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HomeMy WebLinkAbout; Master Plan of Sewerage 1987; Master Plan of Sewerage; 1987-12-30CITY OF CARLSBAD MASTER PLAN OF SEWERAGE December, 1987 Wilson Engineering Consulting Engineers CITY OF CARLSBAD City Council Members Claude A. Lewis-Mayor Ann J. Kulchin - Mayor Pro-Tenn John J. Mannaux Mark V. Pettine Eric Larson WILSON ENGINEERING DEXTER S. WILSON. P.E. KEVIN E. SCHMIDT. P.E. ANDREW M. OVEN. RE. December, 1987 101-007 City of Carlsbad 2075 Las Palmas Drive Carlsbad, CA 92009 Attention: City of Carlsbad Council Subject: Master Plan of Sewerage In accordance with our agreement approved by Council on February 17, 1987, we are submitting a report on the sewerage system improvements and the fiscal impact of these improvements on the City of Carlsbad. The report presents a phased program for the construction of major sewage facilities to serve the study area beyond the year 2000. The total estimated costs for the future recommended facilities for the City of Carlsbad is $56,824,000. Of this total, $49,126,000 is to be funded through capacity fees and will be constructed by the City of Carlsbad. In order to finance these facilities, this report recommends increasing the capacity fee to $1,247 per unit. The remaining $7,698,000 will be funded through development. This report is prepared in accordance with and as required by the Growth Management Program. It is designed to effectively assist in the administration of the Growth Management Program, and should be updated annually. We appreciate the opportunity to provide you with the engineering services involved in the preparation of this report. We would be pleased to discuss our findings and recommendations with you. Wilson^ Engineering Dexter S. Wilson DSW:jaa 2185 FARADAY AVENUE, SUITE 140 CARLSBAD. CALIFORNIA 92008 (619) 438-4422 TABLE OF CONTENTS VOLUME 1 PAGE NO. LIST OF TABLES v LIST OF FIGURES vii CHAPTER 1. INTRODUCTION Master Plan Modification . 2 History 2 Summary 3 Chapter 2 - Description of Study Area .... 3 Chapter 3 - Land Use and Population Planning in Study Area 3 Chapter 4 - Existing Sewerage System 3 Chapter 5 - Wastewater Flow Projection Criteria 3 Chapter 6 - Design Criteria and Unit Construction Costs 4 Chapter 7 - Improvement Program 4 Chapter 8 - Revenue Program Requirements ... 4 Chapter 9 - Reclamation Program 4 Conclusions 5 Acknowledgments 6 CHAPTER 2. DESCRIPTION OF STUDY AREA Study Area 7 Topography 7 CHAPTER 3. LAND USE AND POPULATION PLANNING IN STUDY AREA Land Use 12 Current Land Use 12 Projected Land Use 12 Population Projections 12 Present Population 15 Future Population 15 CHAPTER 4. EXISTING SEWERAGE SYSTEM Description of Existing Conveyance System 17 Vista/Carlsbad Interceptor 19 Buena Vista Lift Station (Unit C) 19 Agua Hedionda Lift Station (Unit G) . . . . 19 North Agua Hedionda Interceptor 23 Foxes Landing Lift Station 23 Trunk Sewers 23 Buena/San Marcos Interceptor System 27 Buena Interceptor 27 San Marcos Interceptor 27 North Batiquitos Interceptor 31 North Batiquitos Lift Station 31 Trunk Sewers 31 TABLE OF CONTENTS (Continued) Other Existing Lift Stations Wastewater Treatment Facilities Encina Water Pollution Control Facility (Unit I) Treatment Plant Ownership and Capacity (Unit I) Encina Ocean Outfall System (Unit J) . .' Lake Calavera Hills Water Reclamation Plant CHAPTER 5. WASTEWATER FLOW PROJECTION CRITERIA Flow Factors Average Daily Flow [ Peak Flows [ [ Flow Projections CHAPTER 6. DESIGN CRITERIA AND UNIT CONSTRUCTION COSTS Design Criteria Gravity Sewers Force Mains and Sewage Lift Stations .... Unit Costs Gravity Sewers and Force Mains Sewage Lift Stations CHAPTER 7. IMPROVEMENT PROGRAM Conveyance System Improvements Wastewater Treatment System Improvements . . ! ! Encina Capital Improvement Program Phase IV Project Solids Management Program Ocean Outfall Improvements Lake Calavera Hills Water Reclamation Plant Improvements to the Lake Calavera Hills Water Reclamation Plant CHAPTER 8. REVENUE PROGRAM REQUIREMENTS Use of Funds Sewer Service Charges [ [ Capacity Fees [ Capacity Fee !!!!!