Findings Of Fact The Petitioner is a utility regulated by the Commission that is in the business of acquiring and operating water and sewer systems in Florida, principally in Central Florida. It now operates 39 systems, of which at least 30 water systems and 5 sewer systems are located in Orange, Lake and Seminole counties. In this case, the Central Florida Division has one water system in Lake County (Picciola Island) , two water systems in Orange County (Daetwyler Shores and Lake Conway), three water systems and one sewer system in Seminole County (Bretton Woods/Druid Hills, Dol Ray Manor, and both water and sewer in Chuluota; these systems serve 949 water customers and 98 sewer customers. Southern commenced operating these systems in the spring of 1978, purchased them from Central Florida Utilities, Inc. in October, 1978 and applied to the Commission for a transfer, which application is still pending. (Docket 780278- WS; Hearing Examiner's Recommended Order approving the transfer was filed January 29, 1979) Notwithstanding customer complaints of the quality of the water service (low or fluctuating pressure, excess chlorine, sediment, no noticed interruptions and lack of fire protection capabilities) and Southern's admission of the general disrepair of the systems at the time of the purchase, the systems are in compliance with governmental standards. The utility has spent $52,000 since the test year on repair and upgrading with another $87,000 necessary to complete the required projects, of which $25,000 is for governmentally mandated improvements to the Chuluota wastewater system. The Petitioner's use of the purchase price of $215,800 for the facilities involved in the seven systems as the amount of plant in service as of June 30, 1978, rather than Respondent's use of the 1977 annual reports of the prior owner, is appropriate because: it follows past FPSC decisions on this subject with respect to this utility; the purchase price was considerably less than FPSC's estimated replacement cost of over $800,000; the purchase was an arms-length transaction; the books of the prior owner were considered unreliable; and, following complete integration of operations with Petitioner's other systems in Lake, Orange and Seminole counties, the customers should obtain the best possible service at the lowest rates obtainable. Alternatively, the Utility is entitled to an acquisition adjustment that achieves the same rate base as using the purchase price. Petitioner's rate bases using a 12-month average, rather than the preferred 13-month average, are as follows: Water Sewer Average test year plant $178,305 $ 62,242 Mandated additions 25,000 Accumulated depreciation (1,833) (623) CIAC (net of amortization) (6,703) Working Capital 11,241 1,801 Income tax lag (776) (370) $180,234 $ 89,050 The capital structure and rate of return is as stipulated by the parties as follows: WEIGHTED TYPE AMOUNT RATIO COST COST Common Stock $1,882,055 60.44 14.0 percent 8.46 Long Term Debt 1,037,372 33.31 8.89 2.96 Cost Free 194,768 6.25 0 0 TOTAL $3,114,195 100.00 11.42 perc. Rate of Return The above rate bases and rate of return provide an authorized constructed net operating income from water service of $20,583 and from sewer service of $10,170. This results in the following constructed statement of operations for year ended June 30, 1979: Water Sewer Operating Revenue $122,993 $29,085 Operating Expense Operation 84,760 12,346 Maintenance 4,103 2,065 Depreciation 3,531 1,245 Taxes, other than income 6,138 1,409 Income taxes 3,878 1,850 Total $102,410 $18,915 Net Operating Income $ 20,583 $10,170 It is noted that the above revenue requirement is more than the interim authorized revenue of $97,184 for water and $17,640 for sewer. The staff proposed that the rate structure should be changed from the present block structure far water and flat rate for sewer to a base facility charge for both water and sewer. This concept is appropriate since it serves to conserve water and insures that each customer pays his fair share of the costs of providing service. No evidence opposing this type rate structure was presented.
Recommendation Based upon the foregoing findings of fact and conclusions of law, it is RECOMMENDED that the application of Southern States Utilities, Inc., Central Florida Division, be granted and that the utility be authorized to file new tariffs to be approved by the Florida Public Service Commission that would have provided for the test year ending June 30, 1979 annual gross revenues of $122,993 for water service and $29,085 far sewer service. It is further RECOMMENDED that the utility be required to implement rates for fire protection service in Belle Isle and a base facility charge in structuring water and sewer rates. It is further RECOMMENDED that the refund bond be returned to utility. DONE and ORDERED this 24th day of October, 1980, in Tallahassee, Florida. H. E. SMITHERS Hearing Officer Division of Administrative Hearings Room 101 Collins Building Tallahassee, Florida 32301 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 24th day of October, 1980. COPIES FURNISHED: Kenneth H. Myers, Esquire 1428 Brickell Avenue Miami, Florida 33131 William H. Harrold, Esquire 101 E. Gaines Street Tallahassee, Florida 32301 Sam Owens, Esquire 101 E. Washington Street Orlando, Florida 32801 Steve Tribble, Clerk Florida Public Service Commission 101 E. Gaines Street Tallahassee, Florida 32301 Robert T. Mann, Chairman Public Service Commission 101 E. Gaines Street Tallahassee, Florida 32301
The Issue Whether SFP's revised application for a permit to construct a sewage treatment plant with percolation ponds should be granted or, for failure of SFP to give reasonable assurances that the plant will not cause pollution significantly degrading the waters of Gator Cove, be denied?
Findings Of Fact About 1,500 feet from Santa Fe Lake's Gator Cove, SFP proposes to build an extended aeration package sewage treatment plant to serve a "private club with restaurant and overnight accommodations," SFP's Exhibit No. l, to be built between the plant and the lake, on the western shore of Santa Fe Lake, just south of the strait or pass connecting Santa Fe Lake and Little Santa Fe Lake. The site proposed for the waste water treatment plant lies at approximately 177 or 178 feet above sea level, north of Earleton on county road N.E. 28 near State Road 200A, some three miles north of State Road 26, in unincorporated Alachua County, Section 33, Township 8 South, Range 22 East. SFP's Exhibit No. 1. Santa Fe Lake, also called Lake Santa Fe, and Little Santa Fe Lake, also called Little Lake Santa Fe, are designated outstanding Florida waters by rule. Rule 17-3.041(4)(i), Florida Administrative Code. Lake Santa Fe "is . . . the sixth largest non-eutrophic lake in the State of Florida . . . [and] the last remaining large non-eutrophic lake in Alachua County." (0.367). Recreation is a "beneficial use" of these waters. The Lakes Santa Fe are at an elevation of approximately 140 feet above sea level, and their level varies within a range of four feet. Input The proposed plant is to treat sewage generated by staff, by diners at a 150-seat restaurant, and by inhabitants of 150 lodge or motel rooms, comprising 100 distinct units. On the assumptions that 150 rooms could house 275 persons who would generate 75 gallons of sewage a day for a daily aggregate of 20,625 gallons, and that a 150-seat restaurant would generate 50 gallons of sewage per seat per day, full occupancy is projected to engender 28,125 gallons of sewage per day. This projection is based on unspecified "D.E.R. criteria; (5.35) which the evidence did not show to be unreasonable. Full occupancy is not foreseen except around the Fourth of July, Labor Day and on other special occasions. An annual average flow of between 15 and 20,000 or perhaps as low as 13,000 gallons per day is envisioned. (S.38) The proposed plant is sized at 30,000 gallons per day in order to treat the peak flow forecast and because package plants are designed in 5,000 gallon increments. Sluice-gate valves and baffling are to permit bypassing one or more 5,000 gallon aeration units so plant capacity can be matched to flow. The composition of the sewage would not be unusual for facilities of the kind planned. As far as the evidence showed, there are no plans for a laundry, as such, and "very little laundry" (S.37) is contemplated. The health department would require grease traps to be installed in any restaurant that is built. Gravity would collect sewage introduced into 2,000 feet of pipe connecting lodging, restaurant and a lift station planned (but not yet designed) for construction at a site downhill from the site proposed for the water treatment plant. All sewage reaching the proposed treatment plant would be pumped 3,000 feet from the lift station through a four-inch force main. Influent flow to the treatment plant could be calculated by timing how long the pump was in operation, since it would "pump a relatively constant rate of flow." (S.39) Treatment Wastewater entering the plant would go into aeration units where microorganisms would "convert and dispose of most of the incoming pollutants and organic matter." (S.40) The plant would employ "a bubbler process and not any kind of stirring-type motion . . . [so] there should be very little:; aerosol leaving the plant," (S.42) which is to be encircled by a solid fence. Electric air blowers equipped with mufflers would be the only significant source of noise at the proposed plant, which would ordinarily be unmanned. If one blower failed, the other could run the plant itself. A certified waste water treatment plant operator would be on site a half-hour each week day and for one hour each weekend. SFP has agreed to post a bond to guarantee maintenance of the plant for the six months' operation period a construction permit would authorize. (0.63) The proposed plant would not "create a lot of odor if it's properly maintained." Id. The specifications call for a connection for an emergency portable generator and require that such a generator be "provide[d] for this plant. . . ." (S. 43). The switch to emergency power would not be automatic, however. A settling process is to follow extended aeration, yielding a clear water effluent and sludge. Licensed haulers would truck the sludge elsewhere for disposal. One byproduct of extended aeration is nitrate, which might exceed 12 milligrams per liter of effluent, if not treated, so an anoxic denitrification section has been specified which would reduce nitrate concentrations to below 12 milligrams per liter, possibly to as low as 4 or 5 milligrams per liter. Before leaving the plant, water would be chlorinated with a chlorinator designed to use a powder, calcium hypochlorite, and to provide one half part per million chlorine residual in the effluent entering the percolation ponds. A spare chlorine pump is to be on site. The effluent would meet primary and secondary drinking water standards, would have 20 milligrams or less per liter of biochemical oxygen demand or, if more, no more than ten percent of the influent's biochemical oxygen demand, and total suspended solids would amount to 20 milligrams or less per liter. (5.294- 295). Half the phosphorous entering the plant would become part of the sludge and half would leave in the effluent. Something like ten milligrams per liter of phosphorous would remain in the effluent discharged from the plant into the percolation ponds. (5.202). Although technology for removing more phosphorous is available (S.298, 0.170-171), SFP does not propose to employ it. Allen flocculation treatment followed by filtration could reduce phosphorous in the effluent to .4 milligrams per liter, but this would increase the cost of building the treatment plant by 30 to 40 percent; and operational costs would probably increase, as well, since it would be necessary to dispose of more sludge. (0.170-172). SFP did agree to accept a permit condition requiring it to monitor phosphorous levels in groundwater adjacent to the proposed plant. (0.63). Land Application Three percolation ponds are planned with an aggregate area of 30,000 square feet. At capacity, the plant would be producing