The Issue The issue to be resolved in this proceeding concerns whether an on-site sewage disposal system ("OSDS") construction permit should be issued to the Petitioner based upon the question of whether the property lies within the ten- year flood elevation of the Suwannee River, and if so, whether an appropriate system can be designed which will remove the system an adequate distance above the ten-year flood elevation level and thus comply with Rule 10D-6, Florida Administrative Code.
Findings Of Fact The Petitioner, Allyn B. Giffin, wishes to construct a vacation-type, part-time residence on his lot lying in Dixie County, Florida, in the vicinity of the Suwannee River. The subject proposed disposal system site lies at the Suwannee River Water Management District's river mile no. 50 and the ten-year flood elevation for that site and river mile is 21 feet above mean sea level ("MSL"). The property also lies within the "regulatory floodway" of the Suwannee River, as regulated by the Suwannee River Water Management District, and may require a "works of the district" permit. The elevation of the surface grade at the subject site is approximately 17 feet, 7 inches above MSL, as shown by the survey of Herbert Raker, a certified land surveyor. Because the property lies within the regulatory floodway of the Suwannee River, the pertinent rule requires that an engineer certify that any mounding of the system to raise it above the flood plain and the regulatory floodway level will not cause any alteration in the base flood level in that regulatory floodway of the Suwannee River. Aside from being within the regulatory floodway and beneath the ten- year flood elevation, the property is amenable to the type of subsurface septic tank and drain-field system proposed. The water table at the time of the site evaluation performed by Mr. Fross, of the Department was 72 inches below the existing surface grade. Based upon mottling in the soil, the estimated wet season water table was 42 to 48 inches below surface grade. Since the surface grade elevation at the proposed site is 17 feet, 7 inches, and the ten-year flood elevation is only 21 feet, it was shown to be quite feasible to elevate the septic tank system in a filled mound and mound pad, such that the entire system could be raised the required regulatory distance above the ten-year flood elevation level. Mr. Ted Biddy was accepted as an expert witness in the field of civil engineering with emphasis on sanitary system engineering. He testified on behalf of the Petitioner. Mr. Biddy has designed a sewage disposal system for the Petitioner, which design is admitted into evidence, which is designed to be constructed and to operate above the ten-year flood plain elevation found above. The system is called a "mounded balancing system". It will consist of a raised earthen pad with a raised mound on top of that pad containing the septic tank and drain-field system at an elevation sufficient to maintain the required regulatory differential between the bottom elevation of the drain-field trenches and the ten-year flood elevation. This system was established by Mr. Biddy's testimony to avoid any deleterious effect on public health and environmental safety which might be posed by the sewage effluent entering the system if it were placed below the existing surface grade of the lot in question. The water table elevation is at a minimum of 42 inches below the surface grade of the lot; and if the proposed system were raised above the ten- year flood elevation, the bottom grade of the drain-field trenches would be at least five feet above the surface grade elevation of the lot at the proposed installation site, plus an additional 42 inches above the wet season water table level established by the testimony of Mr. Fross, who did the site evaluation for the Department. It was thus established that such a mounded system will meet all of the parameters contained in Chapter 10D-6 and, specifically, Rules 10D- 6.044-049, Florida Administrative Code, the rules as they applied at the time of application and hearing. Dr. Richard Hunter, testifying as an expert witness for the Department, had not seen this design until the day of the hearing. Upon reviewing it, he agreed that if such a system were installed on the lot in question, it would meet all of HRS regulatory parameters and would be permittable, at least for a two-bedroom dwelling. Mr. Biddy further established that even with a three-bedroom dwelling, as originally proposed by the Petitioner, because it would only have intermittent, occasional use as a vacation retreat, the sewage loading would be substantially less than would the loading from a normal three-bedroom, full-time residence. It is also true, as found above, that the property is in the regulatory floodway of the Suwannee River. Because of this, the Department's rule requires that an engineer certify that installation of such a mounded system will not raise the base flood level of the so-called "100 year flood". This is a balancing system, as described by Mr. Biddy, which involves the removal of approximately 877 cubic yards of fill material from the site or that portion of the site which lies within the regulatory floodway. This is an amount exactly equal to the required amount of fill to construct the mounded system, as proposed. Because of this, the addition of the 877 cubic yards of fill material for the mounded system will not cause additional displacement and resulting raising of the base flood level. Thus, the Department's rule in this regard will be complied with. This is because the fill material will replace an equal amount of material excavated from the lot in that portion below the regulatory floodway level, which excavated material will be removed from the regulatory floodway entirely, thus resulting in no net gain of fill material within the regulatory floodway and, therefore, no additional displacement or elevating of the base flood level. In summary, it has been demonstrated that the addition of the mounded system, as proposed by the Petitioner through the testimony of Mr. Biddy, will not pose any environmental hazards or any potential harm to public health and safety and will result in the sewage disposal system proposed being installed at an elevation properly above the ten-year flood elevation of 21 feet above MSL. The Department has interpreted the Executive Order of the Governor, 90-14, purporting to prohibit such systems beneath the 10-year flood elevation of the Suwannee River as requiring strict prohibition of such systems in those circumstances when it carries out its enforcement of the requirements of Rule 10D-6.047(6), Florida Administrative Code, the rule applicable to this permit application, hearing and circumstances. Further, the Petitioner has agreed to limit the size of his dwelling to a two-bedroom dwelling instead of a three- bedroom dwelling.
Recommendation Having considered the foregoing Findings of Fact, Conclusions of Law, the evidence of record, the candor and demeanor of the witnesses, and the pleadings and arguments of the parties, it is therefore, RECOMMENDED that a Final Order be issued by the Department of Health and Rehabilitative Services granting a permit to the Petitioner, Allyn B. Giffin, authorizing the installation of an on-site sewage disposal system in the manner and under the conditions enumerated in the above Findings of Fact and Conclusions of Law. DONE AND ENTERED this 29 day of May, 1992, in Tallahassee, Leon County, Florida. P. MICHAEL RUFF Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, FL 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this day of May, 1992. APPENDIX TO RECOMMENDED ORDER IN CASE NO. 90-4424 Petitioner's Proposed Findings of Fact 1-7. Accepted. Respondent's Proposed Findings of Fact The Respondent submitted no proposed findings of facts. COPIES FURNISHED: Sam Power, Agency Clerk Department of HRS 1323 Winewood Boulevard Tallahassee, FL 32399-0700 John Slye, Esq. General Counsel Department of HRS 1323 Winewood Boulevard Tallahassee, FL 32399-0700 Frances S. Childers, Esq. HRS District 3 Legal Office 1000 N.E. 16th Avenue Gainesville, FL 32609 Conrad C. Bishop, Jr., Esq. P.O. Box 167 411 N. Washington Street Perry, FL 32347
Findings Of Fact The Petitioners, Jerome Silcox and Shannon Silcox have applied for an OSDS permit seeking authorization to install a septic tank and drainfield sewage treatment and disposal system on their lots 311 and 312 of Suwannee Shores Edition, NO. 2 subdivision. The property generally is located in the town of Suwannee, Florida in Dixie County near the point where the Suwannee River empties into the Gulf of Mexico. The property is located at "river mile 3." Prior to purchasing the property the applicants had made inquiry with the Department of Health and Rehabilitative Services (Department)(HRS) concerning the acceptability of using an existing septic tank and drainfield system already on the property. That inquiry was made on or about June 29, 1989. A Department representative for Dixie County, inspected the site and issued an opinion to the Petitioners that the existing septic tank was adequate to accommodate a one bedroom residence. The Petitioner subsequently decided to construct a residence on the property for a residence containing approximately three bedrooms. Accordingly they made application through the Dixie County Health Department of HRS for a permit to authorize installation of a 750 gallon septic tank and drainfield treatment and disposal system for the property. The environmental health officer for the Dixie County Health Department of HRS visited the property on March 15, 1990. After examination of the property the health officer determined that the construction of a septic tank system employing a three foot mound above the natural surface grade of the property would be adequate to serve the residence proposed to be constructed on the lots and would comport with the permitting rules, in his opinion. The health officer required that the applicants submit a survey identifying the elevation of their property at the installation site and required them to secure a determination from the Suwannee River Water Management District (District) concerning the elevation of the ten-year flood plain with respect to the property and particularly the installation site. The applicants obtained a survey of the property by Hubert H. Raker, a registered land surveyor. He established the benchmark elevation for the installation site and, based upon that elevation, determined that the actual elevation of the surface grade of the property at the installation site was 4.98 feet above mean sea level (MSL). On or about March 7, 1990 the applicants received a "flood elevation information report" from the District. That report stated that the ten-year flood elevation of the Suwannee River at the installation site was 17 feet above MSL. The report also stated that the property was not located within the regulatory floodway of the Suwannee River. The report of the District concerning flood elevations as well as the elevation survey by Mr. Raker were submitted to the Department's Dixie County office. Thereafter it was reviewed by a different environmental health officer and ultimately the environmental health director for the Department issued a denial letter. The letter denied the permit to install the OSDS because "the bottom surface of the drainfield trench shall not be subject to flooding based' on ten-year flood elevations". Thus the Department takes the position that the bottom surface of the drainfield trench or trenches in the system, as proposed, would be beneath the ten-year flood elevation and therefore in contravention of Rule 10D-6.047(6), Florida Administrative Code. The health officer also opined that the Governor's Executive Order 90-14 had the effect of prohibiting any construction of mounded septic tank and drainfield systems within the ten-year flood elevation as well. Petitioner's property has a benchmark elevation of 5.48 feet above MSL and the actual elevation of the grade surface is 4.98 feet above MSL. The soils characterizing the proposed installation site are organic soils for six inches beneath the surface and then brown, fine sand down to twelve inches. At twelve inches beneath the surface is an impermeable barrier of lime rock. There was no "mottling" or evidence of damp soils, that relates to the possible level of the wet season water table, above that lime rock strata. There was no other indicia of the water table above that lime rock strata. Consequently, the wet season and normal water table levels are beneath the lime rock strata which occurs twelve inches subsurface. The Petitioners proposed, and Mr. Fross acknowledged iii his testimony, that mounding the system proposed to be installed, by placing it in a filled mound of at least 36 inches height above the existing grade level of the lot would be environmentally preferable to installing a septic tank and drainfield system in the natural surface and subsurface of the lot in question, in terms of better protecting the ground and surface waters in the vicinity of the site from degradation through improperly treated sewage effluent. Since the water table elevation is beneath the lime rock strata, which is twelve inches subsurface, if a 36 inch mound were installed on the site for the drainfield trenches or absorption beds, and if appropriate "slight or moderately limited" soils were used in the construction of the mound, a sufficient spatial differential of slight