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HomeMy WebLinkAboutRegional Wastewater Study-1997DCM COPY DCM COPY lease do not remove!!!!! Division of Coastal Management REGIONAL WASTEWATER STUDY prepared for TOWN OF LONG BEACH and STUDY PARTICIPANTS September, 1997 WKD #97419.10 for TOWN OF LONG BEACH 4601 E. Oak Island Dr. Long Beach, NC 28465 by W. K. Dickson & Company, Inc. 1924 Cleveland Avenue Charlotte, North Carolina 28203 704-334-5348 c\re\97419\00001 cvr. TABLE OF CONTENTS Section I - Introduction...........................................................................1 to 2 Section II - Existing Facilities.................................................................3 to 5 Section III - Population/Flow Projections...............................................6 to 7 Section IV - Discussion of Alternatives................................................8 to 15 Section V - Cost Estimates................................................................16 to 19 Section VI - Alternative Analysis........................................................20 to 21 Section VII - Funding Alternatives.....................................................22 to 23 LIST OF TABLES ti Table No. 1.......................................................................... After Page No. 7 Table No. 2.......................................................................... After Page No. 7 Table No. 3........................................................................After Page No. 19 Table No. 3A......................................................................After Page No. 19 Table No. 4........................................................................After Page No. 19 Table No. 5........................................................................After Page No. 19 Table No. 6........................................................................After Page No. 19 Table No. 7............:...........................................................After Page No. 19 Table No. 8........................................................................After Page No. 19 Table No. 9........................................................................After Page No. 19 Table No. 10......................................................................After Page No. 19 Table No. 11......................................................................After Page No. 19 Table No. 12......................................................................After Page No. 19 Table No. 13......................................................................After Page No. 19 Table No. 14......................................................................After Page No. 19 Table No. 15......................................................................After Page No. 21 LIST OF FIGURES Figure1...............................................................................After Page No. 2 Figure2...............................................................................After Page No. 2 SECTION I INTRODUCTION 1.1 Scope of Work This study is being performed and funded under a grant from the North Carolina Division of Coastal Management, Local Planning and Management Grant Program. The purpose of the Study is to inventory the existing facilities in the study area, then develop the projections, alternatives and cost analyses necessary to recommend a plan of action to the participants in this study. As a side benefit, this study will, hopefully, bring about better cooperation among all the participants, at least in the critical area of wastewater. The bulk of the information presented on existing facilities and growth trends has ,been taken from existing studies performed for the different study participants. These study participants are as follows: Boiling Spring Lakes ' • Brunswick County • Town of Caswell Beach ' Town of Long Beach Southeast Brunswick Sanitary District • City of Southport • Town of Sunset Beach • Town of Yaupon Beach ' While the planning, development, funding and design of wastewater collection and treatment facilities is challenging and certainly a consideration in this study, the key issue in this study area is disposal of the treated effluent. That is where much of the ' attention will be focused. A great deal of the information used in this study was gleaned form the following previously completed reports and studies: - Water and Sewer Study, Brunswick County, North Carolina by HDR Engineering, Inc., May, 1996 - Water Quality Management Study, Town of Long Beach, North Carolina, by McKim & Creed Engineers, P.A., July, 1995 ' - Water Treatment Plant Feasibility Study for the Town of Long Beach, Brunswick County, North Carolina, by Rivers & Associates, Inc., November, 1996 ' - Project Scoping Report, SBWASA EIS, Prepared for the SBWASA, by Greiner, Inc., February, 1997 1 - Comprehensive Wastewater Study, Town of Sunset Beach, by Powell Associates of NMB, Inc. and Piedmont Olsen Hensley, June, 1992 - Amendment to Southwest Brunswick, N.C., 201 Facilities Plan, Calabash/Sunset Beach Planning Area, by Powell Associates of NMB, Inc. & Piedmont Olsen Hensley, November, 1993 1.2 Description of the Study Area The study participants generally comprise the municipalities along the Brunswick County beaches along with the southeast corner of the County, as listed earlier. Figure No. 1 shows a map of Brunswick County and figure No. 2 is a breakout of the various participants. In general, Brunswick County was established in 1764 and is situated in the southeast corner of North Carolina as part of the Coastal Plain. While there are several key industries in the county, tourism is the most important, especially within the study area along the coast. This of course plays a major role in the economy and is due to the area's large number of quality beaches, the very favorable climate, and numerous recreational opportunities. These same factors inevitably lead to growth which just as inevitably leads to demand for utilities, especially wastewater collection treatment and disposal facilities. ' 1.3 Regional Approach The regional approach for the purposes of this Study does not mean so much a single close geographical region as it is a level of cooperation and a focusing of resources by ' all parties involved to try and develop effluent disposal alternatives that are suitable for the individual participants involved. There is still a great deal of the geographically regional concept at work here since all the participants involved, except Sunset Beach and Brunswick County, are located in the southeastern region of the County. Brunswick County obviously has the potential to play a major role in the regional concept, regardless of geographical location within the County. The Town of Sunset Beach is somewhat isolated geographically, but by virtue of their involvement with the South Brunswick Water and Sewer Authority, a regional authority, and their desire to open up discussion on some of the disposal alternatives, they are considered part of this "regional" approach. 2 LEGEND COUNTY LINE - - RIVER, STREAMS, ETC. ROAD, HIGHWAYS - APPROXIMATE STUDY AREA LONG BEACH REGIONAL SEWER STUDY LONG BEACH, BRUNSWICK COUNTY LOCATION MAP FIGURE No. 1 ® WK p DICKSON R. 87 #*BaLINSG SPRZN\ LAKE..)L 133 17 OR70M POND LY ... ... BOILING SPRING z LAKES LENNON SROADS SMITH v�2114. ZEI, PS.E. ISLA EIRLINS K S. 87 SOP/PORT ooe7... N INLET LO CASli- 94 �ii;�.-BEACH Sfy _ND f BEACH YAUPON ATLANTIC BEACH OCEAN STRIKIN01 ... BEACH I LONG BEACH REGIONAL SEWER STUDY WK LONG BEACH, BRUNSWICK COUNTY ttv DICKSON STUDY AREA BREAKOUT & FIGURE No. 2 I ' SECTION II EXISTING FACILITIES 2.1 General Most of Brunswick County, and especially the study area, is served by a complete centralized water system. The same cannot currently be said of the wastewater facilities in the County. This goes back to the long standing trend towards lower cost individual treatment facilities for each community versus potentially pumping the raw or ' treated wastewater long distances for regionalization. The list of existing wastewater facilities within the study area has tended to reflect the ' same trend towards individual goals. This has all been fueled by the lack of significant funding for any regional initiatives, and the wide variation in local conditions. ' 2.2 Inventory of Existing Facilities 2.2.1 Boiling Spring Lakes There is no centralized wastewater system currently within the municipality. Only a small portion of the town is currently developed and this area has had to be ditched and ' drained to make it suitable for on -site wastewater systems, which is the only form of wastewater treatment available in the Town. ' The Town has a Land Use Plan, set to be updated in late '97, that encourages developers to build centralized sewer systems. There is also a golf course in town that has the potential for reuse irrigation, although no commitment has yet been made. ' The Town has water service to a small portion and is planning an non -binding 1 referendum for support of expansion of the water system. 