins thinks it is more likely that the Buffer Strip and a good part of the WPA will be restored to marsh-type wetlands and that highly-functioning wetlands will be preserved. Robbins also assumed that, even if highly- functioning wetlands in the WPA were used to impound water, the decision-making authorities would have to obtain a permit from SFWMD, which would require mitigation for impacts to wetlands and require at least 25% of the mitigation to remain in the Western C-9 Basin. As a practical matter, Robbins questioned the feasibility of meeting such a requirement. Finally, the County questions Robbins's definition of unacceptable cumulative impacts. Based on the testimony of several of its witnesses, the County took the position that it is imprudent and risky to set the threshold of unacceptable cumulative impacts at the point where the wading bird population that utilizes the Western C-9 Basin would be placed in jeopardy of collapse. Indeed, such a high threshold is not without risk. The County urges a lower threshold--namely, the point where the ability of the local wildlife population to maintain its current population would be negatively impacted. But such a low threshold would have the effect of allowing practically no cumulative impacts. It is found that, under these circumstances, deference should be given to Robbins's interpretation. His interpretation was reasonable, and none of the County's witnesses had anywhere near Robbins's experience and expertise in interpreting SFWMD's rules and BOR provisions. Secondary Impacts (BOR 4.2.7) Almost the entire Weiss site (except for the proposed onsite mitigation area) will be directly impacted. There is little opportunity for secondary impacts. Construction methodologies for the proposed project do not have an opportunity to cause any secondary impacts to wetland functions. In any event, Weiss will construct a minimum 15-foot, average 25-foot, wide buffer around the proposed onsite wetlands mitigation area to protect wetland functions there. To ensure no adverse impacts to wetland functions after construction, the buffer will be planted with tree species to provide a buffer between the onsite mitigation and the future proposed development. The Weiss project site has only 19 acres that are "nonwetlands." Those are mainly deepwater canals, not uplands. None of the 19 acres are used by wetland-dependant species for nesting or denning. The only archeological site on the Weiss project site is a small one along I-75, and it is being preserved. SFWMD's Staff Report is for a conceptual ERP which covers the entire project site. There will not be additional phases of development. In addition, a conservation easement will ensure against the expansion or phases encroaching into the preserved wetland areas. The evidence was that there will be no adverse secondary impacts from the Weiss project. There was no evidence to the contrary. Public Interest Test (BOR 4.2.3) Prongs (a), (c), and (d) of the "public interest test" (dealing with adverse effects on the public health, safety or welfare or the property of others, navigation, and fishing, recreational values or marine activities) do not apply in this case. Prong (b) of the public interest test deals with the wetland functions relative to fish and wildlife. Due to the mitigation proposed in this case, there will not be a net adverse impact to fish and wildlife or listed species. As found as part of the cumulative impacts analysis, the relatively low functions of the Weiss wetlands are being improved and offset with a combination of onsite and offsite mitigation. Except as to cumulative impact to the basin, the Weiss project will not result in a net adverse impact to fish and wildlife or listed species. Prong (e) considers whether the regulated activity will be of a temporary or permanent nature. The permit at issue in this case is a conceptual approval only and does not authorize any construction. However, it is anticipated that any future construction would be of a permanent nature. Prong (f) considers adverse effects on historical or archeological resources. As indicated under secondary impacts, the only archeological site on the Weiss project site is a small one along I-75, and it is being preserved. Prong (g) considers the current condition and relative value of functions being performed by the areas affected by impacts. As found as part of the cumulative impacts analysis, the relatively low functions of the Weiss wetlands are being improved and offset with a combination of onsite and offsite mitigation. Except as to cumulative impact to the basin, the Weiss project will not result in a net adverse affect in those functions. Standing of Broward County and FPL The evidence was that, in part as a result of the County's work with SFWMD and developers over the years, mitigation projects in Broward County have been grouped so as to coordinate and achieve greater benefits. Collocation and proximity of mitigation areas makes the whole of them function better than the sum of their parts through coordination and interactive effect. Collocation and proximity of mitigation areas helps the mitigation areas to be more easily recognized and utilized by wading birds. Weiss's use of EMB credits for over 75% of the total required mitigation affects the County's substantial interest in the effectiveness of mitigation areas in the County. There also was evidence that mitigation areas within Broward County provide benefits to the citizens of Broward County in terms of improved environmental quality, water quality, wildlife, and quality of life. But as explained in the Conclusions of Law, the County's standing cannot be based on that evidence.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the South Florida Water Management District enter a final order denying Application No. 970509-10 for modification of Permit No. 06-00095-S, as amended to date. DONE AND ENTERED this 27th day of August, 2002, in Tallahassee, Leon County, Florida. ________________________________ J. LAWRENCE JOHNSTON Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 27th day of August, 2002. COPIES FURNISHED: Paul Sexton, Esquire Williams, Wilson & Sexton 215 South Monroe Street Suite 600-A Tallahassee, Florida 32301-1804 Melvin Wilson, Esquire Williams, Wilson & Sexton 110 East Broward Boulevard Suite 1700 Fort Lauderdale, Florida 33301-3503 William L. Hyde, Esquire Ausley & McMullen 227 South Calhoun Street Tallahassee, Florida 32301-1805 William S. Spencer, Esquire Gunster, Yoakley & Stewart, P.A. 500 East Broward Boulevard Suite 1400 Fort Lauderdale, Florida 33394-3076 Frank E. Matthews, Esquire Eric Olsen, Esquire Hopping, Green & Sams 123 South Calhoun Street Tallahassee, Florida 32301-1517 Luna Ergas Phillips, Esquire South Florida Water Management District Post Office Box 24680 West Palm Beach, Florida 33416-4680 Frank R. Finch, Executive Director South Florida Water Management District Post Office Box 24680 West Palm Beach, Florida 33416-4680
The Issue The issues in this case are whether International Paper Company (IP) is entitled to National Pollutant Discharge Elimination System (NPDES) Permit No. FL0002526 issued by Department of Environmental Protection (Department) and whether the Department should approve Consent Order No. 08-0358, for the operation of IP’s paper mill in Cantonment, Escambia County, Florida.
Findings Of Fact The Department is the state agency authorized under Chapter 403, Florida Statutes (2008), to regulate discharges of industrial wastewater to waters of the state. Under a delegation from the United States Environmental Protection Agency, the Department administers the NPDES permitting program in Florida. IP owns and operates the integrated bleached kraft paper mill in Cantonment. FOPB is a non-profit Alabama corporation established in 1988 whose members are interested in protecting the water quality and natural resources of Perdido Bay. FOPB has approximately 450 members. About 90 percent of the members own property adjacent to Perdido Bay. James Lane is the president of FOPB. Jacqueline Lane and James Lane live on property adjacent to Perdido Bay. The mill's wastewater effluent is discharged into Elevenmile Creek, which is a tributary of Perdido Bay. Perdido Bay is approximately 28 square miles in area. U.S. Highway 90 crosses the Bay, going east and west, and forms the boundary between what is often referred to as the "Upper Bay" and "Lower Bay." The Bay is relatively shallow, especially in the Upper Bay, ranging in depth between five and ten feet. At the north end of Perdido Bay is a large tract of land owned by IP, known as the Rainwater Tract. The northern part of the tract is primarily fresh water wetlands. The southern part is a tidally-affected marsh. The natural features and hydrology of the fresh water wetlands have been substantially altered by agriculture, silviculture, clearing, ditching, and draining. Tee Lake and Wicker Lake are small lakes (approximately 50 acres in total surface area) within the tidal marsh of the Rainwater Tract. Depending on the tides, the lakes can be as shallow as one foot, or several feet deep. A channel through the marsh allows boaters to gain access to the lakes from Perdido Bay. Florida Pulp and Paper Company first began operating the Cantonment paper mill in 1941. St. Regis Paper Company acquired the mill in 1946. In 1984, Champion International Corporation (Champion) acquired the mill. Champion changed the product mix in 1986 from unbleached packaging paper to bleached products such as printing and writing grades of paper. The mill is integrated, meaning that it brings in logs and wood chips, makes pulp, and produces paper. The wood is chemically treated in cookers called digesters to separate the cellulose from the lignin in the wood because only the cellulose is used to make paper. Then the "brown stock" from the digesters goes through the oxygen delignification process, is mixed with water, and is pumped to paper machines that make the paper products. In 1989, the Department and Champion signed a Consent Order to address water quality violations in Elevenmile Creek. Pursuant to the Consent Order, Champion commissioned a comprehensive study of the Perdido Bay system that was undertaken by a team of scientists led by Dr. Robert Livingston, an aquatic ecologist and professor at Florida State University. The initial three-year study by Dr. Livingston's team of scientists was followed by a series of related scientific studies (“the Livingston studies"). Champion was granted variances from the water quality standards in Elevenmile Creek for iron, specific conductance, zinc, biological integrity, un-ionized ammonia, and dissolved oxygen (DO). In 2001, IP and Champion merged and Champion’s industrial wastewater permit and related authorizations were transferred to IP. In 2002, IP submitted a permit application to upgrade its wastewater treatment plant (WWTP) and relocate its discharge. The WWTP upgrades consist of converting to a modified activated sludge treatment process, increasing aeration, constructing storm surge ponds, and adding a process for pH adjustment. The new WWTP would have an average daily effluent discharge of 23.8 million gallons per day (mgd). IP proposes to convey the treated effluent by pipeline 10.7 miles to the Rainwater Tract, where the effluent would be distributed over the wetlands as it flows to lower Elevenmile Creek and upper Perdido Bay. IP's primary objective in upgrading the WWTP was to reduce the nitrogen and phosphorus in the mill's effluent discharge. The upgrades are designed to reduce un-ionized ammonia, total soluble nitrogen, and phosphorus. They are also expected to achieve a reduction of biological oxygen demand (BOD) and TSS. IP plans to obtain up to 5 mgd of treated municipal wastewater from a new treatment facility planned by the Emerald Coast Utility Authority (ECUA), which would be used in the paper production process and would reduce the need for groundwater withdrawals by IP for this purpose. The treated wastewater would enter the WWTP, along with other process wastewater and become part of the effluent conveyed through the pipeline to the wetland tract. The effluent limits required by the proposed permit include technology-based effluent limits (TBELs) that apply to the entire pulp and paper industry. TBELs are predominantly production-based, limiting the amount of pollutants that may be discharged for each ton of product that is produced. The proposed permit also imposes water quality-based effluent limits (WQBELs) that are specific to the Cantonment mill and the waters affected by its effluent discharge. The WQBELs for the mill are necessary for certain constituents of the mill's effluent because the TBELs, alone, would not be sufficient to prevent water quality criteria in the receiving waters from being violated. The Livingston studies represent perhaps the most complete scientific evaluation ever made of a coastal ecosystem. Dr. Livingston developed an extensive biological and chemical history of Perdido Bay and then evaluated the nutrient loadings from Elevenmile Creek over a 12-year period to correlate mill loadings with the biological health of the Bay. The Livingston studies confirmed that when nutrient loadings from the mill were high, they caused toxic algae blooms and reduced biological productivity in Perdido Bay. Some of the adverse effects attributable to the mill effluent were most acute in the area of the Bay near the Lanes' home on the northeastern shore of the