to moderate limited soils would exist for the required 24 inches beneath the bottom surface of the drainfield trenches and above the water table level. Thus a mounded system is a possible alternative, however, the Petitioners did not adduce sufficient evidence of technical data to show that such a system would indeed work properly in terms of having a sufficient, unobstructed land surface surrounding the mound in order to comport with the regulatory requirements in Chapter 10D-6, Florida Administrative Code. However, from the standpoint of having sufficient slight to moderate limited soils beneath the drainfield trenches if such a mound were used, assuming that the appropriate soils were used in construction of the mound and assuming that sufficient lot space is available to include the septic tank itself in the mound at an appropriate height above the existing grade and the limerock strata, it would appear that such a system would work adequately so as to protect the public health, the health of the applicants themselves and to prevent degradation of ground or surface waters. The technical details necessary to show that such a system would correctly operate on these lots, however, was not placed into evidence. There is no dispute, however, that the lot size involved is adequate and the site plan in evidence as Petitioner's exhibit 3 indicates that there is sufficient overall surface space on the two lots in question to accommodate such a mounded system. Thus, if the ten-year flood elevation obstacle to permitting did not exist it would seem that a mounded system could be designed and constructed so as to meet the regulatory requirements of Chapter 372, Florida Statutes and Chapter 10D-6, Florida Administrative Code. The Petitioners also suggest that an aerobic septic tank-drainfield system might effectively treat and dispose of the sewage effluent at issue in a manner so as to protect public health and the ground and surface waters involved. An aerobic system functions differently from the normal OSDS system, which is anaerobic in nature, because it functions with aerobic bacteria which require oxygen in order to grow and digest and convert sewage effluent into bacteriologically safe effluent. An aerobic system requires the use of an electric motor and pump system in order to force air into the septic tank so that aerobic bacteria can perform their function. The problem with aerobic systems, although they more effectively treat sewage effluent through a septic tank and drainfield system, is that they are subject to mechanical failure and monitoring the mechanical efficiency and proper operation of such a system can be a problem. If the mechanical motor and pump system malfunction, the system will still function as a normal septic tank and drainfield system and thus remove effluent from the residence so that the homeowner will not necessarily have to immediately effect repairs. This can cause inadequately treated effluent to be dispersed into the ground or surface waters or on the surface of the lot, posing a health hazard and potential degradation of ground or surface waters. The evidence offered by Petitioners does not establish how such a system could be made to work effectively and no detailed technical evidence was offered by Petitioners to show what type of such an aerobic system could be installed which would effectively operate at the installation site and under the circumstances where it might be proposed to be used. This is a possible alternative to the conventional subterranean system at issue but would require further evidence, which was not adduced, to show that it can be safely and effectively employed at the site in question. In any event, however, the proposed installation site was not shown to be above the ten-year flood elevation of the Suwannee River. Because of this, neither a mounded system nor an aerobic system has been shown to be capable of being installed at the site and comporting with the rules contained in Chapter 10D-6, Florida Administrative Code and, particularly, Rule 10D-6.047(6), Florida Administrative Code. That is, with either system in mind, it has not been demonstrated that the bottom of the drainfield trenches or absorption beds at issue, as envisioned in this rule, would be above the ten-year flood elevation. A report prepared by the Suwannee River Water Management District and submitted by the applicants with their application shows a ten-year flood elevation of 17 feet above MSL. The Petitioners adduced the testimony of Mr. William Pierce, an engineer with the District, in their case in chief. Mr. Pierce testified that this 17 foot elevation is indeed the elevation shown in the data contained in the computer model generated and maintained by the District. The information by which this computer model was designed and which resulted in the 17 foot elevation comes from U.S. Army Corps of Engineer data along with data from the Federal Emergency Management Agency (FEMA), the Hydraulic Engineering Center in Davis, California, the U.S. Geological Survey and the Oceanic and Atmosphere Administration. The storm surge component of that ten-year flood elevation came from data generated by a privately contracted study prepared for the federal agencies and supplied to the District. Through the testimony of Mr. Pierce, the Petitioners established substantial doubt as to the accuracy of the 17 foot ten-year flood elevation. Mr. Pierce established that the ten- year flood elevation figure for the Suwannee River decreases as it is measured from the waters of the Suwannee River many miles upstream from the town of Suwannee, when measurement proceeds in a downstream direction. Thus, for instance, the ten-year flood elevation at the town of White Springs, at river mile 177, upstream from the coast, is approximately 81 feet. The ten-year flood elevation at the location known as "Wilcox" some 33 miles above the confluence of the Suwannee River with the Gulf of Mexico is approximately 16 feet. This decreasing ten-year flood elevation figure, as progressively measured downstream toward the coast, is a natural incident to the fact that the elevation of the land surrounding the Suwannee River declines in elevation above sea level as the land elevation is measured going in a downstream or coastward direction. That is, as the surrounding upland elevation declines the waters of the Suwannee River, in a flood event, can spread outward from its channel over a wider area, due to being less confined by higher upland elevations, which results in the flood elevations being lower. Thus one would logically expect that if the ten-year flood elevation at Wilcox, 33 miles upstream, is 16 feet above MSL, then the flood elevation at the town of Suwannee, where the lots in question lie, at river mile 3, would be substantially lower. However, in the District's flood elevation data the element of "storm surge" is additively calculated into the ten-year flood elevation figure. This is designed to take into account surges caused by storms pushing water inland on the Gulf Coast where the Suwannee River makes its confluence with the Gulf of Mexico. According to the District's data and Mr. Pierce's testimony this would effectively raise the actual ten-year flood elevation level. The problem with the 17 foot, ten-year flood elevation figure is that Mr. Pierce was unable, in his testimony, to show how and why the storm surge closely correlates with the river flood stage to produce a 17 foot ten-year flood elevation at river mile 3 of the Suwannee River where these lots lie. Moreover, he was unable to establish in his testimony how the District's flood elevation calculations and figures take into account any probability of the storm surge occurring simultaneously with a ten-year flood event for the Suwannee River or what they probability might be. Thus the Petitioner's evidence casts substantial doubt that the 17 foot, ten-year flood elevation figure is accurate and comports with logic. Thus it can be found herein that the 17 foot ten- year flood elevation figure has not been shown to be accurate. The problem remains however that the Petitioner must establish that the installation site in question does not occur beneath the ten-year flood elevation of the Suwannee River. The Petitioner adduced no evidence to establish what the ten-year flood elevation might actually be nor that the installation site lies above that elevation. Consequently, sufficient proof has not been established to comport with the requirement that the bottom surface of the drainfield trenches or absorption beds lies above the ten-year flood elevation so as to show that the installation site is not subject to inundation. The Petitioner did not formally apply for a variance from the permitting statute and rules, upon having the permit application initially denied by the Department. This is because the Department advised them, in effect, that it would be futile to apply for a variance and to avail themselves of the Department's informal variance procedure because of the effect of the Governor's Executive Order 90-14, entered on January 17, 1990. That Executive Order incorporated recommendation 36 of the "Suwannee River Task Force" report, which recommended that all OSDS installations lying beneath the ten-year flood elevation of the Suwannee River be prohibited and that grant of any permits for OSDS installations be done in strict compliance with pertinent permitting statutes and rules. According to the Department, the Executive Order, in effect, directed that all on- site sewage disposal systems beneath the ten-year flood elevation of the Suwannee River be prohibited. The Department thus takes the position that the entry of that Executive Order took away its discretion to entertain any variance applications for properties lying beneath the ten-year flood elevation and advised the Petitioners to avail themselves of the formal hearing procedure before the Division of Administrative Hearings rather than seek a variance through the Department's own internal variance procedure. In any event, and somewhat parenthetically, it should be pointed out that although the Petitioners will definitely experience a hardship if a permit or variance is not granted, because of the money expended to purchase the lot which will be largely unusable without the ability to establish a residence thereon by installing an OSDS system, it has not been proven that no reasonable alternatives exist to the installation of a conventional OSDS subterranean type system on the property. The Petitioner proposed installation of a mounded system, which has some promise as a reasonable alternative system, although sufficient evidence was not adduced to establish that such a system would adequately treat and dispose of the effluent in question without causing a public health hazard or degradation of ground and surface waters, as discussed above. Nor was sufficient evidence of a lack of adverse environmental effects, in this regard, as to establish any other type of reasonable alternative approach to treatment and disposal of the expected sewage effluent. Thus one element of the variance criteria cited below has not been met. It has neither been established that the installation of an OSDS system of the conventional subterranean type nor any other type would not have an adverse impact on public health or would not cause degradation of the ground or surface water involved. Thus, to the extent the question of entitlement of a variance can be entertained in this proceeding, the elements required for the grant of a variance have not been established by Petitioner's proof, although there is a substantial likelihood that in a variance proceeding, with appropriate proof, the efficacy of the installation of a mounded system in relation to the requirements of the Department's rules could be established, aside from the question of the ten-year flood elevation.
Recommendation It is, accordingly, RECOMMENDED: That a final order be entered denying the application of the Petitioners for an onsite sewage disposal system permit. DONE and ENTERED this 31st day of December, 1990, in Tallahassee, Florida. P. MICHAEL RUFF Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, FL 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 3rd day of January, 1991. APPENDIX Petitioner's Proposed Findings of Fact: 1 - 15 Accepted. Rejected as irrelevant since this is not a rule challenge proceeding pursuant to Section 120.56, Florida Statutes. - 29 Accepted. Respondent's Proposed Findings of Fact: 1 - 4 Accepted. Rejected as not in accordance with the preponderant evidence and as subordinate to the Hearing Officer's findings of fact on this subject matter. Accepted. - 13 Accepted. 14 Rejected as subordinate to the Hearing Officer's findings of fact and as not entirely in accordance with the preponderant evidence. COPIES FURNISHED: Robert Moeller, Esquire P.O. Drawer 1419 Cross City, FL 32628 Frances Childers, Esquire HRS District 3 Legal Office 1000 N.E. 16th Avenue Gainesville, FL 32609 Sam Power, Agency Clerk Department of Health and Rehabilitative Services 1323 Winewood Blvd. Tallahassee, FL 32399-0700 Linda Harris, General Counsel Department of Health and Rehabilitative Services 1323 Winewood Blvd. Tallahassee, FL 32399-0700
The Issue The issue is whether Petitioner's request for a variance from agency rules governing daily domestic sewage flow so as to authorize an increase in the number of seats for his restaurant located in Howey in the Hills, Florida, should be approved.