2.2.2 Brunswick County ' The County operates a modular extended aeration package plant permitted for 250,000 gpd with current capacity of 35,000 gpd. The plant serves the Leland Industrial Park. The treated effluent is discharged to surface waters that form a segment of the Cape ' Fear River. The County is also a member of the South Brunswick Water and Sewer Authority as ' well as having discussed taking over the Town of Belville's 400,000 gpd packaged aeration with filtration wastewater plant. Betville's plant currently operates at about 13,000 gpd, but has 370,000 gpd committed to other areas. The discharge is a surface discharge to the Brunswick River which is a ' tributary to the Cape Fear River. 3 2.2.3 Town of Caswell Beach There is no centralized wastewater treatment system currently within the municipality. There are two privately owned package treatment facilities in the Town. The first is a package plant serving the Caswell Dunes development. It has a permitted capacity of 65,000 gpd and uses subsurface disposal. The second package plant serves the Ocean Greens and Arboretum developments. This facility has a permitted capacity of 100,000 gpd and uses a rapid infiltration basin for effluent disposal. 2.2.4 Town of Long Beach There is no centralized wastewater treatment system currently within the municipality. All of the Town of Long Beach is served by on -site systems. Dutchman Villas and Oak Beach Inn and Marina utilize low pressure pipe systems, on -site. The vast majority of Long Beach is residential and seasonal with on -site septic systems. The Town's Land Use Plan indicates that on the order of 100 septic system repairs occur per year. ' A previous proposal to construct a tertiary treatment system with spray irrigation was rejected by voters. However, there is still interest in some type of system especially in light of current and potential future environmental concerns over on site systems. ' 2.2.5 Southeast Brunswick Sanitary District (SBSD) The SBSD was formed in 1989 to provide wastewater service for the area on and ' around Highway 133, Long Beach Road. The District, at that time had no centralized wastewater system. There was a 25,000 gpd package plant that treated waste from the River Run Shopping Center and had a surface discharge to Jump and Run Creek, then ' into the SA waters of Dutchmans Creek. ' In the past two years, the District has aggressively pursued a centralized system and currently has permits, bids and funding in place for a 0.5 MGD tertiary treatment facility. The effluent from this facility will be used to spray irrigate a new golf course, set to open ' in Fall, '97. The River Run package plant will be decommissioned and, through a 3 party agreement, the flow will be pumped to the City of Southport for treatment and disposal. 2.2.6 City of Southport The City of Southport has centralized collection, treatment and disposal system. The treatment facility is currently permitted for 800,000 gpd and has,a surface discharge to the Intracoastal Waterway, classified SC waters. The treatment facility is actually two different treatment processes that combine for one discharge. The plant is currently operating at approximately 475,000 GPD and has had on -going problems with Inflow/Infiltration. These problems are systematically being corrected. 4 I ' 2.2.7 Town of Sunset Beach There is no centralized wastewater system currently within the Town. The Town is completely served by individual on -site systems with only one small community on -site system serving approximately.100 units at The Colony at Oyster Bay. The Town of Sunset Beach is part of the South Brunswick Water and Sewer Authority ' (SBWASA), but has seen the same problems as the other participants in the study. Problems such as failing septic systems brought on by higher density development, poor soils and high groundwater levels, along with the lack of a centralized treatment facility. ' 2.2.8 Town of Yaupon Beach The Town is currently served by a centralized wastewater system. The collection system serves the entire Town plus the Oak Island Beach Villas in the Town of Caswell Beach. The flow is pumped across the Intracoastal Waterway to a tertiary treatment facility, with filtration, located on Fish Factory Road off of Long Beach Road. The plant ' has a design capacity of 400,000 gpd. The present disposal method is through rapid infiltration basins located adjacent to the plant. Due to problems with the basins, the disposal capacity has been derated to approximately 180,000 gpd. ' The Town has pursued various other disposal options including spray irrigation on land adjacent to the basins and spray irrigation on the Oak Island Golf Course. Both options ' have met with some opposition. II �IJ�I 1 5 SECTION III POPULATION/FLOW PROJECTIONS 3.1 General Due to the nature of this study, no attempt was made to recreate any population or flow projections unless no other information existed for the particular study participant. Therefore, there exists a wide range of projection methodologies and assumptions. The planning period for this Study -has been established at 20 years (1997-2017) with benchmark dates set at 1999, 2001 and 2002. Since the timing and actual impact of sewer availability throughout the study area is ' unknown, no attempt was made to apply any increased growth rates to the projections. However, the growth rates used by the various participants or for this report are generally at least 2.0% per year with some on the order of 4.0% per year or more. The determination of seasonal population is a difficult scenario to analyze. After review of the various previous reports, it was apparent that there is a wide fluctuation in seasonal I' population from one community to another. This study attempts to use the latest seasonal information from other reports for each participant. For those that did not have information available, it was assumed that they had little or no seasonal input. I' This constituted primarily the mainland participants. Table Nos. 1 and 2 show the various participants and their existing as well as projected flows and populations. Along with the growth rates, assumptions were made for the average flow per capita, i.e., gallons per day per person (gpdp). Where data exists, the average is 90 gpdp for permanent residents. The seasonal flow per capita was again a difficult scenario, but a ' figure of 50 gpdp was used. This figure was obtained from EPA studies and tables. 3.2 Population Proiections ' Table No. 1 shows the permanent and seasonal population figures used through the 20 year study period (2017). The population projections for Brunswick County are ' shown, but for reference only, since the rest of the study participants are included in the County numbers. ' The permanent population for the study area is shown increasing from 17,540 in 1997 to 31,032 in 2017, or an average of 3.8% growth per year for the study period. The seasonal figures show approximately a 3.0% growth per year. ' 3.3 Flow Proiections Table No. 2 shows the permanent and seasonal flow figures for the same population ' data described in Section 3.2. The Brunswick County numbers are not shown since, again, they contain the flows for the other study participants. The 90 gallons per day per person figure used to make these projections reflect an almost exclusively 6 domestic/commercial type of wastewater without "wet industries" or industrial process flow. The permanent flow is shown in order to establish the base level and for use during all off season times. In order to get the Peak Seasonal Flow, the Total Seasonal Flow is added to the Total Permanent Flow which yields the results at the bottom of Table 2. 