Bay because the flow from the Perdido River tends to push the flow from Elevenmile Creek toward the northeastern shore. Because Dr. Livingston determined that the nutrient loadings from the mill that occurred in 1988 and 1989 did not adversely impact the food web of Perdido Bay, he recommended effluent limits for ammonia nitrogen, orthophosphate, and total phosphorous that were correlated with mill loadings of these nutrients in those years. The Department used Dr. Livingston’s data, and did its own analyses, to establish WQBELs for orthophosphate for drought conditions and for nitrate-nitrite. WQBELs were ultimately developed for total ammonia, orthophosphate, nitrate-nitrite, total phosphorus, BOD, color, and soluble inorganic nitrogen. The WQBELs in the proposed permit were developed to assure compliance with water quality standards under conditions of pollutant loadings at the daily limit (based on a monthly average) during low flow in the receiving waters. Petitioners did not dispute that the proposed WWTP is capable of achieving the TBELs and WQBELs. Their main complaint is that the WQBELs are not adequate to protect the receiving waters. A wetland pilot project was constructed in 1990 at the Cantonment mill into which effluent from the mill has been discharged. The flora and fauna of the pilot wetland project have been monitored to evaluate how they are affected by IP’s effluent. An effluent distribution system is proposed for the wetland tract to spread the effluent out over the full width of the wetlands. This would be accomplished by a system of berms running perpendicular to the flow of water through the wetlands, and gates and other structures in and along the berms to gather and redistribute the flow as it moves in a southerly direction toward Perdido Bay. The design incorporates four existing tram roads that were constructed on the wetland tract to serve the past and present silvicultural activities there. The tram roads, with modifications, would serve as the berms in the wetland distribution system. As the effluent is discharged from the pipeline, it would be re-aerated and distributed across Berm 1 through a series of adjustable, gated openings. Mixing with naturally occurring waters, the effluent would move by gravity to the next lower berm. The water will re-collect behind each of the vegetated berms and be distributed again through each berm. The distance between the berms varies from a quarter to a half mile. Approximately 70 percent of the effluent discharged into the wetland would flow a distance of approximately 2.3 miles to Perdido Bay. The remaining 30 percent of the effluent would flow a somewhat shorter distance to lower Elevenmile Creek. A computer simulation performed by Dr. Wade Nutter indicated that the effluent would move through the wetland tract at a velocity of approximately a quarter-of-a-foot per second and the depth of flow across the wetland tract will be 0.6 inches. It would take four or five days for the effluent to reach lower Elevenmile Creek and Perdido Bay. As the treated effluent flows through the wetland tract, there will be some removal of nutrients by plants and soil. Nitrogen and phosphorous are expected to be reduced approximately ten percent. BOD in the effluent is expected to be reduced approximately 90 percent. Construction activities associated with the effluent pipeline, berm, and control structures in the wetland tract, as originally proposed, were permitted by the Department through issuance of a Wetland Resource Permit to IP. The United States Army Corps of Engineers has also permitted this work. Petitioners did not challenge those permits. A wetland monitoring program is required by the proposed permit. The stated purpose of the monitoring program is to assure that there are no significant adverse impacts to the wetland tract, including Tee and Wicker Lakes. After the discharge to the wetland tract commences, the proposed permit requires IP to submit wetland monitoring reports annually to the Department. A monitoring program was also developed by Dr. Livingston and other IP consultants to monitor the impacts of the proposed discharge on Elevenmile Creek and Perdido Bay. It was made a part of the proposed permit. The proposed Consent Order establishes a schedule for the construction activities associated with the proposed WWTP upgrades and the effluent pipeline and for incremental relocation of the mill's discharge from Elevenmile Creek to the wetland tract. IP is given two years to complete construction activities and begin operation of the new facilities. At the end of the construction phase, least 25 percent of the effluent is to be diverted to the wetland tract. The volume of effluent diverted to the wetlands is to be increased another 25 percent every three months thereafter. Three years after issuance of the permit, 100 percent of the effluent would be discharged into the wetland tract and there would no longer be a discharge into Elevenmile Creek. The proposed Consent Order establishes interim effluent limits that would apply immediately upon the effective date of the Consent Order and continue during the two-year construction phase when the mill would continue to discharge into Elevenmile Creek. Other interim effluent limits would apply during the 12- month period following construction when the upgraded WWTP would be operating and the effluent would be incrementally diverted from Elevenmile Creek to the wetland tract. A third set of interim effluent limits would apply when 100 percent of the effluent is discharged into the wetland tract. IP is required by the Consent Order to submit quarterly reports of its progress toward compliance with the required corrective actions and deadlines. Project Changes After the issuance of the Final Order in 05-1609, IP modified its manufacturing process to eliminate the production of white paper. IP now produces brown paper for packaging material and “fluff” pulp used in such products as filters and diapers. IP’s new manufacturing processes uses substantially smaller amounts of bleach and other chemicals that must be treated and discharged. IP reduced its discharge of BOD components, salts that increase the specific conductance of the effluent, adsorbable organic halides, and ammonia. IP also reduced the odor associated with its discharge. In the findings that follow, the portion of the Rainwater Tract into which IP proposes to discharge and distribute its effluent will be referred to as the “effluent distribution system,” which is the term used by Dr. Nutter in his 2008 “White Paper” (IP Exhibit 23). The effluent distribution system includes the berms and other water control structures as well as all of the natural areas over which IP’s effluent will flow to Perdido Bay. Most of the existing ditches, sloughs, and depressions in the effluent distribution system are ephemeral, holding water only after heavy rainfall or during the wet season. Even the more frequently wetted features, other than Tee and Wicker Lakes, intermittently dry out. There is currently little connectivity among the small water bodies that would allow fish and other organisms to move across the site. Fish and other organisms within these water bodies are exposed to wide fluctuations in specific conductivity, pH, and DO. When the water bodies dry out, the minnows and other small fish die. New populations of fish enter these water bodies from Elevenmile Creek during high water conditions, or on the feet of water birds. IP's consultants conducted an extensive investigation and evaluation of animal and plant communities in the Rainwater Tract in coordination with scientists from the Department and the Florida Fish and Wildlife Conservation Commission. Among the habitats that were identified and mapped were some wet prairies, which are designated “S-2," or imperiled, in the Florida Natural Area Inventory. In these wet prairies are rare and endangered pitcher plants. IP modified the design of the proposed effluent distribution system to shorten the upper berms and remove 72.3 acres of S-2 habitat. The total area of the system was reduced from 1,484 acres to 1,381 acres. The proposed land management activities within the effluent distribution system are intended to achieve restoration of historic ecosystems, including the establishment and maintenance of tree species appropriate to the various water depths in the system, and the removal of exotic and invasive plant species. A functional assessment of the existing and projected habitats in the effluent distribution system was performed. The Department concluded that IP’s project would result in a six percent increase in overall wetland functional value within the system. That estimate accounts for the loss of some S-2 habitat, but does not include the benefits associated with IP’s conservation of S-2 habitat and other land forms outside of the effluent distribution system. IP proposes to place in protected conservation status 147 acres of wet prairie, 115 acres of seepage slope, and 72 acres of sand hill lands outside the effluent distribution system. The total area outside of the wetland distribution system that the Consent Order requires IP to perpetually protect and manage as conservation area is 1,188 acres. The Consent Order was modified to incorporate many of the wetland monitoring provisions that had previously been a part of the former experimental use of wetlands authorization. IP proposes to achieve compliance with all proposed water quality standards and permit limits by the end of the schedule established in the Consent Order, including the water quality standards for specific conductance, pH, turbidity, and DO, which IP had previously sought exceptions for pursuant to Florida Administrative Code Rule 62-660.300(1). Limitation of Factual Issues As explained in the Conclusions of Law, the doctrine of collateral estoppel bars the parties in these consolidated cases from re-litigating factual issues that were previously litigated by them in DOAH Case No. 05-1609. The Department’s Final Order of August 8, 2007, determined that IP had provided reasonable assurance that the NPDES permit, Consent Order, exception for the experimental use of wetlands, and variance were in compliance with all applicable statutes and rules, except for the following area: the evidence presented by IP was insufficient to demonstrate that IP’s wastewater effluent would not cause significant adverse impact to the biological community of the wetland tract, including Tee and Wicker Lakes. Following a number of motions and extensive argument on the subject of what factual issues raised by Petitioners are proper for litigation in this new proceeding, an Order was issued on June 2, 2009, that limited the case to two general factual issues: Whether the revised Consent Order and proposed permit are valid with respect to the effects of the proposed discharge on the wetland system, including Tee and Wicker Lakes, and with respect to any modifications to the effluent distribution and treatment functions of the wetland system following the Final Order issued in DOAH Case No. 05- 1609; and Whether the December 2007 report of the Livingston team demonstrates that the WQBELS are inadequate to prevent water quality violations in Perdido Bay. Petitioners’ Disputes Petitioners’ proposed recommended orders include arguments that are barred by collateral estoppel. For example, Jacqueline Lane restates her opinions about physical and chemical processes that would occur if IP’s effluent is discharged into the wetlands, despite the fact that some of these opinions were rejected in DOAH Case No. 05-1609. Dr. Lane believes that IP’s effluent would cause adverse impacts from high water temperatures resulting from color in IP’s effluent. There is already color in the waters of the effluent distribution system under background conditions. The increased amount of shading from the trees that IP is planting in the effluent distribution system would tend to lower water temperatures. Peak summer water temperatures would probably be lowered by the effluent. Petitioners evidence was insufficient to show that the organisms that comprise the biological community of the effluent distribution system cannot tolerate the expected range of temperatures. Dr. Lane also contends that the BOD in IP's effluent would deplete DO in the wetlands and Tee and Wicker Lakes. Her contention, however, is not based on new data about the effluent or changes in the design of the effluent distribution system. There is a natural, wide fluctuation in DO in the wetlands of the effluent distribution system because DO is affected by numerous factors, including temperature, salinity, atmospheric pressure, turbulence, and surface water aeration. There are seasonal changes in DO levels, with higher levels in colder temperatures. There is also a daily cycle of DO, with higher levels occurring during the day and lower levels at night. It is typical for DO levels in wetlands to fall below the Class III water quality standard for DO, which is five milligrams per liter (mg/l). An anaerobic zone in the water column is beneficial for wetland functions. DO levels in the water bodies of the effluent distribution system currently range from a high of 11 to 12 mg/l to a low approaching zero. The principal factor that determines DO concentrations within a wetland is sediment oxygen demand (SOD). SOD refers to the depletion of oxygen from biological responses (respiration) as well as oxidation-reduction reactions within the sediment. The