a gallon and a half of effluent a day for each square foot of pond bottom in use. The ponds are designed in hopes that any two of them could handle the output of effluent, even with the plant at full capacity, leaving the third free for maintenance. The percolation ponds would stand in the lakes' watershed, in an area "of minimal flooding, (S.30) albeit outside the 100-year flood plain. Santa Fe Lake, including Gator Cove, and Little Santa Fe Lake are fed by groundwater from the surficial aquifer. All effluent not percolating down to levels below the surficial aquifer or entering the atmosphere by evapotranspiration would reach the lake water one way or another sooner or later. If percolation through the soils underneath the percolation ponds can occur at the rate SFP's application assumes, effluent would not travel overland into Lake Santa Fe except under unusually rainy conditions, which would dilute the effluent. Whether the planned percolation ponds would function as intended during ordinary weather conditions was not clear from the evidence, however. In the event the ponds overflowed, which, on SFP's assumptions, could be expected to happen, if peak sewage flaw coincided with weather more severe than a 25-year rainfall, effluent augmented by rainwater would rise to 179.87 NGVD (S.34), then overflow a series of emergency weirs connecting the ponds, flow through an outfall ditch, drain into a depression west of the ponds, enter a grassed roadside ditch, and eventually reach Lake Santa Fe after about a half a mile or so of grass swales. (5.69). Sheet flow and flow through an ungrassed gulley in the direction of Gator Cove (0.154) are other possible routes by which overflowing waters might reach the lake. (0.263). Since the facilities the plant is designed to serve are recreational, wet weather would discourage full use of the facilities and therefore full use of the water treatment system. Effluent traveling over the surface into Gator Cove would wash over vegetation of various kinds. Plants, of course, do take up phosphorous, but they don't do it forever, and if you leave a plant system alone, it will come to a steady state in which there is no net storage of phosphorous in the plant material. (0.166) Whether by sheet flow or by traversing swales, overland flow would reach Gator Cove within hours. Effluent traveling through the surficial aquifer would not reach the lake for at least five years. (S.238-9). It could take as long as 45 years. (0.316). In the course of the effluent's subterranean passage, the soil would take up or adsorb phosphorous until its capacity to do so had been exhausted. In addition, interaction with certain chemicals found in the soil, primarily calcium, precipitates phosphorous dissolved in groundwater. As between adsorption and precipitation, the former is much more significant: "[W]ith a three-meter distance you can expect at least 70 to 80 percent removal of phosphorous just by a a[d] sorption alone." (0.21). Precipitated phosphorous does not return to solution, unless the soil chemistry changes. (0.19) Adsorption, however, is reversible, although not entirely, because of the "hysteresis phenomenon." (0.19) Eventually, a kind of dynamic equilibrium obtains to do with the binding of the phosphorous to soil constituents, binding or precipitation of phosphorous. At some point . all of the binding sites become saturated . [and] the amount of phosphorous leaving, into the lake really, will be equal to the amount of phosphorous going into the the system. When there is no more place to store the phosphorous in the ground, then the output is equal to the input and that is called the steady state. (0.161) Although precipitation of phosphorous would not reach steady state under "conditions that render the phosphorous-containing compound insolu[]ble," (0.168) these conditions were not shown to exist now "much less . . . on into perpetuity." Id. Spring Seep A third possible route by which the effluent might reach lake waters would begin with percolation through the sand, which is to be placed on grade and on top of which the percolation ponds are to be constructed. Underground, the effluent would move along the hydraulic gradient toward the lake unless an impeding geological formation (an aquiclude or aquitard) forced it above ground lakeward of the percolationi ponds. In this event, the effluent would emerge as a man-made spring and complete its trip to Gator Cove, or directly to the lake, overland. The evidence demonstrated that a spring seep of this kind was not unlikely. Relatively impermeable clayey soils occur in the vicinity. A more or less horizontal aquitard lies no deeper than four or five feet below the site proposed for the percolation ponds. Conditions short of an actual outcropping of clayey sand could cause effluent mounding underground to reach the surface. Nor did the evidence show that an actual intersection between horizontal aquitard and sloping ground surface was unlikely. Such a geological impediment in the effluent's path would almost surely give rise to a spring seep between the pond site and the lakes. In the case of the other percolation ponds in this part of the state that do not function properly, the problem is n [U] sually an impermeable layer much too close to the bottom of the pond," (S.179), according to Mr. Frey, manager of DER's Northeast District. Phosphorous in effluent travelling by such a mixed route would be subject to biological uptake as well as adsorption and precipitation, but again a "steady state" would eventually occur. On Dr. Bothcher's assumptions about the conductivity of the clayey sand (or sandy clay) lying underneath the topsoil, the effluent would accumulate as a mound of groundwater atop the clay unit, and seep to the surface in short order; and "after a matter of probably weeks and maybe months, it would be basically of the quality of the water inside of the percolation pond." (0.278). More Phosphorous in Gator Cove The total annual phosphorous load from all existing sources "to the lake" has been estimated at 2,942 kilograms. Assuming an average effluent flow of 17,000 gallons per day from the proposed plant, "the total phosphorous load [from the proposed plant] will be 235 kilograms per annum," (0.16), according to Dr. Pollman, called by SFP as an expert in aquatic chemistry. Even before any steady state condition was reached, 20.75 to 41.5 kilograms of phosphorous, or approximately one percent of the existing total, would reach the lake annually from the proposed plant, on the assumptions stated by Dr. Pollman at 0.22-23 (90 to 95 percent removal of phosphorous in the soils and average daily flow of 30,000 gallons). Santa Fe Lake is more than two miles across and two miles long, and Little Santa Fe Lake, which may be viewed as an arm of Santa Fe Lake, is itself sizeable, with a shoreline exceeding two miles. But Gator Cove is approximately 200 yards by 100 yards with an opening into Santa Fe Lake only some 50 to 75 yards wide. (0.154). On a site visit, Dr. Parks observed "luxuriant growth of submerged plants" (0.154), including hydrilla, in Gator Cove. If a one percent increase in phosphorous were diffused evenly throughout the more than eight square miles Santa Fe Lake covers, there is no reason to believe that it would effect measurable degradation of the quality of the water. Some nutrients are beneficial, and the purpose of classifying a lake is to maintain a healthy, well-balanced population of fish and wildlife. It's hard to see how 1.4 percent increase would lower the ambient quality. But . . . seepage into Gator Cove, which is a much more confined place [100 by 200 yardsj [would make it] quite probable that there would be a lowering of ambient water quality in the site . R] educed dispersion . . . in this cove would allow . . . phosphorous to build up. (0.156) Overland effluent flow to Gator Cove would increase concentrations of phosphorus there, with a consequent increase in the growth of aquatic plants, and the likely degradation of waters in the Cove, unless rapid and regular exchange of lake and cove waters dispersed the phosphorous widely, promptly upon its introduction Except for testimony that wind-driven waves sometimes stir up phosphorous laden sediments on the bottom, the record is silent on the movement of waters within and between Lake Santa Fe and Gator Cove. The record supports no inference that phosporous reaching Gator Cove would be dispersed without causing eutrophic conditions significantly degrading the water in the Cove. Neither does the record support the inference, however, that effluent moving underground into the lakes would enter Gator Cove. On this point, Dr. Bottcher testified: [T]he further away from the lake that you recharge water the further out under a lake that the water will be recharging into the lake; gives it a longer flow . . . it's going to migrate and come up somewhat out into the lake. (0.281-2) Phosphorous in the quantities the treatment plant would produce, if introduced "somewhat out into the lake" would probably not degrade water quality significantly, notwithstanding testimony to the contrary. (0.349, 354). Sands and Clays DER gave notice of its intent to deny SFP's original application because SFP proposed to place the pond bottoms approximately two and a half feet above an observed groundwater table. Placement in such proximity to groundwater raised questions about the capacity of the ground to accept the effluent. In its revised application, SFP proposes to place sand on the existing grade and construct percolation ponds on top of the sand. By elevating the pond bottoms, SFP would increase the distance between the observed groundwater table and pond bottoms to 5.2 feet. (S.256, 257). This perched water table, which is seasonal, is attributable to clayey sand or sandy clay underlying the site proposed for the percolation ponds. Between January 9, 1985, and January 17, 1985, "following a fairly dry antecedent period," (S.229) Douglas F. Smith, the professional consulting engineer SFP retained to prepare the engineering report submitted in support of SFP's permit applications, conducted six soil borings in the vicinity of the site proposed for the plant. One of the borings (TB 5) is in or on the edge of a proposed percolation pond and another (TB 4) is slightly to the north of the proposed pond site. Three (TB 1, 2 and 3) are east of the proposed pond site at distances ranging up to no more than 250 feet. The sixth is west of the proposed site in a natural depression. Mr. Smith conducted a seventh test boring under wetter conditions more than a year later a few feet north of TB 4. Finally, on September 5, 1986, during the interim between hearing days, Mr. Smith used a Shelby tube to obtain a soil sample four to six feet below grade midway between TB 4 and TB 5. 