Findings Of Fact Based upon all of the evidence, the following findings of fact are determined: Petitioner, Fletcher C. Bishop, Jr., is the owner of a parcel of property located at Lot 22, Block C-2, Lakeshore Heights Subdivision, 102 South Palm Avenue, Howey in the Hills, Florida. The property consists of .0946 acre, or approximately one-tenth of an acre, and is one of several parcels located in Block C-2. Since January 1997, the property has been leased to Robert P. Jencic, who now operates a pizza restaurant on the premises known as Hungry Howies Pizza Shop. According to Jencic, he has a contract to purchase the property from Bishop at the end of his lease, or on March 1, 1998. Whether the property was actually purchased by Jencic on that date is not of record. Lakeshore Heights Subdivision is not served by a central wastewater treatment system; rather, each lot is served by a septic tank and drainfield system. Lot 22 adjoins several other commercial or business establishments situated on Lots 20, 21, 23, and 23A in the western half of Block C-2, and all share a common drainfield easement located to the rear of the lots. Except for Lot 20, all lots have tied into the drainfield and now use the easement for waste disposal purposes. Because they share a common easement, each lot has been allocated a portion of the easement for its respective septic tank and drainfield. In Petitioner's case, he has been allocated approximately 990 square feet. After Jencic signed a commitment in January 1997 to lease and purchase the property, he made extensive renovations in order to convert the property to a restaurant. On or about February 20, 1997, Jencic met with a representative of the Lake County Health Department, an agency under the direction and control of Respondent, Department of Health (Department). At that time, Jencic filed an application for a site evaluation concerning the replacement of the existing onsite sewage disposal system. The application noted that he intended to operate a pizza restaurant with 56 proposed seats. On February 21, 1997, a site evaluation was conducted by Robin Gutting, a Lake County Department of Health environmental supervisor. According to her report [t]he property size of 4120 square feet with available central water will allow a maximum 236 gallons of sewage flow per day . . . This will allow a 12 seat restaurant using single service articles and operating less than 16 hours per day. . . The size of the Onsite Sewage Treatment and Disposal System would be a minimum 900 gallon tank with 197 square feet of drainfield trench configuration. (emphasis added) Jancic received a copy of the report on or about March 12, 1997, and it clearly conveyed to him the fact that he could operate no more than 12 seats in his restaurant due to sewage flow limitations on his property. Despite being on notice that the restaurant would be limited to only 12 seats due to the lot flow restrictions, on March 19, 1997, Jencic filed an application with the Lake County Health Department for a construction permit to replace the existing septic tank with a 900 gallon septic tank, install a 900 gallon grease trap, and utilize a 197 square-foot primary drainfield and a 200 square-foot bed system. The application indicated that Jencic intended to operate a restaurant "for 12 seats, single service, open less than 16 hours per day." On May 28, 1997, Jencic's application was approved for "12 seats, single service, open less than 16 hours per day." After installing the new tank and grease trap, Jencic began restaurant operations subject to the above restrictions. After operating his pizza restaurant for a short period of time, Jencic determined that he could generate a profit only if the restaurant could be expanded to allow more seats, and he could use china and silverware (full service articles) rather than single service articles (throwaway utensils). To do this, however, he would need a larger sewage treatment system. By letter dated November 9, 1997, Jencic requested a variance from various Department standards for onsite sewage treatment and disposal systems so as to "increase the seating from 12 seats to a maximum of 36 seats and [authorize] the use of china, silverware, and dishes." Although the letter does not refer to any rules, the Department has treated the letter as seeking a variance from three of its rules found in Part I, Chapter 64E-6, Florida Administrative Code. First, Rule 64E-6.001(4)(c), Florida Administrative Code, provides that an establishment cannot exceed the lot flow allowances authorized under Rule 64E-6.005(7)(c), Florida Administrative Code. If the seating capacity in the restaurant were increased, Jencic would exceed the lot flow allowances in violation of this rule. Second, Rule 64E-6.005(7)(b), Florida Administrative Code, prescribes the manner in which a determination of lot densities shall be made. Among other things, daily sewage flow cannot exceed an average of 2,500 gallons per day per acre. The easement which Petitioner shares with other lots is far less than an acre, even counting the space allocated to the adjoining lots. Finally, Rule 64E-6.008(1), Florida Administrative Code, provides that minimum design flows for systems serving a structure shall be based on the estimated daily sewage flow as determined by Table I of the rule. That table specifies an estimated daily sewage flow of 20 gallons per seat for restaurants using single service articles only and operating less than 16 hours per day. Therefore, a 12-seat restaurant with those operating characteristics would require a system that could handle at least 240 gallons of sewage flow per day. The table further provides that a restaurant operating 16 hours or less per day with full service will generate an estimated sewage flow of 40 gallons per seat. Thus, a restaurant with up to 36 seats, as Jencic has requested, would require a system handling at least 1,440 gallons of sewage flow per day. In order to qualify for a variance, an applicant must show that (a) the hardship was not caused intentionally by the action of the applicant; (b) no reasonable alternative exists for the treatment of the sewage; and (c) the discharge from the onsite sewage treatment and disposal system will not adversely affect the health of the applicant or significantly degrade the groundwater or surface waters. In its letter denying the variance, the Department asserts that Jancic has failed to show that items (a) and (c) have been satisfied. Jencic, who recently immigrated to this country, will suffer considerable financial hardship if the request for a variance is denied. Indeed, he demonstrated at hearing that his life savings have been invested in the restaurant, and his parents have placed a substantial mortgage on their property to assist him in his endeavor. If he does not purchase the property as required by his contract, he will be forced to restore the property to its original condition at great expense. In short, given his investment in renovations and equipment, unless the restaurant is expanded, he fears he must file for bankruptcy. Both parties agree that Jancic will suffer a hardship if the variance is not approved. However, Jancic was aware of the lot flow limitations before he made application to replace the existing septic tank in March 1997, and well before he began operating the restaurant in May 1997. Unfortunately, then, it must be found that the hardship was intentionally created by Jencic's own actions. If the variance were approved, it would result in a much larger amount of sewage being discharged into the easement, which could not handle that amount of flow. This in turn could cause the system to fail, thus creating a sanitary nuisance and the leaching of sewage into the groundwater. In this respect, Jancic has failed to show that the discharge will not adversely affect the health of the applicant or significantly degrade the groundwater or surface waters. Jencic offered into evidence a summary of his water usage during a representative period in 1997. That document indicated that metered water usage was approximately 3,000 to 4,000 gallons per month, even when he temporarily (and without authority) expanded his restaurant to 24 seats during a recent two-month period to test water consumption at the higher seating capacity. However, because the sewage strength of a restaurant is far greater than that of a residence, a sewage system must be sized on estimated waste flow, and not metered water flow rates. Therefore, the fact that Jancic's monthly metered water usage is less than 4,000 gallons is not relevant to a determination of the issues. The same finding must be made with respect to Jancic's well-intentioned efforts to decrease water flow by installing high pressure toilets and timed spring systems on his hand sinks. Jencic also requested that he be allowed "spike time" during the hours of 11:30 a.m. to 1:00 p.m. and 6:00 p.m. to 7:30 p.m., which are his peak hours of the day. In other words, the undersigned assumes that he is asking that consideration be given to the fact that he has virtually no business during the other hours of the working day, and that the flow during the peak hours alone would not be excessive on a daily basis. However, the Department's rules are calculated to maximum usage, and thus a "spike" allowance is not allowed.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Health enter a Final Order denying Petitioner's request for a variance. DONE AND ENTERED this 11th day of March, 1998, in Tallahassee, Leon County, Florida. DONALD R. ALEXANDER 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 Filed with the Clerk of the Division of Administrative Hearings this 11th day of March, 1998. COPIES FURNISHED: Angela T. Hall, Agency Clerk Department of Health Building 6, Room 102 1317 Winewood Boulevard Tallahassee, Florida 32399-0700 Robert P. Jencic 102 South Palm Avenue Howey in the Hills, Florida 34737 Marya Reynolds Latson, Esquire Post Office Box 2408 Ocala, Florida 34478 James Hardin Peterson, III, Esquire Department of Health Building 6, Room 102 1317 Winewood Boulevard Tallahassee, Florida 32399-0700
Findings Of Fact Upon consideration of the oral and documentary evidence in the record, as well as the pleadings and joint prehearing stipulation, the following relevant facts are found: Cast-Crete owns and operates a concrete batch plant in Hillsborough County, Florida, and manufactures concrete products such as reinforced beams, lintels, seals and drainage structures on the property. The plant is located on the west side of State Road 579, 3/4 mile north of Interstate 4, Section 28, Township 28 South, Range 20 East. The concrete products are manufactured in various forms which are laid out over a large portion of Cast-Crete's property. Lubricating oils are utilized to facilitate the removal of the product from the confining forms. During this process some of the lubricating oil is spilled onto the ground. Also, cleaning solutions containing degreasers are utilized to wash the concrete trucks eight to ten times per day. This solution ends up on the ground. Aggregate limerock (crushed limestone) is used in the concrete formulation process and is stored in large piles on the property. In order to contain the dust, water is sprayed on the aggregate piles 24 hours a day. The wash water from the continuous process of wetting the aggregate, other waste water and some stormwater is channeled through the property and into a settling pond in the northwest corner of Cast-Crete's property. This pond discharges continuously off the property by way of a concrete flume into a county maintained ditch. Water in the ditch travels in a westerly direction approximately 200 to 300 yards before it passes under Black Dairy Road, where the watercourse deepens and widens. The ditch discharges into a marshy area which drains into Six Mile Creek and other water bodies. The pond at the northwest corner of Cast-Crete's property is equipped with a metal skimming device to remove oils and greases floating on the surface of the pond. Nevertheless, it is estimated that approximately 100 gallons of oil per year are discharged by Cast-Crete. Oil and grease in the outflow water is occasionally above 5 mg/L. Oil and grease layers have been observed on water at both Black Dairy Road and Six Mile Creek, probably resulting from road run- off. Approximately 90 percent of the water discharged from the property is a result of the wetting or washdown of the aggregate piles. The excess water which comes from the aggregate piles is laden with dissolved limestone, lime and limestone particles. This limestone dust raises the pH level of the water. Because of the continued wetting of the aggregate, water flows through the settling ponds and off of Cast-Crete's property at a rate of approximately 4.8 gallons per minute, or 7,200 gallons per day or 2.5 million gallons per year. During a rain event, the flow increases markedly. Except during times of heavy rainfall, water flowing from the respondent's property provides a thin stream of water in the drainage ditch approximately six inches wide and several inches deep. The pH of the wastewater from Cast-Crete's discharge flume is between 10 and 11 units. During high volume flows, the pH remains at or above 11 units. An increase of one unit of pH in the wastewater means that the wastewater has become 10 times more basic, since pH is measured on a logarithmic scale. The natural background of unaffected streams in the area of and in the same watershed as the Cast-Crete property is less than 8.5 units. Specific conductance or conductivity is the measure of free ions in the water. Typical conductivity readings from other water bodies in Hillsborough County range between 50 and 330 micromhos per centimeter. The specific conductance of Cast-Crete's wastewater ranges from 898 to 2000 micromhos per centimeter. This is due to the presence of calcium carbonate and calcium hydroxide in the water. Blue-green algae is the dominant plant species in the ditch between the Cast-Crete discharge flume and the first 150 meters of the ditch. A biological survey of the ditch system indicates that the diversity of species east of Black Dairy Road is low. This is attributable in part to the high pH of the wastewater. The low diversity can also be attributed to the fact that the County maintains the ditch by use of a dragline on an annual basis. Background samples from a site within one mile to the northwest of the Cast-Crete property were taken. The site (a stream passing under Williams Road) is an appropriate place to take background samples because the water there is unaffected by Cast-Crete's discharge or other man-induced conditions. The pH background sample ranged from 4.6 units to 5.1 units. The specific conductance background samples ranged from 70 to 100 micromhos per centimeter. Samples taken from a site potentially impacted by Cast-Crete's discharge showed a pH level of from 6.35 to 7.37 units and specific conductance of from 592 to 670 micromhos per centimeter. Cast-Crete discharges water from its concrete plants operation without a permit from the DER.