naturally occurring BOD in a wetland is large because of the amount of organic material. The BOD associated with IP’s effluent would be a tiny fraction of the naturally occurring BOD in the effluent distribution system and would be masked by the effect of the SOD. It was estimated that the BOD associated with IP's effluent would represent only about .00000000001 percent of the background BOD, and would have an immeasurable effect. Dr. Pruitt’s testimony about oxygen dynamics in a wetland showed that IP’s effluent should not cause a measurable decrease in DO levels within the effluent distribution system, including Tee and Wicker Lakes. FOPB and James Lane assert that only 200 acres of the effluent distribution system would be inundated by IP’s effluent, so that the alleged assimilation or buffering of the chemical constituents of the effluent would not occur. That assertion misconstrues the record evidence. About 200 acres of the effluent distribution system would be permanently inundated behind the four berms. However, IP proposes to use the entire 1,381-acre system for effluent distribution. The modifications to the berms and the 72-acre reduction in the size of the effluent distribution system would not have a material effect on the assimilative capacity of system. The residence time and travel time of the effluent in the system, for example, would not be materially affected. Variability in topography within the effluent distribution system and in rainfall would affect water depths in the system. The variability in topography, including the creation of some deeper pools, would contribute to plant and animal diversity and overall biological productivity within the system. The pH of the effluent is not expected to change the pH in the effluent distribution system because of natural buffering in the soils. The specific conductance (saltiness) of IP’s effluent is not high enough to adversely affect the biological community in the fresh water wetlands of the effluent distribution system. IP is already close to maintaining compliance with the water quality standard for specific conductance and would be in full compliance by the end of the compliance schedule established in the proposed Consent Order. After the 2007 conversion to brown paper manufacturing, IP’s effluent has shown no toxicity. The effluent has passed the chronic toxicity test, which analyzes the potential for toxicity from the whole effluent, including any toxicity arising from additive or synergistic effects, on sensitive test organisms. Dr. Lane points out that the limits for BOD and TSS in the proposed NPDES permit exceed the limits established by Department rule for discharges of municipal wastewater into wetlands. However, paper mill BOD is more recalcitrant in the environment than municipal wastewater BOD and less “bio- available” in the processes that can lower DO. In addition, the regulatory limits for municipal wastewater are technology-based, representing “secondary treatment.” The secondary treatment technology is not applicable to IP’s wastewater. Sampling in the pilot wetland at the paper mill revealed a diversity of macroinvertebrates, including predator species, and other aquatic organisms. Macroinvertebrates are a good measure of the health of a water body because of their fundamental role in the food web and because they are generally sensitive to pollutants. Petitioners contend that the pilot wetland at the paper mill is not a good model for the effect of the IP’s effluent in the wetland distribution system, primarily because of the small amount of effluent that has been applied to the pilot wetland. Although the utility of the pilot wetland data is diminished in this respect, it is not eliminated. The health of the biological community in the pilot wetland contributes to IP’s demonstration of reasonable assurance that the biological community in the effluent distribution system would not be adversely affected. The effluent would not have a significant effect on the salinity of Tee and Wicker Lakes. Under current conditions, the lakes have a salinity of less than one part per thousand 25 percent of the time, less than 10 parts per thousand 53 percent of the time, and greater than 10 parts per thousand 22 percent of the time. In comparison, marine waters have a salinity of 2.7 parts per thousand. IP’s effluent would not affect the lower end of the salinity range for Tee and Wicker Lakes, and would cause only a minor decrease in the higher range. That minor decrease should not adversely affect the biota in Tee and Wicker Lakes or interfere with their nursery functions. The proposed hydrologic loading rate of the effluent amounts to an average of six-tenths of an inch over the area of effluent distribution system. The addition of IP’s effluent to the wetlands of the effluent distribution system and the creation of permanent pools would allow for permanent fish populations and would increase the opportunity for fish and other organisms to move across the effluent distribution system. Biological diversity and productivity is likely to be increased in the effluent distribution system. By improving fish habitat, the site would attract wading birds and other predatory birds. Although the site would not be open to public use (with the exception of Tee and Wicker Lakes), recreational opportunities could be provided by special permission for guided tours, educational programs, and university research. Even if public access were confined to Tee and Wicker Lakes, that would not be a reduction in public use as compared to the existing situation. IP’s discharge, including its discharges subject to the interim limits established in the Consent Order, would not interfere with the designated uses of the Class III receiving waters, which are the propagation and maintenance of a healthy, well-balanced population of fish and wildlife. The wetlands of the effluent distribution system are the “receiving waters” for IP’s discharge. The proposed project would not be unreasonably destructive to the receiving waters, which would involve a substantial alteration in community structure and function, including the loss of sensitive taxa and their replacement with pollution-tolerant taxa. The proposed WQBELs would maintain the productivity in Tee and Wicker Lakes. There would be no loss of the habitat values or nursery functions of the lakes which are important to recreational and commercial fish species. IP has no reasonable, alternative means of disposing of its wastewater other than by discharging it into waters of the state. IP has demonstrated a need to meet interim limits for a period of time necessary to complete the construction of its alternative waste disposal system. The interim limits and schedule for coming into full compliance with all water quality standards, established in the proposed Consent Order, are reasonable. The proposed project is important and beneficial to the public health, safety, and welfare because (1) economic benefits would accrue to the local and regional economy from the operation of IP’s paper mill, (2) Elevenmile Creek would be set on a course of recovery, (3) the wetlands of the effluent distribution system would become a site of greater biological diversity and productivity, (4) the environmental health of Perdido Bay would be improved, (5) the Department’s decades-long enforcement action against IP would be concluded, (6) substantial areas of important habitat would be set aside for permanent protection, and (7) the effluent distribution system would yield important information on a multitude of scientific topics that were debated by these parties. The proposed project would not adversely affect the conservation of fish or wildlife or their habitats. The proposed project would not adversely affect fishing or water-based recreational values or marine productivity in the vicinity of the proposed discharge. There is no Surface Water Improvement and Management Plan applicable to IP’s proposed discharge. The preponderance of the record evidence establishes reasonable assurance that IP’s proposed project would comply with all applicable laws and that the Consent Order establishes reasonable terms and conditions to resolve the Department’s enforcement action against IP for past violations.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is: RECOMMENDED that the Department enter a final order granting NPDES Permit No. FL0002526 and approving Consent Order No. 08-0358. DONE AND ENTERED this 27th day of January, 2010, in Tallahassee, Leon County, Florida. BRAM D. E. CANTER Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 27th day of January, 2010.
Findings Of Fact B. D. Taylor, Respondent, is the owner of a wastewater treatment facility near Panama City, Florida, which serves a community of some 125-150 mobile homes at Lane Mobile Home Estates. The facility has a 24,000 gallons per day capacity to provide secondary treatment of wastewater with percolating ponds. It was first permitted in 1971 upon construction and has been in continuous operation since that time. In 1980 Respondent employed the services of a consultant to apply for a renewal of its temporary Permit to operate a wastewater treatment facility. This application stated the temporary operating permit (TOP) was needed to give Respondent time to connect to the regional wastewater treatment facility. The schedule contained in the following paragraph was submitted by Respondent at the time needed to accomplish this objective, Following inspection of the facility, a TOP was issued December 5, 1980 (Exhibit 1), and expired January 1, 1983. TOPs are issued to facilities which do not comply with the requirements for Wastewater treatment. Exhibit 1 contained a schedule of compliance to which Respondent was directed to strictly comply to stop the discharge of pollutants from the property on which the facility is located. These conditions are: Date when preliminary engineering to tie into regional will be complete and notification to DER. July 1, 1981; Date when engineering to tie into regional system will be complete and notification to DER - June 1, 1982; Date construction application will be submitted to phase out present facility - March 1, 1982; Date construction will commence - June 1, 1982; Date construction is to be complete and so certified - October 1, 1982; and Date that wastewater effluent disposal system will be certified "in compliance" to permit - January 1, 1903. None of these conditions or schedules has been met by Respondent. The regional wastewater treatment facility was completed in 1982 and Respondent could have connected to this system in the summer of 1982. This wastewater treatment facility is a potential source of pollution. The holding ponds are bordered by a ditch which is connected to Game Farm Greek, which is classified as Class III waters. The size of Game Farm Creek is such that any discharge of pollution to this body of water would reduce its classification below Class III. On several occasions in the past there have been breaks in the berm surrounding the holding ponds which allow the wastewater in the holding ponds to flow into the ditch and into Game Farm Creek. Even without a break in the berm, wastewater from these holding ponds will enter Game Farm Creek either by percolation or overflow of the holding ponds caused by the inability of the soil to absorb the effluent. On January 28, 1983, this facility was inspected and the results of the inspection were discussed with the operators of the facility. The plant was again inspected on February 8 and February 18, 1983. These inspections disclosed solids were not settling out of the wastewater in the settling tanks; inadequate chlorination of the wastewater was being obtained in the chlorination tanks; samples taken from various points in the system, the ditch along side the holding tanks and in Game Farm Creek, disclosed excess fecal coliform counts; and that very poor treatment was being afforded the wastewater received at the plant as evidence by high levels of total Kejhdal nitrogen and ammonia, high levels of phosphates, high biochemical oxygen demand, and low levels of nitrates and nitrites. In July, 1983, in response to a complaint about odors emanating from the plant, the facility was again inspected. This inspector found the aeration tanks anaerobic, effluent had a strong septic odor, the clarifier was cloudy, the chlorine feeder was empty, no chlorine residual in contact tank, final effluent was cloudy, both ponds were covered with duckweed and small pond was discharging in the roadside ditch (Exhibit 14) Expenses to Petitioner resulting from the inspections intended to bring Respondent in compliance with the requirements for wastewater treatment facilities are $280.32 (Exhibit 9)
The Issue The issues for determination in this case are: Whether the City of Altamonte Springs (City) violated Sections 760.10(1)(a), F.S., by discriminating against Albert Robinson (Robinson) on the basis of his race (Black) or his national origin (Jamaican), with respect to compensation, terms, conditions, or privileges of employment; Whether the City violated Section 760.10(7), F.S., by discriminating against Robinson in retaliation for his opposition to a practice which is an unlawful employment practice under this section or because he assisted or participated in any manner in an investigation, proceeding, or hearing under this section; and If such violations did occur, what relief is appropriate pursuant to Section 760.10(13), F.S.
