The Issue The issue in this case is whether proposed Rule 5E-2.038 is an invalid exercise of delegated legislative authority.
Findings Of Fact On November 5, 1993, Respondent published in the Florida Administrative Weekly the text of a proposed rule to be known as Rule 5E-2.038, which Respondent indicated that it intended to adopt. The proposed rule reads: 5E-2.038 Restrictions on Use of Bromacil in Citrus: Penalties. Definition. For the purpose of this rule "permeable, better drained soils" means those soils defined as such in the U.S.D.A. Agricultural Handbook No. 436 (1975), a copy of which may be obtained from the U.S. Government Printing Office, Washington, D.C. 20402-9328. Use Restriction. The use of Bromacil is prohibited for weed control in areas producing citrus fruit on any permeable, better drained soil identified in the intended site of application. Permeable, better drained soils which occur in citrus producing areas of the state include, but are not limited to, soils unnamed and characteristic of Quartzipsamments, and the following soil series classifications: Adamsville Archbold Astatula Bahiahonda Broward Canaveral Candler Cocoa Dade Florahome Fort Meade Gainesville Lake Lakewood Neilhurst Orlando Palm Beach Paola Satellite St.Augustine St. Lucie Tavares Orsino Penalties. The use or application of bromacil by any person in a manner inconsistent with the provisions of this rule is a violation of Chapter 487, Florida Statutes. Specific Authority 570.07(23) FS. Law implemented 487.031(10), 487.031(13)(g), 487.051(1) FS. History--New. 1/ Bromacil, which is manufactured by Dupont, is a broad- spectrum residual herbicide. It has been used extensively in citrus groves since its introduction about 25 years ago. The application rate of bromacil has generally increased since its introduction in the late 1960s. At first, growers applied bromacil in narrow strips down the rows of trees. In the 1970s, growers applied bromacil in bands out to the drip lines of the trees. By the late 1970s, growers applied bromacil twice annually, rather than once annually, as had been more typical at first. From the 1980s through present, growers began applying bromacil trunk to trunk, row to row. Growers control weeds to reduce competition, especially around young trees. Also, when growers began changing from overhead to microjet irrigation 10-15 years ago, it became more important to clear undergrowth from the area around the microjet, which is only 6-12 inches above the ground. Historically, weed- clearing was done manually and later by mechanically hoeing, but these activities disturb the sandy soil and contribute to rutting when trucks enter the groves during harvesting. There are other herbicides available, although they are less favored among growers due to considerations of cost and efficacy. Some are contact herbicides, rather than the longer- lasting residual herbicides. Bromacil is a pre-emergent herbicide, but other such herbicides are available. Bromacil is a Group C carcinogen, which means that it is a possible human carcinogen. Bromacil has caused tumors in male mice, but not male rats. Sometime in 1988 or later, the U.S. Environmental Protection Agency published a health advisory concerning bromacil. Health Advisories describe nonregulatory concentrations of drinking water contaminants at which adverse health effects would not be anticipated to occur over specific exposure durations. Health Advisories contain a margin of safety to protect sensitive members of the population. Health Advisory Levels (HALs) are typically set for one- day, ten-day, seven-year, and lifetime (70-year) exposures. Group A and B carcinogens, which are known or probable human carcinogens, do not carry recommended HALs for lifetime exposures. The bromacil ten-day HAL for a child is 5000 parts per billion (PPB). The bromacil seven-year HAL for an adult is 9000 PPB. The bromacil lifetime HAL is 90 PPB. In 1986, bromacil had become due for reregistration by the U.S. Environmental Protection Agency. In need of data to support reregistration, Dupont, Respondent, and the then- Department of Environmental Regulation (DER) embarked on a data- collection project to assess the presence of bromacil in the groundwater. By 1987, growers, Dupont, and Florida state agencies were aware that bromacil was entering the groundwater. By this time, the Department of Health and Rehabilitative Services had received reports of bromacil killing oak trees adjacent to citrus groves, although the record is unclear as to the means of exposure. By the end of 1987, Respondent had detected bromacil in a drinking- water well. Bromacil has a typical soil half-life of 120 days. But it degrades more slowly in groundwater, so its primary means of dissipation in groundwater is through dispersal. Little if anything is known of the duration of bromacil in surface water, such as lakes and rivers. To initiate the groundwater monitoring study, DER, Respondent, and Dupont identified the three major types of citrus-growing areas: the flatwoods typical of south-central and southwest Florida citrus land; the coastal region of Indian River; and the central ridge running down the central portion of the state. Due to its predominant well-drained soils, the central ridge is the area that is effectively subject to the prohibition contained in proposed Rule 5E- 2.038. The study site eventually selected in the central ridge site is in the Waverly grove east of Waverly in Polk County. The soil on the 5.7-acre site, which is in the Candler soil series, is typically sandy to a depth of 12.5 feet with low organic matter. The state agencies and Dupont determined that the application history of bromacil was not uncharacteristic for the area. 2/ However, the manner of application was different from prevailing practices to the extent that it was in a banded treatment, which covers only about 60 percent of the grove acre, rather than the trunk-to-trunk treatment, which covers nearly the entire grove acre. The Waverly grove owner decreased treatment rates by 33 percent between 1987 and 1988, and by another 33 percent between 1989 and 1990. Between 1990 and 1991, the grove owner decreased the treatment rate by 20 percent, and by another 33 percent between 1992 and 1993. Between 1987 and 1993, the total decrease in application rate was 77 percent. Ten monitoring wells (MW- ) were installed on the Waverly site during the fall of 1986. 3/ Readings were generally taken on a quarterly basis. As was the case with the sites selected in the flatwoods and coastal region, the state agencies and Dupont chose the Waverly site as a "reasonable 'worst-case'" scenario based on soil, climate, and agronomic conditions. Sampling of the well water at all three sites began in September 1987. Due to the infrequency of detections in the coastal region and flatwoods, sampling of these sites was discontinued in December 1989, and the soils described by the rule are not those typically found in these areas. At about the time that the study was terminated at the flatwoods and coastal region sites, Dupont relabelled its products containing bromacil to reduce the rate of application in the central ridge. 4/ The relabelling was Dupont's response to early indications of the extent to which bromacil was entering the groundwater in the central ridge. At the Waverly site, Dupont and the state agencies determined the direction of groundwater flow, the time required for bromacil to travel through the unsaturated zones to the water table, and the linear velocity of the groundwater. 5/ For MW-1 through MW-10, levels of bromacil over 90 PPB were detected in 14 of 204 samples taken, for a rate of 7 percent. 6/ No readings over 90 PPB were found in MW-1, MW-2, MW-5, MW-6, or MW- 10. However, each shallow well on the Waverly site suffered bromacil contamination in excess of 90 PPB. The northernmost well, which is at the highest elevation (MW-3), four times had readings over 90 PPB, with the highest of 119 PPB. The central well, which is at a mid-elevation (MW-4), eight times had readings over 90 PPB, with the highest of 156 PPB. The southernmost well, which is at the lowest elevation (MW-7), six times had readings over 90 PPB, with the highest of 149 PPB. MW-7, as well as MW-8 and MW-9, are the only wells outside the treated grove area. They are about 90 feet from the grove edge. MW-8 and MW-9 are the only other wells whose readings exceeded 90 PPB. The intermediate well, MW-8, had four readings over 90 PPB with the highest of 103 PPB. The deep well, MW-9, had one reading of 150 PPB, which was the only reading over 90 PPB for this well. Analysis of these data must consider numerous factors, including the timing and amount of bromacil applied in the Waverly grove, the time it takes for peak concentrations of bromacil to reach the water table, and the time it takes for bromacil to be carried with the groundwater to sites outside the treated grove. As noted in footnote 5, peak concentrations of bromacil pass through the unsaturated zone at a rate of 8-9 feet per year. Given the varying thicknesses of the unsaturated zones around MW- 10, MW-1 through MW-3, MW-4 through MW-6, and MW-7 through MW-9, as noted in footnote 3, peak concentrations of bromacil would reach the water table for each of these wells or well clusters, following application, at about 4 years for MW-10, 3 years for MW-1 through MW-3, 2 years for MW-4 through MW-6, and 1 1/2 years for MW-7 through MW-9. Once in the surficial aquifer, bromacil evidently travels at the rate of the groundwater itself, whose linear velocity in the area is 1-2 feet per day. 7/ Based on the factors set forth in the preceding paragraph, Dupont concluded in its analysis that the 1992 readings of bromacil in the groundwater at MW-10 and MW-1 through MW-6 were due to applications made between 1988-1990 and the 1992 readings of bromacil in the groundwater at MW-7 through MW-9 were due to applications made between 1987-1990. The Dupont analysis of MW-10 and MW-1 through MW-6 fails to explain all of the variability of the readings during 1992. Although MW-1 and MW-3 remained constant during 1992, MW- 2, which is the intermediate well in this cluster, experienced its highest reading in September 1992--exceeding its next highest reading by almost 15 PPB. However, the application rate of bromacil decreased by 33 percent during the three years in question and the season of the application remained constant for the first two years. In 1990, the rainy- season applications were discontinued, 8/ so the abnormally high reading was presumably not due to the accelerated transport of bromacil, with excessive rainwater, through the unsaturated zone. The discrepancies persist even if one assumes that the peak levels of bromacil penetrated the unsaturated zone about three years following their application on the surface. About three years earlier, as noted in footnote 2 concerning rates of bromacil application in the Waverly grove, about 1.6 pounds of active ingredient per acre was applied during the rainy season. However, one year earlier the same amount was applied, and two years earlier 2.4 pounds of active ingredient per acre was applied; and the September 1991 and 1990 readings were a relatively modest 21.8 PPB and 33.1 PPB, respectively. 9/ Dupont concluded in its analysis that the 1992 readings of bromacil in the groundwater at MW-7 through MW-9 were due to applications made between 1987 and 1990. Therefore, these three wells, which are downgradient from the grove area and the rest of the monitoring wells, span four years of bromacil applications. During this time, the amount of bromacil applied decreased by 58 percent. Meaningful analysis of the extent of variability between 1992 bromacil levels in MW-7 through MW-9 is impaired by the absence of data regarding pre- 1987 bromacil application amounts. In any event, the Waverly data clearly demonstrate that bromacil persists a long time in groundwater, especially when compared to the relatively short period required for degradation in soil. The Waverly data also shows that bromacil travels in groundwater beyond the area in which bromacil was applied. The Waverly data suggest that the bromacil accumulates at relatively shallow depths in the surficial aquifer, although the relatively higher readings for the down-gradient, deep monitoring wells suggest that, over time, bromacil may penetrate deeper, as well as travel laterally. The Waverly data are also significant for their omissions. The rate of degradation of bromacil in water obviously is quite slow. But the data offer little insight into the two most likely means by which bromacil concentrations are reduced over time--i.e., discharge into surface waters and dissipation of these relatively minuscule amounts of herbicide through dispersal in large volumes of groundwater. There are no data from the intermediate or Floridan aquifers in the vicinity of the Waverly site. There are no data tracking the bromacil in the groundwater once it leaves the Waverly site or after it is discharged from the groundwater into surface water, such as the lake that is located a short distance and downgradient from the Waverly study site. The data offer no basis for determining when and how bromacil is eliminated from the groundwater. In 1987, Respondent found bromacil in existing wells in the Kahn grove two miles southeast of Sebring in Highlands County. Evidently for this reason, the Kahn groves formed part of another groundwater monitoring site involving bromacil. Like the Waverly site study, the study of the Kahn grove, which became known as the DeSoto City site, also began in 1987. Dupont participated in the data collection from this 90-acre test site, which is in the "highly vulnerable" southern end of the central ridge. 