Recommendation Based upon the findings of fact and conclusions of law recited herein, it is RECOMMENDED that a Final Order be entered requiring respondent to submit a complete application for an industrial wastewater permit within thirty (30) days, and that, if it fails to do so, it cease discharging wastewater from its property until such time as an appropriately valid permit is issued by the DER. Respectfully submitted and entered this 3rd day of May, 1985, in Tallahassee, Florida. DIANE D. TREMOR 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 3rd day of May, 1985. COPIES FURNISHED: David K. Thulman Assistant General Counsel Department of Environmental Regulation Twin Towers Office Building Blairstone Road Tallahassee, FL 32301 W. DeHart Ayala, Jr. 501 E. Jackson Street Suite 200 Tampa, FL 33602 Victoria Tschinkel Secretary Department of Environmental Regulation Twin Towers Office Building 2600 Blairstone Road Tallahassee, FL 32301 ================================================================= AGENCY FINAL ORDER ================================================================= STATE OF FLORIDA DEPARTMENT OF ENVIRONMENTAL REGULATION DEPARTMENT OF ENVIRONMENTAL REGULATION, STATE OF FLORIDA, Petitioner, vs. CASE NO. 84-1647 CAST-CRETE CORPORATION OF FLORIDA Respondent. /
The Issue The issues in this case concern the entitlement of Petitioners to the grant of a variance for the purpose of installation of an onsite sewage disposal system on property located in Dixie County, Florida. See Section 381.272, Florida Statutes and Chapter 10D-6, Florida Administrative Code.
Findings Of Fact On April 27, 1989, the property which is at issue was deeded over to Diane H. and Charles A. Miller. The property is located in Dixie County, Florida, and contains 0.377 acres. On Nay 23, 1989, Petitioners were granted an easement for purposes of ingress and egress to and from the property. On May 4, 1989, under the signature of Diane H. Miller, a Petitioner in this case, an application was made for onsite sewage disposal at the aforementioned property. A copy of that application form may be found as Petitioners' exhibit No. 3 admitted into evidence. It states that this application is for a new system at lot No. 2, southwest corner, New Pine Landing Subdivision. Reference is also made to the directions to the property and suggestion that the property is located behind Nevin Kean Public Park [sic]. The warranty deed, a copy of which may be found as Petitioners' exhibit No. 1 admitted into evidence, describes the fact that the property is adjacent to Nevin Keen Public Park. The application form points out that this is a new system which is by type of residence "MH." It would contain two bedrooms and a heated or cooled area which is 12 feet by 60 feet. Also attached in Petitioners' exhibit No. 1 is a paper which purports to establish the benchmark elevation of the property as part of what that paper describes as the unrecorded subdivision at New Pine Landing. It speaks in terms of an elevation of 11.36 feet as allegedly surveyed by Herbert H. Raker. That information is hearsay and may not be used for purposes of fact finding in establishing the true elevation in an instance where Herbert H. Raker has not provided this explanation. See Section 120.58, Florida Statutes. As a consequence, there being no other explanation of the elevation, it is unknown. To the extent that it is accepted that there exists a New Pine Landing Subdivision, of which the Miller property is a part, evidence was not presented at the hearing which would establish the date upon which it was platted. Copies of the warranty deed and easement which were admitted into evidence do not indicate that the property is in New Pine Landing Subdivision, nor do they describe the date upon which the subdivision was platted, if ever. From the proof submitted, especially the warranty deed and easement, it does not appear that the parcel in question is part of a recorded subdivision. This coincides with representations by Ms. Virginia Sessions, whose daughter is Diane Miller. Ms. Sessions speaks in terms of this being an unrecorded subdivision and Petitioners' exhibit No. 4 admitted into evidence directed to Jermone Blake of the Dixie Public Health Unit on stationery of Suwannee River Water Management District refers to this location as New Pine Landing. Under the circumstances it is accepted that this parcel lies within an unrecorded subdivision known as New Pine Landing. There was a period of time during which the applicants did not receive a response from Respondent concerning the request for a permit to install the onsite sewage disposal system. Ms. Sessions testified that her daughter made a phone call to the Respondent to determine the status of the application and that the daughter reported that someone affiliated with Respondent said that Respondent would be getting back in touch with the applicants. This report by Mrs. Sessions of her daughter's remarks concerning a purported conversation between the daughter and the Respondent's employee is hearsay and may not be used to decide whether in fact there was a communication between the daughter and the Respondent. See Section 120.58, Florida Statutes. In any event, Mr. Blake communicated with Mrs. Sessions and informed Mrs. Sessions that the Petitioners would not be given a permit for installation of an onsite sewage disposal system and would need to file a request for variance from the requirements to obtain permission to install the onsite sewage disposal system. In furtherance of that instruction, the appropriate fee was paid and a form executed by Mrs. Sessions requesting a variance. A copy of that variance request may be found as Petitioners' exhibit No. 8 admitted into evidence. The date of that application was July 13, 1989. The form makes reference to the authority of the agency to examine the request for variance as being set forth in Chapter 381, Florida Statutes, and Chapter 10D-6, Florida Administrative Code. The form points out to the applicants that the variance may not be granted unless: The Department is satisfied the stated hardship was not caused intentionally by the applicant. A reasonable alternative sewage treatment method is not available The sewage discharge will not adversely affect public health and/or significantly degrade ground or surface water quality. The application for variance makes reference to the New Pine Landing Subdivision. It states that the parcel in question is lot No. 2, and makes reference to a book and page number and a plat number and purported page number associated with the plat number allegedly pertaining to the subdivision. Competent evidence was not presented to establish that these references found on the application were correct portrayals of the recordation of the subdivision and plat number. See Section 120.58, Florida Statutes. Again, this leaves the record incomplete as to any recordation of the existence of the subdivision and a plat number associated with that subdivision. The application describes the reason for requesting a variance as related to the fact that the lot is in a flood area where more than 36 inches of fill dirt may not be added. Proof was not submitted at hearing concerning the exact nature of the property in question; however, Mrs. Sessions as the person who had applied for the variance and has a layperson's knowledge of the property in question, is entitled to depict the general nature of the property and her explanation that it is flood prone is accepted. How much fill dirt may be added to the property was not established by competent evidence. Under the instructions for the owner associated with the application for the variance, the applicants are told that they should provide any supportive material and documents to the County Health Unit in Dixie County, Florida. This entails submission of a site plan, site location and reference map. These details were not submitted with the application as far as the record reveals. More importantly they were not provided at hearing. The instructions call upon the applicants to satisfy the terms of Section 381.272(2) and (3), Florida Statutes, and to state the reasons for requesting the variance under the requirements of Chapter 10D-6, Florida Administrative Code. The applicants were told to explain why variance from the requirements would relieve or prevent excessive hardship and to provide technical documentation to support the supposition that a variance would not likely result in pollution or impairment to public health. Written on the form submitted is the suggestion that this project is a variance from the requirements of Rule 10D-6.047(6), Florida Administrative Code, related to the 10 year flood event. The application points out the size of the parcel as being approximately .38 acres and the sewage flow anticipated is 250GPD. It points out that the drinking water supply is a private source. It points out that the type of residence is a single-family retreat that has two bedrooms. It describes the proximity to sanitary sewer as 13 miles and to public water supply as 7,500 feet. The distance to private wells is said to be 775 feet and to a stream 7,400 feet. The proposed system that the applicant has in mind is a septic tank and drain field that is mounded. The system is referred to as a subsurface septic tank and drain field with six inches of fill sand. Although the application describes that the water table during the wettest season of the year is below the ground surface by 36 inches and at the time testing was done that the water table was below the ground surface and "not found 72 inches," competent proof of these assertions was not presented in the course of the hearing. The description of the type of soil as being sand is accepted. Nothing more was revealed about the soil characteristics. The application points out that the 10 year MSL flood elevation is 14 feet and that the property elevation MSL is 11 feet. Competent evidence of those facts was not presented at hearing. Nor was there competent evidence of the adequacy of the surface water drainage at the property site. The application form points out that the Dixie County Health Unit recommended approval of the variance on July 13, 1989. That says that the property is in the Suwannee River floodway where maximum fill allowed is 36 inches and that mounds are subject to erosion and moving water. It is accepted that the property is in the area of the Suwannee River. The other facts that are suggested in these summary remarks were not established by competent evidence. The form reminds the county health unit that procedures associated with the variance requests must comply with Section 120.60, Florida Statutes. The county staff is instructed to list additional details in terms of the site evaluation and tell why standards cannot be met if that is the opinion held. It reminds them to reference the specific sections within Chapter 10D-6, Florida Administrative Code, and Section 381.272, Florida Statutes, that are involved with the variance request and state reasons why a recommendation of approval or disapproval is being made. The completed form is then submitted to the Environmental Health Program ten days prior to any scheduled Variance Review Board meeting date. Substantiating documents must be submitted in place of or in addition to the data just described to include the application for septic tank permit, denial letter and engineering report and USDA Soil Conservation Service reports. Based upon this record an engineer's report has never been submitted. More particularly, an engineer or acceptable substitute did not present evidence supporting the variance. Mrs. Sessions received an August 18, 1989 letter from Richard G. Hunter, PHD, Assistant Health Officer for Environmental Health. A copy of this may be found as Petitioners' exhibit number 5 admitted into evidence. It requests that additional information be provided to the Dixie County Public Health Unit associated with the date that the lot was subdivided from lot 2, if it was subdivided at one time. Mrs. Sessions testified that she responded to this request. The exact information that she provided was not presented at the hearing. Consequently, it is not clear whether the information that was presented satisfied that review group. Within the correspondence of August 18, 1989, is mention of the fact that the review group will consider the variance request at a September 7, 1989 meeting in Tampa, Florida, assuming that the information that had been requested was provided by August 28, 1989. On November 29, 1989, Kevin M. Sherman, PHD, M.P.H., Environmental Administrator, Environmental Health Programs wrote to Mrs. Sessions to advise her that the application for variance had been placed on a meeting agenda for December 7, 1989 in Sarasota, Florida. A copy of this may be found as Petitioners' exhibit No. 6 admitted into evidence. This is seen as an acceptance of the application for purposes of making a decision on the merits. Neither Petitioners nor someone representing their interests attended the December 7, 1989 meeting in Sarasota, Florida. On December 13, 1989, Dr. Hunter wrote to Mrs. Sessions to advise her that the request for variance had been rejected. A copy of this letter of rejection may be found as Petitioners' exhibit No. 7 admitted into evidence. It reminds the applicants that the purpose of the grant of a variance is for relieving or preventing excessive hardships where it can clearly be shown that the public health will not be impaired and where pollution of groundwater or surface water will not result. The basis of rejection was that the request was not considered to be a minor deviation from minimum requirements specified in Rule 10D-6.047(6), Florida Administrative Code. The letter of rejection advised Petitioners of their right to a hearing. That request for hearing was made on January 11, 1990, within the 30 days allowed for making such requests. Testimony presented by Alma Walker did not establish the nature of the New Pine Landing Subdivision and whether it had been recorded or not and the date that the property may have been platted. Mrs. Walker talked with a person within the Dixie County Health Unit whose name is Frost. This gentleman told Mrs. Walker that the case had been referred for a hearing and that the applicants should continue to pursue that matter. His secretary made some remark to Mrs. Walker concerning the impression that six inches of fill is less than allowed for septic tanks. This representation is not considered to be competent evidence as to the amount of acceptable fill. Mrs. Walker's comments concerning the applicants seeking a new benchmark from a surveyor and the suggestion that the surveyor gave this information to Mr. Frost is hearsay and does not establish the fact that a surveyor presented a new benchmark for the property to Mr. Frost. Nonetheless, following this circumstance Mrs. Walker spoke to Mr. Frost about the survey to establish benchmark and was told by Mr. Frost that the applicant still could not get a permit because of not meeting the requirements of the 10 year floodplain. Petitioners' exhibit No. 4 admitted into evidence attempts to describe the impression of the application for a variance as held by the Suwannee River Water Management District. It is hearsay and may not be used to find facts in that competent evidence about the opinion of the Suwannee River Water Management District as to the acceptability of the variance request was not presented at hearing.