Findings Of Fact Petitioner, Albert H. Robinson is a black male, over 18 years of age, born in Jamaica, West Indies. Respondent, the City of Altamonte Springs, is a municipal corporation organized and existing under the Laws of the State of Florida, and admits that it is an "employer" for purposes of the Human Rights Act of 1977, as amended, sections 760.01-760.10 F.S. Robinson's account of how he arrived in the United States approximately seven years ago is bizarre, but uncontroverted, and for purposes of this proceeding is deemed true. In Jamaica, Robinson had been affiliated with the ruling People's National Party. He held the government post of Development Director in the "New Development Agency" and was in charge of approximately 300 underprivileged persons. He was also president of a youth organization within the party, and was involved in organizing youth activities and selecting members to visit Cuba as a party representative. At some point he was approached by an American embassy attache from the CIA who recruited him to provide under-cover information on the party. When that involvement became publicly exposed, he was forced to flee the country. Robinson and his family lived for awhile in Panama and other Latin American countries. When they decided to emigrate to the United States, the U.S. Government made arrangements for Mrs. Robinson and the children to enter through Miami and for Mr. Robinson to cross the border "illegally" at Brownsville, Texas. He was given authorization to work and temporary asylum. He is currently awaiting disposition of his petition for a more permanent status. Through other relatives in Florida, Robinson ended up in Altamonte Springs. At the time that he was hired by the City in September 1984, Robinson presented a letter from the INS permitting him to work during the pendency of his asylum petition. The City was thus aware of his national origin and non- citizen status. Robinson was hired as a laborer in the city water distribution division on September 24, 1984. He received two personnel evaluations during his probationary period, both "average," with every factor rated "average," and few comments. On February 7, 1985, he was promoted from laborer to utility serviceworker, a more responsible position. The serviceworker is generally assisted at a job site by the laborer, who does most of the digging. The Dixon Personnel Board hearing In April 1985, Robinson assisted a black coworker, Patrick Dixon, at his hearing before the City Personnel Board. Dixon and another black utilities worker, Carl Wilder, had been accused of making obscene and inappropriate gestures to two white women while the men were on city duty. Wilder was given a one-day suspension. Dixon, who already had a negative performance record, was given a two-day suspension. Dixon appealed the discipline to the Personnel Board. Robinson's involvement at the hearing on April 3rd was to sit behind Dixon and assist with the documents. Robinson, who had no firsthand knowledge of the incidents, did not testify. Carl Wilder did testify on behalf of Dixon. The Personnel Board, in a unanimous decision by all members present, upheld the disciplinary action. Robinson believed that Patrick Dixon had been the victim of a racial vendetta. Dixon testified in this proceeding that he, also, feels that the charge was racially motivated, yet nothing in the written documents related to his appeal supports that contention. The basis for his appeal was the insufficiency of the evidence against him and his contention that he was a bystander while Wilder, the actual perpetrator, received a lesser penalty. Shortly after the hearing Dixon was terminated for absenteeism. He did not file a discrimination complaint nor take any other action against the city. Wilder is still employed by the city, and in 1987, was promoted from laborer to serviceworker. The performance evaluation On May 3, 1985, Robinson received his first performance evaluation as a utility serviceman. His overall rating by his reporting supervisor, George Simpkins, was "average." However, he received "below average" in four categories: "ability to carry out instructions/orders"; "conduct"; "directs the work of subordinates effectively"; and "ability to make decisions within his authority." The comments in explanation of these ratings related to Robinson's failure to follow operating procedures, his temper and conflict with fellow employees, and his dictatorial manner in dealing with subordinates. Robinson was not pleased with the evaluation and wrote a letter to the Assistant Director of Public Works, Ronald Howse, asking to discuss it. Howse suggested that the discussion take place with Larry Alewine and George Simpkins, who were the supervisors responsible for the evaluation. Alewine was Simpkins' immediate supervisor. The discussion took place. Robinson now claims that Larry Alewine asked him why he followed Patrick Dixon to City Hall and claims that Alewine blamed the evaluation on his involvement with Dixon. Alewine denies this and cannot recall any notoriety with regard to Robinson's association with Dixon. Not following procedures and problems with fellow employees Robinson's difficulties in working with others and in following procedures are well-documented throughout his 1985 and 1986 employment with the city. In June 1985, he received a notice of remedial action after placing a water meter in a location where the customer wanted it, rather than where he had been directed to place it. The customer was happy, but under the city's procedures, the serviceman does not have the authority on his own to change the supervisor's direction. On November 4, 1985, Robinson had an altercation with his supervisor, Larry Alewine, regarding a meeting that Robinson wanted with Chris Hill, the recently-appointed director of the city's water distribution division. Alewine attempted to convey Hill's directive that Robinson put his request in writing, but Robinson became loud, yelled at Alewine and started to leave. When Alewine attempted to call Robinson back to discuss the matter, Robinson retorted that he (Alewine) wasn't his daddy. Right after the incident Robinson apologized for getting loud and Alewine explained that he would still have to "write him up," because he had refused to come back in the building and was hollering. Robinson claims that the incident occurred prior to 7:30 A.M., when he was still on his own time, but this claim is unsupported by Alewine or any of the other several witnesses. On November 26, 1985, Robinson and Carl Wilder were at a job site trying to locate a buried water meter. Wilder, as the laborer, was doing the digging. Robinson, his superior, insisted that Wilder keep digging in a place where Wilder did not believe the meter was located. Both men's tempers flared and Wilder called the supervisor to the site to prevent further argument. Because it was near the end of the day, Robinson was excused and Wilder was taken back to the city garage. Chris Hill spoke with both Robinson and Wilder and determined that no disciplinary action was warranted. He told Wilder that if he had any complaints or grievances about Robinson, he would have to put them in writing. Chris Hill asked other employees if they had problems working with Robinson; he did not, as alleged by Robinson, solicit written statements against Robinson from other employees in the division. Chris Hill Most of Robinson's claims of discrimination by the city are directed toward Chris Hill, who, in October 1985, was placed in charge of the city's water distribution division. The City Manager, Philip Penland, was concerned about the management of the division. The Dixon/Wilder incident was an example. Larry Alewine and George Simpkins, both white Americans, were considered to be weak leaders. Robinson and Carl Wilder were identified as employees with whom there had been problems. Chris Hill started working for the City of Altamonte Springs in 1977 as temporary summer help and laborer. He gradually worked his way up through various levels of management and was highly regarded by his supervisors and by Philip Penland as a competent and capable employee, with a positive, "can-do" attitude. He was regarded as a tough manager who could obtain top performance from his employees. In addition to his duties at Altamonte Springs, he also is in charge of water plant operations in the neighboring towns of Eatonville and Maitland. Lack of tact and finesse in dealing with people, including subordinates, have been considered Hill's weak points. Hard times in the Water Distribution Division These characteristics and Hill's direction to shape up the division led to some tense months in the division. Larry Alewine, whose management style was certainly more relaxed, openly referred to Hill as "God" and "asshole." Alewine's position had been downgraded as a result of the reorganization, and he eventually left the city in 1987 after his position was eliminated from the budget. George Simpkins left a bitter resignation notice when he resigned in October, shortly after Chris Hill's appointment. In February 1986, Larry Alewine prepared an evaluation of Robinson which was reviewed, consistent with procedures, by Chris Hill. Hill did not believe the evaluation was strong enough, in light of his knowledge of the incident with Wilder and other minor problems with fellow employees. Both Hill and Scott Gilbertson, the Assistant Director of Public Works, met with Alewine and suggested that the evaluation should be changed. When Alewine declined, Chris Hill changed the evaluation. The evaluation, dated 3/6/86, rates Robinson overall as "Employee needs improvement." The written comments are very similar to those made by George Simpkins on the May 1985 evaluation; that is, the quality of his work was deemed generally good, but his conduct, ability to follow instructions, and ability to get along with fellow employees was noted as the real problems. While it is not apparent from the evaluation itself and the testimony in this proceeding how much of the evaluation was completed by Larry Alewine, it is clear that at least some of the negative written comments were made by him. (Respondent's exhibit #2.) The meeting with management officials and its aftermath Robinson wrote a protest of his evaluation which precipitated a meeting with himself, Chris Hill, Scott Gilbertson, Philip Penland, and the City Personnel Director, Sam Frazee. The evaluation was discussed; Robinson was told that his signing the evaluation only acknowledged its receipt and that he could provide his written notations on the back of the evaluation regarding portions with which he disagreed. The group also discussed an appointment Robinson had made with the city's worker's compensation physician. He had attempted to arrange his own follow-up visit for treatment of a work-related injury. The city's policy required that the appointments with the city's physician be made after notification to the supervisor. While explaining his actions, Robinson gave contradictory versions of what he had been told by the nurse in the doctor's office regarding the procedures. His testimony at hearing was also confused and inconsistent on this point. On direct, he testified that he had been told that authorization from the city is not necessary for follow-up visits. On rebuttal, however, he stated that the nurse had told him that the city personnel department would have to be notified, but not his foreman. (TR, Vol I, p. 77, Vol IV, p. 324-325). In the course of the same meeting, Robinson made allegations of wrongdoing by Larry Alewine, stating that Alewine had a meeting with his employees and encouraged them to write grievances against Chris Hill and had called Hill an "asshole" and "God." The City Manager considered these allegations to be serious and promised Robinson that an investigation would be made. The meeting then broke up. Ed Haven, an officer with the Professional Standards Bureau of the City Police Department was assigned to investigate the allegations of misconduct. This bureau normally conducts personnel-related internal affairs investigations and considers them administrative, not criminal. The investigation was initially inhibited by Robinson's refusal to answer Officer Haven's questions unless the investigation was expanded to include Chris Hill as well. Robinson was then ordered by the City Manager to participate. The inquiry sustained the allegations that Alewine had called Hill "asshole" and "God." This investigation spawned a second investigation as to whether Robinson had ever told another employee that he lied about Alewine in order to get an investigation against Chris Hill. The issue was never resolved, but Officer Haven found that a "preponderance of evidence indicates Robinson was untruthful during this investigation...," that Robinson did have a conversation with an employee, Barry Beavers, but denied it. (Petitioner's composite exhibit #1, Memorandum of Internal Inquiry #86-9998-03, April 15, 1986). The lead Utility serviceworker positions In Spring 1986, the city created two supervisor positions in the Water Distribution Division, titled "lead utility serviceworker," to supervise and oversee the work of the utility workers and their laborers. All three utility serviceworkers applied for the jobs: Robinson, Ronnie Oliver (Black American) and Barry Beavers (White American). Robinson was never considered a viable candidate and was interviewed as a matter of courtesy. Oliver and Beavers were chosen. Robinson concedes that Beavers was qualified and properly promoted, but he disputes Ronnie Oliver's qualifications. Ronnie Oliver began work one month after Robinson, in October 1984. He worked under Robinson as a laborer for some time and he freely acknowledges that Robinson taught him a lot. Oliver also had considerable personal initiative and taught himself with the use of materials he acquired from Larry Alewine. Oliver's performance evaluations were substantially better than Robinson's; by May 1986, the time of the promotion, he was evaluated as an "Outstanding" employee. Robinson had, in fact, been on the job less than Oliver, as he had sustained a work-related injury in December 1985, and was out for weeks at a time. He had not been cleared for full-time duty when he was interviewed and was absent from work when the positions were filled. Light duty Robinson alleges that he was given "make-work" light duty when he was returned to work after his injury, and was later denied light duty. The city furnishes injured employees with light duty on a case-by-case basis, depending on the capabilities and physical condition of the individual and the needs of the employer. Robinson was first assigned floor sweeping duties in June after his recurring back problems. Later he was given the task of painting an area near Hill's office. An assistant was assigned to paint the high and low portions of the wall. He was also given a chair to sit on and rest his back. This was the lightest duty available at the city at time. Other employees including a black who had cancer, were also given routine maintenance chores. While painting, Robinson injured his neck, shoulder and hands. He never returned to work after this injury in June 1986. The city informed him in July and August that it did not have light duty available. In September 1987, the City agreed to pay Robinson $47,000.00 (including $7,000.00 to his attorney), to settle his worker's compensation claim of permanent back injury. He has since applied for reemployment. As of the hearing in this proceeding, the city was reviewing his request for reemployment. This request is not at issue here. Various grievances In Spring 1986, as the result of some publicity about the arrest of illegal aliens, the city reviewed the work authorization status of its employees. Since Robinson had initially given the city a letter from INS stating that he was eligible to work pending an application for political asylum, he was asked again for authorization. He refused at first, and claimed this was harassment. He also claimed that he was subject to derision for being a CIA spy. He had told some fellow employees about his past and the news circulated. The employees mostly did not take the matter seriously, but in an employee meeting, someone asked Chris Hill whether it was true that Albert was a CIA spy. He replied that this was what Robinson claimed. At the same employees' meeting, Hill also stated that he did not think that Robinson was going to be around much longer. He made this remark based on his knowledge of Robinson's disciplinary problems. Hill was strongly reprimanded for this remark. He did not have the authority to terminate Robinson, and management had not taken steps to terminate him. Robinson has attributed various derogatory statements and epithets to Chris Hill. He claims that Hill said that no one would take the word of a "nigger" against him and that he didn't want Americans to take orders from a Jamaican. Hill vigorously denies these statements and no credible evidence was produced to support Robinson's claims. Nor was credible evidence presented of Robinson's claim that on July 3, 1986, Hill lost his temper and spat in his face. At hearing on November 2, 1987, Robinson, through his attorney, withdrew his allegation that he was defrauded of sick leave through a forged signature. (TR Vol IV, p. 293-294.) Summary of Findings Beyond his own unsubstantiated claim that Alewine told him so, there is no evidence that Robinson's problems with the city were the result of his rather inconspicuous involvement at the Patrick Dixon hearing. His problems clearly began when he was promoted to a position of some authority over others and his temper, loud mannerisms and difficulty working with others became an issue. Beginning with his response to his first slightly negative personnel evaluation, Robinson's reaction to every event in his employment, major and minor, was lengthy, rambling, confused and confusing written grievances, memoranda and letters. Robinson also carried a tape recorder to memorialize his encounters and (in his words) "...to intimidate people from molesting me..." (TR, Vol I, p. 243). Robinson's inconsistent accounting and mixing of facts in his scenario of alleged discrimination fail to make sense. Pressure was applied to blacks and whites, alike; of the four employees targeted as "problems," the two whites are gone (Alewine and Simpkins) and one black (Wilder) has been promoted. Evidence is clear that there were serious management problems in the city's Water Distribution Division in 1985, and the atmosphere which prevailed with reorganization of the division and Hill's arrival could very well have fueled Robinson's paranoia. His vehement protestations and repetitious and rambling litany of wrongs are either a sincere confused perception, or a deliberate attempt to manipulate a situation, which because of justifiable criticism of his job performance, was becoming increasingly uncomfortable. Nevertheless, his myriad allegations of discriminatory harassment, retaliation and of unlawful failure to promote, are unsupported by competent evidence.