10/ The DeSoto City site, whose predominant soils are yellow fine sand, initially involved four installed sand point wells (SP- ) and four existing drinking and/or water supply wells. Readings were generally done on a quarterly basis. After several months, seven more monitoring sand point wells were installed for a total of 11 sand point wells. 11/ Four of the new sand point wells were in the grove in which the four original sand point wells were installed. The other three new sand point wells were placed in the grove immediately east of the location of the other eight sand point wells and immediately north of an existing residential area. Eventually, 89 individual drinking water wells in the residential area were added to the DeSoto City study. The individual drinking water wells, which are typically sunk in the surficial aquifer, are downgradient from a portion of the Kahn groves immediately to the north. As was done in the Waverly grove study, Respondent or Dupont determined the application history of bromacil in terms of amount and timing of applications. 12/ As is the case at the Waverly grove site, all applications were banded rather than trunk to trunk. The DeSoto City grove owner increased treatment rates for the western portion of the grove between 1986 and 1987 by over threefold, then decreased the rate by over 80 percent between 1987 and 1988. Skipping any application in 1989, the grove owner increased the rate by 2.5 times between 1988 and 1990. The only difference in the application on the eastern portion of the grove is that the fairly light application of 1988 was omitted. All applications were during the dry season except for the heaviest single application of 3.18 pounds of active ingredient per acre applied in July 1987. The DeSoto City site has comparable soils to the predominant soils of the Waverly site. With a slope of only about 17 feet over 2400 linear feet, the DeSoto City site is more level than the Waverly site. The water table is considerably higher at the DeSoto City site than at the Waverly site. With an average of 9-10 feet of unsaturated zone beneath the western portion of the groves, this area of the DeSoto City site has a thinner unsaturated zone than any location tested at the Waverly site, where the thinnest unsaturated zone was about 12 1/2 feet at MW-7 through MW-9. Peak concentrations of bromacil penetrate eight feet of unsaturated zone in 9-10 months. The eastern portion of the groves, where SP-8 through SP-10 are located, sit over thicker unsaturated zones--22-24 feet for SP-8 and SP-9 and 14 feet for SP-10. Peak concentrations of bromacil would take two to three years to reach the surficial aquifer in the areas of SP-8 and SP-9. Typical depths to groundwater estimated for the residential area, for which well- drilling data are unavailable, range from 9 to 11 feet. The direction of the groundwater flow in the DeSoto City grove areas is generally to the south-southwest, although groundwater flows in a more southerly direction in the residential area. The average linear velocity of groundwater in the surficial aquifer in the area is estimated to be 1-2 feet per day. The northernmost wells in the western portion of the grove, as well as two wells north of the grove, disclose that the shallow surficial aquifer has generally eliminated most of the bromacil, but the intermediate surficial aquifer remains heavily contaminated. 13/ Some of the data for the northernmost wells do not correlate with bromacil applications in the grove immediately above the well. For instance, SP-3 reached 180 PPB in September 1989, dropped dramatically for 6-9 months, and then remained over 100 PPB from September 1990 through February 1991. However, the most recent bromacil application before September 1989 was March 1988--about double the estimated time that it takes peak bromacil concentrations to penetrate the unsaturated zone in the area. SP-4, which is about 600 feet east of SP-3, behaved more predictably in response to surface applications of bromacil. The same is true of SP-7, which is about 500 feet southwest of SP-3. SP-6I and SP-6II, which are the only clustered wells on the DeSoto City site, are equidistant between SP-3 and SP-4, about 300 feet to the south. SP-6I never had a reading over 90 PPB. However, SP-6I was installed at the very top of the surficial aquifer. SP-6II, which was installed roughly 13-14 feet deeper in the surficial aquifer, never had any readings less than 90 PPB and had readings over 200 PPB. SP-6II was the only well drawing water from intermediate depths of the surficial aquifer. Even after the use of bromacil was discontinued in the Kahn grove after the October 1990 application, readings at SP- 6II remained quite high. A year after the final application, by which time peak concentrations should have reached at least the top of the surficial aquifer, SP-6II had bromacil levels of 467 PPB. Consistent with vertical travel time estimates, the readings went down after that, but, despite the absence of additional applications, bromacil levels were 188, 237, 179 and 164 PPB for the next four quarters. The Dupont study notes that SP-6II is about 1700 downgradient from a residential well at 5107 DeSoto Road. It is impossible to verify this assertion from the groundwater data presented in the report. Very high bromacil concentrations in this residential well, which was the site of a parked spray rig that likely discharged bromacil spray, were detected in July 1988. Peak concentrations at SP-6II of 1221 to 1463 PPB were detected between December 1990 and February 1991, which would translate to a travel rate of two feet per day. If SP-6II is in fact downgradient from the well at 5107 DeSoto Road, the Dupont study has accounted for the two extremely high bromacil readings at SP-6II, although not the remaining high readings unless one assumes that the well at 5107 DeSoto Road is an ongoing point source of bromacil contamination. The Dupont study observes ominously that the sand point wells lacked locks, so the possibility of sabotage cannot be discounted. 14/ The data from the two wells in the central part of the western portion of the grove reveal little more. The well at the barn had substantial readings, but these may have involved point source pollution from the barn. The other well, SP-2, approached 90 PPB one time, but has been below 2.0 PPB since December 1989. 15/ One sand point and one existing well are at the southern end of the grove west of the residential area. An additional existing well is just across a road from the southern end of this area of the grove. 16/ The readings at SP- 1, whose most recent reading is 8 PPB, correlates with at least the last bromacil applications; four readings over 90 PPB took place five, eight, four, and eight months after the relevant applications. However, the only 90+ PPB readings after the highest application of bromacil in July 1987 were 3 and 15 months following the date of application. The only 90+ PPB readings of the existing well north of the road are December 1991, March 1992, June 1992, and September 1992. This well is identified as the "shop" or "mixing/loading" area. Again, the possibility of point source contamination exists at this site. However, the pattern of higher recent readings is repeated at a site perhaps less likely to be an isolated source of pollution. The existing well across the street from the grove, which is known as the "office" well, has had its three highest readings in March, June, and September 1992, although none of these readings was over 68.17 PPB. The Dupont study concludes that bromacil would require 3.3-6.6 years to travel in the groundwater from SP-3 at the north end of the western portion of the grove to the road. There thus are insufficient data to determine if any correlation exists between readings at SP- 3 and the office well. There are three sand point wells in the eastern portion of the grove. 17/ The highest readings in the northernmost well, which may be just north of the grove, have been made in the four most recent months prior to the last reported reading in September 1992. The last reading was 96.3 PPB, which was the only time that SP-9 exceeded 90 PPB. SP-8 and SP-10 have not shown very high levels of bromacil in recent readings. Summarizing the DeSoto City site, except for the residential area, 60 of the 219 samples, or 27 percent, tested over 90 PPB for bromacil. SP-2, SP-5. SP-6I, SP-10, the office well, and the trailer well never had a sample over 90 PPB. SP-9 had one such sample, SP-4 had three such samples, the shop well and SP-7 each had four such samples, SP-3 had six such samples, SP-1 and SP-8 each had seven such samples, and SP-6II had 19 such samples. The sampling of the residential area added to the DeSoto City groves study area began as early as October 1987 and extended generally to September 1992. Out of 646 total samples, bromacil was detected 575 times, or in 89 percent of the samples. Sixteen percent of these detections, or 104, were over 90 PPB. The highest levels of bromacil so detected ran into the mid-100s PPB. No levels over 90 PPB were detected in 1987. Four such detections were made in 1988. Eighteen were detected in 1989, 20 in 1990, 31 in 1991, and 19 in the part of 1992 covered by the data. It is apparent from readings of residential wells that a plume of bromacil is moving through the surficial aquifer under the residential area. The plume is traveling at the estimated speed of the groundwater. The data from the DeSoto City study do not indicate that any substantial degradation of the bromacil in the groundwater has taken place during the time involved in the study. It is unclear whether the plume of bromacil will be tracked if and when it leaves the surficial aquifer under the residential area. Again, there are no data suggesting the manner or rate at which bromacil is eliminated from the groundwater or its fate in surface waters. But the DeSoto City study provides one piece of new information. In the Waverly study, the shallower wells were the most impacted; in the DeSoto City study, the most impacted well was the deepest well. The DeSoto City study also provides some data concerning the efficacy of bromacil-removal processes. A carbon filter practically eliminates all bromacil from drinking water. However, in one case, the carbon filter failed after nine months at one residence. 18/ With the assistance of DER, the residential area is in the process of obtaining service with municipal water as the private water source is contaminated not only with bromacil, but nitrate. A third major study is the Polk County Very Intensively Studied Area (VISA). The Polk VISA is one of a number of VISAs created by DER throughout the state to obtain data on groundwater. Unlike the Waverly and DeSoto City studies, the Polk VISA covers the surficial aquifer and the Floridan aquifer. The seven wells penetrating the Floridan aquifer have cased depths ranging from 137 to 412 feet. Seventeen wells tap the surficial aquifer. The Southwest Florida Water Management District sampled 23 of the Polk VISA wells in July 1990 and all 24 of the Polk in April 1993. All of the bromacil detections were in 1993. Readings of over 90 PPB of bromacil were detected in three of the surficial wells. Lesser amounts of bromacil were detected in 13 of the remaining 14 surficial wells. In the Floridan aquifer, bromacil was detected in four of seven wells, in amounts of 0.97 PPB, 2.8 PPB, 0.72 PPB, and 1.4 PPB. In subsequent discussions with state agencies, Dupont argued that a reduced rate of application of bromacil in the central ridge would sufficiently address the groundwater- contamination problem, largely because recent high readings were obviously from off-site sources. Concerned in part about the lack of data concerning the persistence of bromacil in the groundwater, state agency representatives sensibly rejected these arguments. Instead, Respondent proposes to adopt Rule 5E-2.038. The state agencies and Dupont are in the process of preparing a study protocol that would permit more accurate conclusions concerning the means by which bromacil enters the groundwater. It is unclear if subsequent studies will address other important issues, such as how far and in what concentrations can bromacil be transported by groundwater, how and at what rate is bromacil eliminated from groundwater, to what extent is bromacil in surface water, and how and at what rate is bromacil eliminated from various types of surface water.