1/ The sites at which samples were taken are at ground elevations ranging from 173 to 178 feet above sea level. From the original borings and by resort to reference works, Mr. Smith reached certain general conclusions: The top four feet or so at the proposed pond site consists of silty sand, 17 percent silt and 83 percent quartz sand. This topsoil lies above a two-foot layer of clayey sand, 20 percent clay, 6 percent silt and 74 percent sand. Below the clayey sand lies a layer some eight feet thick of dense, silty sand, 23 percent silt, 7 percent clay and 70 percent sand, atop a one and one-half foot layer of clayey sand, separating loose, quartz sands going down 40 feet beneath the surface from what is above. These formations "are very heterogeneous, in the sense of the position and occurrence of the clay layers or the sandy layers . . .," (0.230) and all occur within the surficial aquifer. "There are layers of clay within it, and so perched water tables are rather common." (0.225). In March of 1986, the regional water table was some 17 feet down. SFP Exhibit 1B. Below the surficial aquifer lie the Hawthorne formation and, at a depth of 110 feet, the limestone of the Floridan aquifer. The soils above the Hawthorne formation are not consolidated. (S.254, 255). Conductivity Measurements The applicant offered no test results indicating the composition or conductivity of soils lying between the easternmost test boring and Gator Cove, some 1,200 feet distant. No tests were done to determine the conductivity of the deeper layer of clayey sand beneath the site proposed for the ponds. Tests of a sample of the topsoil in TB 7 indicated horizontal permeability of 38.7 feet per day and vertical permeability of six feet per day. On the basis of an earlier test of topsoil in TB 3, "hydraulic conductivity of the surface soils was measured to be 8.2 feet per day. . . ." SFP's Exhibit No. 1B. From this measurement, vertical hydraulic conductivity was conservatively estimated at .82 feet (9.84 inches) per day. Id. The design application rate, 2.41 inches per day, is approximately 25 percent of 9.84 inches per day. Id. The initial test done on a sample of the clayey sand, which lay beneath the topsoil at depths of 3.5 to 5.5 feet, indicated a permeability of 0.0001 feet per day. Thereafter, Mr. Smith did other testing and "made some general assumptions" (S. 235) and concluded that "an area-wide permeability of this clayey sand would be more on the order of 0.0144 feet per day." (S. 234). Still later a test of the sample taken during the hearing recess indicated hydraulic conductivity of 0.11 feet per day. SFP's Exhibit No. 10. The more than thousandfold increase in measured conductivity between the first laboratory analysis and the second is attributable in some degree to the different proportions of fines found in the two samples. The soil conductivity test results depend not only on the composition of the sample, but also on how wet the sample was before testing began. Vertical Conductivity Inferred On March 6, 1986, ground water was observed on the site about two and a half feet below the surface. SFP's expert, Mr. Smith, concluded that it was "essentially a 1.5 foot water table, perched water table over the clay." (0.422). There was, however, groundwater below, as well as above, the clay. On March 12, 1986, the water table at this point had fallen six inches. In the preceding month rainfall of 5.9 inches had been measured in the vicinity, after 5.1 inches had been measured in January of 1986, but in November and December of 1985 "there was a total of 0.6 inches of rainfall." (0.421). Later in the year, notwithstanding typically wet summer weather, no water table was measured at this point. From this Mr. Smith concluded that, once the clayey sand layer is wetted to the point of saturation, conductivity increases dramatically. If that were the case, a more or less steady stream of effluent could serve to keep the clayey sand wetted and percolation at design rates should not be a problem. But Dr. Bottcher, the hydrologist and soil physicist called as a witness for the Association, testified that the six- inch drop over six days could be attributed, in large part, to evapotranspiration. He rejected the hypothesis that the clayey sand's conductivity increased dramatically with saturation, since "the actual water table was observed . about three weeks after the very heavy rainfall had stopped" (0.290) and had probably been present for at least a month; and because the soil survey for Alachua County reports that perched water tables ordinarily persist for two months (0.227) in this type of soil. Certain soils' hydraulic conductivity does diminish with dessication, but such soils usually regain their accustomed conductivity within hours of rewetting. Dr. Bottcher rejected as unrealistically optimistic the assumption SFP's expert made about the conductivity of the clayey sand on grounds that "the conductivity that . . . [SFP] used, if you went out there you couldn't perch a water table for a month." (0.277). In these respects, Dr. Bottcher's testimony at hearing has been credited. In the opinion of the geologist who testified on behalf of the Association, Dr. Randazzo, a minimum of seven or eight additional augur borings in "definitive patterns to the northeast and to the northwest" (0.240) to depths of 15 to 20 feet, with measurements within each augur boring every two feet, are necessary to determine "how permeable the soils are and how fast the waters would move through them." (0.240). This testimony and the testimony of the soil physicist and others to the same general effect have been credited, and Mr. Smith's testimony that no further testing is indicated has been rejected. Wet Ground In the expert opinion of a geologist who testified at hearing, "it is reasonable to assume that saturation conditions of the surficial aquifer in this area can be achieved," (0.238) even without adding effluent from a wastewater treatment plant. The evidence that soils in the vicinity of the site have a limited capacity to percolate .water came not only from engineers and scientists. Charles S. Humphries, the owner of the property 150 feet from the proposed percolation site, "put a fence post line . . . every ten feet, and every ten feet [he] hit clay." (0.372). Three quarters of an inch of rain results in waters standing overnight in neighboring pastures. In parts of the same pastures, rain from a front moving through "will stay for a week or so." (0.373). It is apparent that the area cannot percolate all the rainfall it receives. This is the explanation for the gully leading down toward Gator Cove. Six-feet deep (0.377), "the gully is a result of natural surface runoff." (0.263).
Findings Of Fact Petitioner sat for the Civil/Sanitary Engineer Examination on April 15, 1988. He received a failing grade with an original score of 41 raw points. Since that time, he has been awarded an additional 3 raw points and has a score of 44 raw points. A passing grade is 48 raw points and is, therefore, 4 raw points from passage. Petitioner contests the score given him on three of the problems on the examination. They are problems 120, 122, and 421. He did not have the test booklet he used at the examination available to him at the hearing. Though he recognizes that the grader who assessed his scores was not allowed to look at his test booklet during the scoring process, many of his calculations for problems 120 and 122 were made in it. Problem 120 requires the examinee to compute 6 stations and the coordinates of the 6 points of the two involved curves on a railroad spur line. Petitioner computed the six points to what he considers an acceptable tolerance and had also started to compute the coordinates as required by Requirement (b). His solution page for Requirement (a) of this problem reflects only the six points, of which 5 are marked incorrectly, and bears the grader comment, "show computations." The second page, relating to Requirement (b), on which the first 3 calculations are marked as incorrect, reflects only cursory calculations and bears the grader comment, "Incomplete." Petitioner was awarded a score of "4" for his solution to problem 120. According to the National Council of Engineering Examiners Standard Scoring Plan Outline, the guideline relating to "4", "BORDERLINE UNQUALIFIED", reads: Applicant has failed to demonstrate adequate knowledge in one or more categories. For example, approach may be correct but the solution is unreasonable. Significant constraints may have been overlooked. Solution is unacceptable but marginally so. The scorer's remarks concerning Petitioner's solution state: A solution which fails to demonstrate an adequate understanding of horizontal curve geometry as a result of logic errors, math errors, and failure to complete several parts. According to Petitioner, he used the Civil Engineering Reference Manual in his calculations. He also contends that Requirement (a) is far more important to the problem than is Requirement (b). Once the former is achieved, it is easy to achieve the latter. Admittedly, Petitioner did not complete Requirement (b) and, therefore, does not expect credit for it. However, he contends that having completed Requirement (a) correctly, he should have been awarded more than 40% credit. Petitioner also contends that the use of the term, "Not To Scale" in the test problem was deliberately deceptive which was not necessary to test engineers at this level of achievement. In this case, Petitioner contends the lack of availability of the examination test booklet in which he did many of his calculations hinders him in demonstrating the correctness of his solution. These computations, he contends, would show his computations in Requirement (a) were "close enough" to be graded correctly and without these computations, the scorer would not know if he did them or merely copied the answers. He would not, also, have any way of knowing if Petitioner has knowledge of horizontal curve geometry. Mr. Lippert, a licensed registered engineer testifying on behalf of Petitioner, believed that the answers to the problems to be more important than the computations. In a practical application he may be correct. However, in the instant case Petitioner is a candidate for certification as a Professional Engineer and was being examined on his qualifications for that status. In such a situation, it is not at all unreasonable to expect the candidate to demonstrate his method of arriving at his solution to demonstrate his understanding of the concept sufficiently to indicate his answer was neither copied nor a fluke. Since the candidate is seeking a higher degree of recognition, a requirement that he demonstrate a higher degree of professional skill is not unreasonable. Under the fact situation demonstrated here, the award of a "4" as a grade for Petitioner's solution to this problem is appropriate. In Problem 122, the candidate was required to use and show equations for his calculations of (a), the average maximum and minimum sanitary wastewater flows expected, in gallons per day, for the total complex in issue; (b), the theoretical full flow capacity and velocity with no surcharge; and (c), depth and velocity of flow for the estimated maximum flow rate. The candidate was instructed to conclude, if possible, that the sewer is not overloaded. The problem deals with a troublesome wastewater disposal system for a retirement community of 490 units with a population of 1,475. Here, Petitioner was awarded an a score of "8" and feels he should have received more. As to (a), Petitioner cited in his answer the reference manual he was using, a manual used by many engineers and one accepted in the profession, yet the grader apparently felt that the use of only the title was insufficient. He wanted the author's name, publisher, date of publication, and other salient information. Petitioner felt this was unnecessary in light of the well known status of the book. In (b), the problem calls for 10" UCP pipe. All pipe, depending upon the material from which constructed, has a different diameter. Petitioner's solution was marked at least partially incorrect because he assumed the interior diameter of the pipe as .83' when the problem stated the interior diameter was 10". Petitioner contends that even with that unnecessary calculation based on an incorrect assumption, his solution of 2.295 feet/second velocity was sufficiently close to the grader's solution of 2.35 feet/second to be marked correct. Similarly, Petitioner contends his velocity in (c) was within a "tolerable" margin and that his conclusions is "OK". While the grader considered his method in this section as "OK", he marked the calculation almost entirely wrong. This may be related to the formula used by Petitioner in (b) which, he admits, is wrong. He contends he must have brought the wrong number over from his calculations which he accomplished in his test booklet. This booklet is not now available, but, in any case, would not have been seen by the scorer. Petitioner also claims that the gallons per capita per day figure of 100 is the standard "everyone uses" to calculate problems involving sewage. Here, because he was taking an examination, he used a figure of 112.5 gallons per day, a compromise between 100 and 125, which he took from the reference manual without citing page number from which taken. Consequently, he contends the grader's comment that his figure is too high is in error but even if it was too high, he ran the calculations correctly and should be given full credit. It