7 PERMANENT POPULATION ONLY MUNICIPALITY 1990 1997 1999 2001 2002 2017 Boiling Spring Lakes 1650 1956 2045 2137 2185 2732 Brunswick County 50985 63085 65981 68740 70050 87200 Town of Caswell Beach 175 225 243 262 272 477 Town of Long Beach 3816 4722 4965 5192 5305 9384 Southeast Brunswick Sanitary District 2700 3100 3350 3625 3770 6790 City of Southport 3600 4755 SOBS 5351 5451 6875 Town of Sunset Beach 311 1909 2647 2754 2809 3708 Town ofYaupon Beach 734 873 891 909 918 1066 TOTALS ( W/O BRUNSWICK COUNTY) 12986 17540 19226 20230 20710 31032 SEASONAL POPULATION ONLY MUNICIPALITY 1990 1997 1999 2001 2002 2017 Boiling Spring Lakes 7 7 7 ? 7 7 Brunswick County 7 7 7 ? 7 ? Town of Caswell Beach 1435 1900 2055 2222 2312 4164 Town of Long Beach 7 19085 19875 20695 21118 28245 Southeast Brunswick Sanitary District ? 1240 1340 1450 1508 2716 City of Southport ? 7 ? ? 7 ? Town of Sunset Beach 311 15167 16722 17938 18375 25130 Town ofYaupon Beach 7 2700 2810 2930 2990 4060 TOTALS (W/O BRUNSWICK COUNTY) 1746 TABLE 1 40092 42802 45235 46303 64315 LNGBCH.XLS PERMANENT FLOW ONLY MUNICIPALITY 1990 1997 1999 2001 2002 2017 Bolling Spring Lakes 148,500 176,040 184,050 192,330 196,650 245,880 Brunswick County NIA NIA NIA NIA NIA NIA Town of Caswell Beach 15,750 20,250 21,870 23,580 24,480 42,930 Town of Long Beach 343,440 424,980 446,850 467,280 477,450 844,560 Southeast Brunswick Sanitary District 243,000 279,000 301,500 326,250 339,300 611,100 City of Southport 324,000 427,950 457,650 481,590 490,590 618,750 Town of Sunset Beach 27,990 171,810 238,230 247,860 252,810 333,720 Town of Yaupon Beach 66,060 78,570 80,190 81,810 82,620 95,940 TOTAL PERMANENT FLOW 1,168,740 1,578.600 1,730,340 1,820.700 1,863,900 2,792,880 SEASONAL FLOW ONLY MUNICIPALITY 1990 1997 1999 2001 2002 2017 Boiling Spring Lakes 7 ? ? 7 ? ? Brunswick County NIA NIA NIA NIA NIA NIA Town of Caswell Beach 71,750 95,000 102,750 111,100 115,600 208,200 Town of Long Beach ? 954,250 993,750 1,034,760 1,055,900 1,412,250 Southeast Brunswick Sanitary District 7 62,000 67,000 72,500 75,400 135,800 City of Southport ? ? 7 7 ? 7 Town of Sunset Beach 15,550 758,350 836,100 896,900 918,750 1,256,500 Town of Yaupon Beach ? 135,000 140,500 146,500 149,500 203,000 TOTAL SEASONAL FLOW 87,300 2.004,600 2,140,100 2,261,750 2,315,150 3,215,750 TOTAL PERMANENT & SEASONAL FLOW 1,256,040 3,583,200 3,870,440 4,082,450 4,179,050 6,008,630 TABLE 2 LNGBCN.XLS SECTION IV DISCUSSION OF ALTERNATIVES 4.1 General This listing will look at all possible wastewater/effluent disposal alternatives regardless of any other factors. The discussion of each alternative will then present the relative advantages and disadvantages of each and look at suitability of each alternative for the Regional concept, as outlined in Section 1.3. If certain alternatives are more or less appropriate for different participants, that discussion will also be presented. 4.2 Discussion of Alternatives 4.2.1 Alternative No. 1 - Golf Course Reuse Golf course reuse falls under the N.C. Division of Water Quality's recently adopted reuse/reclamation rules. They require tertiary treatment, but allow irrigation of areas subject to use by the general public. The effluent is well suited for irrigation of a golf course and the required irrigation ponds can fit well with the landscaped nature of courses. (Generally speaking, a well sited and maintained 18 hole golf course can accept at least 300,000 gpd, and there are currently about 23 golf courses in the study area. Advantages: • Availability of numerous existing and proposed courses throughout the study area • Fits well with reuse rules, especially because of the careful maintenance associated with golf courses. • Provides for a symbiotic relationship between the golf course owner and POTW owner. Disadvantages: • Golf courses are land intensive, expensive and are limited to good soils if they are to be effective for reuse. • The reuse rules require a very high level of treatment, plus process duality and a 5 day holding pond in addition to the irrigation ponds. This alternative is potentially suitable for all participants. P 4.2.2 Alternative No. 2 - Industrial Reuse Certain types of industrial reuse are allowed in the new reuse regulations. The category of Industrial Reuse, for this study, includes such things as industrial process water, industrial cooling water and cleaning/washing operations. There are only a few potential industries in the study area that have the water demand and technical needs suitable for accepting reuse water. The primary candidate would be Cogentrix, located near Southport/Boiling Spring Lakes. They currently use over 2.9 MGD of potable water, with 2.0 - 2.5 MGD of that being used as cooling water. Previous negotiations were held with Cogentrix which indicated a high level of interest in purchasing reuse water to use as cooling water. These negotiations were never completed due to the contractual relationship between Cogentrix and CP&L, but the potential for successfully completing those negotiations and disposal option for over 2 MGD of flow still exists. Advantages: • Provides an environmentally low impact disposal option that is very marketable. • The cost of disposal facilities is low • The Cogentrix facility is centrally located in the SE corner of the county. ' Disadvantages: Limited ability to accept flow (2.5 MGD maximum) • Requires contractual relationships that may be difficult or impossible to ' obtain. • Requires tertiary treatment of wastewater with duality, etc. This alternative, using Cogentrix, is potentially suitable for all but Brunswick County and the Town of Sunset Beach. No other viable industries currently exist near Sunset Beach, or elsewhere in the County. 4.2.3 Alternative No. 3 - Spray Irrigation Spray Irrigation , especially on forest lands, is an option in this area due to the large number and size of tree farms in the region. Depending on soil types and wetland locations, as much as 2,000-3,000 gallons per acre could be sprayed on either forest lands or other areas. Advantages: • There is an abundance of large tracts of forest land in the area. • Would only require treatment to secondary limits, to avoid clogging of spray system. Disadvantages: • Would likely require high pumping costs and extensive spray facilities. 9 • Would necessitate a long term contractual relationship with the land owner requiring that the land used be dedicated for the purpose of timber and spray irrigation. • Extensive environmental studies may be needed over large areas to determine feasibility. • Would require that public access be restricted for the area sprayed. This alternative is potentially suitable for all participants in the study. 4.2.4 Alternative No. 4 - Complete Reuse Systems The systems proposed in this alternative would follow the State's new reuse rules. However, instead of limiting the reuse to golf courses, complete reuse distribution systems would be set up much like potable water systems. These systems would run parallel with potable water and would have separate meters, storage facilities, pumping, etc. The reuse water could be used for most exterior watering purposes such as car washing, lawn sprinklers, and plant watering. The methods required are currently in use, and have been for sometime, in California, Nevada, Florida and other areas both in the U.S. and other countries. This method is likely the future of reuse in this country. Advantages: • Perhaps the truest form of reuse, with the producer also being the end user. • Allows for cost recovery by way of individual meters. • Avoids any potential conflict due to intraregional transfer of reuse water. Disadvantaqes: ' The concept of reuse is new to North Carolina which may create problems with public perception. These reuse systems are potentially very costly due to the need to ' essentially duplicate the potable water distribution system. Would not realize the same cost benefits as using a regional disposal site. I', 1 This Alternative is potentially suitable for all participants. ' 4.2.5 Alternative No. 5 - Habitat Restoration Reuse/reclaimed water has been used, in other parts of the country, to help recharge and enhance wetlands. This recharge, enhancement or construction of wetlands is ' known as habitat restoration. Specific to North Carolina and Brunswick County is the use of either constructed or existing wetlands as a non -discharge treatment alternative. In the coastal areas of Brunswick County there are numerous opportunities to utilize ' existing wetlands areas. The South Brunswick Water and Sewer Authority (SBWASA), of which the Town of Sunset Beach is a member, has looked specifically at the use of 10 Carolina Bays for further treatment of secondary treated effluent. Other such areas exist within close proximity of virtually all of the participants in this study. Advantages: • Utilizes existing and constructed wetlands which are abundant in the study area. • Allows for secondary treatment levels rather than tertiary. • Has a high degree of environmental acceptability. Disadvantages: • Not a common treatment method in North Carolina, leading to potential public perception problems. • Potentially requires long pumping distances and therefore higher costs. This Alternative is potentially suitable for all participants. 