The Issue The issue in this case is whether the Notice of Violation (NOV) and Orders for Corrective Action (OCA) filed by the Department of Environmental Protection (DEP) against Respondents, Thomas Kerper (Kerper) and All Salvaged Auto Parts, Inc. (ASAP) , in DEP OGC File No. 02-0447 should be sustained.
Findings Of Fact 1. The real property located at 3141 Sharpe Road, Apopka, Florida, is owned by the heirs of Donald Joynt, who owned it for the 30 years prior to his death in 2002. The property consists of approximately 40 acres in the shape of a right triangle with the west side bordered by Sharpe Road, the south side by a potting soil business, and the northeast side (the hypotenuse of the right triangle) bordered by a railroad track. Prior to his death, Joynt used the property primarily for the purpose of operating a junkyard and recycling business ultimately entitled Don's Auto Recycling. 2. At some time before 2000, Joynt became desirous of selling his property. He offered it to a neighbor named José Luis Benitez for $600,000. Benitez counter-offered for between $350,000 and $400,000 because he thought it would cost $200,000 to $250,000 to clean the property up. Joynt rejected the counter-offer, and asked Benitez to help him find a buyer who would pay more than Benitez. At some point, Joynt listed the property with a real estate broker for $600,000. 3. In 1999, Kerper was operating an automobile parts salvage business at a location near Joynt's property. Kerper needed a new location to move his business and inventory. A real estate broker showed him Joynt's property. The broker told Kerper that the seller's broker said the property was clean and had no environmental problems. The broker also told Kerper that Orange County had recently purchased an easement for $300,000 to run a drainage ditch through the property to a local lake, which was true. While this gave Kerper some level of assurance, the broker advised Kerper to have an environmental assessment done before going forward with the sale. 4. After being shown the property by the broker, Kerper spoke with Joynt directly. It was agreed that they could save the real estate commission and split the savings by waiting until the listing expired. Joynt personally assured Kerper that there were no environmental issues, as evidenced by Orange County's purchase of the easement for a drainage ditch. In late March of 2000, after expiration of the real estate commission, Kerper and Joynt entered into an informal agreement allegedly written on a scrap of paper, which was not placed in evidence. Kerper testified that the agreement was for him to buy the property for $500,000, with $100,000 down, and the balance payable over time at seven percent interest. He also testified that the required $100,000 down payment would be payable in installments, with $25,000 payable whenever Joynt cleaned 25 percent of the site to make it usable by Kerper for his business operations. 5. When it came time for Kerper to move onto Joynt's property, Kerper discovered that Joynt had not done any clean-up or removed any of his property from the site. Used cars, car parts, and tires that belonged to Joynt remained throughout the site. According to Kerper, it was agreed that Kerper would help Joynt clean off the western half of the property, which was split approximately in half by a stream, while Joynt worked on cleaning off the eastern half of the property.” 6. Starting from the gate at Sharpe Road, Kerper began removing junk from the western side to the eastern side of the site for Joynt to remove from the property. Pieces of equipment and used car parts that had been left there by Joynt were removed from this section of the property. When enough space was cleared off, Kerper began setting up his auto salvage operations on the western side. He used a bulldozer to level the driveways and spread powdered concrete where the ground was soft. He also used the bulldozer to level an area near the scale house, which was on the western side of the property, but continued to be used by Joynt for Don's Auto Recycling business. In doing this work, his workers encountered steel reinforcement bars, which Kerper had them cut with a torch. Some tires and battery casings also were visible in the ground. Kerper had several truckloads of fill dumped in the area and installed a concrete pad for storing and dismantling automobiles. 7. In September or October of 2000, Kerper was evicted from his prior business location, and he had to move to Joynt's property regardless of its condition. As he increased business operations on the cleared spaces, Kerper continued to clear more space on the western side of the property. Another concrete pad was installed farther to the north. Eventually, Kerper was operating ASAP on approximately ten acres on the western side of the 40-acre site. 8. As Kerper continued to move north, his heavy equipment began encountering assorted kinds of buried material. When a buried propane tank exploded, Kerper stopped working his heavy equipment in the area and confronted Joynt. Joynt denied any knowledge of buried tanks and stated they must have been placed there by someone else. Joynt told Kerper he would let Kerper move his operations to the east side of the property when Joynt finished cleaning it up, and then Joynt would finish clearing the western side for Kerper. Kerper agreed, and continued making payments on the required down payment. According to Kerper, he eventually paid $90,000 of the down payment. 9. By August of 2001, Kerper began to have serious misgivings about Joynt's promises and the condition of the site, and he decided to seek advice. Kerper hired David Beerbower, vice-president of Universal Engineering, to perform an assessment of the northern portion of his side of the site (in the vicinity where the exploding tanks were encountered). During his assessment on August 20, 2001, Beerbower observed various automotive parts including numerous crushed fuel tanks, antifreeze containers, and motor oil containers being excavated from the upper three feet of soil. It was determined by Beerbower, and stated in his written report to Kerper, dated September 21, 2001, that these parts appeared to have been buried there several years ago. This determination, which DEP does not dispute, was based on the high level of compaction of the soil found around these items that could be attributed to either the passing of a significant amount of time or a bulldozer passing over the items. Since the excavations Beerbower observed were in a separate location from where Kerper had already bulldozed, the soil compaction around these items could not be attributed to Kerper's bulldozing. It was stated in Beerbower's letter that the “amount of buried automotive debris qualifies this area essentially as an illicit landfill." ad 10. Mark Naughton from the Risk Management Division of the Orange County Environmental Protection Division (OCEPD), which runs the petroleum storage tank and cleanup program for Orange County under contract with DEP, was also present during the time Beerbower conducted his assessment. Naughton agreed with Beerbower's assessment that Kerper is not liable for the assessment or remediation of this area. Naughton also advised Kerper to move ASAP off Naughton's property and to seek legal advice from attorney Anna Long, who used to be the Manager of OCEPD. 11. Meanwhile, according to Kerper, Joynt changed his position and began to maintain that it was Kerper's responsibility to clean up the western side of the property. Given the newly-discovered environmental condition of the property, Kerper did not feel it was in his best interest to purchase the property "as is," and contacted Long to help him negotiate to extricate himself from his arrangement with Joynt. While negotiations proceeded, Kerper began to scale down ASAP's operations in anticipation of relocating. Kerper began fixing up more whole automobiles for resale, and had a car crusher used in connection with ASAP's business begin crushing more cars for removal from the site for recycling. 12. Eventually, Long had Beerbower conduct another assessment of portions of Joynt's property to try to establish responsibility for contamination as between Kerper and Joynt. On 10 February 13, 2001, Beerbower took a surface water sample froma "drain pipe under the north driveway," a soil sample "where the car crusher was," and another soil sample from "the sandblasting area." The evidence was not clear as to the exact location of these samples, particularly the soil samples, as described in Beerbower's written report to Long dated March 11, 2002. But it appears that the "car crusher" refers to the location of Respondents' car crusher operation in the northern part of the site, just across the northern driveway; it appears that the sandblasting area refers to a location used by Joynt on the eastern side of the property, but located just east of the trailers used by Kerper for his offices. These samples were analyzed and found not to contain volatile organic compounds (VOC) or total recoverable petroleum hydrocarbons (TRPH) in excess of Florida's cleanup target levels. 13. Kerper continued to operate his junkyard until the beginning of March of 2002. On March 5, 2002, Long filed a citizen's complaint with OCEPD on Kerper's behalf. While acknowledging that Kerper was operating on the site at the same time as Joynt in recent years, the complaint alleged Kerper's discovery that Joynt had been burying waste batteries, tires, and gasoline tanks on the property and covering the burial sites with broken concrete pieces. The complaint alleged that Kerper had been moving his personal property off of the site since August of 2001, when he backed out of his "lease to purchase" agreement 11 with Joynt, and would be "completely off the property by 3/10/02." 