is his position that in a case like this, error on this high side, which would give greater capacity, is better than being short. Being correct would be even better, and Petitioner's solutions was not correct. In the scoring plan outline for this problem, an "8" is described as: QUALIFIED; All categories satisfied, errors attributable to misread tables or calculating devices. Errors would be corrected by routine checking, Results reasonable though not correct. and a "9" is described as: QUALIFIED: All categories satisfied, correct solutions but excessively conservative in choice of working values; or presentation lacking in completeness of equations, diagrams, orderly steps in solution, etc. The scorer's comments were: CQ. Fundamentals are correct. Solutions are basically correct and complete but contain math, unit, or tolerance errors making answers unacceptable; or the record is different, or in combination. Here, Petitioner contends that his ultimate solution, only .05 feet/second off in velocity is so close that the error is insignificant. It is close but the difference between an "8" and a "9" lies in the correctness of the ultimate solutions. "Close" is not "correct" and Petitioner's errors are not attributable to misread equations or devices but to his own improper assumptions. Because his calculations were done in a test booklet which is not now available it cannot be determined where the error originates which caused (c) to be marked as it was. Under the circumstances shown here, the score of "8" awarded is not inappropriate. Problem 421 calls for the candidate to find the required volume in cubic feet of on site storage so that post development flows on the parcel of land in question do not exceed the pre-development flows to the existing stream for the 25 year frequency rainfall. Petitioner determined the pre and post development numbers correctly but did the retention area in the old fashioned way resulting in his solution equating to 1/2 of the correct solution. The grader indicated that Petitioner's "procedures [sic] [were] in error here." Petitioner has a one page solution to the problem and got credit for his answer of "4.22" to the first stage of the problem as well as his answer to the second part. He admits, however, that his third step was wrong and that threw the problem answer off. He contends, however, that he was undergraded when awarded a "4" and while he admits to not deserving a "6", feels he should have received a "5". Grades for this problem were awarded on a 2-4-6-8-10 point scale. A "5" was not an authorized score. The scoring plan for this problem describes a "4" as: BORDERLINE UNQUALIFIED; Applicant has failed to demonstrate adequate knowledge in one or more categories. For example, approach may be correct but the solution is unreasonable. Significant constraints may have been overlooked. Solution is unacceptable but marginally so. A grade of "6" is described as: MINIMALLY QUALIFIED: All categories satisfied at a minimally adequate level. Here the scorer indicated: Pre and post calculation OK. An attempt at detention calculation made but no significant progress toward conclusion. Fails to demonstrate knowledge necessary to calculate detention as existing. Detention calculations fail to demonstrate knowledge of hydrograph [sic] nature of storage calculations. Only one data point obtained. The comments of the grader on the Petitioner's answer sheet clearly indicate that the answer given was incorrect and that the Petitioner failed to demonstrate adequate knowledge of the procedures in issue. Since there is no provision made to award any grade between "4" and "6", and since Petitioner's answer clearly, and by his own admission, does not qualify for a "6", the awarded score of "4" is appropriate. Based on the above, it is found that Petitioner has failed to demonstrate that the scores given him on the problems in issue were incorrect, unsupported, or inappropriate.
Recommendation Based on the foregoing Findings of Fact and conclusions of Law, it is, therefore: RECOMMENDED that a Final Order be entered affirming the score awarded to Petitioner on questions 120, 122, and 421, respectively, of the Civil/Sanitary Engineer Examination administered to him on April 15, 1988. RECOMMENDED this 4th day of April, 1989 at Tallahassee, Florida. ARNOLD H. POLLOCK Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 4th day of April, 1989. COPIES FURNISHED: Leonard A. Smally Longboat Key, Incorporated 501 Bay Isles Road Longboat Key, Florida 33548 H. Reynolds Sampson, Esquire Department of Professional Regulation 130 North Monroe Street Tallahassee, Florida 32399-0750 Allen R. Smith, Jr. Executive Director Board of Professional Engineers 130 North Monroe Street Tallahassee, Florida 32399-0750
The Issue Whether Petitioner's application to increaseits water and sewer rates to its customers in Seminole County should be granted.
Findings Of Fact Based upon the evidence presented at hearing, including consideration of the demeanor and credibility of witnesses, the following facts are determined: I. Application and Retroactive Implementation of Interim Rate Increase By its application, the UTILITY, seeks to increase its water revenue to $158,890, and its sewer revenue to $83,830, by increasing service rates to its customers in Winter Springs, Seminole County, Florida. During the test year ending September 30, 1979, the UTILITY suffered combined losses from its water and sewer operation of $420,692. This is the first rate increase requested by the UTILITY since its inception in 1973. On April 24, 1980, the COMMISSION issued Order No. 9344 which suspended the UTILITY's proposed rate increases but granted it an interim increase under bond. The UTILITY was directed to file revised tariff pages containing residential and general service rates which would allow it to earn total annual gross revenue for water service of $139,277 and total annual gross revenues for sewer service of $83,830. The Order also stated: ". . .that the rate increase contained herein shall become effective for all bills on or after thirty (30) days after the date of this order. . . (Testimony of Blair, Fabelo; P.E. 1, 2, R.E. 3.) The UTILITY implemented the interim rate increase, within its normal billing cycle, on the June 2, 1980, water and sewer service bills. However, these bills were based on meter readings taken on May 10, 1980, for service provided from April 10 to May 10, 1980. Thus, the UTILITY increased its rates to its customers fourteen (14) days prior to April 24, 1980, the effective date of the COMMISSION's order authorizing such increase. The UTILITY's action was, however, taken in good faith, and based on a COMMISSION staff member's representation that the interim rates could properly be included in the June billing. The amount of revenues received from the interim rate increase and collected prior to the effective date of Order No. 9344 is approximately $8,700. (Testimony of Fabelo, Blair; P.E. 1, R.E. 3.) However innocently imposed, the UTILITY's action constitutes improper retroactive ratemaking. The UTILITY should refund to customers of record during the period in question their pro-rata share of revenues collected by the retroactive rate increase. The amount of each refund will depend on the amount of water consumed and paid for during the period of retroactive rates-- approximately April 10 through April 24, 1980. The UTILITY may minimize costs by distributing the refunds as separately itemized credits on its regular service bills. (Testimony of Fabelo; R.E. 3.) II. Factors Relevant to Ratemaking In determining whether a rate increase is justified, the COMMISSION must consider several factors, including (1) quality of service, (2) rate base, (3) a fair rate of return on the utility's investment, and (4) operation and maintenance expenses; each is separately addressed below. (Testimony of Asmus, Lowe.) III. Quality of Service During 1979, several customers of the UTILITY experienced occasional low water pressure in their homes. It is likely that these water pressure problems were caused by fluctuating amounts of electricity supplied the UTILITY by Florida Power Corporation. The UTILITY has recently installed an electronic control panel and Florida Power has installed a direct transmission line to the UTILITY in order to prevent this from reoccurring in the future. Several times during 1980, the UTILITY had its water service interrupted due to a cable-TV company cutting its water lines while laying cable; repairs, however, were quickly made. Few customer complaints have been made to regulatory agencies concerning the quality of the water and sewer service provided by the UTILITY: one complaint on water service was made to the Florida Department of Environmental Regulation in 1979, and subsequently determined to he unfounded; no complaints were made to the Department concerning sewer service. Although several customers testified that the water sometimes caused irritation, tests show that the water meets Florida and federal safe drinking water standards. The sewage treatment provided by the UTILITY also complies with state and federal requirements. The water and sewer service is, therefore, determined to he of satisfactory quality. (Testimony of Blair, Bostwick, Customers.) IV. Rate Base A regulated utility is entitled to an opportunity to earn a fair rate of return on its investment in plants and facilities which are used and useful in providing water and sewer service to the public. The utility investment is referred to as "rate base". Here, the average water and sewer rate base for the UTILITY's test year ending September 30, 1979, is calculated as follows: AVERAGE RATE BASE WATER SEWER Utility Plant in Service $847,287 2/ $1,218,363 Utility Plant held for Future Use (271,153) (608,476) Accumulated Depreciation (82,099) (97,306) Contributions in Aid of Construction (183,749) 3/ (178,456) 3/ (CIAC)--Net Allowance for Working Capital 11,983 4/ 11,851 TOTAL RATE BASE $322,627 $ 354,433 (Testimony of Blair, Asmus, Heiker, Lowe; Respondent's Proposed Findings of Fact and Conclusions of Law, Pg. 3; P.E. 4, R.E. 2.) V. Rate of Return A fair rate of return is the percentage factor that, when multiplied by the rate base, produces revenue that will pay the costs of capital--interest on debt to lenders, and return on equity to stockholders. In this case, after considering the UTILITY's capital structure and that of its parent company, Gulfstream Land and Development Corporation, the parties stipulated that a fair rate of return is determined to be 12.40 percent, and is calculated: COST OF CAPITAL Test Year Ending September 30, 1979 COMPONENT RATIO COST RATE WEIGHTED COST Common Equity 33.3 percent 15.50 percent 5.16 percent Long-Term Debt 53.0 13.67 7.24 Cost-Free Capital 13.7 -0- -0- TOTAL 100.0 percent Midpoint 12.40 percent (Testimony of Lowe, Asmus; Joint Stipulation of Parties, Joint Exhibit 2; P.E. 10.) VI. Operations and Maintenance Expenses The adjusted operation and maintenance expenses, including depreciation and taxes, of the UTILITY for the test year are set out below: CONSTRUCTED STATEMENT OF OPERATIONS Test Year Ending September 30, 1979 WATER SEWER Operating Revenues: $160,531 5/ $83,830 5/ Operating Expenses: Operation 84,275 6/ 90,480 7/ Maintenance 11,586 4,324 Depreciation 12,219 16,014 Taxes Other than Income Tax 7,330 8/ 4,581 8/ Provision for Income Taxes 9,786 9/ -0- TOTAL EXPENSES $125,196 $115,399 Operating Income (Loss): $35,334 ($31,569) (Testimony of Asmus, Lowe; COMMISSION's Proposed Findings of Fact; P.E. 10, R.E. 1.) The depreciation expense indicated above includes an adjustment of $2,015 (water) and $6,788 (sewer) proposed by the UTILITY as a result of a rate base adjustment which properly reclassified plant balances to their proper month. The UTILITY had inadvertently posted plant additions to a year-end entry, rather than to the months the additions were completed. At hearing, the COMMISSION agreed to the rate base adjustment and agreed, "in principle", to the UTILITY's proposed correlative adjustment to depreciation expense. However, in its posthearing Proposed Findings of Fact, the COMMISSION's counsel disputed the UTILITY's adjustment, and offered a substitute adjustment: ". . .However, in actual calculation, the. . . [COMMISSION] disagrees. The utility's adjustment does not consider used and useful as applied to the expense. In addition, the. . . [UTILITY's] adjustment includes expense on pro-forma plant. The. . .