Recommendation Based upon the consideration of the facts found and the conclusions of law, it is, RECOMMENDED: That a Final Order be entered which denies Petitioners request for a variance from the requirements to obtain a permit for onsite sewage disposal. DONE and ENTERED this 8th day of June, 1990, in Tallahassee, Florida. CHARLES C. ADAMS, Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, FL 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 8th day of June, 1990. APPENDIX CASE NO. 90-1204 The following discussion is made of the fact finding suggested by the parties. Petitioners' Facts Paragraph 1 is subordinate to facts found. Paragraph 2 is subordinate to facts found with the exception of suggestion that a benchmark elevation was determined. No competent evidence was presented to establish the benchmark elevation. Paragraph 3 is subordinate to facts found in the sense that it is acknowledged that an application for onsite sewage disposal system permit was made. Proof was not established that all necessary information required by law was presented with the application. Paragraph 4 with its discussion of the significance of information provided by the Suwannee River Water Management District is not accepted to the extent that it attempts to describe the entitlement to a permit based upon remarks made by the Suwannee River Water Management District. The issue of whether adequate reasons were given for denying the permit application was not noticed for consideration at the final hearing and to the extent that that issue has any relevance in considering the variance request Petitioner's have failed to demonstrate any prejudice to their cause in pursuing the variance request. Paragraphs 5 and 6 are subordinate to facts found. The indication in paragraph 7 that Petitioners were having to reapply for a variance does not coincide with the understanding of this process in which the facts tend to establish that the initial variance request was processed to conclusion. In Paragraph 8 the idea of reapplication is rejected as is the contention that there was a failure in the explanation as to the reasons why the variance was denied. The explanation was adequate to notice the Petitioners of the reasons which the agency had in mind in denying the variance application. Respondent's Facts Paragraphs 1-7 are subordinate to facts found. Paragraph 8 constitutes a conclusion of law. COPIES FURNISHED: Sam Power, Department Clerk Department of Health and Rehabilitative Services 1323 Winewood Boulevard Tallahassee, FL 32399-0700 Frances S. Childers, Esquire Department of Health and Rehabilitative Services District 3 Legal Office 1000 N.E. 16th Avenue Gainesville, FL 32601 Michael Smith, Esquire Post Office Drawer 579 Perry, FL 32347 =================================================================
The Issue The issue for consideration in the proceeding concerns whether the Petitioner is entitled to an on-site sewage disposal system permit ("OSDS") authorizing installation of an on-site sewage disposal system for property the Petitioner owns near the Suwannee River in Gilchrist County, Florida, in consideration of the relevant provisions of Section 381.272, Florida Statutes, and Chapter 10D-6, Florida Administrative Code, and whether the Petitioner should be entitled to pursue a variance from the permitting statute and rules embodied in that chapter of the code.
Findings Of Fact The Petitioner owns certain real property located in Gilchrist County, Florida on the east bank of the Suwannee River, adjoining the river. The property is more particularly described as Lot 9, Block B, Two River Estates. The property was purchased on January 3, 1985 and was platted as a subdivision on January 5, 1959. The lot in question upon which the OSDS would be installed should a permit be granted, is approximately one acre in size. On April 30, 1990, the Petitioner made application for an OSDS seeking authorization to install such a conventional septic tank and drain-field system for disposing and treating household sewage effluent on the subject property. The system would be designed to serve a single-family residence, containing approximately two bedrooms, and approximately 1,200 heated and cooled square feet of living space. Upon making application, the Petitioner was informed that he would have to obtain a surveyed elevation of his property, as well as the ten-year flood elevation for his property for the river mile of the Suwannee River at which his property is located. The Petitioner consequently retained Herbert H. Raker, a registered land surveyor, who surveyed the elevation for his property. Mr. Raker established a bench mark elevation of 29.24 feet above mean sea level ("MSL"). The site of the proposed OSDS installation on that lot has an elevation at the surface grade of 28.5 feet. The subsurface of the lot at the installation site is characterized by appropriate, "slight-limited" soil extending 72 inches below the surface grade of the lot. The wet season water table is 68 inches below the surface grade of the lot. Consequently, there is more than adequate slight-limited soil to handle disposal and treatment of the sewage effluent from a single-family residence, such as is proposed, since the wet season water table is 68 inches below the surface of the property. Thus, a more than adequate treatment space and appropriate soil beneath the bottom surface of any proposed drain field to be installed at the site would exist so as to comply with the pertinent rules cited herein. The problem with a grant of the subject permit consists only of the fact that the property lies beneath the ten-year flood elevation, that is, it is approximately 1.5 feet beneath that elevation. The Suwannee River Water Management District report submitted to the Respondent agency by the Petitioner in the application process for the OSDS permit (in evidence) reveals that the ten-year flood elevation for the property in question is 30 feet above MSL. The soils prevailing at the proposed installation site, the great depth of the wet season water table, and the fact that the lot is approximately one acre in size and above the minimum size requirements for the installation of an OSDS, all militate in favor of a grant of the permit, except for the basis for its denial initially, that is, that it is simply beneath the ten-year flood elevation for purposes of the prohibition contained in Rule 10D-6.047, Florida Administrative Code. Although located within the ten-year flood elevation, the site is not located within the regulatory flood way so that if a mounded system or other raised OSDS alternative system were proposed and installed, an engineer's certification would not be required regarding the issue of raising the base flood level by the deposition of fill at the installation site for purposes of Rule 10D-6.047(6), Florida Administrative Code. There is no central water system available to the property; however, although there was conflicting testimony about the distance the proposed installation site would be from a neighbor's potable water well, the testimony of the Petitioner is accepted as being most certain in establishing that more than the required distance from that potable water well exists between it and the proposed septic tank and drain-field installation site, since the Petitioner established that approximately 110 feet is the actual separation distance. The Petitioner purchased the property to construct a single-family residence for himself and his family. He expended a substantial sum of money for the property and is unable to use it for its intended purpose without the subject permit or at least a variance so as to authorize him to install an OSDS. The Petitioner offered no concrete proposals or plans for an alternative system which might reasonably accomplish treatment and disposal of the sewage effluent in question without harm to ground or surface waters or the public health. No substantial proof was offered of a system which would either dispose of and treat the effluent at a location above the ten-year flood elevation or, if still below it, would adequately treat and dispose of the effluent sewage to safeguard the public health and the ground or surface waters involved, such that its existence slightly beneath the ten-year flood elevation would only be a "minor deviation" from that portion of the permitting rules. In point of fact, it would seem that a mounded system would be feasible on a lot this size, especially in view of the fact that the bottom surface of the proposed drain-field trenches or absorption beds would only have to be raised slightly over 1.5 feet from the surface grade of the subject lot and installation site in order to comply with the ten-year flood elevation parameter, which was the only basis for denial of this permit application. No proof was offered concerning how such a mounded system would be designed, installed and otherwise accomplished, however. Upon denying the initial application for the OSDS permit, the Respondent advised the Petitioner that he should pursue a formal administrative hearing process rather than make application for a variance and proceed through the internal variance board mechanism operated by the department in order to obtain a variance from the requirements of Rule 10D-06.47(6), Florida Administrative Code. The Respondent advised the Petitioner of this because the subject property was located within the ten-year flood elevation of the Suwannee River; and as the Respondent interpreted the Governor's Executive Order Number 90-14, which incorporated by reference the "Suwannee River Task Force Report" commissioned by the Governor, the Order absolutely prohibited the granting of any variances authorizing installation of OSDS's beneath the ten-year flood elevation of the Suwannee River or the granting of any OSDS permits themselves authorizing such installations.
Recommendation Having considered the foregoing Findings of Fact, Conclusions of Law, the evidence of record, the candor and demeanor of the witnesses, and the pleadings and arguments of the parties, it is therefore, RECOMMENDED that a Final Order be entered denying the Petitioner's application for an OSDS permit. DONE AND ENTERED this 5th day of March, 1991, in Tallahassee, Leon County, Florida. P. MICHAEL RUFF Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, FL 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 5th day of March, 1991. APPENDIX TO RECOMMENDED ORDER The Petitioner did not file a Proposed Recommended Order. Respondent's Proposed Findings of Fact 1-10. Adopted. COPIES FURNISHED: Sam Power, Agency Clerk Department of HRS 1323 Winewood Boulevard Tallahassee, FL 32399-0700 Linda K. Harris, Esq. General Counsel Department of HRS 1323 Winewood Boulevard Tallahassee, FL 32399-0700 John Gary Wilson P.O. Box 2061 Lake City, FL 32055 Frances S. Childers, Esq. Department of HRS 1000 N.E. 16th Avenue Gainesville, FL 32609
The Issue The issue in this case is whether the Department of Health (Department or DOH) should fine the Petitioner, Jeffery Benefield, $500 and require him to move the drainfield of his onsite sewage disposal system so that no part of it is within ten feet of the potable water line of his neighbors, the Intervenors, Robert and Wanda Schweigel.