414. It is not clear exactly when Kerper and ASAP were completely off the property. The testimony and evidence on the point is inconsistent. Kerper, after some confusion, placed the date at March 9, 2002. His wife said it was March 2, 2002. An attorney representing Kerper and ASAP in an eviction proceeding filed by Joynt and his wife, filed a notice "that as of the evening of March 15, 2002, [ASAP had] vacated the property." In any event, the evidence seemed clear that Kerper and ASAP did not go on Joynt's property on or after March 15, 2002. 15. On March 15, 2002, DEP representatives inspected Joynt's property in response to Long's complaint. Kerper remained outside the front gate of the property and did not participate in the inspection. This inspection covered the entire property including the section that had been occupied by Kerper and ASAP. 16. doynt told the DEP inspectors that Respondents were responsible for a 55-gallon drum found tipped over on its side on the western half of the site and leaking a substance that appeared to be used oil from a hole in the side of the drum. DEP's inspectors righted the drum, which still was partly full of its contents. There also were several other unlabeled 55-gallon drums and 5-gallon containers "of unknown fluids"; a burn pile containing burned oil filters, battery casings, and electrical 12 wiring; other broken battery casings; and an area of dark-stained soil which appeared to be soaked with used oil. Joynt accepted responsibility for other contamination on the site, but told DEP that Kerper and ASAP were responsible for these items. Kerper denied the allegations. 17. As to the leaking oil drum, Kerper first contended that DEP did not prove that the overturned drum contained used oil. But the evidence was clear that DEP's inspectors were ina position to determine that the liquid was oily. Respondents also contended that the drum would have been empty, not still partly full, if Kerper or ASAP had left it on its side at the site when they vacated the property several days earlier. Kerper alleged that Joynt could have put the hole in the drum and turned it over shortly before the arrival of DEP's inspectors. But, as stated, it was not clear when Kerper and ASAP vacated the site, and it was not clear from the evidence that Respondents were not responsible. 18. Similarly, the other unlabeled drums and containers were in a part of the site occupied and used by Respondents. Despite Kerper's denials, it is not clear from the evidence that they belonged to Joynt or that they were placed where DEP found them after Respondents vacated the site. Testimony that Respondents had containers properly labeled "used oil," "antifreeze," and "gasoline" inside one of the trailers on the site did not negate the existence of unlabeled drums and 13 containers on the site. However, there was no proof whatsoever as to what the closed drums and containers held. But some were open, and DEP's inspectors could see that these held an oily substance (possibly hydraulic fluid), mixed with other substances. 19. As to the dark-stained soil, none of it was tested, and Respondents contended that it was just naturally darker in color or possibly wet from water or some other liquid, DEP's witness conceded could explain the color variation. (Natural reasons such as different soil or rainwater probably do not explain the color variations in the site.) Joynt told DEP's inspectors that the discoloration seen by them on March 15, 2002, was froma hydraulic hose on a piece of heavy equipment that burst earlier. The evidence was not clear who Joynt was saying owned and operated the equipment. But Respondents also blamed Joynt's employees for repeatedly blowing hoses on aged heavy equipment all over the site. It is found that the dark-stained soil probably was the result of one or more releases of hydraulic fluid or motor oil. However, the testimony and evidence was not clear that all of the releases were Joynt's doing and that Respondents bear no responsibility at all for the releases observed on March 15, 2002, in the areas where Respondents were operating. 20. Respondents were able only to produce documentation of proper disposal of 232 gallons of oily water through IPC/Magnum, 14 dated February 13, 2002, and 29 batteries through Battery World, dated March 8 and 14, 2002. 21. The testimony of Kerper and others was that Respondents generally removed gasoline from automobiles and placed it ina marked container for reuse within a day or two by Respondents and their employees. The testimony was that used oil and antifreeze generally also were removed from automobiles and placed in marked containers until proper disposition. The testimony was that batteries were removed from automobiles and that most were given to one of the employees to sell for a dollar apiece. There was no documentation to support this testimony. 22. There was testimony that, when Respondents had cars crushed, E & H Car Crushing Co., Inc., managed the collection and proper disposition of gasoline, used oil, and batteries. But the documentation placed in evidence contained no description of the wastes removed, but only provided a weight calculation of the materials removed from Respondents’ facility. 23. There was testimony that Gabriel Lynch, who was properly licensed, removed freon from automobiles at Respondents’ facility every two to three days, or upon request. Respondents would trade the freon Lynch recovered and used in his business, Gabe's Auto Tech, for repair work on Respondents' vehicles. However, no documentation of these transactions was produced. (Lynch testified that he did not know it was required that he provide documentation to Respondents.) 15 24. Runoff from where Respondents were operating on Joynt's property entered the stream running north-south through the center of the property. Neither Joynt nor Respondents had a stormwater permit or an exemption from stormwater permitting. 25. Kerper argued that his duties were limited to managerial responsibilities for ASAP, and that he was not at any time responsible for ASAP's day-to-day operations and did not conduct any activities that may or could have resulted in hazardous waste or petroleum discharge violations so as to be liable as an "operator." But the evidence was clear that Kerper was involved in ASAP's day-to-day operations. 26. While the evidence did not totally absolve Respondents from the allegations in the NOV, several people testified on Respondents' behalf as to their practice of properly disposing of hazardous materials generated by his business. For example, Rafael Rivera, a former employee, testified that Kerper would get mad at him if any gas or oil was spilled and left on the ground or was not disposed of properly. Meanwhile, it appeared that environmental problems at Joynt's site existed for years before the arrival of Respondents. Mrs. Sandra Lovejoy, a neighboring property owner for the past 30 years, testified that she had experienced problems with her water quality, such as a foul smell or funny taste, for many years before Respondents moved onto Joynt's property. An inspection was conducted by OCEPD in September of 2000, in response to Lovejoy's complaint regarding 16 fuel odor and a drinking well which was no longer in service. In part, OCEPD's written report on the complaint found "[m]any spots of surficial petroleum contamination . . . from gasoline, motor oil and other petroleum products leaking or spilled from the junk vehicles" at Don's Auto Recycling and included a recommendation "referring this site to the FDEP task force that has been put together to inspect and deal with junk yard facilities," although "[n]o Petroleum Cleanup issues were found at [that] time." For reasons not explained by the evidence, it does not appear that Don's Recycling was referred to any task force, or that OCEPD followed up on the reported contamination. 27. Respondents contend that this entire proceeding against them was part of a vendetta against Kerper for going to the local television station to expose the condition of the site, the failure of OCEPD and DEP to follow up on the September 2000, report and recommendation, and Orange County's purchase of a north-south drainage easement through the western portion of the property in 2000. The evidence did not prove this contention. However, it is clear that Joynt was responsible for the condition of most of the 40-acre site, not Respondents, and that Joynt shared responsibility with Respondents for the conditions alleged in the NOV. 28. While this case has been pending, Joynt's heirs have cooperated with DEP in cleaning up the site, and DEP acknowledged in its PRO that several items in the OCA--specifically, those 17 relating to Counts II, III, and VII of the NOV--are moot and unnecessary in light of Respondents' eviction from the property and subsequent cleanup operations by Joynt's heirs. It also is suggested that the corrective actions requested in DEP's PRO to address Counts IV, V, and VI of the NOV--relating to failure to document proper disposal of wastes--are unnecessary. It seems clear that, to the extent such disposals occurred, any available documentation would have been placed in evidence during the final hearing. Ordering that they be produced within 30 days of the Final Order, as suggested in DEP's PRO, would be a futile act. 29. Count VIII of the NOV alleged costs "of not less than $500. In its PRO, DEP requested recovery of $1,367.31 of costs. Some of these costs--$867.31--were itemized in the PRO. The balance appears to relate to the $500 alleged in the NOV. There was no evidence introduced at the final hearing as to any of these alleged costs, and the costs itemized in the PRO seem to represent travel costs of counsel for DEP.