[COMMISSION's] calculation considers these adjustments. (Pg. 4, Paragraph D.) Because factual issues are difficult to resolve by posthearing submittal, evidence should be presented at hearing, where it is subject to cross- examination and rebuttal. At hearing, the COMMISSION did not object to the depreciation expense adjustment presented by the UTILITY; neither did it cross- examine to elicit the method used for its calculation nor move for a continuance based on surprise or inability to adequately verify the UTILITY's figures. Rather, it chose to defer examination of and rebuttal to the UTILITY's evidence until after the conclusion of hearing. Under such circumstances, the COMMISSION's posthearing submittal is insufficient to overcome the competent evidence adduced by the UTILITY. (Testimony of Asmus, Lowe; Respondent's Proposed Findings of Fact, Pg. 3, 4; P.E. 10.) VII. Tariff Modifications By its application, the UTILITY also requested COMMISSION approval of proposed water and sewer tariff modifications. By stipulation of the parties, the following modifications to the UTILITY's tariffs are warranted: The initial connection charge and reconnect charge on delinquent accounts is TEN AND NO/100 DOLLARS ($10.00) during working hours and FIFTEEN AND NO/100 DOLLARS ($15.00) after working hours. Customer deposit shall be FIFTY AND NO/100 DOLLARS ($50.00) for both water and sewer service and TWENTY-FIVE AND NO/100 DOLLARS ($25.00) for either water service alone or sewer service alone. Customer deposits may be increased to the foregoing sums on delinquent accounts after giving thirty (30) days' written notice, which notice shall be separate and apart from any bill for service. (Testimony of Fabelo; Prehearing Stipulation; P.E. 1, R.E. 3.) VIII. Rates The UTILITY seeks, and the COMMISSION recommends approval of these specific rates and charges: WATER RATES RESIDENTIAL RATES Base facility charge per month based on meter sizes for zero consumption. METER SIZE 5/8" x 3/4" $ 5.00 1" 12.50 1-1/2" 25.00 2" 40.00 Gallonage Charge-Per 1,000 gallons .75 General Service Base Facility charge per month based on meter sizes for zero consumption. METER SIZE 5/8" x 3/4" $ 5.00 1" 12.50 1-1/2" 25.00 2" 40.00 3" 80.00 4" 125.00 Gallonage Charge-Per 1,000 gallons .75 SEWER RATES RESIDENTIAL RATES Base facility charge per month $ 5.00 First 10,000 gallons-Per 1,000 gallons .75 Over 10,000 gallons-Monthly flat rate 12.50 General Service Base facility charge per month based on motor size for zero consumption. METER SIZE 5/8" x 3/4" 5.00 1" 12.50 1-1/2" 25.00 2" 40.00 3" 80.00 4" 125.00 Gallonage Charge-Per 1,000 gallons .75 These requested rates are structured using a base facility charge (BFC) rate design. This rate design requires customers to pay: (1) their pro-rata share of the UTILITY's fixed facility costs, and (2) a charge for pumping, treating, and delivering the actual water gallonage consumed, by 1,000 gallon increments; it equally distributes the costs of providing utility service and the COMMISSION encourages its use. (Testimony of Fabelo; Respondent's Proposed Findings of Fact; P.E. 1, P.E. 3.) These rates proposed by the UTILITY will generate water revenues of $158,890 and sewer revenues of $58,865, which provide a rate of return on water rate base of 10.52 percent, and a zero return on sewer rate base. Combined water and sewer operations will earn a rate of return of .35 percent, whereas a fair rate of return in this case has been stipulated to be 12.40 percent. Although the proposed rates will not provide the UTILITY with a fair return, the quality of its present water and sewer service will not suffer, or be decreased in any manner. (Testimony of Blair, Asmus; P.E. 10.)
Conclusions The water and sewer rate increases and tariff modifications requested by Petitioner are just, reasonable, not unjustly discriminatory, and should be granted. Although the rates will provide less than a fair return, it has not been shown that Petitioner's service will suffer. Petitioner's collection of interim rate increases from its customers prior to the effective date of Order No. 9344 violates Section 367.081(1), Florida Statutes (1979); all revenue so collected should be refunded to its customers. Revised tariff pages should be filed, a letter explaining the rate increases should be sent to Petitioner's customers, and the Petitioner's letter of credit, returned.
Recommendation Based on the foregoing findings of fact and conclusions of law, it is RECOMMENDED: That the UTILITY's application for approval of the rates specified in Paragraph 11, infra, be granted; That the UTILITY be required to submit, for COMMISSION approval, revised tariff pages containing the new rates and rate structure; That the UTILITY be required to send to its customers a letter, approved in form by the COMMISSION, explaining the rate increases and reasons therefore; That the irrevocable letter of intent drawn on the Pan American Bank, dated May 3, 1980, be returned to the UTILITY and the bank releaned thereafter; That the tariff modifications contained in Paragraph 10, infra, be approved; and That the UTILITY be required to expeditiously refund to its customers the interim rate increases collected prior to the effective date of PSC Order No. 9344. DONE AND ENTERED this 24th day of November, 1980, in Tallahassee, Florida. R. L. CALEEN, JR. Hearing Officer Division of Administrative Hearings Room 101, Collins Building Tallahassee, Florida 32301 (904) 488-9675
Findings Of Fact At all times pertinent to the allegations herein, the Petitioner, Pinellas County Construction Licensing Board, (Board), was the Pinellas County agency responsible for the certification and regulation of construction specialties. Respondent was certified by the Board as an irrigation systems specialty contractor under license C-5997 in force at the time. Respondent was the qualifying contractor for Sun City Lawn Irrigation. On or about May 17, 1994, Respondent contracted with William J. Schneider, who resided at 5661 25th Avenue North in St. Petersburg, to install a lawn irrigation system in Mr. Schneider's front lawn. The automatic system was to incorporate 2 zones and was, according to the contract and the testimony of Mr. Schneider, to be connected to Schneider's then existing 1/2 horsepower electric pump which drew water from several wells on his property. Mr. Schneider claims there are four wells. No evidence was introduced to contradict that. On the day the system was installed, Mr. Schneider was not at home. Respondent's employees performed a test of the water capacity on Mr. Schneider's property. At first, the wells produced 10 gpm, which was adequate for the system, but after a few minutes of drawdown, they found that the wells were producing only 4 gpm, along with some air. At that time Mr. Freestone, Respondent's sales manager, spoke with Mrs. Schneider about the situation, advising her there were two options open. One was to install a larger pump and the second was to connect the system to the city water supply. Mrs. Schneider returned to the house, presumably to call Mr. Schneider to get his decision on the matter. He claims she did not reach him. Respondent claims that she thereafter returned with directions to install a water line for connection to the city system. This is completely contrary to what Mr. Schneider had wanted and to what is included in the contract. Mr. Schneider claims he did not want to connect to city water because of the added expense of doing so, and he claims he made this very clear to Respondent's employees at the beginning and at all times thereafter. In any case, the system was installed and was, somehow, connected to the city water system near the place where the water line enters the house. In addition, no backflow preventer was installed to insure against contamination getting into the water system as is required by the building code. Most, if not all, the work on this project was completed by Respondent's son and employee, Scott, who was not present at the hearing. Respondent attempted to introduce an unsworn written statement by Scott Bosworth, but it was not accepted. Scott advised Mr. Schneider, when he returned from work that day, that they had been unable to use his pump and wells. Nonetheless, Mr. Schneider paid Respondent in full for the work for which he had contracted, except for a supplemental charge in the amount of $190.95 for the tie in to the city water and the valves and other items connected therewith. Mr. Schneider claims that he made several calls to Respondent's office in an effort to correct the situation but was unable to reach anyone who could give him satisfaction. However, the evidence indicates that on at least one occasion, Mr. Schneider got through and was called back by Mr. Freestone with whom he discussed the situation and the additional charges. He was subsequently advised by counsel that he did not have to pay the additional sum and did not do so. Some time thereafter, Mr. Schneider was advised by the city that he would be fined because of the illegal installation. He then contacted another irrigation company, run by Mr. Williams, who examined the system and determined that the irrigation system installed by Respondent had been connected to the city water system and that no backflow preventer had been installed. A check with the city's building department revealed that no permit had been procured for this installation. Respondent's license to install irrigation systems does not include authority to connect that system with the public water system. That procedure must be done by a licensed plumber. Respondent and Mr. Freestone, the only individuals in the company who had the authority to arrange with a plumber to make the actual hook up to the city system, both deny that any arrangement was made by them to have the system connected to the city water system. Mr. Schneider arrived home on the day in question to find only Respondent's son, Scott, at work on the project. Scott indicated it would be necessary to move two bushes near the house to facilitate connection of the system with the water supply. Mr. Schneider contracted with Scott to move the bushes and remove them from the premises. Scott moved them but failed to remove them. In light of the fact that Scott was working on the system at the time Mr. Schneider arrived home, and the system was found to be connected to the city system thereafter without anyone else touching it, it must be concluded that the connection was made him. Respondent admits he did not come to the property in question while the system was being installed.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is, therefore: RECOMMENDED that a Final Order be issued by the Board suspending the license of the Respondent for a period of six months with provision for withholding execution of the suspension for a period of one year conditioned upon such criteria as may be deemed appropriate by the Board. RECOMMENDED this 31st day of March, 1995, in Tallahassee, Florida. ARNOLD H. POLLOCK Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 31st day of March, 1995. COPIES FURNISHED: William J. Owens Executive Director Pinellas County Construction Licensing Board 11701 Belcher Road Largo, Florida 34643-5116 Larry J. Bosworth 8901 14th Street North St. Petersburg, Florida 33716