Findings Of Fact The Petitioner's home at 10920 Lake Minneola Shores Road (Lake County Road 561-A) was built in 1977. It included an onsite septic tank and drainfield sewage disposal system. On March 31, 2003, the Petitioner personally applied for a permit to repair his existing sewage disposal system by replacing the drainfield. His application did not identify any potable water lines. Department personnel evaluated the site and calculated system specifications, and the Department issued a construction permit on April 3, 2003, based on the estimated size of the existing system. To replace the existing drainfield and meet specifications, 375 square feet of drainfield was required. However, the Petitioner wanted to add 125 square feet to what was required by the specifications, which is acceptable so long as required setbacks are maintained. The Petitioner's drainfield was replaced by a licensed contractor on April 29, 2003. Some work may have been done the following day to complete the job, but it appears that the contractor called for the final inspection on April 29, 2003. On inspection, it was clear that the new drain line closest and (like the other three) parallel to the property line was less than ten feet from a water line, riser, and spigot on the neighboring property, which was owned by Robert and Wanda Schweigel. Specifically, the closest of the new drain lines was estimated to be just five feet from the Schweigels' water line, riser, and spigot. (The next closest was just under ten feet from the Schweigels' water line, riser, and spigot.) As a result, the Department disapproved the installation. The Petitioner disputed the disapproval, initially contending that the Schweigels' water line, riser, and spigot did not convey potable water. It was decided that the new drainfield should be covered while pending a decision as to whether the water line was potable. By the end of July 2003, the Department decided that the Schweigels' water line was indeed potable. In that approximate time frame, the Petitioner's contractor offered to pay to have the Schweigels' water line "sleeved" to a distance at least ten feet from the nearest portion of the Petitioner's drainfield.2 He believed that solution would be much simpler and less costly than moving the Petitioner's drainfield to a distance at least ten feet from any part of the Schweigels' potable water line. This alternative was presented to the Schweigels in that approximate timeframe, but they refused (and continue to refuse.) In August 2003, the Petitioner took the position that, regardless whether the Schweigels' water line was potable, the Petitioner's new drainfield was in the same location as the existing drainfield, and the part of the water line closest to the new drainfield (i.e., the part including the riser and spigot) was not there until after the middle of April 2003 and was recently installed either just before or while the Petitioner's new drainfield was being installed. The evidence was not clear as to the configuration and precise location of the drain lines in the Petitioner's original drainfield. However, it appears to have had three drain lines emanating from the septic tank, starting in the direction of the Schweigels' property and then curving away in the direction of Lake Minneola, which is behind the Petitioner's and the Schweigels' properties, before terminating. The replacement drainfield had pipe emanating from the septic tank and running towards the Schweigels' property line before making a 90-degree turn towards the lake before connecting to the middle of a header pipe. Connecting to the header pipe are four equally-spaced drain lines, one on either end of the header pipe and two in between, that are perpendicular to the header pipe and parallel to each other and to the Schweigels' property line (and potable water line) and run towards the lake. As indicated, it was not clear from the evidence precisely where all of the old drain lines were located, or how close they got to the Schweigels' property (and potable water line.) However, it does not appear that they got as close as two of the four new drain lines in the replacement system. See Petitioner's Exhibits 13 and 21. There was conflicting evidence as to when the Schweigels' potable water line was installed. It is clear from the evidence that there are now three "T's" off the water line from the potable water source near the street. One "T- off" leads to near the front corner of the house, one leads to the middle of the side of the house, and one leads to near the rear corner of the house. The line then extends past the last "T" to the location of the water riser and spigot. The Petitioner's evidence proved that the water line riser and spigot now within ten feet of the Petitioner's drainfield were not there either in May 1999 or on April 14, 2003. But the Schweigels maintained, and the evidence as a whole was persuasive, that the potable water lines currently in place were installed in 1996 or 1997, but were cut and moved to enable the Schweigels to install footers for construction of a concrete privacy wall in approximately 1999. After installation of the footers, the water line had to be moved several inches closer to the Schweigels' house when replaced, and the "T's" were reconnected to the line. In approximately April 2003, the water line riser and spigot were damaged (the evidence was not clear how) and had to be replaced. The evidence was that the Schweigels got a permit to build their privacy wall but did not get a permit for the plumbing work that was necessary in conjunction with the installation of the footers for the wall. Although it appears from the evidence that a plumbing permit was required, the Schweigels did not think a separate plumbing permit was necessary. It is not found that the Petitioner participated in this proceeding for an "improper purpose"--i.e., "primarily to harass or to cause unnecessary delay or for frivolous purpose or to needlessly increase the cost of litigation, licensing, or securing the approval of an activity."
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Health enter a final order that the Petitioner pay a $500 fine and either: (1) pay the reasonable cost of having the Schweigels' potable water line "sealed with a water proof sealant within a sleeve of similar material pipe to a distance of at least 10 feet from the nearest portion of the system," so long as no portion of the Schweigels' potable water line "within 5 feet of the drainfield shall be located at an elevation lower than the drainfield absorption surface"; or (2) move or relocate his drainfield to meet the setback requirements of the current Rule 64E-6.005(2)(b). DONE AND ENTERED this 15th day of February, 2005, in Tallahassee, Leon County, Florida. S 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 15th day of February, 2005.
The Issue Schofield Corporation of Orlando has applied to the Department of Environmental Regulation for a permit to construct and operate a Class III trash/yard trash landfill in Orange County, Florida. The issues are whether the applicant is entitled to the permit and, if so, what conditions should attach. Also at issue is Schofield Corporation's motion for attorney's fees and costs, pursuant to Section 403.412(2)(f), F.S.
Findings Of Fact The applicant, Schofield Corporation of Orlando (Schofield), owns the proposed landfill site and existing permits for the site. The proposed site is located in West Orange County, southwest of the intersection of State Road 545 and Schofield Road on the west half of the northwest quarter of section 32, township 23 south, range 27 east, comprising approximately sixty acres within a larger eighty-acre parcel. In some undetermined distant past the site was cultivated in citrus. It is currently being excavated as a borrow pit. The materials proposed to be placed in the landfill include trash, yard trash, construction and demolition debris and clean debris, as defined in DER Rule 17-701.020, F.A.C. The northern half of the site is flat and will be used first for the composting operation. The southern excavated portion of the site will receive the permitted fill material until it is flattened. Then, the two functions will alternate; the composting will occur on the south, and the north end will be excavated to receive fill. The proposed facility will be operated by Chambers Corporation, a nationally recognized waste management company with approximately 20 years of experience in solid waste management. The landfill site will be completely fenced, with a gate entrance mid-site between the landfill and compost area. The gate will be locked when the facility is not in operation, and will be patrolled by security personnel 24 hours a day. "Spotters", or inspectors will be employed to examine incoming waste loads at the gate, from a high gantry, and at the place where the waste is deposited. The loads will be monitored by a television camera, and all haulers will be under contract. The landfill will not accept loads from trucks coming off the road looking for a place to dump. Receptacles will be maintained on site to receive errant non-permitted waste that is found in a load, and that waste will be properly disposed of elsewhere. Schofield has several permits related to its proposed operation. These include a type III landfill permit from Orange County, a compost facility permit from DER, a general construction and demolition debris landfill permit from DER, a surface water management permit from the South Florida Water Management District, and a permit to excavate or mine from the Florida Department of Natural Resources. Schofield also has a contract to receive yard waste from Orange County. The initial term of contract requires at least ten percent of the yard waste to be composted or recycled, with the percentage amount to be renegotiated in subsequent contract renewals. In the hierarchy of landfills, DER considers Class III the least environmentally sensitive. Problems with unauthorized waste and with water quality occur more frequently with Class I landfills, defined as accommodating more than twenty tons a day of residential garbage. In this case DER has proposed to grant Schofield its Class III permit without the requirement of a bottom liner or a leachate or gas control system because of the nature of the waste that will be accepted and because of the rigorous controls, described above, to avoid receiving unauthorized or hazardous waste. The Petitioners are an individual and a homeowners' association representing a residential area approximately a half mile south of the proposed site. Petitioners contend that the applicant's data is insufficient to provide reasonable assurances that water quality standards will not be violated. Petitioners contend that the landfill, if approved, should be required to have a liner to prevent leachate from polluting the groundwater. They further contend that the groundwater monitoring plan submitted by the applicant is inadequate to detect vertical movement of contaminated leachate into the Floridan aquifer, a major source of water supply in Orange County. Hydrogeology The site of the proposed landfill is within a high recharge area. Water percolates rapidly though the soil, moving downward into the aquifer, and laterally off site. The site is considered Karst terrain, underlined with limerock. There is evidence of relic sinkholes, thousands of years old, but there is a low probability of future open sinkhole development. The geology in the area of the site provides adequate structural support for the proposed facility. An aquifer is generally defined as a unit of material which contains water and can give up a sufficient amount of yield to provide some productive flow for pumpage. Below the site there are two aquifers: the shallow water table, or surficial aquifer, containing clean well-drained fine sands, about 70 feet down; and the Floridan, primarily limestone, encountered at a depth of approximately 115 feet. The two are separated by a confining layer of less permeable sands and clay. Flow in the Floridan at the site is primarily from the west to east. Flow in the surficial is also generally from west to east, but the Petitioners theorize, and have presented competent supporting evidence, that there are fissures in the confining layer, allowing some internal drainage within the site, causing surficial water to flow vertically into the Floridan, rather than laterally off-site in an eastward direction. Based on recent data taken from two piezometers installed near the middle of the site, the applicant's hydrogeologist, James Golden, concedes that "mounding" exists along the eastern boundary of the site, reflecting some flow westerly back into the interior of the site. Petitioners' theory regarding internal draining of the site is based in part on data as to groundwater elevation. Groundwater elevation or high groundwater table is the elevation at which water stands on a continuous surface under the site. Jammal and Associates is a consultant firm which has done field studies of this and neighboring sites in the past, for various purposes. Some open bore readings taken by Jammal and Associates in a 1983 study for the Orange County Rapid Infiltration Basin project indicate groundwater table levels on site up to 126 feet, National Geodetic Vertical Data (NGVD). Open bore readings are less reliable than cased hole readings; due to collapses within the hole, artificially high readings are sometimes obtained. Data from the applicant's consultants reveals groundwater tables at 96-98 NGVD. This data was most recently obtained in December 1991 from sealed and surveyed piezometer casings, but not from the area of the site where Jammal's higher readings were obtained. Although it may be conjectured that Jammal's high readings are anomalous, additional sealed borings need to be obtained before the anomaly is confirmed. Groundwater elevations are significant also to determine the depth to which the landfill may be excavated. Based on its December 1991 readings, obtained after the application for permit was filed, the applicant agreed to raise the proposed bottom of the landfill to approximately five feet above the level of the estimated high (wet