Recommendation Based on the foregoing, it is, hereby RECOMMENDED: That Albert Robinson's charges that the City of Altamonte Springs violated subsections 760.10(1)(a) and (7), F.S., by harassment failure to promote, and retaliation, be DISMISSED. DONE and RECOMMENDED this 16th day of February, 1988, in Tallahassee, Florida. MARY CLARK 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 16th day of February, 1988. APPENDIX TO RECOMMENDED ORDER, CASE NO. 87-2482 The following constitute my specific rulings on the findings of fact proposed by the parties: Petitioner's Proposed Findings of Fact 1-5. Addressed in summary form in paragraph 3. Adopted in paragraphs 4. and 5. Addressed in paragraph 5. Adopted in part in paragraph 8. The account of discussion with Alewine is rejected as contrary to the weight of credible evidence. Adopted in part in paragraphs 6.-8., otherwise rejected as contrary to the weight of credible evidence. Adopted in paragraphs 6.-15. Addressed in paragraph 12. The characterization of Simpkins' motives and the mandate to fire the four employees are rejected as contrary to the weight of evidence. Addressed in paragraphs 15. and 16. Adopted in part in paragraph 18., otherwise rejected as unsupported by the weight of evidence or immaterial. 14-16. Rejected as contrary to the weight of evidence, except for the comment about Robinson being terminated. See paragraph 34. Rejected as cumulative, unnecessary and argumentative (rather than factual). Addressed in paragraph 14.; otherwise rejected as contrary to the weight of evidence. Rejected as unnecessary. Addressed in paragraph 13., otherwise rejected as contrary to the weight of evidence and unnecessary. Adopted in substance in paragraph 19. Addressed in paragraph 21. Rejected as contrary to the weight of evidence. Addressed in paragraph 21. Addressed in paragraph 22. Addressed in paragraph 25; otherwise rejected as unnecessary and unsupported by the competent evidence. Rejected as unnecessary. Addressed in paragraphs 33 and 34, otherwise rejected as contrary to the evidence. Addressed in paragraphs 26. through 28. Addressed in paragraphs 29. through 30. Rejected as contrary to the weight of evidence. Rejected as unnecessary. Addressed in paragraph 31. 34-35. Rejected as irrelevant. The "fraud" charge was withdrawn. See paragraph 36. 36-37. Rejected as irrelevant. Respondent's Proposed Findings of Fact Adopted in paragraph 1. Adopted in paragraph 2. Adopted in paragraph 3. Adopted in paragraph 4. Adopted in paragraph 5. 6-12. Adopted in paragraphs 6. through 8. 13-15. Rejected as cumulative. 16-22. Addressed in paragraphs 15. and 16., otherwise rejected as unnecessary. 23. Adopted in paragraph 13. 24-27. Addressed in paragraph 14. 28-34. Addressed in paragraph 19. 35-38. Adopted in substance in paragraph 20. 39-40. Adopted in paragraph 21. Rejected as unnecessary. Adopted in paragraph 22. Adopted in paragraph 23. 44-49. Adopted in paragraphs 24. and 25. in substance. 50-60. Rejected as cumulative and unnecessary. 61-66. Addressed in paragraph 32. 67-69. Addressed in paragraph 33. 70-72. Addressed in paragraph 34. 73-89. Addressed in paragraphs 26.-28.; otherwise rejected as unnecessary. Adopted in substance in paragraph 35. Adopted in paragraph 28. Adopted in paragraph 29. 93-94. Adopted in substance in paragraph 29. 95-96. Adopted in substance in paragraph 30. Rejected as cumulative. Adopted in paragraph 30. 99-102. Adopted in substance in paragraph 31. 103-110. Rejected as irrelevant. The "fraud" charge was withdrawn at hearing. See paragraph 36. COPIES FURNISHED: Tobe Lev, Esquire Egan, Lev & Siwica, P. A. Post Office Box 2231 Orlando, Florida 32802 David V. Kornreich, Esquire Muller, Mintz, Kornreich, Caldwell, Casey, Crossland, & Bramnick, P. A. Suite 1525, Firstate Tower 255 South Orange Avenue Orlando, Florida 32801 Donald A. Griffin Executive Director Commission on Human Relations 325 John Knox Road Building F, Suite 240 Tallahassee, Florida 32399-1925 Dana Baird, Esquire General Counsel Commission on Human Relations 325 John Knox Road Building F, Suite 240 Tallahassee, Florida 32399-1925 Sherry B. Rice, Clerk Commission on Human Relations 325 John Knox Road Building F, Suite 240 Tallahassee, Florida 32399-1925
The Issue Whether, and to what extent, Magnolia Valley Services, Inc., should be allowed to increase its water and sewer service rates.
Findings Of Fact Based on the evidence presented at hearing, the following facts are determined: I. The Application By application filed on August 14, 1980, APPLICANT sought authority to increase its water and sewer rates, on an interim and permanent basis, in amounts sufficient to produce $60,847 in annual gross water revenues, and $100,768 in sewer revenues. By Order No. 9571 dated September 30, 1980, the COMMISSION authorized an interim sewer revenue increase, under bond, of $8,205, and denied an interim increase in water revenues. The COMMISSION has approved APPLICANT's use of a test year ending December 31, 1979. At hearing, the APPLICANT amended its application by reducing its requested water revenues to $50,287, and increasing requested sewer revenues to $101,522. (Testimony of Gregg, Prehearing Statement; P-4.) II. Depreciation Rate Depreciation is a method of allocating the cost of fixed assets to their estimated useful life. As an above-the-line operating expense, it affects a utility's net operating income; by its impact on accumulated depreciation of plant-in-service and accumulated amortization of contributions-in-aid-of- construction, it also effects calculation of rate base. (Testimony of Walker, Gregg; P-3, R-1.) The COMMISSION has promulgated no rules as guidelines which establish generally, or in particular, the useful life of utility assets or the method by which their depreciation should be calculated. In practice, however, it has allowed utilities to apply a straight-line 2.5 percent depreciation rate and a 40-year useful life to all depreciable assets. Any deviation from this 2.5 percent across-the-board rate must be justified by the utility. (Testimony of Heiker.) Here, the APPLICANT proposes depreciation rates which vary according to the estimated useful life of the plant or equipment involved. In contends that its shorter estimates of useful life of specific assets reflect reality and actual experience more accurately than an across-the-board 40-year life standard. For example, rate meters are routinely replaced on a 20-year basis and lack of reserve capacity and changing voltages have substantially reduced the expected life of electrical motors and equipment. The APPLICANT's estimates of useful life were established by the opinion of a utility consultant and engineer whose qualifications went unchallenged by the COMMISSION; no competent evidence was offered to discredit or rebut his conclusions. The COMMISSION's engineer candidly admitted that depreciation "is really a nebulous thing," (Tr. 64) and declined to assert that the APPLICANT's depreciation schedules were erroneous. (Tr. 69.) The COMMISSION disputed the APPLICANT's depreciation schedules by referring to an unpublished 1973 staff memorandum retained at the agency's offices and not produced at hearing. That memorandum purportedly adopted 1973 depreciation rates developed by the American Water Works Association. Upon motion of APPLICANT, testimony concerning the contents of that memorandum was subsequently stricken. The COMMISSION engineer also testified that he was unfamiliar, even generally, with how the American Water Works Association's depreciation rates were derived. In light of the quality of the evidence presented of record, the APPLICANT's depreciation rates (including estimated useful life) are accepted as persuasive. (Testimony of Heiker, Gregg; P-1, P-3.) III. Attrition Allowance The APPLICANT seeks to include in operating expenses an attrition allowance of $1,992 for water and $8,161 for sewer operations based on alleged attrition it experienced between 1975 and 1979. It defines attrition as increased annual expenses which cannot be recovered at the time they are incurred. The COMMISSION opposes the requested attrition allowance on the grounds that: (1) the attrition study performed by the APPLICANT is unreliable, and (2) that the recent enactment of Section 367.081(4), Florida Statutes (Supp. 1980), which allows the passing through of certain increased expenses to customers, eliminates the need for a special attrition allowance. (Testimony of Gregg, Walker; P-2.) The COMMISSION's position is well taken. First, a major portion of the cost increases experienced by the APPLICANT in the past will be able to be passed through to its customers pursuant to Section 367.081, Florida Statutes (Supp. 1980). 2/ Those costs include increased power costs and ad valorem taxes. The APPLICANT responds that Section 367.081(4), supra, will not enable it to fully recover increasing expenses when they occur because rates may be adjusted, based on increased operating costs, not more than twice a year. Section 367.081(4)(e), supra. However, this new law should be implemented before it is pronounced inadequate to fulfill its purpose. Experience may show that major costs increase sporadically, or at predictable cycles, which facilitate carefully timed rate increases under Section 367.081(4), and that two such increases a year may prove fully adequate. (Testimony of Gregg, Walker; P- 2, R-1.) Secondly, the attrition study (P-2) submitted by the APPLICANT does not reasonably justify, or provide a reliable basis for projecting an attrition rate into the future. The 1975-1979 historical cost increases have not occurred at a constant rate. The 1979 increase in water operation costs was less than one- half of the average increase experienced between 1975 and 1979; in sewer operations, the 1979 cost increases were less than one-third of the four-year average. Moreover, a major factor in increased sewer costs was the 1978 conversion to a spray irrigation, total retention, sewage treatment system. Since this system meets the 1983 federal Clean Water Act standard of no- discharge, it is unlikely that increased operational costs relating to treatment changes will continue to occur. In short, the 1975-1979 historical cost increases of APPLICANT have been sporadic and do not support an assumption that they will continue to occur at the same rate. To include an attrition allowance based on such an assumption would be unwarranted. (Testimony of Gregg, Walker; P-2, R-1.) IV. Allowance of an Undocumented Operating Charge The APPLICANT proposed a $600 sewer expense item which was opposed by the COMMISSION because of lack of documentation. In response, the APPLICANT submitted--immediately prior to hearing--a cancelled check in the amount of $1,000. The discrepancy between the two amounts remains unexplained. Such action falls short of providing adequate documentation, and the proposed $600 sewer expense item must therefore be rejected. See, 25-10.77, FAC. V. Elements of Ratemaking and Applicant's Gross Revenue Requirements The parties agree: (1) that 14.5 percent is a fair and reasonable rate of return on rate base and reflects the actual cost of capital to APPLICANT; that the new rates should be designed in accordance with the base facility design concept, and that the quality of APPLICANT's water and sewer service is satisfactory. The remaining elements of ratemaking--rate base and net operating income--are not in dispute, and are depicted below: 3/ RATE BASE Test Year Ended 12/31/79 Water Sewer Plant in Service Accumulated $269,887 $511,200 Depreciation $(37,384) 4/ $(54,685) Net Plant $232,503 $456,515 Contributions in Aid of Construction (179,251) (360,055) Accumulated Amortization 22,421 Net Contributions in Aid of 4/ 41,231 4/ Construction (156,830) (318,824) Working Capital 3,515 7,082 TOTAL $ 79,188 $144,773 OPERATING STATEMENT Test Year Ended 12/31/79 Water Sewer Operating Revenues $53,300 $72,608 Operating Expenses: Operations 25,552 45,353 Depreciation 3,848 5/ 4,876 5/ Maintenance 2,572 6/ 11,306 6/ Amortization 1,439 Taxes Other Than Income 4,654 7/ 8,338 7/ TOTAL Operating Expenses $36,626 $71,312 Net Operating Income$16,674 $ 1,296 By applying a 14.5 percent rate of return against a rate base Of $79,188 for water and $144,773 for sewer, it is concluded that the APPLICANT should be allowed an opportunity to earn a return, or net operating income of $11,482 for water and $20,992 for sewer. Annual gross revenues of $48,108 (water) and $92,304 (sewer) are required to produce such a return--resulting in a net annual reduction of water revenues of $5,192 and a net increase of $19,696 in sewer revenues. VI. Interruption of Service Treatment Without Advance Notice Although the overall quality of its service has been adequate, infra, the APPLICANT has unnecessarily inconvenienced customers by interrupting water service without advance notice. These interruptions were planned in advance and not made on an emergency basis. The APPLICANT failed to adequately explain or excuse its failure to give timely notice. (Testimony of Pepper.)