4.2.6 Alternative No. 6 - Ocean Outfall As they exist now, ocean outfalls of any kind for treated effluent area not allowed by the North Carolina Division of Water Quality. With that in mind, the discussion should still proceed from a technical feasibility standpoint. There are two options available for ocean outfalls. First is the use of the existing Carolina Power & Light (CP&L) Brunswick Nuclear Facility's cooling water canal and outfall. This outfall takes flow from the Lower Cape Fear River and draws it into the facility for cooling purposes. It then pumps it from the facility, across the Intracoastal Waterway, to Oak Island and through a 2000 LF +/- ocean outfall for discharge. The flow through this outfall is approximately 1,000,000 gpm. The discharge side of the canal runs from the Nuclear Facility, northwest of Southport, along the eastern border of the Southeast Brunswick Sanitary District, across the waterway and into the vicinity of Yaupon and Caswell Beaches. The second option would involve construction of a new ocean outfall, exclusively for effluent discharge. This option would have to be pursued as a true geographically regional disposal alternative in order to be cost effective and to help with environmental approval which will certainly require an Environmental Impact Statement. Advantages, Option 1. CP&L Canal: • Allows use of an existing outfall facility which will greatly reduce costs. • The existing facility is located geographically close to all participants in the study except Sunset Beach. • Negotiations have already taken place with CP&L and some state regulators to determine viability. • The existing canal flows at 1,000,000 gpm+, which would allow tremendous dilution of the effluent flow. 11 I Disadvantages, Option 1, CP&L Canal: ' Would certainly require a major environmental effort with the public and the State of North Carolina. ' Would require contractual agreements with CP&L. Likely will require tertiary treatment for any participant's effluent. • Creates problems by virtue of the fact that the entire canal/outfall flow is pumped, not gravity. • The existing outfall extends only 2,000 LF +/- into the ocean, which is relatively short. Advantages, Option 2, New Outfall: • Provides a new custom designed facility that can handle the effluent ' disposal needs for all participants for the future. Disadvantages. Option 2, New Outfall: ' The capital cost of a new ocean outfall will be extremely high. The State of North Carolina currently opposes any ocean outfall for treated effluent. ' • This concept does not promote beneficial use of effluent. • Would likely require tertiary treatment levels for all participants. ' The environmental process for a new ocean outfall would be arduous, with no guarantee of success. ' Both options may only be suitable for the SE corner participants. 4.2.7 Alternative No. 7 - Surface Discharge ' As with the ocean outfall alternative, there are two general options for a surface discharge. The first option would be a discharge to inland surface or fresh waters. This would follow the Division of Water Quality's normal N.P.D.E.S. permitting format. The problem to be solved would be to find a suitable creek or swamp with enough flow to accommodate a regional discharge flow. This would also require a major environmental effort with consideration given to virtually all other alternatives, especially reuse alternatives, prior to consideration of an inland surface discharge. The second option is also a surface discharge, but this would be to estuarine waters. Currently, the City of Southport has such a discharge to SC waters of the Intracoastal Waterway. Also included in the consideration of discharge locations would be the Lower Cape Fear River as a new discharge. Discussions have already been held with the Division of Water Quality concerning the Lower Cape Fear River discharge. Preliminary limits were obtained in a letter (included 12 in Appendix) which called for tertiary requirements, with nutrient limits. This discharge would be geographically favorable, as would a potential expansion of the Southport plant (see 4.2.10) and discharge. Either point would also be able to handle the amount of flow from all the participants because of the very large dilution. No discharge would be allowed to SA waters or tributaries to SA waters. Advantages. Option One, Inland Surface Discharge: • Depending on pumping requirements, maybe one of the lowest capital cost alternatives. Depending on discharge location, could be very geographically favorable. Disadvantages, Option One, Inland Surface Discharge: • Virtually no adequate location for discharge due to lack of dilution flow. • Difficult environmental process, with other alternatives, especially reuse, given consideration first. • Pumping requirements would likely mean high capital and O&M costs for all participants. • Does not promote beneficial use of treated effluent. • Will require tertiary treatment with nutrient limits. Advantages. Option Two, Estuarine Discharge: • The likely location is geographically close to all study participants except Sunset Beach. • Preliminary limits and discussions have already happened with the Division of Water Quality. • The City of Southport has a current discharge to the Intracoastal Waterway (see 4.2.10). • Relatively low cost alternative with direct surface disposal. Disadvantages, Option Two, Estuarine Discharge: • Difficult environmental process, with other alternatives, especially reuse, given consideration first. • Pumping requirements would likely mean high capital and O&M costs for all participants. • Does not promote beneficial use of treated effluent. • Will require tertiary treatment with nutrient limits. 4.2.8 Alternative No. 8 - Land Application For the purposes of this study, land application means subsurface application of treated effluent in a restricted access area, dedicated to effluent disposal. The treatment level is secondary, at a minimum, so as to prevent clogging of the soil structure, but in some cases, tertiary treatment may be required. 13 This disposal method does not include injection of the treated effluent for the purposes of groundwater recharge, which is currently not allowed in N.C. Advantages: • Relatively low capital and O&M cost disposal alternative. • Depending on final application process, may only require secondary treatment of effluent. Disadvantages: • Would require a relatively large amount of land, suitable for the disposal purpose and in close proximity to the participants. • The disposal site would have to be dedicated to disposal and off limits to public access. • Environmental approval may be difficult since this does not truly promote beneficial use of the effluent. This Alternative is potentially suitable for all participants. I I 4.2.9 Alternative No. 9 - Rapid infiltration Rapid infiltration involves the application of treated effluent over a deep permeable sand bed at a high rate by rotary distributors. The effluent is treated further by several I' processes as it travels through the soil filter matrix. Pre -application treatment levels can vary from primary treatment only, to help avoid premature soil clogging, to tertiary levels to avoid nuisance conditions in populated areas. The treated effluent is applied to the surface by flooding the shallow basin over a variable period of time which helps drive air through the matrix. As the soil matrix begins to clog and slow infiltration rates, tillage of the sand bed or removal of the top few inches will generally restore full infiltration capability. Storage/equalization basins area often included for periods between flooding periods. Advantages: • Relatively simple process of disposal. • May only require primary or secondary treatment prior to flooding basin. • Relatively low land requirements due to high application rates. • Capital and O&M costs are relatively low. Disadvantages: • Recent technical and environmental concerns may create serious siting and permitting problems. • Does not promote beneficial use of the treated effluent. 