weather) groundwater table in the area. Water Quality and Monitoring Specific conditions of the proposed permit include DER's requirements that Class GII water quality standards be met at the boundary of the zone of discharge, in accordance with Rule 17-3, F.A.C. The zone of discharge for this facility is a three-dimensional volume defined in the vertical plane as the top of the ground to the base of the most surficial aquifer, and horizontally 100 feet from the edge of the waste-filled area, or the property boundary, whichever is less. The groundwater monitoring plan proposed by the applicant includes one upstream monitoring well on the west side of the site and five wells along the east side of the site, with an additional well at the south, between the project and the Petitioners' residential area. The wells extend down into the upper zone of the surficial aquifer, but not into the deeper limestone Floridan. The downstream wells should detect any contamination in the surficial aquifer flowing from west to east at the zone of discharge. However, they will not pick up contamination draining internally within the site and into the Floridan. Such contamination is possible, even though leachate from Class III- type wastes is expected to be relatively benign. Volatile organic carbons (VOCs) have not typically been a problem in Class III landfills, unless those landfills were previously operated as Class I sites. Secondary drinking water standards for certain metals have been violated at some Class III sites, but such violations are often related to the problem of sampling newly-installed wells. From DER records, Petitioners presented evidence of consistent drinking water quality standard violations in Class III landfills. That such violations can occur in Class III landfills is clearly established. It is not so clear that such violations will occur in this facility, given the proposed controls on load content. However, even acceptable materials will not avoid the production of leachate or gas. Within demolition waste there are chemically bound components which are inseparable, for example, creosote and other preservatives, glues, paints, resins, varnishes and stains. The lignin, tannins and volatile organic acids which are produced when wood decomposes alter the pH of the groundwater. As the water becomes more acidic, heavy metals that were typically bound up in the waste or in the soil, are released in soluble form and travel with the water. The decomposition process occurring in the construction and demolition waste is enhanced by the addition of yard trash which becomes the food source for the biodegradation. Summary of Findings and Proposed Permit Conditions If, as applicant suggests, all groundwater moves primarily from west to east within the site, given the proposed operational controls and the proposed monitoring plan, reasonable assurances have been provided that water quality standards will not be violated beyond the zone of discharge. That is, any contamination likely to occur will be contained within the surficial aquifer and within the 100 feet or property line horizontal boundary. Transmissivity of the surficial aquifer is low enough to allow mixing of the leachate before it reaches the zone of discharge. The Petitioners, however, have presented credible evidence sufficient to question the groundwater flow premise and sufficient to require additional conditions on the permit. If leachate reaches the Floridan through fissures in the confining layer, it will move rapidly off site. In its proposed recommended order DER has suggested additional permit conditions and in its adoption of the proposed recommended order, the applicant has accepted those additional permit conditions. Those permit conditions recognize the fact that data presently provided by the applicant is insufficient to overcome the evidence by Petitioners as to the hydrogeological characteristics of the site with the possibility of internal drainage and vertical intrusion of contaminated water into the Floridan aquifer. The proposed recommended order provides this finding: ...that the ground water monitoring plan as proposed in this proceeding is adequate, provided that there be added to the permit conditions that the permittee conduct appropriate water table testing with cased piezometers during the next wet season to determine whether ground water flow is internal within the site and therefore not intercepted by the present ground water monitoring wells. The permittee shall consult with DER and get approval for the location and construction of these wells prior to their installation. The results shall be immediately submitted to the DER. The ground water monitoring requirements should be modified if necessary at that time pursuant to Rule 17-28.700(5) to assure proper monitoring at this site. (DER proposed Recommended Order, p. 17) The ground water monitoring plan modification suggested by DER is that deeper monitoring wells, into the Floridan aquifer, be required if the additional testing reveals the likelihood of internal on-site ground water drainage. These conditions are still inadequate since they lack specificity with regard to the extent of testing, the location and construction of the wells, and the amendments to the monitoring program to be required if internal drainage is confirmed. Moreover, the proposed conditions fail to address the possibility that the permit should require a liner for the landfill if the data to be obtained reveals the likelihood that contaminates will penetrate into the groundwater of the Floridan. Monitoring programs, however effective, only predict or detect problems; they do not remediate them. Groundwater contamination by landfills is not quickly and easily reversed. Unlike discharges from other facilities such as spray application or deep well injection, the leachate from a landfill is not "turned off". Without the additional data which all parties agree is needed, it is impossible to determine what additional conditions, if any, should be required or what amendments, if any, need to be made to the applicant's proposed monitoring plan.
Recommendation Based on the foregoing, it is hereby, RECOMMENDED: That the Department of Environmental Regulation issue its Final Order denying the application for Class III land fill permit. DONE AND RECOMMENDED this 17th day of June, 1992, in Tallahassee, Leon County, Florida. MARY CLARK 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 17th day of June, 1992. APPENDIX TO RECOMMENDED ORDER The following constitute specific rulings on the findings of fact proposed by the parties: Petitioner's Proposed Findings of Fact Adopted in paragraph 1. Adopted in substance in paragraph 10. 3.-11. Rejected as unnecessary. 12.-23. Rejected as argument or summary of testimony, rather than findings of fact. 24. Rejected as unnecessary. 25.-30. Rejected as argument or summary of testimony, rather than findings of fact. 31. Rejected as unnecessary. 32.-41. Rejected as argument or summary of testimony, rather than findings of fact. Rejected as unnecessary. Adopted in substance throughout the recommended findings. 44.-50. Adopted in Preliminary Statement and paragraph 4. 51. Rejected as unnecessary. 52.-53. Adopted in paragraph 2. 54.-55. Rejected as statement of testimony rather than finding of fact. Adopted in paragraph 3. Rejected as unnecessary. 58.-97. Rejected as argument or statement of testimony, rather than findings of fact. Subparts a), b), c) and e) are rejected as unsupported by competent evidence. The evidence suggests that violations might occur and that insufficient data has been produced. Subpart d) is adopted, by implication in paragraph 18. 99.-101. Adopted in summary in paragraph 20. Respondent's Proposed Findings of Fact Addressed in Preliminary Statement. Adopted in paragraphs 1, 2 and 5. 3.-4. Adopted in paragraph 4. Adopted in summary in paragraph 11. Adopted in paragraph 13. Rejected as unnecessary or irrelevant, given the stipulation related to Section 403.412, F.S. standing. Rejected as cumulative. Adopted in paragraph 10. Adopted in paragraph 9. Adopted in substance in paragraph 9. 12.-13. Adopted in paragraph 13. Adopted in substance in paragraph 16. Rejected as unsupported by the evidence. If internal drainage is shown to exist, conditions other than additional monitoring wells may be required. Adopted in paragraph 17. 17.-18. Adopted in paragraph 3. 19.-21. Rejected as unnecessary. Adopted in paragraph 4. Adopted in paragraph 12. 24.-26. Adopted in general in paragraph 14. 27. The unlikelihood that unauthorized waste will be dumped is adopted in paragraph 3. Whether there will be a violation of ground water quality standards at the zone of discharge was not established, given the need for additional data on internal draining. COPIES FURNISHED: Thomas B. Drage, Jr., Esquire P.O. Box 87 Orlando, FL 32802 Irby G. Pugh, Esquire 218 Annie Street Orlando, FL 32806 Douglas H. MacLaughlin Asst. General Counsel DER-Twin Towers Office Building 2600 Blair Stone Road Tallahassee, FL 32399-2400 Carol Browner, Secretary DER-Twin Towers Office Building 2600 Blair Stone Road Tallahassee, FL 32399-2400 Daniel H. Thompson General Counsel DER-Twin Towers Office Building 2600 Blair Stone Road Tallahassee, FL 32399-2400
The Issue The issue for consideration in this proceeding concerns whether the Petitioner is entitled to a variance for installation of an on-site sewage disposal system ("OSDS") for property located near the Suwannee River in Dixie County, Florida, in accordance with the provisions of Section 381.272, Florida Statutes, and Chapter 10D-6, Florida Administrative Code.
Findings Of Fact The Petitioner is the owner of certain real property located in Dixie County, Florida, more particularly described as Lot 4, Wonderland Subdivision. The property is approximately 60 by 150 feet in size and was purchased in 1982 for a price of $9,000.00. It is presently appraised at $11,000.00; however, if an OSDS could be permitted and installed, the property would appraise for approximately $22,000.00. The lot was platted in 1957. On October 19, 1989, the Petitioner made an application for a variance from the OSDS permit requirements for the property. The application form indicated, and the Petitioner intends, that this would be a new system for a single-family residence. The residence would contain two bedrooms and would produce approximately 250 gallons per day of sewage flow. The Petitioner desires to construct a residence on the property to have a pleasant place to live and is suffering a hardship because of the investment which he has made in the property, which is of no use to him if he cannot obtain the subject permit or variance and install the OSDS so that he can construct his residence. Alternatively, he is unable to sell the property readily without the ability to obtain an OSDS permit or variance for the property. At the behest of the Respondent in the permit application or variance application process, the Petitioner obtained a survey of the property by a registered land surveyor (see Petitioner's Exhibit No. 2 in evidence). That survey resulted in a benchmark elevation being established of 12 feet above mean sea level ("MSL"). The site of the proposed OSDS installation is 11.71 feet above MSL. The ten-year flood plain elevation for this property is 16 feet above MSL, as verified by records of the Suwannee River Water Management District in evidence without objection. The property is also located within the regulatory floodway of the Suwannee River. Although the Petitioner acknowledged in a general way that he would be amenable to consideration of various alternative types of systems involving piping of sewage effluent to an appropriate upland disposal and treatment area, the use of chemical toilets or other appropriate non-discharge types of treatment and disposal systems, no concrete evidence was adduced from the Petitioner to establish that such are or are not reasonable alternatives to the conventional subterranean septic tank and drainfield type of disposal system with which the variance application is concerned. Consequently, the Petitioner's proof does not establish that no reasonable alternatives exist in order to secure the grant of a variance nor did the Petitioner's proof establish that the type of system proposed would not pollute the ground or surface waters or pose a threat to public health in terms of the standard subterranean OSDS or any alternative systems which the Petitioner might theoretically employ, including the types mentioned above. The Petitioner's proof simply did not establish that installation of a standard subterranean OSDS would only pose a minor deviation from the permitting statute and rules cited herein nor did the Petitioner establish that no reasonable alternatives exist to the establishment of a standard OSDS, as that relates to the substantiality of the hardship which the Petitioner is experiencing in not getting the OSDS originally requested permitted; and the Petitioner did not establish that any system proposed would not pose a threat to public health or pollute ground or surface waters. In summary, the Petitioner did not establish that a sufficient hardship is experienced, because reasonable alternatives have not adequately been explored and considered by the Petitioner nor made a part of the subject of Petitioner's proof nor has the Petitioner established that a grant of a variance would involve only a minor deviation from the permitting statute and rules standards because it has not been proven that the public health nor the ground or surface waters would not be adversely affected. Finally, because the property is located in the regulatory floodway of the Suwannee River, under Rule 10D- 6.047(6), Florida Administrative Code, before a mounded or filled OSDS could be permitted and installed, which is one alternative under consideration, a registered professional engineer must certify that the mounding of the system and installation of fill in the regulatory floodway area would not cause elevation of the "base flood" of the Suwannee River. No such engineering evidence or testimony has been adduced iii this proceeding; therefore, such an alternative system cannot herein be recommended for approval.