Conclusions David J. Tarbert, Esquire Jason Sherman, Esquire Department of Environmental Protection The Douglas Building, Mail Station 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 Albert E. Ford II, Esquire Webb, Wells & Williams, P.A. 994 Lake Destiny Road Suite 102 Altamonte Springs, Florida 32714
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Environmental Protection enter a final order providing: 1. Under Count I of the NOV, Respondents shall be jointly and severally liable, along with Donald Joynt and Don's Auto Recycling, for cleaning up the releases of used oil evidenced by the discolored soils photographed by DEP's inspectors on 24 March 15, 2002 (DEP Exhibit 20, photographs 5 and 7 on page 2 of the exhibit). As such, they shall be responsible, along with Donald Joynt and Don's Auto Recycling, for implementation of DEP's Initial Site Screening Plan to assess and remove all contaminated soils resulting from those releases. If the results of the Initial Site Screening indicate that further assessment and/or remediation of the contamination is required, Respondents shall also participate, along with Donald Joynt and Don's Auto Recycling, in completing the required work, consistent with the "Corrective Actions for Contaminated Site Cases" (DEP Exhibit 16). 2. Counts II through VIII of the NOV are dismissed. 3. Respondents' Motion for Attorney's Fees and Costs is denied. DONE AND ENTERED this 19th day of December, 2003, in Tallahassee, Leon County, Florida. Vane ya J. LAWRENCE JOHNSTON Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 19th day of December, 2003. 25
Findings Of Fact Since 1984, the Department has been the state agency charged with the responsibility to establish rules and regulate underground pollutant storage facilities in Florida. In 1988, the Legislature added the administration of the newly enacted Florida Petroleum Liability and Restoration Program to the Department's duties. The program was to be established on or before January 1, 1989. The Applicant is the owner of a petroleum storage system in Jacksonville, Florida. Since 1984, it has been subject to the rules regarding underground pollutant storage facilities promulgated by the Department. On September 18, 1989, an odor indicative of possible petroleum contamination was discovered at the site during the installation of monitoring wells. A Discharge Notification Form was sent to the Department by the Applicant on October 23, 1989. The form advised that there were no leaks in the system. It was suggested that the odor may have resulted from surface spill at the site over a number of years. In response to the notification, an inspection of the site was completed by the Department on December 5, 1989. The inspection revealed the following on-site violations: Registration requirements were not being met. The forms had not been updated to include the presence of monitoring wells and overfill protection at the facility. Two underground tanks had not been properly abandoned. Inventory and reconciliation records had not been properly maintained, as required by rule since 1987. This violation was reviewed, and discussed in detail with on-site representatives of the Applicant. The monitoring wells were not installed by the time deadlines set forth in the Department's rules regarding stationary tanks. Since the wells were installed in September 1989, samples had not been taken for visual signs of petroleum contamination. The purpose of the system is to allow the owner of the storage tanks to learn if there is a leak in the tanks that can be quickly controlled to limit contamination. The day after the inspection, the Applicant applied for a determination of eligibility for participation in the restoration coverage portion of the new Florida Petroleum Liability Insurance and Liability Program. An affidavit was signed stating that all of the Department's rules regarding stationary tanks were being complied with by the Applicant. Six days after the inspection, the Department sent the Applicant written notice of the results of the inspection. The Applicant was given time frames and instructions for correcting the listed violations that could be corrected. A contamination assessment and clean up were also required in the letter. This letter did not address the issue of eligibility for the restoration funding program because that was a matter unrelated to the inspection results. On March 7, 1990, the Department determined the facility was ineligible for participation in the restoration funding provided by the Florida Petroleum Liability and Coverage Program. The following reasons were given: Failure to properly abandon underground storage tanks, pursuant to Section 17-61.050(3)(c), Florida Administrative Code. Failure to maintain inventory records, reconciliations, and significant loss/gain investigation as per Section 17-61.050(4)(c), Florida Administrative Code. Failure to install monitoring system and overfill protection by the dates set forth in Section 17-61.06(2)(c)2, Florida Administrative Code. Failure to properly monitor leak detection system, pursuant to Section 17-61.050(5)(c), Florida Administrative Code. The 10,000 gallon fuel oil tank and the 3,000 gallon waste oil tank present at the facility were abandoned in March 1990. The notice issued by the Department after its inspection in December 1989, gave the Applicant sixty days after receipt of the notice to properly abandon the tanks. The Applicant substantially complied with this requirement after the written notice was received. Although the Applicant failed to maintain the inventory records, reconciliations, and significant loss/gain investigations required by the Department rules, some of these violations had been corrected prior to the Department's inspection in December 1989. Correct inventory recordkeeping was discussed during the inspection, and the need to immediately implement the proper recordkeeping practices was emphasized in the post-inspection notice of violations. All of the recordkeeping violations were not cured until August 1990. The records kept by the Applicant during the noncompliance period from 1984 to August 1990, did not provide a substantially equivalent degree of information regarding possible leak detection or prohibited discharges as the required recordkeeping procedures. Two underground stationary storage tanks on the site have been part of the Applicant's petroleum storage system since 1970 and 1975, respectively. The monitoring wells and overfill protection for these tanks should have been in place by December 31, 1987. Neither monitoring system was installed until September 1989. The Applicant began the contract negotiations for installation in September 1988. The Applicant did not demonstrate that the facility contained an alternative procedure between December 31, 1987 and September 1989, that provided a substantially equivalent degree of protection for the lands, surface waters, or groundwaters of the state as the established requirement for monitoring wells and overfill protection. In December 1989, the Department's notice advised the Applicant that the monitoring wells should be sampled monthly for visual signs of petroleum contamination. Since April 1990, the Applicant has been completing the monthly sampling in the monitoring wells as part of its leak detection system, as required by the Department's rule regarding underground stationary tanks.
Recommendation Accordingly, it is RECOMMENDED: That the Department enter a Final Order denying Petitioner's application for restoration coverage in the Florida Petroleum Liability and Restoration Program at the Jacksonville location. DONE and ENTERED this 28 day of December, 1990, in Tallahassee, Leon County, Florida. VERONICA E. DONNELLY 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 _28_ day of December, 1990. APPENDIX TO RECOMMENDED ORDER The proposed findings of fact submitted by Petitioner are addressed as follows: Rejected. Improper interpretation of law. As for the facts in the first sentence, they are accepted. See HO #8. Rejected. Irrelevant. See HO #9. Rejected. Contrary to fact. See HO #9 and #11. Rejected. Contract to fact. See HO #11. Rejected. Contrary to fact. See HO #12 and #13. Rejected. Contrary to fact. Improper shifting of duty ad legal responsibility. Rejected . Improper application of law. The Respondent's proposed findings of fact are addressed as follows: Accepted. Accepted. Accepted. Accepted. See HO #8. Accepted. See HO #8. Accepted. See HO #3. Accepted. See HO #3. Accepted. See HO #3. Accepted. See HO #5. Accepted. Accepted. See HO #4. Accepted. See HO #4. Accepted. Accepted. See HO #6. Accepted. See HO #4 and #6. Accepted. See HO #4 and #6. Accepted. Accepted. Accepted. See HO #4 and #9. Accepted. Accepted. See HO #4 and #9. Accepted. Accepted. See HO #9. Accepted. See HO #4 and #10. Accepted. Rejected. Contrary to fact. See HO #10. Accepted. Accepted. Accepted. See HO #10. Accepted. See HO #3 and #12. Accepted. Accepted. See HO #13. Accepted. Accepted. See HO #6. Accepted. See HO #4 and #6. Accepted. See HO #6. Accepted. Rejected. Not established by evidence. See HO #6. Accepted. Accepted. Accepted. Accepted. See HO #7. Accepted. Accepted. COPIES FURNISHED: William Chadeayne, Qualified Representative 8933 Western Way, Suite 16 Jacksonville, Florida 32256 Janet E. Bowman, Esquire Assistant General Counsel Department of Environmental Regulation 2600 Blairstone Road Tallahassee, Florida 32399-2400 Dale H. Twachtmann, Secretary Department of Environmental Regulation 2600 Blairstone Road Tallahassee, Florida 32399-2400 Daniel H. Thompson, Esquire General Counsel Department of Environmental Regulation 2600 Blairstone Road Tallahassee, Florida 32399-2400
The Issue The issues in this case are whether Respondent violated certain rules of the Department of Environmental Protection (Department) related to petroleum contamination site cleanup criteria as alleged in the Department’s Notice of Violation, Orders for Corrective Action, and Administrative Penalty Assessment (NOV); whether Respondent is liable for the administrative fines and investigative costs assessed by the Department; whether mitigation of the administrative fine is appropriate; and whether Respondent should be required to take the corrective action described in the NOV.
Findings Of Fact The Parties The Department is the state agency charged with the power and duty to administer and enforce the provisions of Chapters 376 and 403, Florida Statutes (2008),1 and the rules promulgated in Florida Administrative Code Title 62, pertaining to petroleum contamination. Respondent Z.K. Mart, Inc., is a Florida corporation, and owns and operates a retail fueling facility (DEP Facility No. 8507091) located at 5077 Normand Boulevard, Jacksonville, Florida (“the facility”). In January 2004, soil sampling in conjunction with the removal of an underground petroleum storage tank at the facility showed petroleum contamination. Respondent reported the contamination to the Department in a Discharge Report Form on January 29, 2004. Respondent removed the tank that was the source of the contamination, conducted source removal activities, and submitted various reports to the Department, including a Site Assessment Report (SAR), submitted in February 2006. In March 2006, the Department determined the SAR was incomplete and requested that Respondent submit a SAR addendum. To date, Respondent has not submitted the SAR addendum. Respondent’s insurer, Mid-Continent Casualty Company, refused coverage for the assessment and cleanup costs associated with the reported discharge, asserting that the contamination “arose out of” the tank removal. Respondent contends that the contamination occurred before the tank removal. In October 2004, Respondent sued Mid-Continent in the circuit court for Duval County for wrongful denial of coverage. Respondent requested that the Department also file suit against Mid-Continent, pursuant to Section 376.309(2), Florida Statutes, for violating financial responsibility requirements. In December 2008, the Department sued Mid-Continent. The litigation is ongoing. Respondent spent over $300,000 to remove 2,503 tons of contaminated soil and to conduct site assessment activities associated with the reported contamination. In August, September, and October 2006, Respondent filed financial affidavits and additional materials with the Department in support of Respondent’s claim that it was unable to pay for additional assessment work. By letter dated November 3, 2008, the Department rejected Respondent’s claim that it was financially unable to undertake the requested site assessment. Respondent submitted a financial affidavit prepared by Abdul Khan, the vice president and secretary of Z.K. Mart, Inc., which states that the net income of Respondent was $36,479 at the end of 2005. Financial information for later years, including 2008, was also submitted by Respondent. However, no financial analysis was included. No evidence was submitted to establish the estimated costs of future site assessment activities. It cannot be determined from the financial information in the record whether Respondent is currently financially able to conduct additional site assessment activities. The Department states in the NOV that Count I constitutes a violation of Florida Administrative Code Rule 62- 770.800(5). That rule provides that it is a violation of Chapters 376 and 403, Florida Statutes, for a responsible party to fail to submit additional information or meet any time frame “herein.” The Department explained that Count I was intended to charge Respondent with failing to complete site assessment. The only applicable time frame in Florida Administrative Code Rule 62-770.800, entitled “Time Schedules,” is in subsection (3), which requires a responsible party to submit additional information within 60 days of the Department’s request for the information. That violation, however, is more specifically charged in Count II. Count II of the NOV charges Respondent with violating Florida Administrative Code Rule 62-770.600(11), which states that, if a SAR is incomplete, the Department shall inform the responsible party and the responsible party shall submit a SAR addendum within 60 days. Counts I and II charge Respondent with the same offense, failing to submit requested information within 60 days of the request. As stated in the Conclusions of Law, Respondent cannot be made to pay administrative fines under a duplicate charge. Count III of the NOV charges Respondent with liability for the Department’s investigative costs of $500 incurred in conjunction with this enforcement matter. These are nominal costs and were never disputed by Respondent.