14 • Requires areas of land for the exclusive use of disposal with restricted access. This Alternative is potentially suitable for all participants. 4.2.10 Alternative No. 10 - City of Southport This Alternative is very similar to Alternative No. 7 - Surface Discharge, but with some specific refinements. In the past 2 years, and even more intensively in the past few months, there have been numerous discussions concerning the use of the City of Southport's POTW as a regional facility. In the Fall of 1995, the Southeast Brunswick Sanitary District (SBSD) had brief discussions with City personnel concerning the City accepting wastewater from SBSD for treatment and discharge to the Intracoastal Waterway. Due to time constraints associated with the expansion and upgrade necessary at the Southport POTW to accept all of the SBSD's flow, this idea was not pursued any further. Subsequent to those initial discussions, an agreement was reached for Southport to treat and discharge up to 100,000 gpd from the SBSD as part of the solution to the problems with the River Run Shopping Center Packaged Plant. In the last few months, discussions have been held between several of the study participants and the City of Southport towards having the Southport POTW become a truly regional facility by treating and disposing of wastewater potentially from the Town of Long Beach, the Town of Yaupon Beach, the Town of Caswell Beach at a minimum. Pursuit of this Alternative would require construction of separate collection systems with pumping to Southport. At the Southport end, an expansion and likely upgrade of their existing POTW would have to occur. This might also mean a relocation of the plant site and discharge point. ' Advantages: Provides a truly regional approach to treatment and disposal. ' Would likely be very cost effective with individual collection, but common treatment and a surface discharge • Discussions have already taken place among several of the study ' participants. Will help promote cooperation among the study participants ' Disadvantages: • Does not promote beneficial use of the effluent, as presented. • Geographically, would not benefit the Town of Sunset Beach directly. ' Will likely require a relocation of Southport's POTW. • Will require relatively large pumping costs by each participant. ' 15 ' SECTION V COST ESTIMATES 5.1 General ' The basic cost information has been generated using actual data, as much as possible. We have attempted to use recent bid tabulation information for similar projects and types of work. These estimates cover a very broad range of types of work and potential cost items. They are not meant to be an exhaustive and detailed construction cost estimate, but rather a summary of the major elements of each alternative and approximate costs for each, for comparison. 5.2 Methodology/Assumptions Because the main purpose and scope of this study is to look at disposal alternatives and the relative costs of each, no estimates are provided for individual municipal collection or treatment systems. The following list shows a summary of specific assumptions made for each Alternative. 5.2.1 Alternative No. 1 Assumptions: • The municipality would participate in the construction of a new golf course, specifically in the irrigation system costs. • Pumping distance assumed to be 20,000 LF maximum for each participant to each golf course. • For an existing course the municipality would participate in the costs for irrigation pond additions, piping modifications and signage. • Each golf course is assumed to be able to irrigate up to 400,000 gpd. • Costs shown represent the costs per each course See Table Nos. 3 and 3A for a breakdown of the anticipated costs for an existing course and a new course, respectively. Only Table NO. 3A, Alternative 1A is used for the present worth calculations and further comparison. 5.2.2 Alternative No. 2 ' Assumotions: • Because of the limited capacity of the Cogentrix facility, only those flows, not already being treated/disposed, will be considered. ' Actual, scaled force main distances will be considered. • No flow is considered from the Town of Sunset Beach. ' 16 ' • No effluent storage facilities are included; they are assumed to be part of the ' individual treatment facilities. • Engineering and administrative costs reflect one contract for all work. See Table No. 4 for a breakdown of the anticipated costs for all Southeast county participants to go to Cogentrix. ' 5.2.3 Alternative No. 3 Assumptions: • That suitable forest lands exist within 10 miles of the southeast corner of Brunswick ' County, making them accessible to all but the Town of Sunset Beach. • That each acre of forest land can dispose of 3,500 gallons per day of treated effluent. ' • The forest land to be used will be purchased, assumed cost to be $2,000/acre. • Common force mains will be used, as much as possible. • All municipalities will use existing methods, with any new or expanded flow to go to ' the forest. • Each sprinkler head will cover approximately 5,000 SF (0.11 acres). tSee Table No. 5 for a breakdown of the anticipated cost for all southeast county participants going to a single forest tract. The Town of Sunset Beach could utilize their I' own system, perhaps within closer proximity. They would need potentially several hundred acres in order to plan for 20-year flows (seasonal and permanent). I' 5.2.4 Alternative No. 4 It would be very difficult, and beyond the scope of this study, to do a detailed cost estimate for each municipality for a complete reuse system. With the exception of the actual treatment processes, there is virtually no difference between this type of system and a potable water system from an equipment standpoint. What will be presented in the cost estimate is a basic type system with approximately 1000 connections. While a purely residential/commercial system may not be cost effective at first, the idea of a small scale, trial system may be attractive in order to build public confidence and secure more customers, both residential and industrial, for the future. • That there will be 1000 residential connections to the system, with meters. • That each connection will use an average of 50 gpd. • That there will be a large commercial, recreational or municipal use that can account for at least 5,000 gpd. • A minimum 50,000 gallons of enclosed ground storage will be provided. • That there will be approximately 40,000 LF of 4" lines, 20,000 LF of 3" lines and 10,000 LF of 2" lines. See Table No. 6 for a breakdown of anticipated costs. 17 I ' 5.2.5 Alternative No. 5 Assumptions: That the southeast county area will find suitable land within five miles of the participants and to the greatest extent possible, use a common force main. • That the Sunset Beach area will have suitable land within five miles. • That this will be a constructed wetlands area with conditions site adapted. ' Construction for both the southeast county area and the Sunset Beach area will occur under one contract. 1 1 1 I I I - See Table No. 7 for a breakdown of anticipated costs. 5.2.6 Alternative No. 6 Assumptions: • That this will be a viable alternative after negotiations with C.P.& L and the Division of Water Quality. • All effluent will be discharged to a single point in the canal. • Each participant will already meet the minimum treatment levels required by the regulatory authorities. • Each participant will already have any storage, facilities, in place that may be required. • The discharge will be designed to take all the 20-year flow from each participant, with the exception of any flows that are committed elsewhere. • No estimate is provided for a new outfall due to the extremely high costs, especially with such a small total flow, i.e., the economies of scale are not there. See Table No. 8 for a breakdown of anticipated costs. 5.2.7 Alternative No. 7 Assumptions: • The discharge point will be to the class SC estuarine waters of the Cape Fear River northeast of Southport. • All participants will use a common force main, to the greatest extent possible. • The discharge will be designed to take all the 20-year flow from all participants, with the exception of any flows that are committed elsewhere. Each participant will be responsible for their own treatment and any storage that may be required. See Table No. 9 for a breakdown of anticipated costs. 