Recommendation Having considered the foregoing Findings of Fact, Conclusions of Law, the evidence of record, the candor and demeanor of the witnesses, and the pleadings and arguments of the parties, it is therefore, RECOMMENDED that a Final Order be entered denying the Petitioner's application for a variance from the statutory and regulatory requirements for an OSDS permit. DONE AND ENTERED this 10th day of December, 1990, in Tallahassee, Leon County, Florida. P. MICHAEL RUFF Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, FL 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 11th day of December, 1990. APPENDIX TO RECOMMENDED ORDER IN CASE NO. 90-3111 Respondent' Proposed Findings of Fact: All of Respondent's proposed findings of fact are accepted. COPIES FURNISHED: Sam Power, Agency Clerk Department of HRS 1323 Winewood Boulevard Tallahassee, FL 32399-0700 Linda K. Harris, Esq. General Counsel Department of HRS 1323 Winewood Boulevard Tallahassee, FL 32399-0700 Marilou Clark Suwannee Plantation Realty Rt. 3, Box 73 Old Town, FL 32680 Frances S. Childers, Esq. Assistant District III Legal Counsel Department of HRS 1000 Northeast 16th Avenue Gainesville, FL 32609
The Issue Whether Gar-Con's revised application for a permit to construct a sewage plant, and soakage trenches to dispose of the effluent, should be granted?
Findings Of Fact Eight to ten miles south of Melbourne Beach and 8.3 miles north of Sebastian Inlet, Gar-Con plans to develop a parcel of land stretching west from the Atlantic Ocean, across Highway A1A, to the Indian River. Gar-Con expects to build a motel and residential complex complete with tennis courts, parking garage, water treatment plant and the sewage treatment facility for which a construction permit is sought in these proceedings. The sewage treatment plant would be built on a site 480 feet west of Highway A1A and 90 feet south of Gar-Con's northern property line, at an elevation of 11 or 12 feet above mean sea level. Ocean Way Water and Sewer Association, Inc. is to be organized as a nonprofit corporation to own and operate the wastewater treatment facility. The Public Service Commission, through the director of its water and sewer treatment, has taken the position that the proposed "sewer system will fall within the exemption described in Section 367.022(7), Florida Statutes." DER's Composite Exhibit A. PACKAGE PLANT PROPOSED The facility Gar-Con proposes is designed to treat 100,000 gallons of sewage daily, which is the estimated "total flow" (T. 75) the sanitary engineer who designed the system anticipates from the development. Sewage generated by the development would flow to the plant, through a bar rack designed to remove rags and other large objects, and into aeration tanks where, over a 24 hour period, interaction with air and a biological mass would supply oxygen and cause the formation of biological floccules. The flocculant sewage would then move to a clarifier hopper. During its five hour stay there, solids which were not earlier segregated as the sewage moved over a weir into the clarifier, would be precipitated and removed. The clear, residual liquid would be pumped through one of two sand filters (each of which would also have granular activated carbon and be capable of filtering 100,000 gallons daily) into one of two chlorine contact chambers where a gas chlorinator would introduce chlorine for an hour. Under ordinary circumstances, the chlorinated effluent would then be pumped into one of two soakage trenches. The soakage trenches, each designed for use every other week, are to be gravel-filled ditches covered over first with felt paper, then with compacted fill. The gravel would lie at least one foot beneath the surface of the ground in a space ten feet wide and three feet deep stretching the 940 foot length of each soakage trench. Punctured like sieves, two six-inch PVC pipes would run through the gravel, sweating effluent from their pores. There is also a plan to dig a percolation pond or grassed swale five feet deep, 120 feet long and 80 feet wide near the wastewater treatment plant, which could serve as a receptacle for effluent, in case of "a 1:10 year storm or when the filters are down and/or if soakage trenches would need repair." Gar- Con's Exhibit 2-A. It would hold about 100,000 gallons. The solids caught by the weir, those extracted in the clarifying process, and those recovered from backwashing the filters would serve as catalyst for the aeration process as needed. Excess sludge, about 3,000 pounds monthly, would undergo "aerobic digestion," before being removed to Brevard County's Central Disposal Facility on Adamson Road, for disposal there. Gar- Con's Exhibit No. 7. Primary and secondary drinking water standards would be met by the effluent as it left the plant (although the engineer who designed the system would not drink the effluent himself), except that, from time to time, nitrate concentrations might reach 12 milligrams per liter, and except in the "event that a homeowner might put some type of [inorganic toxic or carcinogenic] material into the sewer system." (T. 86) The biological oxygen demand (BOD) would be ten milligrams per liter; suspended solids would probably amount to about five milligrams per liter; pH would probably be slightly under seven; nitrates would average approximately eight milligrams per liter but would "peak out at certain times during the year, for maybe extended periods up to two months, at twelve milligrams per liter," (T. 80); and there would be a chlorine residual after 60 minutes of two milligrams per liter. AMBIENT WATERS There would be no direct discharge to the Atlantic Ocean, Indian River or any other body of surface water, nor would any indirect effect on surface waters be measurable. No body of surface water lies within 500 feet of the site proposed for the plant and soakage trenches. Potable groundwater underlies the site; the groundwater table slopes toward the Atlantic Ocean, 9.5 to 12.5 feet below ground. "[D]uring the traditional rainy season," Gar-Con's Exhibit 2B, Attachment, p.3, the groundwater may rise to within seven feet of the surface. The PVC pipes in the soakage trenches are to be placed two and a half feet deep. As effluent percolated through the sandy soil, there would be "mounding" of the groundwater underneath the soakage trenches, and dispersal in all directions. Surface flow is to be diverted from the soakace trenches so that only rainwater falling directly on them would percolate down through the gravel beds. Taking soil characteristics into account, and assuming a "water table depth" of 20 feet, an engineer retained by Gar-Con predicted that "the maximum expected groundwater rises beneath the east and west trenches are 2.4 and 2.1 feet, respectively under a loading of 100,000 gpd for a period of 7 days." Gar-Con's Exhibit No. 3. The water table depth, "the height, the top of the groundwater from the first restrictive layer," (T. 172), is probably more like 40 feet than 20, which accounts in part for the "conservatism" of the mounding predictions. Under very severe weather conditions (a 100 year storm), groundwater would rise as high as the bottom of the trenches making them unavailable to receive effluent, but the effluent would not be forced above ground. In a 100 year flood, water would be expected to rise to seven feet above mean sea level. Under such conditions, people could be expected to evacuate the area. In a 25 year storm, the system could be expected to continue to function. Groundwater to the north and east of the proposed site was sampled, and the samples were analyzed. The water to the north had 380 milligrams of chlorides per liter and the water to the east had 450 milligrams of chlorides per liter. As it left the proposed treatment plant, the effluent would contain approximately 150 milligrams of chlorides per liter. SOUND AND LIGHT Lights like those used as street lights are to be installed at four places in the wastewater treatment plant. A timer, which can be overridden, would turn the lights on at dusk and off at eleven o'clock at night. The lights would illuminate the plant adequately. Pumps would move sewage to and through the proposed plant. Most of the pump motors would be submerged and unable to be heard. Two electric blowers, a flow meter and a totalizer would also have electrical motors. The blowers and the blower motors are to be equipped with insulated fiberglass covers and the blowers would also have intake and double outlet silencers. Four feet from the plant the noise of the motors would be comparable to that of a home air conditioning unit. At the nearest residence the noise level would scarcely exceed background noise. At hearing, Gar-Con revised its application and agreed to install an emergency generator which would also be encased in insulated housing and is to be equipped with a muffler. AEROSOL AND ODOR Unless the proposed plant loses electric power for 24 hours or longer, no offensive odors would emanate from it. The bar rack and weirs would be regularly hosed down. Against the possibility of a power failure, Gar-Con agreed at hearing to install permanently an emergency generator with sufficient capacity to keep both the wastewater treatment plant and the water treatment plant it plans to build operable. No aerosol drift is foreseen. The surface of the liquid In the aeration tanks would be 1.4 feet below the top of the rim. Walkways four feet wide along the inside perimeters of the aeration holding tanks would prevent dispersal of most of aerosol. A decorative hedge around the treatment plant, which would eventually be 15 feet high, is a final fail-safe. WELLS To the north are two shallow wells within 500 feet of the site proposed for the wastewater treatment plant. Both wells belong to Kel Fox, who wrote Gar-Con that he had no objection to their proposed wastewater treatment facility in light of Gar-Con's agreement to furnish drinking water to existing facilities on his property and reimburse him expenses incurred in disconnecting the two shallow wells. Gar-Con's Exhibit 2E. There is a deep well within 500 feet to the south. DER and Gar-Con have entered into the following stipulation, dated September 2, 1983: Existing Wells. Prior to the operation of its waste water treatment plant, Gar-Con will offer to supply drinking water at a reasonable cost to owners of property on which are located operational or approved shallow drinking water wells that are within 500 feet of Gar-Con's land application site. Gar-Con will make this offer to all such owners known to it prior to the operation of its plant. Gar-Con will further offer to provide reasonable compensation to such owners to disconnect their shallow wells. Gar-Con will endeavor to arrange for provision of drinking water to these owners and the disconnection of those wells prior to the operation of its plant. Future Wells. Should nearby individual (non-corporate) property owners propose to construct shallow drinking wells located within 500 feet of Gar-Con's land application site after Gar-Con begins operation of its waste water treatment plant, Gar-Con also will offer to supply them with drinking water at a reasonable cost and to provide reasonable compensation to them to disconnect those wells. However, Gar-Con shall have no obligation to make any such offer to owners of future wells if sampling of monitoring wells located at or near its external property line indicates that the groundwater meets the primary drinking water standards and, after July 1, 1985, the secondary drinking water standards listed in Florida Administrative Code Rule 17-22.104. Gar-Con agrees to record a master notice of restriction barring future owners of lots within the Ocean Way development, which are owned by Car-Con at the time of permit issuance, from installing shallow drinking water wells on such property or otherwise using the shallow aquifer beneath their property as a source for irrigation or for potable water, so long as use of the proposed sewage disposal system continues, and the Department has not found that this restriction is unnecessary. This restriction, which shall be a covenant running with the land, further shall require future owners to purchase water from Gar-Con or any successor owner of the development's water system if Gar-Con or the successor provides water service. These restrictions also shall be contained in all other appropriate documents of title. In addition, Gar-Con plans to create a non-profit water and sewer association to own and control the development's water and sewer system. Gar-Con will include in the Articles of Incorporation of this association a requirement that all property owners served by the system must be members of the Association. Gar-Con is entitled to a zone of discharge extending to its current property line with the exception that the zone of discharge shall not include the area contained within a 100' radius of Gar-Cons's proposed water supply wells. DER Staff concurs that the above conditions, in conjunction with the sewage treatment and disposal system and the groundwater monitoring program proposed by the applicant, to meet the requirements of Chapter 17-4, F.A.C. will provide reasonable assurance that existing and future off-site and on-site property owners will be protected from any adverse effects that might result from the operation of the proposed sewage treatment disposal system. Petitioner's Exhibit No. 10. There are to be a half dozen monitoring wells to allow sampling of the groundwater at strategic points in the shallow aquifer. NATURAL RESOURCES Turtles nest in the general vicinity but off the site of the proposed project. Construction and operation of the proposed waste water treatment facility would have no impact on the turtles apart from making it possible for more people to live closer to where they nest.