Findings Of Fact On March 14, 1984, an inspector for the Petitioner, examined gasoline storage facilities from which Respondent, Zippy Mart #145 was dispensing gasoline. This store is found at 12524 San Juan Boulevard, Jacksonville, Duval County, Florida, (This product that was being dispensed by the Respondent at this location was the subject of consumer complaint.) Subsequent testing of the product known as Zippy Unleaded, as taken from the storage tank, revealed a 90 percent evaporated temperature of 376 degrees Fahrenheit and an end point of 493 degrees Fahrenheit. This was in keeping with laboratory procedures of the Petitioner. These matters were retested showing 90 percent evaporated temperature of 379 degrees and a 489 degree Fahrenheit end point. In lieu of the confiscation of the three thousand gallons which remained in the subject tank, related to the unleaded fuel at the store location, Respondent was allowed to post a bond in the amount of a thousand dollars and to remove the product from the premises and place new product in the tank. The reason for the values as shown in the sample pertaining to the 90 percent evaporated temperature and end point was due to the presence of diesel fuel within the tank designated for unleaded gasoline. The product as dispensed from that tank would cause engine damage to the automobile using that fuel, as evidenced by knocking and poor acceleration.
Findings Of Fact The Respondent, Philip G. Nicholson, does business as Allstate Termite Control. The Respondent holds a pest control identification card issued by the Office of Entomology of the Department of Health and Rehabilitative Services. On or about September 23, 1977, the Respondent entered into a subterranean termite control contract and service agreement with Roland E. Cooley and Alma P. Cooley with respect to the Cooleys' residence in Lake Worth, Florida. The chemical specified for use on the contract was chlordane. On or about that same date, the Respondent entered into a contract with Roland E. Cooley and Alma P. Cooley to perform a dry wood termite attic prevention treatment on the Cooley's residence. The chemical specified in the dry wood contract was "dri die". Only hearsay testimony was offered to establish what, if any, representations the Respondent made to the Cooleys to induce them to enter into the contracts. The work performed by the Respondent on the Cooleys' residence was not sufficient to provide the protection specified in the contracts, and in the case of the dry wood treatment, was unnecessary. The Cooleys' residence is constructed on a concrete slab. With such structures, the chlordane label, which governs use of the chemical, requires that all voids in hollow masonry units of the foundation be treated at the rate of at least one gallon per five linear feet of wall. It is thus necessary to drill each masonry block so that the chemical can be injected into it. Hollow masonry blocks were used in constructing the foundation of the Cooley house. Only one drill hole was made on the north side of the house into the masonry blocks, and none were made on the south side. If each of the masonry units had been treated as required, drill holes would have been placed at every eighteen inches along the foundation. This was not done, and the treatment for subterranean termite control was thus not in accordance with the label on the chemical, and was substandard. The treatment was inadequate to provide the Cooleys with the protection provided in the subterranean termite control contract. As to the dri die treatment at the Cooley house, the sort of treatment specified would not give the Cooleys any significant termite protection, since it would only protect them from dry wood termites in their attic. It is not a sort of treatment that is ordinarily performed. In order to be performed effectively, however, the dri die must be applied in accordance with the label which gives directions for its use. It is required that all wood surfaces be covered with the chemical at a recommended rate of one pound per one thousand square feet of area. At the Cooley residence, dri die was placed in the area, however, it was placed in a small pile in one part of the attic. It was not evenly spread, all wood surfaces were not covered, and insufficient chemical was utilized. The treatment specified would have provided the Cooleys only with dry wood termite prevention in the one part of the attic where the chemical was piled. The treatment was not in accordance with the label instructions, and was substandard. On or about September 27, 1977, the Respondent entered into a subterranean termite control contract and service agreement with Mr. and Mrs. Walter J. Delaney, for their residence in Lake Worth, Florida. The type of chemical specified for use in the contract was chlordane. The contract sets out the street address and zip code of the Delaneys' residence, but does not state the city. The address set out on the contract is sufficient to establish the location of the Delaneys' residence. Only hearsay evidence was offered at the final hearing to indicate what, if any, representations the Respondent made to the Delaneys in order to induce them to enter into the contract. The work performed by the Respondent on the Delaney home was insufficient to comport with the label instructions for application of chlordane, was substandard, and did not provide the Delaneys with the protection specified in the contract. The Delaneys' home is of concrete slab on-ground construction. The foundation is constructed of hollow masonry units. The voids in the hollow masonry units were not each treated as required on the chlordane label. Only one drill hole was made on the south side of the house and none were made on the north side. Several drill holes were made on the other sides of the house, however, four of them were fake, in other words they did not go all the way through the slab. On or about September 28, 1977, the Respondent entered into a subterranean termite control contract and service agreement with Mrs. Ann Sahlem, for her residence in West Palm Beach, Florida. The chemical specified for use in the contract was chlordane. Only hearsay evidence was offered to establish what representations, if any, were made by the Respondent to induce Mrs. Sahlem to enter into the contract. The work performed by the Respondent on the Sahlem residence did not comport with the label instructions for us of chlordane, was substandard, and was not sufficient to provide Mrs. Sahlem with the protection specified in the contract. The Sahlem residence is constructed on an on-ground concrete slab. The foundation is constructed of hollow masonry units. The voids in each of the hollow masonry units were not filled as required by the chlordane label. No drill holes were made on the west side of the home, and only one was made on the east side. On the north side of the home the holes were too far apart to treat all of the voids. The address set out on the Sahlem contract does not give the city of Mrs. Sahlem's residence although it does give the street address and zip code. The address as given is sufficient to identify the residence. On or about September 30, 1977, the Respondent entered into a subterranean termite control contract and service agreement, and a dry wood termite attic prevention treatment agreement with Mrs. Elizabeth A. Hughes. The chemical specified for use in the subterranean termite control contract was chlordane. The chemical specified in the dry wood termite prevention treatment was "dri die". The contracts were for Mrs. Hughes' residence in Lake Worth, Florida. The contracts do not specify the city of Mrs. Hughes' residence, although the street address and zip code are set out. The address as set out is sufficient to adequately identify the location of Mrs. Hughes' residence. No evidence was offered from which it could be concluded that the Respondent made any misrepresentations to Mrs. Hughes to induce her to enter into the contracts. The work performed under the contracts was, however, not in accordance with the label instructions for chlordane and dri die treatments, was substandard, and was not sufficient to provide the treatment specified in the contracts. Mrs. Hughes' home is constructed on a concrete slab. The foundation is constructed of hollow masonry units. The voids in the masonry units were not each treated as required on the chlordane directions. Furthermore, the drill holes were made three feet above the ground along one wall, and five feet above the ground along another wall, which would be insufficient to allow introduction of the chemicals below the concrete slab. The dri die was not distributed evenly over the attic wood surfaces as required on the dri die label. An insufficient amount of the chemical was utilized, and it was placed at one spot in the attic. The dri die treatment was unnecessary, and even if it had been advisable, it was not accomplished in a manner which would provide any useful protection to Mrs. Hughes. On or about October 27, 1977, the Respondent entered into a subterranean termite control contract and service agreement with Mrs.. Fred J. Schultz. The contract was for Mrs. Schultz's residence in Lake Worth, Florida. No direct evidence was offered to establish what, if any, representations were made by the Respondent to induce Mrs. Schultz to enter into the contract. It appears that the contract was solicited and performed by employees of the Respondent, and not by him directly, although he signed the contract and was responsible for the work. The chemical specified for use in the contract is Gold Crest, 72%, which is a trade name for chlordane. The work performed by the Respondent did not comport with the label instructions for use of chlordane, was substandard, and was not sufficient to provide the protection specified in the contract. The Sdchultz's home is constructed on piers with a crawl space. The instructions for application of chlordane contained in the label provide that in treating such structures it is necessary to either rod or dig a narrow trench to the top of the footing along the inside of the foundation walls, around all piers, sewers, pipes, and conduits; and to rod or dig a narrow trench to the top of the footing along the outside of the foundation wall. The Respondent, or his employees who performed the work at the Schultz residence did not make any trenches whatever, and did not even enter the crawl space below the Schultz's home in order to treat the piers. No evidence was presented from which it could be determined that the Respondent performed any dry wood termite treatment on the Schultz's residence. No evidence was presented from which it could be determined that any such work that may have been performed was done improperly, or that it was accomplished with or without a contract. On or about October 21, 1977, the Respondent entered into a subterranean termite control contract and service agreement with Mrs. Hulda Radke. The contract related to Mrs. Radke's residence in West Palm Beach, Florida. The chemical specified for use in the contract was chlordane. The Respondent also entered into contracts to perform home repairs for Mrs. Radke. No evidence was offered from which it could be concluded that the Respondent made any misrepresentations in order to induce Mrs. Radke to enter into the contract for termite control. The termite control work performed by the Respondent on Mrs. Radke's residence did not comport with the label instructions for use of chlordane, was substandard, and was not sufficient to provide the protection specified in the contract. Mrs. Radke's home was of pier constructions with a crawl space. No trenches were made, and the chemical was not trenched or rodded around each pier, and around each foundation wall. The chemical was broadcast along the top of the soil, but was not placed below the surface. The label instructions specify that a chemical should not be broadcast sprayed. On or about October 26, 1977 the Respondent entered into a subterranean termite control contract and service agreement with Mrs. Charles Thompson, for her residence in West Palm Beach, Florida. The chemical specified for use in the contract was chlordane. No direct evidence was offered to establish what, if any, representations were made by the Respondent to induce Mrs. Thompson to enter into the contract. The work performed by the Respondent on the Thompson residence did not comport with the label instructions for use of chlordane, was substandard, and was insufficient to provide the protection specified in the contract. The Thompson residence is of pier and crawl space construction. No trenches or rodding was done as specified on the chlordane label, and each pier was not treated. The address set out on the Thompson contract is insufficient. It gives only a street address, and no city or zip code. The Respondent testified that he used a process known as "long rodding" to treat under concrete slabs. Long rodding is a method whereby the end of a spray assembly is extended, and chemicals introduced under a slab. It is used typically where hollow masonry is not used in constructing the foundation. The process does not work well because the end of the rod cannot be adequately controlled. Even if this process were utilized, the chlordane label would required that all voids in hollow masonry units be treated. Failure to treat each of the voids would render the treatment substandard. It appears that since these incidents occurred, the Respondent has performed numerous termite control contracts in Hillsborough and Pinellas counties without complaint.