Recommendation Based on the foregoing findings of fact and conclusions of law, it is RECOMMENDED: That Magnolia Valley Services, Inc., be authorized to file new rates structured on the base facility charge concept and designed to generate gross annual revenues of $48,108 for water operations and $92,304 for sewer operations, based on the average number of customers served during the test year. It is further RECOMMENDED that the utility be directed to strictly comply in the future with Section 25-10.56, Florida Administrative Code, by giving advance notice of service interruptions which are not emergency in nature. DONE AND ORDERED this 1st day of April, 1981, in Tallahassee, Florida. R. L. CALEEN, JR. Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32301 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 1st day of April, 1981.
Findings Of Fact Cooper City Utilities, Inc. provides water and sewer service to its customers in Broward County, Florida, under the jurisdiction of the Commission pursuant to Chapter 367, Florida Statutes. The company was incorporated in 1973. All of the outstanding stock of the utility was owned by Moses Hornstein until his death on October 28, 1979, when ownership thereof became vested in the estate of Moses Hornstein, deceased. The personal representatives of this estate are Gertrude Hornstein, S. Lawrence Hornstein, and Judith A. Goldman. Gertrude Hornstein serves as president of Cooper City Utilities, Paul B. Anton as vice president, and Lawrence Lukin as secretary. Quality of Service At the hearing, a representative of the Broward County Health Department testified concerning the quality of service. Although some customer complaints had been received, there are no outstanding citations against Cooper City Utilities, Inc., and the quality of the utility's service will be improved when its new lime-softening plant, under construction, is completed in approximately August, 1980. The investigation by the Commission's staff engineer did not reveal any outstanding citations against either the water or sewer treatment facilities. Accordingly, on the basis of the entire record, the evidence supports a finding that the utility is in compliance with all state standards, and that the quality of its water and sewer service is satisfactory. Rate Base and Operating Statement Between the time in July when public hearings commenced, and September 24 when the hearings concluded, the utility abandoned its position on several matters which had been in dispute, leaving only two controverted subjects for resolution. These two remaining areas of disagreement are, (1) the cost of money [because of a pending petition for approval of additional financing (Docket No. 800562-WS)], and (2) the expense for an additional field laborer hired subsequent to the test year, which the utility seeks to have included as a pro forma expense. Based on the stipulation of the parties, the following schedule sets forth the rate base of Cooker City Utilities (Exhibit 15): Water Sewer Utility plant in service $2,331,137 $3,723,347 Plant held for future use (47,989) (166,375) Accumulated depreciation (286,651) (460,297) CIAC (net of amortization) (1,322,487) (2,302,707) Working capital allowance 51,083 37,680 Rate Base $ 725,093 831,648 Based on the stipulation of parties, prior to any consideration of the allowance of any expense for the laborer hired subsequent to the test year, the following schedule sets forth the utility's operating statement (Exhibit 15): Water Sewer Operating Revenues $ 368,562 $ 489,886 Operating Expenses: Operation 346,916 232,406 Maintenance 61,750 69,030 Depreciation 22,447 25,543 Amortization -0- -0- Taxes other than income 55,853 75,043 Other expenses -0- -0- Income taxes -0- -0- Total Operating Expenses $ 486,566 $ 402,022 Operating Income (Loss) $ (118,404) 87,864 5. On the matter of allowance of sufficient revenue to cover the cost of one additional laborer hired after the test year, the estimated annual expense is approximately $7,240. However, to the extent that this employee was hired due to an increase in the number of customers subsequent to the test year, or due to plant capacity not used and useful, it is not a proper pro forma adjustment. Without an affirmative showing that the laborer was necessary during the test year for existing customers, the adjustment should be disallowed, and there is insufficient evidence in this record to support such a finding. On the issue of cost of money, during the test year the utility's capital structure was composed of one hundred percent debt at a stated cost of ten percent. In Docket No. 800562-WS the company seeks Commission authority to borrow an additional sum of $450,000, and it plans to amend this application to include authority to borrow $400,000 more in order to make refunds to customers in compliance with a Commission order which was upheld in Cooper City Utilities, Inc. v. Mann (Fla. Sup. Ct. Case No. 58,047, September 12, 1980). However, the utility's proposed debt has not yet been approved by the Commission, and will not be incurred until some time in the future, if approved. In these circumstances, it is not appropriate to take the cost of new debt into consideration in determining cost of capital in this rate case. The evidence in the record supports a ten percent cost of capital. The earned rate of return for the water system is a negative 16.33 percent. The earned rate of return for the sewer system is 10.57 percent. Therefore, the utility's water rates should be increased, and its sewer rates should be decreased, to achieve an overall ten percent rate of return. Accordingly, the annual revenue requirement for the water system is $564,370, which amounts to an annual revenue increase of $195,808. The annual revenue requirement for the sewer system is $485,067, which amounts to an annual revenue decrease of $4,819. Rate Structure The present rates of Cooper City Utilities are structured in the conventional manner, consisting of a minimum gallonage charge and a one-step excess rate over the minimum. The utility proposes. rates with the same basic structure, but with changes in the minimum charge and the minimum gallonage allowance. However, the Commission has consistently taken the position that any rate that requires customers to pay for a minimum number of gallons, whether used or not, is discriminatory. Invariably, a base facilities type of rate structure has been required to be implemented in these circumstances. Under the base facilities charge, each customer pays a pro-rata share of the related facilities cost necessary to provide service, and in addition, pays only the cost of providing the service actually consumed under the gallonage charge. The evidence in this record supports the implementation of the base facilities charge form of rate structure. Under its tariff, Cooper City Utilities is authorized to charge guaranteed revenues in an amount equal to the minimum rate for water service and the applicable rate for sewer service for each equivalent residential connection to be served for a period of one calendar year in advance. Under the base facilities charge type of rate structure, the utility should be authorized to collect guaranteed revenues solely in the amount of the base facilities charge.
Recommendation Based upon the findings of fact and conclusions of law set forth above, it is RECOMMENDED that the application of Cooper City Utilities, Inc., 3201 Griffin Road, Suite 106, Fort Lauderdale, Florida, 33312, be granted for the water system and denied for the sewer system, and that the utility be authorized to file revised tariff pages, containing rates designed to produce annual gross revenues of $564,370 for its water system and $485,067 for its sewer system. It is further RECOMMENDED that the utility be required to implement a base facility charge type of rate structure. It is further RECOMMENDED that the utility be required to make appropriate refunds to its sewer customers in amounts to be approved by the Commission. It is further RECOMMENDED that the rate-refunding bond filed in this docket be maintained until the utility has accomplished the refunds indicated above. THIS RECOMMENDED ORDER entered on this 18th day of November, 1980, in Tallahassee, Florida. WILLIAM B. THOMAS Hearing Officer Division of Administrative Hearings 101 Collins Building Tallahassee, Florida 32301 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 18th day of November, 1980. COPIES FURNISHED: Andrew T. Lavin, Esquire Post Office Box 650 Hollywood, Florida 33022 Sam Spector, Esquire Post Office Box 82 Tallahassee, Florida 32302 James L. Ade and William A. Van Nortwick, Esquires Post Office Box 59 Jacksonville, Florida 32201 John W. McWhirter, Jr., Esquire Post Office Box 2150 Tampa, Florida 33601 Alan F. Ruf, Esquire 2801 East Oakland Park Boulevard Fort Lauderdale, Florida 33306 William H. Harrold, Esquire Florida Public Service Commission 101 East Gaines Street Tallahassee, Florida 32301 ================================================================= AGENCY FINAL ORDER ================================================================= BEFORE THE FLORIDA PUBLIC SERVICE COMMISSION In re: Application of Cooper City DOCKET NO. 800415-WS (CR) Utilities, Inc. for a rate increase ORDER NO. 9699 to its water and sewer customers in DOAH CASE NO. 80-1188 Broward County, Florida. ISSUED: 12-16-80 / The following Commissioners participated in the disposition of this matter: WILLIAM T. MAYO GERALD L. GUNTER JOSEPH P. CRESSE JOHN R. MARKS, III Pursuant to notice, the Division of Administrative Hearings, by its duly designated Hearing Officer, William B. Thomas, held public hearings in this matter on July 16 and 17, and on September 23 and 24, 1980, in Cooper City, Florida. The Division of Administrative Hearings assigned Case No. 80-1188 to the above-noted docket. APPEARANCES: Andrew T. Lavin, Esquire Post Office Box 650 Hollywood, Florida 33022 and Sam Spector, Esquire Post Office Box 82 Tallahassee, Florida 32302 for the Petitioner, Cooper City Utilities, Inc. James L. Ade and William A. Van Nortwick, Esquires Post Office Box 59 Jacksonville, Florida 32201 for PCH Corporation Intervenor in opposition. John W. McWhirter, Jr., Esquire Post Office Box 2150 Tampa, Florida 33601 and Alan F. Ruf, Esquire 2801 East Oakland Park Boulevard Fort Lauderdale, Florida 33306 for the City of Cooper City, Florida, Intervenor in opposition. William H. Harrold, Esquire Florida Public Service Commission 101 E. Gaines Street Tallahassee, Florida 32301 for the Respondent, Florida Public Service Commission and the public generally. The Hearing Officer's Recommended Order was entered on November 18, 1980. The time for filing exceptions thereto has expired and no exceptions have been filed. After considering all the evidence in the record, we now enter our order.