5.2.8 Alternative No. 8 The assumptions for this Land Application Alternative are much the same as Alternative No. 3 - Spray Irrigation of Forest Lands, for the purposes of cost estimating. This Alternative uses the same estimate as for Alternative No. 3 due to the similarities in size 18 and scope and the assumption that suitable land exists within 10 miles of the participants. See Table No. 10 for a breakdown of anticipated costs. 5.2.9 Alternative No.9 The pumping and site location are assumed to be the same as for Alternative Nos. 3 and 8. The only real difference is the size and nature of the site necessary to dispose of the effluent. While the site size needed is smaller than Alternative Nos. 3 & 8, the specific site requirements are more difficult and the rapid infiltration basin would need to be specifically site built. See Table No. 11 for a breakdown of anticipated costs. 5.2.10 Alternative No. 10 For cost estimating purposes, the assumptions for this alternative are very similar to Alternative No. 7, with the exception of the location of the discharge point being near the existing wastewater treatment plant and the plan to have regional treatment as well. That means that each participant will collect its own wastewater, then pump it, untreated, to the new Southport facility. It is also assumed that the new Southport facility will be relocated on a new site nearby. The final assumption is, similar to Alternative No. 7, that Sunset Beach will not be a part of this approach. See Table No. 12 for a breakdown of anticipted costs. 5.3 Net Present Worth Table No. 13 shows a Net Present Worth Analysis summary based on actual capital cost estimates, plus the annual operation and maintenance cost taken over a 20-year period with an 8% discount rate and a 3% annual escalation rate. Table No. 14 is a chart of the same information presented in Table No. 13. 19 1 2 3 4 5 ESTIMATE OF ANTICIPATED COST ALTERNATIVE NO. 1 - GOLF COURSE REUSE, EXISTING COURSE LONG BEACH REGIONAL SEWER STUDY LONG BEACH, BRUNSWICK COUNTY, NORTH CAROLINA TABLE NO. 3 ITEM QUANTITY UNIT PRICE TOTAL Effluent Pumping Station (0.4 MGD Average) 1 LS 100,000 $ILS $ 100,000 10" Force Main 20,000 LF 20 $1LF $ 400,000 Irrigation Pond Construction 1 LS 250,000 $ILS $ 250,000 Piping Modifications at Course 1 LS 50,000 $ILS $ 50,000 Signage , Miscellaneous Modifications 1 LS 20,000 $ILS $ 20,000 ENGINEERING, SURVEYING & CONSTRUCTION ADMINISTRATION CONSTRUCTION OBSERVATION LEGAL & ADMINISTRATIVE RIGHTS OF WAY & EASEMENTS CONTINGENCY (10 % ) TOTAL PROJECT COST SUBTOTAL $ 820,000 $ 100,000 $ 75,000 $ 10,000 $ 10,000 $ 101,500 $ 1,116,500 ALTERNATIVE NO.1 TABLE NO.3 ESTIMATE OF ANTICIPATED COST ALTERNATIVE NO. 1A - GOLF COURSE REUSE, NEW COURSE LONG BEACH REGIONAL SEWER STUDY LONG BEACH, BRUNSWICK COUNTY, NORTH CAROLINA TABLE NO. 3A ITEM 1 Effluent Pumping Station (0.4 MGD Average) 2 10" Force Main 3 Irrigation Pond Construction 4 Spray Irrigation System , Complete 5 Seeding, Pond Piping & Misc. Modifications ENGINEERING, SURVEYING & CONSTRUCTION ADMINISTRATION CONSTRUCTION OBSERVATION LEGAL & ADMINISTRATIVE RIGHTS OF WAY & EASEMENTS CONTINGENCY (10 % ) TOTAL PROJECT COST QUANTITY 1 LS 20,000 LF 1 LS 1 LS 1 LS UNIT PRICE 100,000 $ILS 25 $ILF 300,000 $ILS 800,000 $ILS 75,000 $ILS SUBTOTAL ANNUAL OPERATION AND MAINTENANCE COSTS ITEM 1 Staff 11 Operator ) 2 Utilities ( PIS Electrical ) 3 Pump Station Maintenance 4 Line Maintenance TOTAL ANNUAL O & M COST TOTAL $ 100,000 $ 500,000 $ 300,000 $ 800,000 $ 75,000 $ 1,775,000 $ 160,000 $ 75,000 $ 10,000 $ 20,000 $ 204,000 $ 2,244,000 ESTIMATED ANNUAL COST $ 45,000 S 5,000 $ 5,000 $ 5,000 $ 60,000 ALTERNATIVE NO. 1A TABLE NO.3A 1 2 3 4 5 6 7 8 ESTIMATE OF ANTICIPATED COST ALTERNATIVE NO. 2 - INDUSTRIAL REUSE @ COGENTRIX LONG BEACH REGIONAL SEWER STUDY LONG BEACH, BRUNSWICK COUNTY, NORTH CAROLINA TABLE NO.4 ITEM Effluent Pumping Station (2.25 MGD Average ) Effluent Pumping Station( 0.25 MGD Average) 12" Force Main from Long Beach 8" Force Main from Caswell Beach 8" Force Main from Boiling Spring Lakes 8" Force Main from S B S D 8" Force Main from Yaupon Beach Vaiving / Piping Modifications @ Cogentrix ENGINEERING, SURVEYING & CONSTRUCTION ADMINISTRATION CONSTRUCTION OBSERVATION LEGAL & ADMINISTRATIVE RIGHTS OF WAY & EASEMENTS CONTINGENCY (10 % ) TOTAL PROJECT COST QUANTITY 1 EA 4 EA 45,000 LF 20,000 LF 45,000 LF 5,000 LF 5,000 LF 1 LS UNIT PRICE 750,000 $/EA 75,000 $/EA 30 $/LF 20 $/LF 20 $/LF 20 $/LF 20 $/LF 50,000 $/LS SUBTOTAL ANNUAL OPERATION AND MAINTENANCE COSTS ITEM 1 Staff (1 Operator, 1 Asst. ) 2 Utilities ( PIS Electrical ) 3 Pump Station Electrical 4 Line Maintenance TOTAL ANNUAL O & M COST TOTAL $ 750,000 $ 300,000 $ 1,350,000 $ 400,000 $ 900,000 $ 100,000 $ 100,000 $ 50,000 $ 3,950,000 $ 450,000 $ 250,000 $ 50,000 $ 50,000 $ 475,000 $ 5,225,000 ESTIMATED ANNUAL COST $ 70,000 $ 55,000 $ 25,000 $ 25,000 $ 175,000 ALTERNATIVE NO. 2 TABLE NO. 4 1 2 3 4 5 6 7 8 9 10 11 12 13 14 1 2 3 4 5 ESTIMATE OF ANTICIPATED COST ALTERNATIVE NO. 3 - SPRAY IRRIGATION LONG BEACH REGIONAL SEWER STUDY LONG BEACH, BRUNSWICK COUNTY, NORTH CAROLINA TABLE NO. 5 ITEM Effluent Pumping Station (2.25 MGD Average) Effluent Pumping Station( 1.75 MGD Average) Effluent Pumping Station( 0.25 MGD Average) 20" Common Force Main 12" Force Main from Long Beach 8" Force Main from Caswell Beach 8" Force Main from Boiling Spring Lakes 8" Force Main from S B S D 8" Force Main from Yaupon Beach 14 " Force Main ( Sunset Beach ) Spray I Sprinkler System , Per Head Spray / Sprinkler System , Per Head Spray Irrigation Site , Per Acre ( S.E. County ) Spray Irrigation Site , Per Acre ( Sunset Beach ) ENGINEERING, SURVEYING & CONSTRUCTION ADMINISTRATION CONSTRUCTION OBSERVATION LEGAL & ADMINISTRATIVE RIGHTS OF WAY & EASEMENTS CONTINGENCY (10 % ) TOTAL PROJECT COST QUANTITY UNIT PRICE TOTAL 1 EA 750,000 $IEA $ 750,000 1 EA 500,000 $IEA $ 500,000 4 EA 75,000 $IEA $ 300,000 25,000 LF 40 $/LF $ 1,000,000 15,000 LF 30 $/LF $ 450,000 10,000 LF 20 $ILF $ 200,000 25,000 LF 20 $/LF $ 500,000 5,000 LF 20 $ILF $ 100,000 5,000 LF 20 $ILF $ 100,000 25,000 LF 35 $ILF $ 875,000 10,000 HD 500 $IHD $ 5,000,000 5,000 HD 500 $IHD $ 2,500,000 1,100 AC 2,000 $IEA $ 2,200,000 600 AC 2,000 $IEA $ 1,200,000 SUBTOTAL $ 14,925,000 ANNUAL OPERATION AND MAINTENANCE COSTS ITEM Staff 11 Operator, 2 Assts. ) Utilities ( PIS & Site Electrical ) Pump Station Electrical Line Maintenance Spray System Maintenance TOTAL ANNUAL O & M COST $ 1,250,000 $ 250,000 $ 100,000 $ 50,000 $ 1,657,500 $ 18,232,500 ESTIMATED ANNUAL COST S 100,000 $ 80,000 $ 35,000 $ 35,000 $ 50,000 $ 300,000 ALTERNATIVE NO. 3 TABLE NO. 6 ESTIMATE OF ANTICIPATED COST ' ALTERNATIVE NO.4 - COMPLETE REUSE SYSTEMS LONG BEACH REGIONAL SEWER STUDY ' LONG BEACH, BRUNSWICK COUNTY, NORTH CAROLINA TABLE NO. 6 ' ITEM QUANTITY UNIT PRICE TOTAL 1 Effluent Pumping Station ( 0.15 M.G.D. w/ V.S.D.) 1 EA 200,000 $/EA $ 200,000 2 4" Reuse Main ( Includes Valving ) 40,000 LF 15 $/LF $ 600,000 3 3" Reuse Main ( Includes Valving) 20,000 LF 12 $/LF $ 240,000 4 2" Reuse Main ( Includes Valving) 10,000 LF 10 $/LF $ 100,000 Long Meter Service 400 EA 750 $/EA $ 300,000 '5 6 Short Meter Service 600 EA 450 $/EA $ 270,000 7 0.05 MG Ground Storage Tank w/ Pumps 1 LS 175,000 $/LS $ 175,000 1 SUBTOTAL $ 1,885,000 ENGINEERING, SURVEYING & CONSTRUCTION ' ADMINISTRATION $ 225,000 CONSTRUCTION OBSERVATION $ 150,000 -LEGAL & ADMINISTRATIVE $ 30,000 ' RIGHTS OF WAY, EASEMENTS & LAND $ 30,000 CONTINGENCY (10 %) $ 232,000 TOTAL PROJECT COST $ 2,552,000 ANNUAL OPERATION AND MAINTENANCE COSTS ITEM 1 Staff ( 1 Operator , 2 Assts. ) 2 Utilities ( P/S Electrical) 3 Pump Station Electrical 4 Line I System Maintenance TOTAL ANNUAL O & M COST ESTIMATED ANNUAL COST $ 100,000 $ 4,000 $ 5,000 $ 20,000 $ 129,000 ALTERNATIVE NO.4 TABLE NO.5 ESTIMATE OF ANTICIPATED COST ' ALTERNATIVE NO. 5 - HABITAT RESTORATION LONG BEACH REGIONAL SEWER STUDY LONG BEACH, BRUNSWICK COUNTY, NORTH CAROLINA ' TABLE NO. 7 ITEM QUANTITY UNIT PRICE TOTAL 1 Effluent Pumping Station (2.25 MGD Average) 1 EA 500,000 $IEA $ 500,000 2 Effluent Pumping Station ( 1.5 MGD Average) 1 EA 250,000 $IEA $ 250,000 Effluent Pumping Station (0.25 MGD Average) 4 EA 75,000 $IEA $ 300,000 '3 4 20" Common Force Main (S.E. County) 25,000 LF 40 $ILF $ 1,000,000 5 12" Force Main ( Sunset Beach) 25,000 LF 30 $ILF $ 750,000 6 Misc. Site Work ( S.E. County ) 1 LS 175,000 $ILS $ 175,000 7 Misc. Site