Findings Of Fact The Petitioner is a utility regulated by the Commission that is in the business of acquiring and operating water and sewer systems in Florida, principally in Central Florida. It now operates 39 systems, of which at least 30 water systems and 5 sewer systems are located in Orange, Lake and Seminole counties. In this case, the utility serves 547 water customers and 528 sewer customers in a subdivision known as University Shores. Southern commenced operating these systems in June, 1978, purchased them from University Shores Utilities, Inc. in September, 1978, and applied to the Commission for a transfer, which application was approved November 1, 1978, by Order 8550. The rates for service by these systems were granted by Order 6822 on August 6, 1975. Notwithstanding customer complaints of the quality of the water service (smell, taste, excess chlorine, sediment and no-noticed interruptions), the systems are in compliance with governmental standards. No customer complaints had been made to regulatory agencies, and the utility had handled only five for 1979 and to date in 1980. Due to a large increase in number of customers, a year end, rather than average, test year is appropriate; and the facilities are used and useful. Petitioner's rate bases are computed as follows: WATER SEWER Year end test year plant $526,737 $957,176 Construction Work in Progress 2,500 -0- Acquisition adjustment (net of amortization) (41,490) (78,300) Accumulated depreciation (67,172) (128,393) CIAC (net of amortization) (186,470) (489,438) Working Capital 5,476 6,386 Income tax lag (2,951) (4,225) $236,630 $263,214 The following capital structure and rate of return is that agreed to by the Petitioner and Respondent prior to intervention by the customers: WEIGHTED TYPE AMOUNT RATIO COST COST Common Stock $1,882,055 60.44 14.0 percent 8.46 Long Term Debt 1,037,372 33.31 8.89 2.96 Cost Free 194,768 6.25 0 0 TOTAL $3,114,195 100.00 11.42 percent The above rate bases and rate of return provide an authorized constructed net operating income from water service of $22,523 and from sewer service of $30,059. Although the return on water service is only 9.52, the revenue is limited to that in the application. This results in the following constructed statement of operations for year ended June 30, 1979: WATER SEWER Operating Revenue $94,550 $117,814 Operating Expense Operation 41,853 49,838 Maintenance 1,950 1,244 Depreciation 5,964 7,451 Amortization (860) (1,598) Taxes, other than income 8,363 9,726 Income taxes 14,757 21,124 TOTAL $ 72,027 $ 87,785 Net Operating Income $ 22,523 $ 30,059 Rate Base $236,630 $263,214 Rate of Return 9.52 11.42 percent It is noted that the above revenue requirement is more than the interim authorized revenue of $68,841 for water and $81,720 for sewer. The staff proposed that the rate structure should be changed from the present block structure for water and flat rate for sewer to a base facility charge for both water and sewer. This concept is appropriate since it serves to conserve water and insures that each customer pays his fair share of the costs of providing service. No evidence opposing this type rate structure was presented.
Recommendation Based on the foregoing findings of fact and conclusions of law, it is RECOMMENDED that the application of Southern States Utilities, Inc., University Shores Division, be granted and that the utility he authorized to file new tariffs to be approved by the Florida Public Service Commission that would have provided for the test year ending June 30, 1979 annual gross revenues of $94,550 for water service and $117,814 for sewer service. It is further RECOMMENDED that the refund bend be returned to utility. DONE and ORDERED this 25th day of November, 1980, in Tallahassee, Florida. H. E. SMITHERS Hearing Officer Division of Administrative Hearings 101 Collins Building Tallahassee, Florida 32301 (904) 488-9675 COPIES FURNISHED: R. M. C. Rose, Esquire 1020 East Lafayette Street Tallahassee, Florida 32301 William H. Harrold, Esquire Florida Public Service Commission 101 East Gaines Street - Fletcher Bldg. Tallahassee, Florida 32301 Jack Shreve, Esquire Stephen C. Burgess, Esquire Benjamin H. Dickens, Jr., Esquire Office of Public Counsel Holland Building - Room 4 Tallahassee, Florida 32301 Steve Tribble, Clerk Florida Public Service Commission 101 East Gaines Street - Fletcher Bldg. Tallahassee, Florida 32301 Robert T. Mann, Chairman Public Service Commission 101 East Gaines Street - Fletcher Bldg. Tallahassee, Florida 32301
The Issue The issue to be determined in this case is whether the City of Tarpon Springs (“City”) is entitled to a industrial wastewater facility permit for its proposed discharge of demineralization concentrate into the Gulf of Mexico adjacent to Pasco County, Florida.
Findings Of Fact The Parties Henry Ross is a resident of Tarpon Springs. In his petition for hearing, he alleges that he is a recreational fisherman and a "consumer of fish taken from the area" where the proposed wastewater discharge would occur. He presented no evidence at the final hearing to prove these allegations. Neither the City or the Department stipulated to facts that would establish Ross's standing. The City of Tarpon Springs is a municipality in Pinellas County and the applicant for the industrial wastewater permit that is challenged by Ross. The Department is the agency charged by law with the duty, and granted the power, to regulate the discharge of pollutants into waters of the State. The Proposed Permit - General Due to the cost of obtaining potable water from Pinellas County Utilities, the City decided to look for another source of drinking water. In February 2004, an alternative water supply plan was developed by the City’s Office of Public Services which analyzed potable water supply options. It determined that the withdrawal and treatment of brackish groundwater represented the best option for the City. The proposed permit authorizes the City to discharge industrial wastewater into waters of the State. The wastewater is demineralization concentrate, which is produced when RO technology is used to remove salts from brackish water to convert it to potable water. The wastewater would be produced in conjunction with the operation of a not-yet-constructed WTP that would supply public drinking water to the residents of the City. The City must also obtain a consumptive use permit from the Southwest Florida Water Management District for the proposed withdrawal of groundwater. Whether the Town is entitled to a consumptive use permit is not at issue in this proceeding. The industrial wastewater permit would authorize a maximum daily discharge of 2.79 million gallons per day ("mgd") of RO concentrate. The initial operation of the WTP, however, is expected to discharge 1.05 mgd. The RO concentrate would be transported via a force main from the WTP in the City to an outfall in Pasco County. The outfall would discharge the wastewater into a canal which is already being used for the discharge of cooling water from Progress Energy Florida, Inc.’s Anclote Power Generation Facility. The outfall would be 50 feet north of the point in the canal where Progress Energy is required to demonstrate compliance with its own permitting requirements, so as not to interfere with Progress Energy's ability to demonstrate compliance. There is a floating barrier in the channel north of the proposed point of discharge, and a fence along the side of the canal, to prevent swimmers, boaters, and persons on foot from getting near the Progress Energy power plant. The floating barrier and fence would also prevent swimmers, boaters, or pedestrians from reaching the proposed discharge outfall and the area of the canal where the discharge will initially mix. After being discharged into the canal, the wastewater would become diluted and flow northward, out of the canal and into the open waters of the Gulf. The prevailing currents in area would most often force the wastewater south toward Pinellas County and the mouth of the Anclote River. To determine the characteristics of the wastewater, the City's consultants collected water from the three proposed well fields for the new WTP and ran the water through a small, pilot-scale RO unit to generate an RO concentrate that is representative of the proposed RO discharge. It was determined that eight constituents of the wastewater would likely be present in concentrations that would exceed applicable state water quality standards: aluminum, copper, iron, gross alpha (a radioactivity measurement), total radium, selenium, nickel, and zinc. The Mixing Zones The Department may authorize mixing zones in which a wastewater discharge is allowed to mix with the receiving waters. See Fla. Admin. Code R. 62-4.244. Within the mixing zone, certain minimum water quality criteria must be met. At the outer boundary of the mixing zone, the applicable state water quality standards must be met. In this case, the water quality standards for Class III marine waters are applicable. The City's consultants analyzed the wastewater, receiving waters, and other factors and used an analytical model to simulate a number of mixing scenarios. In cooperation with Department staff, a separate mixing zone was established for each of the eight constituents that are not expected to meet water quality standards at the outfall. The largest mixing zone, for copper, is 1,483.9 square meters. The smallest mixing zone, for nickel, is 0.7 square meters. The mixing zones are conservatively large to assure sufficient mixing. Under most conditions, the mixing is expected to occur in a smaller area. Toxicity Analysis Among the minimum criteria that must be met within a mixing zone is the requirement to avoid conditions that are acutely toxic. See Fla. Admin Code R. 62-302.500(1)(a). A wastewater discharge is tested for potential acute toxicity by exposing test organisms to the undiluted discharge and determining whether more than 50 percent of the organisms die within a specified time period. The test organisms, mysid shrimp and silverside minnow, are sensitive species. Therefore, when a discharge is not acutely toxic to these organisms, it can be reasonably presumed that the discharge would not harm the native organisms in the receiving waters. The acute toxicity test for the proposed RO concentrate indicated zero toxicity. The Department requested that the City also analyze the potential chronic toxicity of the proposed discharge. A wastewater discharge shows chronic toxicity if exposure to the discharge adversely affects the growth and weight of the test organisms. The tests performed on the representative discharge showed that the proposed discharge of RO concentrate would not create chronic toxicity in the mixing zones. Petitioner’s expert witness, Ann Ney, did not review the toxicity analyses or other water quality data that were submitted to the Department by the City. However, she expressed a general concern about a salty discharge that could create stratification in the canal with higher salinity at the bottom of the canal that might be hypoxic (little or no dissolved oxygen). The more persuasive evidence shows that salinity stratification, or a hypoxic condition, is unlikely to occur. The proposed permit requires the City to conduct quarterly chronic toxicity tests. The permit also requires the City to periodically test the water and sediments for any unexpected cumulative effects of the discharge. Evaluation of Disposal Options Florida Administrative Code Rule 62-620.625(6) requires that an applicant for a permit to discharge demineralization concentrate must investigate disposal options potentially available in the project area. The City evaluated blending the discharge concentrate with the City's re-use water irrigation program or with the City’s domestic wastewater discharge into the Anclote River. The RO concentrate was too salty for irrigation use and there was an inadequate volume of domestic wastewater available throughout the year. In addition, the Anclote River is an Outstanding Florida Water and, therefore, is afforded the highest water quality protection under Department rules. See Fla. Admin. Code R. 62-4.242(2). The City also looked at underground injection but that was economically unreasonable and there was concern about upward migration of the discharge. It was economically unreasonable to discharge the concentrate farther out into the Gulf. Anti-degradation Analysis For a proposed new discharge, a permit applicant must demonstrate that the use of another discharge location, land application, or recycling that would avoid the degradation of water quality is not economically and technologically reasonable. See Fla. Admin. Code R. 62-4.242(1)(d). As discussed above, the City investigated other disposal options, but they