The Issue Whether Petitioner's site, Hughes Supply, Inc. located at 2920 Ford Street, Fort Myers, Lee County, Florida is eligible for restoration under Section 376.3072, Florida Statutes.
Findings Of Fact Upon consideration of the oral and documentary evidence adduced at the hearing, the following relevant findings of fact are made: Hughes is a Florida Corporation in good standing and authorized to do business in the State of Florida. The Department's facility no. 36-8519331 (the Facility), owned and operated by Hughes and the subject matter of this proceeding, is located at 2920 Ford Street, Ft. Myers, Lee County, Florida, and is a "Facility" as defined in Section 376.301(5), Florida Statutes. The Facility consisted of (a) two underground storage tanks (USTs), one 4000 gallons UST (gasoline tank) and one 8000 gallons UST (diesel tank), and (b) four monitoring well, and is a "petroleum storage system" as defined in Section 376.301(15), Florida Statutes. At all times material to this proceeding, Hughes held, and was the name insured of, an effective third party pollution liability insurance policy (No. FPL 7622685 - Renewal No. FPL 7621566) applicable to the Facility that was issued in accordance with, and qualified under, Section 376.3072, Florida Statutes. Hughes paid annual premiums exceeding $20,000.00 for the above insurance. In accordance with Sections 376.3072, Florida Statutes, and Chapter 17- 769, Florida Administrative Code; the Department issued to Hughes a Notice of Eligibility pertaining to the Facility and the third party pollution liability insurance referred to in Finding of Fact 4 above. Lee County, Florida has a local program approved by the Department pursuant to Section 376.3073, Florida Statutes, to provide for the administration of the Department's responsibilities under certain sections of Chapter 376, Florida Statutes. Diesel fuel was placed into the diesel tank at the Facility on August 12, 1991, and no diesel fuel has been placed in the diesel tank at the Facility since that date. On Thursday, August 29, 1991, a contractor bidding on the removal of the tanks detected free product in one of the monitoring wells at the Facility and told Larry Carman, the Warehouse Manager for Hughes. Mr. Carman told Phillip Ross, the Branch Manager for Hughes, who in turn informed Gene Kendall, the Operations Coordinator for Hughes. All of this occurred on August 29, 1991. On Friday, August 30, 1991, an employee of IT Corporation, acting upon the request of Gene Kendall, sampled the four monitoring wells at the Facility and found six inches of free product in the northwest monitoring well. On Tuesday, September 3, 1991, Fred Kendall discussed the discharge with Bill W. Johnson, Supervisor, Lee County Storage Tank Local Program. During this discussion, Johnson learned that the diesel tank had not been emptied. Johnson advised Kendall that the diesel tank had to be emptied of its product and placed out of service. On Tuesday, September 3, 1991 Mr. Kendall completed the Discharge Reporting Form (DRF) pertaining to the discharge and mailed the DRF to Johnson on September 4, 1991. The DRF indicated August 30, 1992, the day that IT Corporation confirmed the discharge, as the day of discovery of the discharge. The discharge was diesel fuel as indicated by the DRF and a "petroleum product" as defined in Section 376.3-1(14), Florida Statutes. The discharge reported in the DRF constitutes a "discharge" as defined in Section 376.301(4), Florida Statutes, which constitutes an "incident" as defined in Section 376.3072(2)(c), Florida Statutes, and as described in Rule 17-769.600, Florida Administrative Code. On Wednesday, September 4, 1991, Mr. Kendall also mailed a letter to Johnson stating Hughes' intent to seek restoration coverage for the Facility, pursuant to Policy No. FPL 762285, Renewal No. FPL 7621566. On September 13, 1991 when Hooper, Inspector for the Lee County Storage Tank Local Program, inspected the Facility the diesel tank contained a total of 39 5/8 inches of diesel and water, of which 4 3/4 inches was water. On September 16, 1991 when Hooper again inspected the Facility, the diesel tank contained a total of 36 1/2 inches of diesel and water, of which 4 1/2 inches was water. On this date, Hooper advised Hughes that the diesel tank had to be emptied of its product. The inspection report issued on September 16, 1991 by Hooper advised Hughes that the Facility was not in compliance with Chapter 17-761, Florida Administrative Code. On September 17, 1991, Hughes had the diesel tank emptied of all its product. Although Hughes was in the process of emptying the diesel tank by giving diesel away, at no time between August 30, 1991 and September 16, 1991 was the diesel tank completely empty of its product. Between August 30, 1991 and September 16, 1991 Hughes did not test the diesel tank to determine if the diesel tank was leaking and, if so, to pinpoint the source of the leak. There was no evidence that either the Department or Lee County Storage Tank Local Program personnel ever informed Hughes before September 16, 1991 that there was a time frame within which the diesel tank had to be emptied of all of its product, and placed out of service in order for Hughes to be in compliance and eligible for reimbursement for restoration under the FPLIRP. Likewise, Hughes did not request any information from the Department or the Lee County Local Program personnel concerning any time frames within which the diesel tank had to be tested for leaks or emptied of its contents to prevent any further discharge in order to be eligible for reimbursement for restoration under the FPLIRP. Between August 29, 1991 and September 17, 1991 Hughes bailed the monitoring wells at the Facility on a daily basis, removed the free product from the monitoring wells, and placed the free product in a sealed 55-gallon drum. When the discharge was discovered, Hughes made the decision to close the Facility by tank removal, and at this point did not intend to repair or replace the Facility. As a result of an inspection of the Facility by the Lee County Local Program personnel in May, 1991, Hughes was made aware that the Facility was not in compliance with Chapter 17-761, Florida Administrative Code, since the gasoline tank had not been used in over three years, and there had been no closure of the gasoline tank. This noncompliance with Chapter 17-761, Florida Administrative Code, concerning the gasoline tank was also a portion of the noncompliance report filed by Hooper on September 16, 1991. The gasoline tank comes within the definition of "unmaintained" as defined by Rule 17-761.200(2), Florida Administrative Code. Both the diesel tank and the gasoline tank were removed on October 28, 1991 by a Florida licensed storage tank system removal contractor, and the Facility permanently closed by IT Corporation on October 29, 1991. In December, 1991, Hughes filed a tank closure assessment report pertaining to the removal of the diesel and gasoline tanks from, and closure of, the Facility. The tank closure assessment report was prepared by IT Corporation upon a request made by Hughes to IT Corporation on September 3, 1991 for a tank closure assessment proposal which was submitted by IT Corporation to Hughes on September 4, 1991. In April or May, 1992, Hughes filed with Lee County a contamination assessment report prepared by IT Corporation pertaining to the removal of the USTs from and closure of the Facility. Subsequent to discovery of the discharge. Hughes has expended approximately $60,000.00 as of June 10, 1992, on the Facility in connection with the USTs. Site rehabilitation costs for the Facility have been estimated in a range of $220,000.00 to $245,000.00 as of June 10, 1992. In the early part of 1991 water was present in the diesel tank, and approximately six months before discovering the discharge in August, 1991, Hughes had the water pumped out of the diesel tank. Hughes gave no explanation for the presence of water in the diesel tank. Neither the Department nor the Lee County Local Program personnel were notified of this unexplained presence of water in the diesel tank.