Findings Of Fact Although numerous customers were present, four of them testified at the hearing. No service quality problems were described with regard to either water or sewer service. Indeed, several of the customers described water quality as being good or excellent. The primary concern of the customers was the magnitude of the proposed rate increase, although a number of then opined that some increase in rates may he necessary. Expert engineering witnesses presented by both the Comission and the Petitioner established that the Utility has not been cited by any local, state or federal agency for health or environmentally related violations. No corrective orders are in force either by the Department of Environmental Regulation, the Lee County Health Department, or the Public Service Commission. The water and sewer treatment exceeds all governmental quality standards extant. In order to enhance service quality, the company has constructed a one million gallon ground storage tank and has installed an additional high-service pump. All parties agree that the cost of these improvements should be added to the Utility's rate base for purposes of this proceeding. Rate Base The Utility propounded evidence alleging its proper water rate base to be $1,872,470.00 and the appropriate sewer rate base to be $1,917,931.00. In arriving at the Utility's net investment in property used in the public service (rate base), it is necessary to calculate the amount of contributions-in-aid-of-construction, which serve to decrease the Utility's investment. Normally, where there has been a previous rate case for a utility in which the utility's net investment would have been determined by the Commission, the calculation of the utility investment in a current rate case is generally competed by adding additions to plant-in-service and subtracting additional contributions-in-aid-of construction in order to arrive at the current net "return yielding" investment. In the instant proceeding, however, Lehigh has elected to take issue with the amount of contributions-in-aid-of-construction (CIAC) previously determined by the Commission in the last rate case. In that last case (Docket No. R-73384-WS), the amount of CIAC was determined by multiplying water connections by $350.00 and sewer connections by $400.00. (See Exhibits 10, 19 and 20) The Utility in the prior proceeding agreed with that method of calculation and, further, two land sales contracts in evidence show that a charge of $750.00 for "sales price of water and sewer" to purchasers of houses in the service area has been imposed by the Utility or its predecessor, Lehigh Corporation (development company), when the Utility was merely a division of the development company. Notwithstanding that prior position, the Utility in this proceeding has elected to attempt to prove its level of CIAC ab initio and has conducted a "Special CIAC Study" in an attempt to show that the amount of contributions is now substantially less than the amount it and the Commission agreed to be applicable in the last rate proceeding and that which the Commission maintains is germane to this proceeding. The Utility thus is alleging that the appropriate charge per connection for CIAC is $650.00 for a water and sewer connection as opposed to the Commission's contention that the figure should be $750.00 per connection. Although a developer's agreement with an affiliated company shows a water and sewer connection charge of $650.00, the testimony of a senior officer of the Utility establishes that there were a total of 1,308 such contracts indicating a sales price for water and sewer service of $750.00. The Utility contends that only $650.00 of the $750.00 charge in question was actually transferred to the utility company and that, therefore, the $650.00 is the appropriate amount to attribute to CIAC. There is no question, however, that with regard to these 1,308 land sales contracts, that $750.00 was actually collected from the lot purchasers involved as the sales price of water and sewer service. Thus, the actual amount of CIAC paid by those 1,308 customers was $750.00 each, for a total of $981,000.00 for water and sever service and that figure represents in its entirety contributions-in-aid-of-construction. The contracts for which the customers involved paid $750.00 for water and sewer service, were entered into in the latter 1960's and early 1970's. Prior to that time, the same type of contracts carried an amount of $650.00 for water and sewer and following the period of time when the fee was $750.00, the line item in the contract was changed so that there was no longer any separate item providing for "sales price of water and sewer." The water and sewer charge was thereafter included in the amount charged for "sales price of improvements." Thus, contrary to the position of Lehigh, because of the segregation of the items in the purchase price shown in these land sales contracts into separate figures for price and for the sales price of water and sewer service, there have been shown to be definite, proven amounts of contributions-in-aid-of-construction supported by company records. The remaining portion of the contributions attributable to the Utility and not represented by these contracts were contributed in the sum of $650.00 per connection, with which figure both parties agree. An additional issue regarding contributions and the "Special CIAC Study" concerns contributions recorded as income from the inception of the Utility operation until November 30, 1964. As demonstrated by Exhibit 12, the amount of contributions recorded as income equals $756,656.00. The Utility's own "Special CIAC Study" refers to contributions recorded as income and Lehigh received sums of money for the availability of water and sewer service in the early 1960's which it treated as income. During the early 1960's when the Utility was regulated by Lee County, the Lee County regulatory board allowed it and other water and sewer utilities to receive and record service availability fees as revenue. This was done in order to enhance the apparent financial posture of the utilities and therefore improve their credit status as an aid to financing improvements. There is no question that those fees during this time period were paid into the Utility or its predecessor for water and sewer service availability and hence should properly be accounted for as CIAC. It might be argued, as the Utility does, that if Lehigh declared the contributions it received to be revenues with the Internal Revenue Service, then the benefit of those contributions or the amount of revenue they represent to the Utility would be reduced by the amount of the resulting income tax, and that if they are now determined to be contributions instead of revenue that an additional detriment to the Utility would occur by the reduction by that amount of its rate base and, therefore, its dollar return. It should be pointed out, however, that because of the tax advantages of the Utility's demonstrated operating loss carry-overs and investment tax credits, as well as accelerated depreciation, all of which tax advantages this Utility has been able to employ, no actual income tax has been paid on such "revenue." Further, Lehigh is depreciating this $756,655.00 in assets in its returns to the Internal Revenue Service and is thereby recovering the costs of the assets. If the Utility is permitted to treat them for regulatory rate-making purposes as revenue instead of CIAC, then the effect would be to maintain rate base and return at a correspondingly higher level than if these amounts are determined to be CIAC, which would reduce rate base and thereby the net investment upon which a return could be earned for regulatory purposes. Thus, the appropriate amount of contributions-in-aid-of-construction for the water system as of the closing date of March 31, 1979, equals $1,057,000.00. The amount of contributions-in-aid-of-construction attributable to the sewer system as of that date equals $1,389,977.00. (Net of amortization). The detailed calculations and adjustments supportive of the above findings with regard to rate base are attached hereto and incorporated by reference herein as Schedules I, II and II. The first issue to be concerned with in calculating the operating expense basis for the revenue requirement is the cost of the above-referenced CIAC study. The Utility prepared this special CIAC study because of its fear that, in view of the Commission's decision in Tamarac Utilities, Inc. v. Hawkins, 354 So.2d 437, that it would not otherwise be able to meet its burden of proof on the issue of contributions and therefore would suffer a dismissal of the petition. In the Tamarac case, the Public Service Commission auditors encountered numerous problems resulting from a lack of primary data supporting the amount of contributions and the Commission issued an order allowing the Utility to provide clarifying evidence. When the Utility failed to satisfactorily perform this task, it ultimately suffered a dismissal of its petition and a refund of monies collected under interim rates. In this case, however, it has been demonstrated that there is no dearth of primary data or books and record supportive of the level of CIAC; nor has an order been issued requiring this Utility to provide such clarification or a "study" of its CIAC. Moreover, in the case of this utility, a previous rate case has been finalized wherein it was found by the Commission that there was a definite, specific level of contributions which were also consistent with those alleged by the petitioner in that proceeding. Thus, there is adequate primary data upon which a determination of CIAC can be computed in this proceeding without resort to a "Special CIAC Study" and the additional increment of rate case expense it represents. It should be further noted that even if the instant case involved a "Tamarac situation" where financial books and records were not adequate to properly document contributions-in-aid-of-construction that, in that event, if a CIAC study were made, then the proper rate-making treatment would be to amortize tile cost of that study over several years, since it is a large, nonrecurring expense in the Utility's operation, as opposed to allowing the entire expense to be written off (and charged to the customers through rates) based upon one year. The Utility has alleged that certain additional pro-forma adjustments to various expense items should be accomplished in order to arrive at the appropriate revenue which will support an adequate rate of return. Thus, the increased costs alleged for purchases of lime, chlorine and gasoline, depicted in the attached schedules incorporated herein, were undisputed, agreed to, are reasonable and therefore should be accepted. The alleged pro-forma cost for payroll is a mere estimate and not supported by competent, substantial evidence. Additionally, it was established by the Commission's accounting witness that certain rate case expenses arose from a prior rate case and therefore should be removed from consideration in arriving at revenue requirements for purposes of this proceeding. This adjustment was not contested, nor were similar adjustments to remove depreciation expense on construction work in progress, to remove depreciation expense on the contributed property, to remove unsupported property taxes, and to remove property tax as an expense and depreciation expense attributable to non-used and useful portions of the Utility's invested plant. None of these adjustments were disputed by the Utility. They are appropriate and reasonable and should be adopted. The Utility has also requested allowance of a $55.00 annual fire hydrant charge and a $10.00 charge for the initial commencement of service. The Utility submitted evidence (Exhibits 6 and 7) supportive of the actual number of water and sewer connections made during the test years as well as the costs upon which the initial commencement of service charge requested is based. The Commission did not dispute, therefore, the requested $10.00 charge for initial commencement of service and, inasmuch as the current $25.00 annual fire hydrant charge was established in the late 1960's and was shown to be no longer sufficient to cover costs, the Commission also did not dispute the increase in the annual fire hydrant charge from $25.00 to $55.00, which accordingly should be increased. Cost of Capital The Utility has requested a rate of return of 11.76 percent which includes an attrition allowance of .78 percent. There is no dispute as to the debt-equity ratios in the capital structure of the Utility. The common stock equity represents approximately 49.57 percent of the total capitalization. Long-term debt makes up 35.96 percent of capital and cost-free capital items make up 14.47 percent. The cost rate of the equity in the capital structure was established by the Commission's financial expert witness to be 14.5 percent or the midpoint in a range for companies and utility companies possessing a similar degree of risk to equity investors of 13.5 percent to 15.5 percent. The 14.5 percent cost of equity figure represents an accurate assessment of the opportunity costs of equity capital for such a company. The imbedded cost of long-term debt is 8.3 percent, which is a very advantageous rate to be enjoyed by such a company in today's money market and reflects a high degree of management efficiency on the part of the operation and management personnel of the petitioner. These two items, when combined with a zero cost factor shown to be appropriate for the cost-free capital items, results in a calculated rate of return of 10.35 percent, which does not take into account an attrition allowance due to inflation. The Utility advocated an attrition allowance equal to 10 percent of the weighted cost of equity capital to help offset the erosion in earnings caused by inflation. There can be little doubt that attrition of earnings due to significant inflation in costs of operation experienced by such companies is a very real factor. However, this record contains no substantial and competent evidence to demonstrate whether the utility wants coverage of capital attrition or attrition of its ability to cover operation and maintenance expenses nor which could justify the alleged 10 percent factor or any other quantification of attrition of earnings which may be experienced. Thus in the absence of a definitive establishment of the appropriate attrition factor, a cost of equity and a corresponding return on rate base in the midpoint of the range found above is appropriate. Thus, the proper return on rate base for this Utility has been shown to be 10.35 percent, which is within the range 9.85 percent to 10.84 percent. A summary of the cost of capital structure and weighted cost of capital calculation is depicted as follows: CALENDAR YEAR 1979 COMMON STOCK EQUITY RATIO 49.57 COST RATE 14.5 WEIGHTED COST 7.19 LONG TERM DEBT 35.96 8.8 3.16 COST FREE 14.47 -0- -0- 10.35 Floor CSE at 13.5 9.85 Ceiling CSE at 15.5 10.34 In summary, the required operating revenue for the Utility's water system should be $658,451.00 which results in an operating income of $211,407.00. The sewer system requires an annual, gross operating revenue of $475,629.00 in order to obtain a return or operating income of $130,017.00. The operating expenses and adjustments supportive of these figures are depicted in more detail in Schedules IV, V and VI attached hereto and incorporated by reference herein. The sewer revenue requirement found herein is less than the interim revenues authorized for sewer service, thus a refund is in order.