were not economically or technologically reasonable. An applicant for a permit authorizing a new discharge must demonstrate that any degradation is desirable under federal standards and under circumstances that are clearly in the public interest. See Fla. Admin. Code R. 62-302.300(17). In determining whether a proposed discharge is desirable under federal standards and under circumstances that are clearly in the public interest, the Department is required by Rule 62-4.242(1)(b) to consider the following factors: Whether the proposed project is important to and is beneficial to public health, safety or welfare (taking into account the policies set forth in Rule 62-302.300, F.A.C., and, if applicable, Rule 62-302.700, F.A.C.); and Whether the proposed discharge will adversely affect conservation of fish and wildlife, including endangered or threatened species, or their habitats; and Whether the proposed discharge will adversely affect the fishing or water-based recreational values or marine productivity in the vicinity of the proposed discharge; and Whether the proposed discharge is consistent with any applicable Surface Water Improvement and Management Plan that has been adopted by a Water Management District and approved by the Department. The proposed project is important to and is beneficial to public health, safety or welfare because it would provide drinking water for the public. In addition, the treatment and use of brackish groundwater converts otherwise unusable water into a valuable resource. The use of brackish water avoids the use of water in the surficial aquifer that is used by natural systems, such as wetlands. The Florida Legislature has found that the demineralization of brackish water is in the public interest, as expressed in Section 403.0882, Florida Statutes (2010): The legislature finds and declares that it is in the public interest to conserve and protect water resources, provide adequate supplies and provide for natural systems, and promote brackish water demineralization as an alternative to withdrawals of freshwater groundwater and surface water by removing institutional barriers to demineralization and, through research, including demonstration projects, to advance water and water by-product treatment technology, sound waste by-product disposal methods, and regional solutions to water resources issues. The proposed discharge would not adversely affect conservation of fish and wildlife. Because the discharge is not toxic to sensitive test organisms provides reasonable assurance that the native fish and other aquatic life would not be adversely affected by the discharge. The only identified threatened or endangered species that frequents the canal waters is the endangered Florida Manatee. Manatees use the canal because of its relatively warm waters. Manatees come to the surface to breathe and they drink fresh water. There is no reason to expect that a manatee moving through the mixing zones would be adversely affected by the RO concentrate. The Florida Fish and Wildlife Conservation Commission, which has primary responsibility for the protection of endangered and threatened species, did not object to the proposed permit. Manatees and many other aquatic species use seagrasses as food or habitat. There are no seagrasses in the area of the canal into which the RO concentrate would be discharged, but there are dense seagrass beds nearby. The proposed discharge would have no effect on the seagrasses in the area. The proposed discharge would not adversely affect fishing or water-based recreational values or marine productivity in the vicinity of the proposed discharge. Because the proposed discharge is non-toxic and would meet Class III water quality standards before reaching the closest areas where humans have access to the canal and Gulf waters, there is no reason to believe that the proposed discharge would be harmful to humans. The proposed discharge would not adversely affect recreational activities, such as swimming, boating, or fishing. Petitioner presented the testimony of two fishermen about fishing resources and water flow in the area, but no evidence was presented to show how the proposed discharge would reduce marine productivity. Petitioner contends that the proposed discharge would adversely affect the Pinellas County Aquatic Preserve. However, the aquatic preserve is two miles away. The proposed discharge would probably be undetectable at that distance. It would have no effect on the waters or other resources of the aquatic preserve. With regard to the requirement that the proposed discharge be consistent with an adopted and approved Surface Water Improvement and Management Plan for the area, there is no such plan.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law it is RECOMMENDED that the Department issue a final order determining that Petitioner lacks standing, and approving the issuance of the industrial wastewater facility permit to the City. DONE AND ENTERED this 16th day of December, 2010, in Tallahassee, Leon County, Florida. S BRAM D. E. CANTER Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 16th day of December, 2010. COPIES FURNISHED: Nona R. Schaffner, Esquire Department of Environmental Protection 3900 Commonwealth Boulevard, Mail Station 35 Tallahassee, Florida 32399-3000 Thomas J. Trask, Esquire Frazer, Hubbard, Brandt & Trask, LLP 595 Main Street Dunedin, Florida 34698 Henry Ross 1020 South Florida Avenue Tarpon Springs, Florida 34689 Lea Crandall, Agency Clerk Department of Environmental Protection Douglas Building, Mail Station 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 Tom Beason, General Counsel Department of Environmental Protection Douglas Building, Mail Station 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 Mimi Drew, Secretary Department of Environmental Protection Douglas Building 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000
Findings Of Fact Based upon the evidence presented, the following facts are determined: The UTILITY is owned by Florida Land Company, a Florida corporation, which is a wholly owned subsidiary of The Continental Group, Inc., a New York corporation. In 1975, the UTILITY constructed a water and sewage treatment system to serve a residential and commercial development known as Greenwood Lakes. The UTILITY's water and sewer rates and charges have not changed since the COMMISSION's approval of initial tariffs in 1976. (Testimony of Crosby; P.E. 1.) I. Elements of Ratemaking In fixing the water and sewer rates to be charged by a public utility, the COMMISSION must consider: (1) the value and quality of the service, (2) the utility's rate base, (3) the cost of providing the service, and (4) a fair return on the utility's rate base. Section 367.081(2), Florida Statutes (1979). Each element is addressed separately below. Quality of Service The UTILITY's water supply is provided by two deep wells with a total capacity, based on present pumps, of 2.376 million gallons per day. Treatment is provided by aeration and chlorination. The water system operates under an operating permit issued by the Department of Environmental Regulation. Water samples and reports are made monthly, and the water system presently meets all drinking water standards of the Department. (Testimony of Crosby, Heiker; R.E. 1.) The UTILITY's sewage treatment system consists of a .10 million gallon per day package plant; treatment consists of extended aeration followed by gravity flow to evapo-percolation ponds providing on-site disposal. It operates under an operation permit issued by the Department of Environmental Regulation, and complies with Department's sewage collection and treatment standards. (Testimony of Crosby.) Rate Base Rate base consists of the UTILITY property that is used and useful in providing the service for which rates are charged. In its application, the UTILITY proposed a rate base; after review, the COMMISSION suggested several adjustments, which are not opposed by the UTILITY. Use of a year-end test year is appropriate because of the extraordinary growth experienced by the UTILITY during 1979. For the test year ending December 3l, 1979, the UTILITY's adjusted water rate base is $135,977; the adjusted sewer rate base is $131,764. They are calculated as follows: RATE BASE Test Year Ending December 31, 1979 WATER SEWER Utility Plant in Service $190,969 $225,722 Construction Work in Progress 1,214 4,297 Accumulated Depreciation 18,920 2/ 14,801 2/ Contribution in Aid of Construction (CIAC)-Net of Amortization -48,831 -86,458 Working Capital Allowance 3,030 3,198 Income Tax Lag -0- - 194 RATE BASE $135,977 $131,764 (Testimony of Lowe; P.E. 1, 2, 3, R.E. 3.) Operating Statement The following Operating Statement reflects the UTILITY's revenue earned, costs of operation, and not-operating income during the test year. It shows that the UTILITY suffered a loss of $26,429 in its water operations and a loss of $19,101 in its sewer operations. OPERATING STATEMENT Test Year Ending December WATER 31 , 1979 SEWER Operating Revenues: $10,172 Operating Expenses: Operatic 25,314 $14,365 22,436 Maintenance -0- -0- Depreciation 18,199 10,132 Amortization -0- -0- Taxes Other Than Income 1,088 898 Other Expenses -0- -0- Income Taxes -0- -0- TOTAL OPERATING EXPENSES $44,601 $33,466 Operating Income ($26,429) (Testimony of Lowe; P.E. 1, 2, 3, R.E. 3.) ($19,101) The UTILITY requests an annual water revenue increase of $36,154, and a sewer revenue increase of $31,715, which would produce gross annual revenue of $54,326, and $46,080, respectively. The adjusted Operating Statement, constructed to reflect this additional requested revenue, is as follows: CONSTRUCTED OPERATING STATEMENT Test Year Ending December 31, 1979 WATER SEWER Operating Revenues: Operating Expenses: $54,326 $46,080 Operation 30,634 25,580 Maintenance -0- -0- Depreciation 3,812 2/ 3,436 2/ Amortization -0- -0- Taxes Other Than Income 2,280 1,941 Other Expenses -0- -0- Income Taxes 1,424 968 TOTAL OPERATING EXPENSES $38,150 $31,925 Operating Income $16,176 $14,155 Rate Base $135,977 $131,704 Rate of Return 11.90 percent 10.74 percent (Testimony of Lowe; P.E. 1, 2, 3, R.E. 3.) Rate of Return The capital structure of the UTILITY is as follows: AMOUNT PERCENT TO TOTAL Debt 4/ $1,450,000 60.90 Customer deposits 6,389 .27 Common Equity 924,550 30.83 TOTAL $2,380,947 100.00 The proposed annual gross water revenues of $54,326, and sewer revenues of $46,080 will allow the UTILITY to earn a rate of return of 11.90 percent on its water rate base, and 10.74 percent on its sewer rate base. With debt service costs now in excess of 12.50 percent, the return on equity will be nominal; however, there is no evidence that this will cause the UTILITY's service to suffer. (Testimony of Smith; P.E. 6.) II. Capitalization of Interest on Non-Used and Useful Equipment The UTILITY's plant is larger than necessary to serve its present customers. In its application, the UTILITY seeks COMMISSION approval to capitalize its interest costs on that portion of the UTILITY's plant which is non-used and useful, and excluded from rate base. Capitalization will allow the UTILITY to recover its interest expenses over the useful life of the property involved. The COMMISSION has previously allowed capitalization of interest under similar circumstances, Docket No. 760054-WS, Application of North Orlando Water and Sewer Corporation, Order No. 7455, dated October 4, 1976. Here, the UTILITY's request is reasonable, concurred in by the COMMISSION, and should be granted. (Testimony of NewIon, Cooke, Lowe; P.E. .) III. Rate Structure The UTILITY currently uses a conventional two-tier rate structure. A base facility charge (BFC) rate structure is a more equitable method of distributing costs associated with providing a utility service. Under a BFC structure, customers pay a base charge which covers their pro-rata share of the UTILITY's fixed costs, and a gallonage charge which covers the costs of pumping, treating, and distributing the actual water gallonage used. Such a structure would require the UTILITY to alter its current customer service policy to insure that the base charge is paid during temporary discontinuances of service. (Testimony of Washington.)