Work ( Sunset Beach) 1 LS 75,000 $ILS $ 75,000 8 Control Structures @ Wetland ( S.E. County) 1 LS 175,000 $ILS $ 175,000 Control Structures @ Wetland ( Sunset Beach j 1 LS 75,000 $ILS $ 75,000 '9 10 Wetlands, Per Acre ( S. E. County ) 20 AC 5,000 $/AC $ 100,000 11 Wetlands, Per Acre ( Sunset Beach ) 10 AC 5,000 $/AC $ 50,000 SUBTOTAL $ 3,450,000 ENGINEERING, SURVEYING & CONSTRUCTION ADMINISTRATION $ 450,000 CONSTRUCTION OBSERVATION $ 150,000 LEGAL & ADMINISTRATIVE $ 50,000 RIGHTS OF WAY & EASEMENTS $ 50,000 CONTINGENCY (10 %) $ 415,000 TOTAL PROJECT COST $ 4,565,000 ANNUAL OPERATION AND MAINTENANCE COSTS ITEM 1 Staff 11 Operator, 2 Assts. ) 2 Utilities ( PIS Electrical ) 3 Pump Station Maintenance 4 Line Maintenance 5 Onsite System Maintenance TOTAL ANNUAL O & M COST ESTIMATED ANNUAL COST $ 100,000 $ 80,000 $ 35,000 $ 35,000 $ 50,000 $ 300,000 ALTERNATIVE NO. 5 TABLE NO.7 ESTIMATE OF ANTICIPATED COST ' ALTERNATIVE NO. E - OCEAN OUTFALL , C. P. & L CANAL / OUTFALL LONG BEACH REGIONAL SEWER STUDY LONG BEACH, BRUNSWICK COUNTY, NORTH CAROLINA ' TABLE NO. 8 ITEM QUANTITY UNIT PRICE TOTAL 1 Effluent Pumping Station (2.25 MGD Average) 1 EA 750,000 $/EA $ 750,000 2 Effluent Pumping Station ( 0.25 MGD Average) 4 EA 75,000 $/EA $ 300,000 3 12" Force Main from Long Beach 25,000 LF 30 $/LF $ 750,000 t 4 8" Force Main from Caswell Beach 10,000 LF 20 $/LF $ 200,000 5 8" Force Main from Boiling Spring Lakes 45,000 LF 20 $/LF $ 900,000 6 8" Force Main from S B S D 15,000 LF 20 $/LF $ 300,000 ' 7 8" Force Main from Yaupon Beach 5,000 LF 20 $/LF $ 100,000 8 Valving / Piping Modifications @ Cogentrix 1 LS 50,000 $/LS $ 50,000 ' SUBTOTAL $ 3,350,000 ENGINEERING, SURVEYING & CONSTRUCTION ADMINISTRATION $ 450,000 ' CONSTRUCTION OBSERVATION $ 150,000 LEGAL & ADMINISTRATIVE $ 50,000 ' RIGHTS OF WAY & EASEMENTS CONTINGENCY (10 %) $ $ 50,000 405,000 TOTAL PROJECT COST $ 4,455,000 ANNUAL OPERATION AND MAINTENANCE COSTS ESTIMATED ANNUAL COST ITEM 1 Staff ( 1 Operator, 1 Asst. ) $ 70,000 ' 2 Utilities ( P/S Electrical ) $ 55,000 3 Pump Station Electrical $ 25,000 4 Line Maintenance $ 25,000 ' TOTAL ANNUAL O & M COST $ 175,000 I ' ALTERNATIVE NO.6 TABLE NO.8 1 ESTIMATE OF ANTICIPATED COST ' ALTERNATIVE NO.7 - SURFACE DISCHARGE LONG BEACH REGIONAL SEWER STUDY ' LONG BEACH, BRUNSWICK COUNTY, NORTH CAROLINA TABLE NO. 9 ITEM QUANTITY UNIT PRICE TOTAL ' 1 Effluent Pumping Station( 2.25 MGD Average) 1 EA 750,000 $IEA $ 750,000 2 Effluent Pumping Station( 0.25 MGD Average) 4 EA 75,000 $IEA $ 300,000 12" Force Main from Long Beach 35,000 LF 30 $ILF $ 1,050,000 '3 4 8" Force Main from Caswell Beach 10,000 LF 20 $ILF $ 200,000 5 8" Force Main from Boiling Spring Lakes 55,000 LF 20 $ILF $ 1,100,000 6 8" Force Main from S B S D 15,000 LF 20 $ILF $ 300,000 7 8" Force Main from Yaupon Beach 5,000 LF 20 $ILF $ 100,000 8 Valving I Piping Modifications @ Cogentriz 1 LS 50,000 $ILS $ 50,000 ' SUBTOTAL $ 3,850,000 ENGINEERING, SURVEYING & CONSTRUCTION ADMINISTRATION $ 500,000 ' CONSTRUCTION OBSERVATION $ 200,000 LEGAL & ADMINISTRATIVE $ 50,000 ' RIGHTS OF WAY & EASEMENTS CONTINGENCY (10 %) $ $ 75,000 467,500 TOTAL PROJECT COST $ 5,142,500 ANNUAL OPERATION AND MAINTENANCE COSTS ITEM 1 Staff ( 1 Operator, 1 Asst. ) 2 Utilities ( PIS Electrical) 3 Pump Station Maintenance 4 Line Maintenance TOTAL ANNUAL 0 & M COST ESTIMATED ANNUAL COST $ 70,000 $ 55,000 $ 30,000 $ 30,000 $ 185,000 ALTERNATIVE NO.7 TABLE NO. 9 1 2 3 4 5 6 7 8 9 10 11 12 13 14 1 2 3 4 5 ESTIMATE OF ANTICIPATED COST ALTERNATIVE NO. 8 - LAND APPLICATION LONG BEACH REGIONAL SEWER STUDY LONG BEACH, BRUNSWICK COUNTY, NORTH CAROLINA TABLE NO. 10 ITEM QUANTITY UNIT PRICE TOTAL Effluent Pumping Station (2.25 MGD Average) 1 EA 760,000 $/EA $ 750,000 Effluent Pumping Station ( 1.75 MGD Average) 1 EA 500,000 $/EA $ 500,000 Effluent Pumping Station( 0.3 MGD Average) 4 EA 75,000 $/EA $ 300,000 20" Common Force Main 25,000 LF 40 $/LF $ 1,000,000 12" Force Main from Long Beach 15,000 LF 30 $/LF $ 450,000 8" Force Main from Caswell Beach 10,000 LF 20 $/LF $ 200,000 8" Force Main from Boiling Spring Lakes 25,000 LF 20 $/LF $ 500,000 8" Force Main from S B S D 5,000 LF 20 $/LF $ 100,000 8" Force Main from Yaupon Beach 5,000 LF 20 $/LF $ 100,000 14 " Force Main ( Sunset Beach ) 25,000 LF 35 $/LF $ 875,000 Spray / Sprinkler System , Per Head 10,000 HD 500 $/HD $ 5,000,000 Spray / Sprinkler System , Per Head 5,000 HD 500 $/HD $ 2,500,000 Spray Irrigation Site , Per Acre ( S.E. County) 1,100 AC 5,000 $/EA $ 5,500,000 Spray Irrigation Site , Per Acre ( Sunset Beach) 600 AC 5,000 $/EA $ 3,000,000 SUBTOTAL $ 20,775,000 ENGINEERING, SURVEYING & CONSTRUCTION ADMINISTRATION $ 1,400,000 CONSTRUCTION OBSERVATION $ 300,000 LEGAL & ADMINISTRATIVE $ 100,000 RIGHTS OF WAY & EASEMENTS $ 100,000 CONTINGENCY (10 %) $ 2,267,500 TOTAL PROJECT COST $ 24,942,500 ANNUAL OPERATION AND MAINTENANCE COSTS ITEM Staff ( 1 Operator, 2 Assts. ) Utilities ( P/S Electrical) Pump Station Electrical Line Maintenance Onsite Maintenance TOTAL ANNUAL O & M COST ESTIMATED ANNUAL COST $ 100,000 $ 80,000 $ 35,000 $ 35,000 $ 70,000 $ 320,000 ALTERNATIVE NO. 8 TABLE NO. 10 ESTIMATE OF ANTICIPATED COST ' ALTERNATIVE NO. 9 - RAPID INFILTRATION LONG BEACH REGIONAL SEWER STUDY ' LONG BEACH, BRUNSWICK COUNTY, NORTH CAROLINA TABLE NO. 11 1 2 3 4 5 6 7 8 9 10 11 12 13 14 1 2 3 4 5 ITEM Effluent Pumping Station (2.25 MGD Average) Effluent Pumping Station ( 1.75 MGD Average) Effluent Pumping Station ( 0.3 MGD Average ) 20" Common Force Main 12" Force Main from Long Beach 6" Force Main from Caswell Beach 6" Force Main from Boiling Spring Lakes 6" Force Main from S B S D 6" Force Main from Yaupon Beach 14 " Force Main ( Sunset Beach ) Site Preparation ( S.E. County ) Site Preparation ( Sunset Beach ) Rapid Infiltration Site , Per Acre ( S.E. County ) Rapid Infiltration Site , Per Acre ( Sunset Beach ) ENGINEERING, SURVEYING& CONSTRUCTION ADMINISTRATION CONSTRUCTION OBSERVATION LEGAL & ADMINISTRATIVE RIGHTS OF WAY & EASEMENTS CONTINGENCY (10 % ) TOTAL PROJECT COST QUANTITY 1 EA 1 EA 4 EA 25,000 LF 15,000 LF 10,000 LF 25,000 LF 5,000 LF 5,000 LF 25,000 LF 1 LS 1 LS 60 AC 25 AC UNIT PRICE 750,000 $/EA 500,000 $IEA 75,000 $IEA 40 $ILF 30 $ILF 18 $ILF 18 $/LF 18 $ILF 18 $ILF 35 $ILF 1,200,000 $/LS 500,000 $ILS 5,000 $/AC 5,000 $IAC SUBTOTAL ANNUAL OPERATION AND MAINTENANCE COSTS ITEM Staff ( 1 Operator, 2 Assts. ) Utilities ( PIS Electrical) Pump Station Maintenance Line Maintenance Onsite System Maintenance TOTAL ANNUAL O & M COST TOTAL $ 750,000 $ 500,000 $ 300,000 $ 1,000,000 $ 450,000 $ 180,000 $ 450,000 $ 90,000 $ 90,000 $ 875,000 $ 1,200,000 $ 500,000 $ 300,000 $ 125,000 $ 6,810,000 $ 675,000 $ 175,000 $ 50,000 $ 20,000 $ 763,000 $ 8,393,000 ESTIMATED ANNUAL COST $ 100,000 $ 80,000 $ 50,000 $ 50,000 $ 100,000 $ 380,000 ALTERNATIVE NO.9 TABLE NO. I ESTIMATE OF ANTICIPATED COST ' ALTERNATIVE NO. 10 - CITY OF SOUTHPORT LONG BEACH REGIONAL SEWER STUDY LONG BEACH, BRUNSWICK COUNTY, NORTH CAROLINA TABLE NO. 12 ITEM QUANTITY UNIT PRICE TOTAL 1 Effluent Pumping Station (2.25 MGD Average) 1 EA 750,000 $/EA $ 750,000 2 Effluent Pumping Station( 0.25 MGD Average) 4 EA 75,000 $/EA $ 300,000 3 12" Force Main from Long Beach 25,000 LF 30 $ILF $ 750,000 4 8" Force Main from Caswell Beach 10,000 LF 20 $ILF $ 200,000 5 8" Force Main from Boiling Spring Lakes 40,000 LF 20 $ILF $ 800,000 6 8" Force Main from S B S D 15,000 LF 20 $ILF $ 300,000 7 8" Force Main from Yaupon Beach 5,000 LF 20 $ILF $ 100,000 SUBTOTAL $ 3,200,000 ENGINEERING, SURVEYING & CONSTRUCTION ADMINISTRATION $ 450,000 CONSTRUCTION OBSERVATION $ 150,000 LEGAL & ADMINISTRATIVE $ 50,000 RIGHTS OF WAY & EASEMENTS $ 50,000 CONTINGENCY (10 %) $ 390,000 TOTAL PROJECT COST $ 4,290,000 ANNUAL OPERATION AND MAINTENANCE COSTS ITEM 1 Staff ( 1 Operator, 1 Asst. ) 2 Utilities ( PIS Electrical ) 3 Pump Station Maintenance 4 Line Maintenance TOTAL ANNUAL O & M COST ALTERNATIVE NO. 10 TABLE NO. 12 ESTIMATED ANNUAL COST $ 70,000 $ 55,000 $ 25,000 $ 25,000 $ 175,000 NET PRESENT WORTH ANALYSIS LONG BEACH REGIONAL SEWER STUDY LONG BEACH, BRUNSWICK COUNTY, NORTH CAROLINA TABLE NO. 13 ALTERNATIVE ALTERNATIVE ALTERNATIVE ALTERNATIVE ALTERNATIVE ALTERNATIVE ALTERNATIVE ALTERNATIVE ALTERNATIVE ALTERNATIVE ITEM NO IA NO.2 NO.3 NO.4 NO.5 NO.6 NO.7 NO.8 NO.9 NO 10 CAPITAL COST $ 2,244.000 $ 5,225,000 $ 18.232.500 $ 2,552,000 $ 4,565,000 $ 4,455,000 $ 5,142,500 $ 24,942,500 $ 8.393.000 $ 4,290,000 ANNUAL 0 & M COST $ 60,000 $ 175,000 $ 300.000 $ 129,000 $ 300.000 $ 175.000 $ 185.000 $ 320,000 $ 380,000 $ 175.000 NET PRESENT WORTH COSTS N. P. W. OF 0 3 M $ 757.080 $ 2.208.150 $ 3,785.400 $ 1.627.722 $ 3.785.400 $ 2.208.150 $ 2,334,330 $ 4.037.760 $ 4.794,840 $ 2,208,150 TOTAL CAPITAL COST $ 2.244,000 $ 5,225.000 $ 18,232.500 $ 2,552,000 $ 4,565,000 $ 4,455,000 $ 5,142.500 $ 24,942,500 $ 8,393,000 $ 4,290,000 TOTAL PRESENT WORTH $ 3.001.080 $ 7.433.150 $ 22.017.900 $ 4,179.722 $ 8.350,400 $ 6.663,150 $ 7,476,830 $ 28,980.260 $ 13.187.840 $ 6,498,150 NET PRESENT WORTH TABLE NO.13 $30,000.000 $25,000.000 $20,000.000 $15,000.000 $10,000,000 $5.000,000 S- O Z W a z Lu w N CM a} Z Z Z W W W � J � ¢ ¢ ¢ Lu Lu LLI LONG BEACH REGIONAL SEWER STUDY PRESENT WORTH ANALYSIS CHART TABLE NO.14 Ln <u i- Z Z Z W W W > > 1 z z zLu Ill LLJ PRESENT WORTH ANALYSIS CHART TABLE NO.14 w rn o Z Z Z Lu Ill > W r- I- w w '--+-ANNUAL 0 & M COST -6 N.P. W. OF O & M -A-TOTAL CAPITAL COST - X TOTAL PRESENT WORTH SECTION VI ALTERNATIVE ANALYSIS 6.1 General Table No. 15, Alternative Analysis Matrix shows a matrix comparing several basic factors that are important to the selection of a recommended alternative. Each alternative is rated for each factor on a scale of 1 to 10 with 1 being the least acceptable/favorable and 10 being the most acceptable/favorable. Special notice should be taken of several items: 1. Each of the factors in this matrix is given equal importance. Any form of "weighting" can be applied in order to more accurately reflect the goals of the participants in this study. 2. The same logic applies to the individual ranking within each factor, i.e., it can be adjusted based on additional input from the study participants. I' 3. Several of these factors are self explanatory, such as "Capital Cost", "Total Present Worth", Promotion of Beneficial Use", "Promotion of Regionalization" and "Land Requirements and Restrictions". 4. "Environmental Acceptability" involves the potential ease of receiving a Finding of No Significant Impact (FONSI) through the State review process. 5. "Technical Feasibility" is a measure of the compatibility of each alternative with existing, commonly used technologies. 6. "Future Expandability" deals with the ease of, or restrictions on, expandability to handle any possible 20 year flows or even beyond. 7. "Public Acceptability" refers to the public that will be directly affected and served by the particular alternative and their potential positive or negative reaction to any part of it. This is partly related to "Environmental Acceptability", but this deals more with individual responses vs. State and Federal agencies. 8. "Regulatory Acceptability" reflects the acceptability by the various State permitting authorities for each alternative. This is partly related to virtually all the other factors with the possible exception of cost issues. 9. 'Other Issues" tries to account for any other forces at work in this discussion such as work already done on an alternative, past negative or positive reactions to ideas and political sensitivity. 20 ' 6.2 Recommendations ' Overall, Alternative No. 10 - Regional treatment and discharge by the City of Southport ranks the highest and would therefore be the recommended alternative. ' Some other issues that must be dealt with are as follows: 1. Virtually all of the participants are at different places in the development of ' wastewater systems. This makes it very difficult to determine individual cost shares and timing. This study assumes that, at a minimum, each participant will develop its own collection system, and in some cases, their own treatment facilities as well. ' The recommended alternatives does assume that a regional treatment plant will be built in Southport. Costs for this plant were not included in order to have a fair comparison with the other alternatives. ' 2. Any future treatment facilities should be planned around tertiary treatment levels in order to be compatible with all possible disposal options, if individual treatment is desired. ' 3. Those participants that currently have permits and facilities in place for effluent disposal should continue with those facilities for now, but shouid look for the future ' elimination of those facilities, when a regional alternative becomes a reality. 4. A regional authority or entity should be established that will look after and promote regionalization throughout the County and not just among the study participants. ' 5. Discussions should be held early on with any affected environmental and regulatory entities since virtually all of the Alternatives have some potential negative ' impacts. This will allow an open dialogue and decision making process by partnering all involved parties. It should also serve to make the permitting and environmental approval processes go smoother. 6. All possible funding options should be pursued initially, until the most viable sources are identified. 21 ALTERNATIVE ANALYSIS MATRIX LONG BEACH REGIONAL SEWER STUDY LONG BEACH, BRUNSWICK CUUN I Y , NUK I H CAKULINA ALTERNATIVES N `o Z y 1 i U) 1 '° I w' h 12 l °° Z I °> O i K 0 0 i 00' Oai1 O O� Oa' Off! 6r- Oa z ww z w I zF wa; zDI ww z i w za! wI+ Z3: wy za� to z�i w Zx wI- >� FD >x! ��! >C7 FBI >� I pw > ~ol >j! ~oi >� I ~w J aa' >t aLL » aN Z o Z z Z— I Z w i Z Z Z J i Z V Z Q Z�' Z a i w col I.- a J e6 gal t�z I �O FACTORS r--- J o J o J a IIIII.- J o ; ►.--W J J ►w-� J 7 J Iw-di J J a�f a�� a_q,� au ate. a�_-1--aU) ag a�w a0 ENVIRONMENTAL ACCEPTABILITY 91 10 71 5 8 1 11 3 7 i 4! 3 CAPITAL COST 10 4 2I 9 6 7! 5 1! 31 8 TOTAL PRESENT WORTH 10 61 2i 9I 4 7 5 1 31 8 PROMOTION OF BENEFICIAL USE 81 91 7. 10 61 1 5 ` 41 1 ! 1 _1 3I 7! 1 7 -1 9 8� 7 71 10 PROMOTION OF REGIONALIZATION I — TECHNICAL FEASIBILITY 3 6. 4! 71. 1 101 101 5 2 10 I FUTURE EXPANDABILITY 3 1 61 4 21: 101 9! 6 7 9 PUBLIC ACCEPTABILITY 8 10 41 1; 6! 2i 71 4i 3 9 REGULATORY ACCEPTABILITY 9 10I 8i 5i 6 1' 1i 81 4i 3 LAND REQUIREMENTS & RESTRICTIONS 5, 9 11 6' 4, 10 8 1 I 3' 7 OTHERISSUES 7 2 51 8; 6! 91 41 ; 1-- 10 -_ TOTALS, 73 70' 531 65i 56 611 661 49 41j 78 ANALYSIS MATRIX TABLE NO.15 ' SECTION VII FUNDING ALTERNATIVES 7.1 Funding Currently, there are several different funding methods available. Among these are: 1. North Carolina Revolving Loan Fund This fund has a very favorable interest that is half the market rate and requires no Facilities Plan Amendment. However, funding is limited and the maximum loan amount is 3 million dollars. Also, a high priority is given to POTW's that are under a JOC or an SOC and have completed plans and specifications. 2. EPA/NC Revolving Loan Fund This fund also has a very favorable interest rate, but requires a Facilities Plan, has a limited budget and does require plans and specifications prior to priority ranking. 3. North Carolina Bond Program This is the newest fund but it currently has no money available. When in existence, it had the highest interest rate, required a facilities plan and plans and specifications. This fund was a non -revolving loan program. Extra ranking points were given to areas that had interjurisdictional agreements in place to achieve regionalization. 4. Various Grant Funds ' These include EDA, CDBG-ED, Industrial Development and Supplemental Grants. They have varying maximum amounts that are relatively small and require some form of justification of economic hardship. 5. General Obligation/Revenue Bonds These are the traditional ways for local municipalities to fund large scale capital improvements. They require adequate financial resources for payback and a vote of the citizens for General Obligation Bonds or approval by elected officials for revenue bonds, among other requirements. 6. U.S.D.A./Rural Development Administration (RDA) Grants and Loans The Rural Development Administration still offers a small amount of grants-in-aid for - extremely low income communities. 22 I 11. I' A large majority of water and sewer projects in North Carolina are financed through the Rural Development Administration loan program. Over the past several years approximately 25 million dollars has been made available each year in North Carolina ' under the loan program. Utilization of a RDA loan through General Obligation Bonds can be a viable alternative for study participants in this area. ' 7. Local Lending Institutions Many governmental bodies are looking to local banks and other lenders to provide funding for capital projects. A local institution may see an advantage in helping to develop the community. Loan policies, interest rates and maximum loan amounts will vary. 23