Recommendation In consideration of the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the application of Lehigh Utilities, Inc. be granted in part, and that the Utility be authorized to receive a gross annual water revenue of $658,451.00 and gross annual sewer revenue of $475,629.00 to be achieved by rates filed with and approved by the Public Service Commission. It is further RECOMMENDED that the Utility be required to file revised tariff pages containing rates designed to produce annual revenues in the above amounts. It is further RECOMMENDED that the Utility be required to refund the interim sewer revenues previously authorized in this proceeding which exceed those sewer revenues determined to be appropriate herein. It is further RECOMMENDED that the above refunds be accomplished within ninety (90) days. This Recommended Order entered this 13th day of October, 1980, in Tallahassee, Florida. P. MICHAEL RUFF Hearing Officer Division of Administrative Hearings 101 Collins Building Tallahassee, Florida 32301 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 13th day of October, 1980. COPIES FURNISHED: R. M. C. Rose, Esquire 1020 East Lafayette Street Tallahassee, Florida 32301 William H. Harrold, Esquire 101 East Gaines Street Tallahassee, Florida 32301
Findings Of Fact Upon consideration of the oral and documentary evidence presented at the hearing, the following relevant facts are found: In 1984, the citizens of Pasco County approved a "straw ballot" proposal providing for the establishment of a resource recovery facility financed with non-ad valorem revenue bonds for the purpose of disposing of the County's solid waste in lieu of utilizing sanitary landfills as a primary disposal method. The Board of County Commissioners of Pasco County thereafter commissioned the consulting engineering firm of Camp Dresser and McKee (CDM) to perform a resource recovery feasibility study and to identify a site for the facility. CDM concluded that a resource recovery facility was an economically feasible approach to solid waste management for Pasco County. After evaluating seven sites for such a facility, CDM recommended a 751-acre site on Hays Road in western Pasco County. The County purchased the site at a cost of approximately three million dollars. In 1987, the Legislature adopted a Special Act, Chapter 87-441, Laws of Florida, establishing a solid waste disposal and resource recovery system within Pasco County and giving the County exclusive control over the collection and disposal of solid waste generated or brought within the area affected by the Act. The solid waste disposal and resource recovery system proposed by the County will convert solid waste into electrical power through a process of combustion, utilizing a mass-burn technology, followed by landfilling of the ash residue. Initially, the "waste-to-energy" facility will have three combustion/steam generation units, which will dispose of 900 tons of refuse each day and produce approximately 22 megawatts of electricity. A fourth combustion unit may be added in the future, thus allowing the facility to dispose of 1,200 tons of refuse each day and produce 29 megawatts of electricity. The resource recovery facility and landfill/ashfill is designed with the purpose of complying will all applicable environmental regulations. Best available control technology will be utilized to minimize the emissions of air pollutants. The facility will use a baghouse with fabric filters to control particulate emissions and a dry scrubber to control acid gas emissions. The landfill will have two synthetic liner systems and two leachate collection systems to maximize the protection of groundwater resources. Stormwater on the site will be treated in retention/detention basins, and there will be no discharges of wastewater on the site. Ferrous metals in the solid waste will be recovered and recycled. The undeveloped 751 acre parcel of land owned by the County is located in an unincorporated area of northwest Pasco County. It is approximately two and a half miles north of Highway 52 and about four to five miles west of Route The site is accessible by Hays Road, which forms its southern and western boundaries. Shady Hills Road runs to the east of the site and Blue Bird Lane runs along the northern perimeter. The parcel is bisected by Florida Power Corporation power lines, which run in a north/south direction. All development on the site relating to the proposed resource recovery facility will be east of the power lines. The site primarily consists of grasslands and wooded areas. Most of the areas near the site boundaries are wooded. An access road from Hays Road would be constructed to lead to the resource recovery facility, and the site would also contain a landfill/ashfill and several stormwater retention ponds. The resource recovery facility will be located on the southeastern portion of the site, approximately 4,600 feet from the site's northern boundary. The facility will be approximately 2,400 feet from the nearest residence, which is located on Hays Road. There will be at least 250 feet of buffer area between the resource recovery facility and the property boundaries. There will be at least 700 feet of buffer area between the landfill and the northern boundary of the site. The ashfill portion of the project would be developed over a 25 to 35 year period. The areas surrounding the site consist of agricultural and very low density residential developments. The areas to the east, southeast, and southwest are very sparsely populated. There is scattered low density residential development to the north, northeast and northwest, and some scattered residences south and southwest of the site. The subject parcel of land lies within the Pasco County Zoning Code's A-C Agricultural District. According to the Pasco County Zoning Code, Ordinance No. 75-21, the purpose of the A-C Agricultural District is to preserve the rural and open character of various lands within Pasco County. The principal permitted uses within this District include agriculture, general farming and horticulture; single family dwellings; duplexes; home occupations; public and private parks and playgrounds; mineral extraction activities; and residential treatment and care facilities. Accessory uses include private garages and parking areas, private swimming pools and cabanas, and signs. Special exemption uses within the A-C Agricultural District include country club and golf course, aircraft landing fields, cemeteries, animal hospitals, sanitary landfills and public buildings and public utility facilities which do not cause an undue nuisance or adversely affect existing structures, uses and residents. Ordinance Number 82-04, Section 2, amended the Pasco County Zoning Code to exempt from its provisions "development and other activities conducted by Pasco County." (Exhibit No. 3) It was the opinion of Pasco County's Zoning Administrator that the proposed resource recovery facility and landfill/ashfill were exempt from the County's Zoning Code. The County's present Planning Director concurred with this opinion. It was further the opinion of the Zoning Administrator that even if the project were subject to the requirements of the Zoning Code, it could be built as a special exemption use in the A-C Agricultural District. Pasco County has an ordinance, known as the New Development Fair Share Contribution for Road Improvements Ordinance, which requires developers to pay impact fees for transportation purposes. According to the County Planning Director, this ordinance expressly excludes County projects from its provisions. It was the opinion of the County's land use planning and zoning experts that the use of the site for a resource recovery facility would be compatible with surrounding land uses. The project will be designed so as to be barely visible from surrounding areas and to give as pleasing an aesthetic appearance as possible to the site. When a detailed site plan for the facility is prepared, the project will be evaluated by the Pasco County Development Review Committee, composed of County employees from various departments, to ensure that the project is consistent with existing regulations and compatible with surrounding land uses. The Pasco County comprehensive land use plan was adopted in 1982 and is currently being revised. It is a policy document containing various planning elements, with goals, objectives, policies and recommendations. It does not currently include a land use map that specifically identifies the permissible land uses for the site of the proposed resource recovery facility. In the process of updating its comprehensive plan, the County will adopt a future land use map. The Chief Planner for the Pasco County Planning Department testified that the land use map to be submitted for future adoption will designate the proposed site as a resource recovery site. The County's comprehensive plan contains a solid waste and resource recovery element. The plan recognizes waste disposal as a crucial concern, and the goal of this element is to dispose of the County's domestic and industrial waste in the safest and least expensive manner. From an engineering perspective, the project will be designed to comply with applicable state and federal requirements pertaining to air and water pollution. The economic feasibility of a resource recovery facility has been studied, with positive results. Other elements of the Pasco County comprehensive plan relevant to the proposed resource recovery facility include the traffic circulation element, the water element, the conservation/coastal zone protection element, the drainage element and the utilities element. A traffic analysis demonstrated that current levels of service on State Road 52 and on Hays Road will not be diminished as a result of project operations. The use of reclaimed water will promote the objective of water conservation. The proposed site has not been designated for preservation or conservation and the project will have minimal impact on wetland areas. The stormwater management system will be designed so that runoff will not be channelized into any natural surface water body. The retention basins will be of sufficient size to allow adequate settling of suspended solids collected with the stormwater. By producing electrical power as a by-product of solid waste disposal, the project will further the objective of the comprehensive plan's utility element of encouraging the conservation of limited resources in the operations of utility systems. On December 31, 1987, notice of the land use hearing was published in the Pasco Times newspaper, a daily newspaper of general circulation which has been continuously published at Port Richey in Pasco County, Florida, each day for a period in excess of one year preceding the publication of notice in this case. In addition, notice of the land use hearing was published in the Florida Administrative Weekly, Volume 13, Number 53, on December 31, 1987. The Department of Environmental Regulation issued a news release concerning the land use hearing on December 24, 1987. By letters dated December 28, 1987, notice was given by certified mail to the Executive Director of the Tampa Bay Regional Planning Council, the Pasco County Planning Department and the Pasco County Zoning Administrator. Notice of the land use hearing was also posted at the project site. Eight persons, all of whom resided or owned property near the proposed site, testified at the land use hearing as members of the general public. All opposed the construction and operation of a resource recovery facility and landfill/ashfill at that site. Though none of the witnesses claimed to have expertise concerning the subject matter of their testimony, their concerns included the impacts of the proposed project upon the environment; the value and use of their land, homes and businesses; the recreational value of surrounding properties and the general agricultural character and nature of the surrounding land. Concerns were also expressed over the safety features and costs involved in the operation of the facility. These citizens of Pasco County did not believe it was proper for the County to exempt itself from the County's zoning laws and impact fees.
Recommendation Based upon the findings of fact and conclusions of law recited herein, it is RECOMMENDED that the Governor and Cabinet, sitting as the Siting Board, enter a Final Order finding that the use of the site chosen by Pasco County for the location of its proposed solid waste and resource recovery facility is consistent with and in compliance with the applicable land use plans and zoning ordinances. Respectfully submitted and entered this 25th day of March, 1988, in Tallahassee, Florida. DIANE D. TREMOR 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 25th day of March, 1988. APPENDIX "A" TO RECOMMENDED ORDER, CASE NO. 87-5337 Pasco County's proposed findings of fact have been fully considered and are accepted and incorporated in this Recommended Order, with the following exceptions: 16, second sentence: Rejected as speculative. See Finding of Fact Number 10. 22, last sentence: Rejected as improper factual finding, but addressed in the Conclusions of Law. 23, last sentence: Rejected as argumentative and improper factual finding, but addressed in Conclusions of Law. COPIES FURNISHED: David S. Dee Carlton, Fields, Ward, Emmanuel, Smith & Cutler, P.A. Post Office Drawer 190 Tallahassee, Florida 32302 Richard T. Donelan, Jr. Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399 C. Lawrence Keesey Rhyne Building 2740 Centerview Drive Tallahassee, Florida 32399 Edward B. Helvenston 2379 Broad Street Brooksville, Florida 34609-6899 Mike Twomey Florida Public Service Commission 101 East Gaines Street Tallahassee, Florida 32301 Honorable Bob Martinez Governor The Capitol Tallahassee, Florida 32399 Honorable Bob Butterworth Attorney General The Capitol Tallahassee, Florida 32399 Honorable Doyle Conner Commissioner of Agriculture The Capitol Tallahassee, Florida 32399 Honorable Gerald Lewis Comptroller The Capitol Tallahassee, Florida 32399 Honorable Bill Gunter Insurance Commissioner The Capitol Tallahassee, Florida 32399 Honorable Betty Castor Commissioner of Education The Capitol Tallahassee, Florida 32399 Honorable Jim Smith Secretary of State The Capitol Tallahassee, Florida 32399