Recommendation Based on the foregoing findings of fact and conclusions of law, it is RECOMMENDED: That the UTILITY's application for increased sewer rates and charges be granted and that it be authorized to file revised tariff pages containing rates designed in accordance with the base facility charge concept to produce gross annual water revenues of $54,326 and annual sewer revenues of $46,080; That the UTILITY be required to notify each customer of any rate increase authorized, explaining the reasons for such increase. A letter of explanation should be submitted to the COMMISSION for prior approval; That the UTILITY be allowed to retain all interim revenues collected pursuant to COMMISSION Order No. 9416 and cancel the rate refunding bond previously submitted; and That the UTILITY be allowed to capitalize interest on non-used and useful equipment which is excluded from rate base. DONE AND ENTERED this 5th day of December, 1980, in Tallahassee, Florida. R. L. CALEEN, JR. Hearing Officer Division of Administrative Hearings Room 101, Collins Building Tallahassee, Florida 32301 (904) 488-9675
The Issue The issue posed herein is whether or not the Respondent, Arthur M. Jones, Jr.'s Wastewater Treatment Plant Operator's license should be suspended or revoked based on conduct set forth hereinafter in detail based on allegations as set forth in the Petitioner's Administrative Complaint filed January 31, 1979.
Findings Of Fact Based upon my observation of the witnesses and their demeanor while testifying, the arguments of counsel and the documentary evidence received, the following relevant facts are found. Respondent, Arthur M. Jones, Jr., is a duly certified Class C Wastewater Treatment Plant Operator, certified pursuant to Chapter 17-16, Florida Administrative Code. Respondent holds license No. 793 originally issued by the Florida Department of Health and Rehabilitative Services on May 13, 1971. The responsibility for certification of wastewater treatment plant operators was transferred to the Florida Department of Pollution Control by Executive Order 72-75. The Florida Department of Environmental Regulation is the successor agency to the Florida Department of Pollution Control by virtue of Chapter 75- 22, Laws of Florida, and is authorized by Section 403.101, Florida Statutes, to issue and revoke operators' certificates pursuant to its rules and Chapter 120, Florida Statutes. At all times material to this complaint, Respondent was employed by the Duval County School Board in Jacksonville, Florida. At all times material, Respondent was employed by the School Board as a School Sewer/Water Plant Mechanic, a position requiring certification by the Department as a Wastewater Treatment Plant Operator. In his capacity as a School Sewer/Water Plant Mechanic and Class C Operator, Respondent was responsible for the operation, supervision, maintenance and collection of influent and effluent samples from various Duval County schools. Persons responsible for the operation, supervision, maintenance and collection of influent and effluent samples must be licensed and certified by the Department as a Wastewater Treatment Plant Operator. Additionally, Respondent, in his capacity as a School Sewer/Water Plant Mechanic and Certified Class C Wastewater Treatment Plant Operator, was responsible for the proper collection of composite samples of raw sewage and the treated effluent from each such plant. According to instructions given the Respondent, a composite sample was to be taken by filling one-third of a sample bottle at two-hour intervals until the bottle was full. The composite sample of raw sewage was to be taken from the influent line and the composite sample of treated final sewage was to be taken from the effluent line. After the collection process, Respondent was responsible for properly and accurately labeling the composite samples and for depositing them in a refrigeration unit at School No. 98. The composite samples are then picked up at School No. 98 by authorized personnel for laboratory analysis to determine whether sewage is being adequately treated. The complaint, in summary fashion, alleged that the Respondent on or about February 15 and March 15, 1978, completely filled a raw sample bottle from the filter bed rather than from the influent line of the plant at School No. 94. That sample was submitted as a composite sample and placed in the refrigeration unit for pickup and analysis by laboratory personnel. Additionally, the complaint alleges that on February 15, 1978, at School No. 82, Respondent filled raw and final sample bottles for Schools Nos. 82, 64, 83 and 153, none of which were a proper composite sample. The samples, it is alleged, were all taken from School No. 82. The complaint alleges that similar acts occurred on March 15, 1978; on April 4, 1978 and April 11, 1978, all of which acts "constitute gross neglect and fraud in the performance of duties as an operator of a wastewater plant." Based thereon, the Petitioner seeks revocation of the Respondent's Class C Wastewater Treatment Plant Operator's license. L. L. Masters is Respondent's foreman and is in charge of the wastewater treatment plant facilities. Masters is Respondent's immediate supervisor. On March 15, 1978, Foreman Masters assigned Respondent the duties of taking composite samples of Schools 94, 64, 83, 82 and 159. Evidence reveals that Foreman Masters arrived at School 82 at 9:00 o'clock a.m. and departed at 2:00 p.m. Evidence also reveals that Foreman Masters had a clear view of the entire wastewater treatment plant and that it was impossible for the Respondent to enter and leave the treatment plant in a manner whereby composite samples could be collected without Foreman Masters seeing him. In this regard, Respondent's work orders reflect that he reported having arrived at School 82 at 10:40 a.m. and departed at 12:10 p.m. (Petitioner's Exhibits 5, 6, 7 and 8.) On April 4, 1978, Respondent was assigned to collect composite samples from Schools 72, 233, 76 and 208. (Petitioner's Exhibit 9.) Foreman Masters observed Respondent on April 4, 1978, with employee Carl Casey. Masters went to School 77 at 8:30 and Respondent was not there, although he had given a dispatcher a routing which would have taken him to School 76. When Foreman Masters noted that Respondent had not arrived at School 76 by 8:30 a.m., he took employee Carl Casey to School 233 and left Casey at School 233 while he returned to School 76. The Respondent was not there and Masters drove to School 208 where the Respondent arrived at approximately 9:30 a.m. It suffices to say that the Respondent then left for School 233 and arrived there at 10:30. From approximately 10:45 to 11:45, the Respondent was in the wastewater treatment area of School 233 and took three samples from the effluent line and three samples from the influent line at School 233 from the period 10:30 a.m. through 11:45 a.m. (Petitioner's Exhibits 9, 10 and 11.) Employee Pat Wilson testified that he accompanied Respondent on February 15, 1978, and that all samples were taken from the filter beds of Schools 98 and 82. Detective Jack C. Adams of the Jacksonville Police Department was assigned to the surveillance of Respondent on April 11, 1978. Detective Adams credibly testified that the Respondent did not take composite samples from the assigned schools as reflected by the work orders submitted by Respondent Respondent appeared and testified that one of the events for which he had been charged occurred as alleged; however, he testified that inasmuch as he questioned the procedures, he was of the opinion that since no harm was done, and since no school experienced problems, he is not guilty of gross neglect and fraud in the performance of his duties as an operator of a wastewater treatment plant as alleged. The evidence herein reveals that the Respondent was instructed as to the proper procedures for testing, collecting and preserving composite raw and final samples from wastewater treatment plants by his employer. He testified that he had attended a seminar wherein the instructions for such procedures were outlined to him and that he was given a manual on the methods for collecting raw and final samples. Barry McAlister, a certification officer for the Department, testified that Class C operators are instructed as to the proper procedures for collecting samples. Additionally, he testified that the submitting agencies rely heavily on the operators to properly collect samples which are submitted for analysis. Chapters 17-19.04, Florida Administrative Code, additionally set forth the sampling and testing methods for collection and preservation of composite samples. Although there was some conflicting testimony respecting the adherence to the procedures uniformly by the various wastewater treatment plant operators employed by the School Board, the undersigned is of the opinion that the Respondent was not at liberty to select and choose the manner within which he would collect composite samples for analysis by his employer in view of outstanding instructions which were in effect during his employment.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is hereby, RECOMMENDED: That the Respondent, Arthur M. Jones, Jr.'s license as a Class C Wastewater Treatment Plant Operator be suspended for a period of two (2) years. RECOMMENDED this 28th day of September, 1979, in Tallahassee, Florida. JAMES E. BRADWELL, Hearing Officer Division of Administrative Hearings Room 101, Collins Building Tallahassee, Florida 32301 (904) 488-9675 COPIES FURNISHED: Silvia Morell Alderman, Esquire Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Reed Tallahassee, Florida 32301 Joseph S. Farley, Jr., Esquire Mahon, Mahon & Farley 350 East Adams Street Jacksonville, Florida 32202
Findings Of Fact In light of the aforementioned stipulations entered into by the parties, the parties agreed that the only remaining disputed issue was the quality of service being provided by Petitioner. In this connection, the record establishes that Petitioner operates nine water systems in Duval County, one of which is known as the "Milmar Plant." Water furnished through this plant has, in the past, violated applicable regulatory standards with regard to high iron levels and corrosivity, to such an extent that the system was the subject of a Corrective Order entered by the Duval County Public Health Division of the Department of Health and Rehabilitative Services in 1980. However, as a result of Petitioner's agreement to connect to the City of Jacksonville water system, these problems should be alleviated when the switch-over and connection are accomplished. Accordingly, as a condition to approval of the requested rate increase, Petitioner should be required to complete the switch-over and connection to the City of Jacksonville water system prior to the entry of a Final Order granting the requested rate increase.