Recommendation Based upon the foregoing findings of fact and conclusions of law, it is recommended that the Department enter a Final Order denying Hughes application for restoration coverage under the Florida Petroleum Liability Insurance and Restoration Program. DONE and RECOMMENDED this 24th day of September, 1992, at Tallahassee, Florida. WILLIAM R. CAVE, 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 24th day of September, 1992. APPENDIX TO RECOMMENDED ORDER IN CASE NO. 91-8334 The following constitutes my specific rulings, pursuant to Section 120.59(2), Florida Statutes, on all of the Proposed Findings of Fact submitted by the parties in this case. Rulings on Proposed Findings of Fact Submitted by the Petitioner The following proposed findings of fact are adopted in substance as modified in the Recommended Order. The number in parenthesis is the Finding(s) of Fact which so adopts the Proposed Finding(s) of Fact:(1); 2-3(2); 4-5(3); 6- 8(4); 9(5); 10(6); 11(8,9); 12(10,11); 14(15,22); 15(10); 16(19); 18(10); 19(13); 20-21(7); 22-23(24); 24(21); 25(17); 26-29(20); 30(15); 31(16); 32(22); 33(23); 35(23); 36(7); 37(23); 38(24); 39(25); 40(26); 41(27); 42-43(27); and 44(15,22). Proposed Findings of Fact 13, 17 and 34 are neither material nor relevant to the conclusion reached in the Recommended Order. Rulings on Proposed Findings of Fact Submitted by the Respondent 1. The following Proposed Findings of Fact are adopted in substance as modified in the Recommended Order. The number in parenthesis is the Finding(s) of Fact which so adopts the Proposed Finding(s) of Fact:1-2(2); 3(3); 4-6(5); 7(6); 8(22); 9(7); 10(8); 11(9); 12(10); 13-16(11); 17(12); 18(13): 19(18); 20(17); 21-22(14); 23-24(15); 25-26(28); 27(16); and 28(23). COPIES FURNISHED: Scott E. Wilt, Esquire Maguire, Voorhis and Wells 2 South Orange Plaza Orlando, Florida 32801 Brigette A. Ffolkes, Esquire Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Carol Browner, Secretary Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Daniel H. Thompson, Esquire General Counsel Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32399-2400
Findings Of Fact Respondent, George Sigountos, is a licensed real estate broker-salesman having been issued license number 0080704 with a principal place of business at 4338 First Street North, St. Petersburg, Florida. Respondent has been licensed in the State of Florida for approximately ten (10) years, having been a broker- salesman in New York for approximately twenty (20) years before coming to Florida. The Respondent Sigountos was at all material times employed by Century 21 Realty, 4922-38th Avenue North, St. Petersburg, Florida. On or before March, 1979, Mr. and Mrs. John Opal listed for sale by the Respondent a house on Benson Avenue which they then occupied. Subsequently, the Opals located another house which they desired to purchase at 5871-78th Avenue North, Pinellas Park, Florida. The Opals obtained financing to purchase the Pinellas Park home although they had not yet sold their Benson Avenue home and requested the Respondent's assistance to sell their original home. On or about March 4, 1979, the Respondent, through his broker, submitted a contract to the seller, Mr. Boyce, from the Opals, who contracted for the purchase of the Boyce home with a closing date on or before April 10, 1979. The bank where financing was arranged informed the involved title company that interest rates were scheduled to increase as of March 19, 1979. As a result of this information, the title company and parties attempted to arrange to close on March 16, 1979. The Opals attended this closing while Mr. Boyce did not. The Opals, however, executed all documents necessary on their part for the closing on March 16, 1979. Included was an agreement requiring the sellers to replace three (3) boards on the back porch because of previous termite damage. This was included as a result of a prior conversation between Mr. Opal and Mr. Boyce concerning termite damage. Mr. Sigountos did not prepare this document and it is unclear how it came into existence. No termite inspection report was filed until March 19, 1979. The Boyce home was not inspected for termites until March 19, 1979, at which time the exterminator, Hobelman Exterminating Service, Inc., left his inspection report with Mrs. Boyce which stated, in part:
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED: That a final order be entered by the Petitioner dismissing the complaint filed April 7, 1981 against the Respondent George Sigountos. DONE and ORDERED this 1st day of October, 1981, in Tallahassee, Florida. SHARYN L. SMITH Hearing Officer Division of Administrative Hearings 2009 Apalachee Parkway Tallahassee, Florida 32301 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 1st day of October, 1981. COPIES FURNISHED: Grover G. Freeman, Esquire Suite 410 4600 West Cypress Avenue Tampa, Florida 33607 Christopher C. Ferguson 5959 Central Avenue St. Petersburg, Florida 33710 C. B. Stafford, Executive Director Florida Real Estate Commision 400 West Robinson Street Post Office Box 1900 Orlando, Florida 32802
Findings Of Fact At all times pertinent to the charges, respondents have been licensed real estate salesmen and brokers. Respondent Ed Wasdin holds real estate salesman's license number 0341534. Respondent Betty L. Green 2/ held real estate salesman's license number 0341467 at the time of the alleged misconduct. She now is a licensed broker. Respondent Ester L. Turner holds broker's license number 0090375. At the time of the alleged misconduct, she was the qualifying broker for Ed Wasdin Realty, Inc., a registered corporate real estate broker. (Pretrial Stipulation; Testimony of Vann.) During the time in question, Mr. Wasdin also owned and operated Ed Wasdin and Son, Inc., a licensed construction company, where Ms. Green served as his full-time secretary and office manager. She worked as a real estate salesman for Ed Wasdin Realty, Inc., on a part-time basis. (Testimony of Vann; Pretrial Stipulation.) II. On November 11, 1980, Hank V. Mannheimer and his wife, Barbara, saw an Ed Wasdin Realty, Inc., "For Sale" sign in front of a house located at 721 West Crossway Road, Tallahassee, Florida. They called the telephone number listed on the "For Sale" sign and made an appointment for respondent Wasdin to show them the house. (Testimony of H. Mannheimer, B. Mannheimer.) Later that day, Mr. Wasdin took the Mannheimers on a tour of the house. They then returned to Mr. Wasdin's office where respondent Green, as his secretary, prepared a standard real estate contract on a form published by the Florida Association of Realtors. The Mannheimers signed the contract as purchasers, and Ed Wasdin signed on behalf of Ed Wasdin and Son, Inc., the seller. The Mannheimers also delivered a $1,000 earnest money deposit check made payable to the seller, Ed Wasdin and Son, Inc. (Testimony of H. Mannheimer, B. Mannheimer; P-10, R-5.) III. The real estate sales contract contained a "Termite Clause" granting the buyers the right to have the property inspected "to determine whether there is any active termite or wood destroying organisms in any improvement on said property, or any damage from prior termite or wood destroying organism to said improvements". (P-10.) During the morning of January 15, 1981, respondent Green, on behalf of the seller, Ed Wasdin and Son, Inc., telephoned Helms Exterminating, Inc., and ordered a termite inspection of the house. David Baker, a termite inspection, was sent to the house to conduct the inspection that same morning. (Testimony of Vann, Baker.) On inspecting the house, Mr. Baker found termite infestation and termite damage to the left front corner of the house. He then telephoned Ms. Green and told her that he had seen evidence of termites. He did not, however, tell her of any termite damage. She told him that she needed a "clear" termite report by that afternoon (since closing was scheduled for that afternoon or the next day) and authorized him to treat the house for termites. She did not speak to respondent Wasdin before authorizing the treatment. (Testimony of Vann.) Mr. Baker testified that he told Ms. Green of termite damage to the house and that she promised to repair the damage in order to get him to issue a "clear" termite report that day. Ms. Green denied that Mr. Baker told of the damage and denied that she promised to make repairs. The testimony of Ms. Green is more credible and worthy of belief than that of Mr. Baker, whose previous statements about this incident have been incomplete, 3/ untrue or contradictory. In his termite inspection report of January 15, 1981, Mr. Baker indicated that no active termite infestation or visible termite damage was observed--the first statement was, at best, incomplete, the second was false. After discovering the termite damage, Mrs. Mannheimer questioned him twice. The first time, he told her that he had only found ter-mites on January 15, 1981, and mentioned nothing of termite damage. Later, when questioned again, he stated that he had also found termite damage. Further, Ms. Green was not authorized to promise structural repairs to a residence, and it is unlikely that she would have made such a promise when she did not know the extent of the damage and had no way of knowing the cost of repair. The conflict in testimony is therefore resolved in Ms. Green's favor. (Testimony of Vann, Baker.) On January 15, 1981 after treating the residence for termites, Mr. Baker issued a termite inspection report indicating that he had observed no active termite infestation or visible damage. The report, on its face, indicated that it was to be mailed to Ed Wasdin Realty at 4432 Kensington Road, Tallahassee, Florida. The Mannheimers did not see the report until after the closing. (Testimony of Baker, Green; P-7.) IV. In negotiating for and purchasing the house from Ed Wasdin and Son, Inc., the Mannheimers believed, and had reasonable grounds to believe, that they were dealing with realtors associated with Ed Wasdin Realty, Inc. The house was advertised by an Ed Wasdin Realty, Inc., "For Sale" sign; they called the number listed on the sign, and Mr. Wasdin showed them the property; a contract identified with the Florida Association of Realtors was executed which contained an Employment of [Real Estate] Agent clause; 4/ both Ms. Green and Mr. Wasdin worked for both companies; and the offices of the Wasdin realty and construction companies were located in the same model home. Although the offices in the model home were separately marked as construction or realty company offices, the conference room (where the closing took place) was not marked as belonging to either. In actuality, the sale of the residence was not a transaction on the account of Ed Wasdin Realty, Inc. The house was not listed with the realty company; a commission was not promised or paid to the realty company; and the deposit was not placed in the realty company escrow account. (Testimony of Vann, H. Mannheimer, B. Mannheimer.) No evidence was presented to show that respondent Wasdin knew, or should have known, that the house in question had a termite infestation or termite damage. There is not a sufficient factual basis to impute such knowledge to him. Neither was any evidence presented to show that respondent Turner, qualifying broker for Ed Wasdin Realty, Inc., knew, or should have known, about the real estate transaction in question, including the termite infestation and damage. The evidence is insufficient to support a factual inference that Ms. Turner was negligent or derelict in her duty to supervise the realty company's operations. Although, in this case, a realty company's sign was used to advertise a property which was not listed with the company, the evidence does not show that this had ever happened before, that this was anything but an isolated mistake. The evidence is insufficient to support a finding that either Mr. Wasdin or Ms. Green saw the termite inspection report prior to closing, or affirmatively represented to the Mannheimers that no termites had been discovered during the January 15, 1981, termite inspection. 5/
Recommendation Based on the foregoing, it is RECOMMENDED: That the administrative complaint against the respondents be dismissed. DONE and RECOMMENDED this 15th day of October, 1982, in Tallahassee, Leon County, Florida. R. L. CALEEN, JR. Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32301 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 15th day of October, 1982.