** CHAPTER 9. RECLAMATION PROGRAM Water Reclamation Issues Cost .*.*.'!.'.* Cost of Reclaimed Water Capital Costs [ Regulations !!!!!* Regional Water Quality Control Board .... State Health Department Existing Reclaimed Water Facilities ....**** 31 35 35 35 36 37 39 39 39 40 45 45 45 46 46 47 49 61 61 62 62 63 63 63 65 65 65 66 67 67 67 68 68 68 69 69 11 TABLE OF CONTENTS (Continued). Conveyance System 69 Water Reclamation Plants 70 The Lake Calavera Hills Water Reclamation Plant 70 Meadowlark Water Reclamation Plant .... 70 Shadow Ridge Water Reclamation Plant ... 70 Gafner Water Reclamation Plant 70 Facilities 70 Summary 73 LIST OF REFERENCES 75 VOLUME 2 Appendices A. Equivalent Dwelling Units and Wastewater Flow Projections by Zone A-l B. Summary of Computer Flow Projections . . . B-1 C. Growth Management Monitoring Program . . . C-l D. Lake Calavera Hills Water Reclamation Plant Report D-1 E. Justification of Flow Generation Factors . E-1 F. Lift Station Data Sheets F-1 G. Interagency Agreements G-1 111 iv LIST OF TABLES PAGE NO, Table 1-1 Summary of Recommended Improvements . . 5 Table 3-1 Population Estimates for Study Area . . 11 Table 4-1 Engineering Data for the Vista/Carlsbad Interceptor 20 Table 4-2 Engineering Data for the North Agua Hedionda Interceptor 24 Table 4-3 Engineering Data for the Buena Interceptor 28 Table 4-4 Engineering Data for the San Marcos Interceptor 28 Table 4-5 Engineering Data for the North Batiquitos Interceptor 32 Table 4-6 Current Encina Water Pollution Control Facility Ownership and Capacity .... 36 Table 4-7 Current Encina Ocean Outfall Ownership and Capacity Rights 37 Table 4-8 Lake Calavera Hills Water Reclamation Plant Capacity of Major Process Units . 37 Table 5-1 Unit Flow Generation Factors 40 Table 5-2 Existing and Future Wastewater Flow Estimates 40 Table 5-3 Wastewater Flow Projection 43 Table 6-1 Unit Construction Costs 46 Table 7-1 Improvements to Vista/Carlsbad Interceptor Sewage Drainage Basin ... 49 Table 7-2 Improvements to North Agua Hedionda Interceptor Sewage Drainage Basin ... 53 Table 7-3 Improvements to South Agua Hedionda Interceptor Sewage Drainage Basin ... 54 Table 7-4 Improvements to Buena/San Marcos Interceptor Sewage Drainage Basin ... 57 Table 7-5 Improvements to North Batiquitos Interceptor Sewage Drainage Basin ... 58 Table 7-6 Improvements to the Encina Water Pollution Control Facility 62 Table 7-7 Improvements to the Lake Calavera Hills Water Reclamation Plant 64 Table 8-1 Connection Fees 66 vi LIST OF FIGURES PAGE NO. Figure 2-1 Figure 3-1 Figure 4-1 Figure 4-2 Figure 4-3 Figure 4-4 Figure 5-1 Figure 7-1 Figure 7-2 Figure 7-3 Figure 7-4 Figure 7-5 Figure 9-1 Exhibit A Study Area and Sewer Drainage Basins 9 Sewer Drainage Zones 13 Vista/Carlsbad Interceptor System . . 21 North Agua Hedionda Interceptor System 25 Buena/San Marcos Interceptor System . 29 North Batiquitos Interceptor System . 33 Peaking Factor Chart 41 Improvements to Vista/Carlsbad Interceptor System ... 51 Improvements to North Agua Hedionda Interceptor System 52 Improvements to South Agua Hedionda Interceptor System 55 Improvements to Buena/San Marcos Interceptor System 56 Improvements to North Batiquitos Interceptor System 59 Reclaimed Water Lines and Potential Use Areas 71 Recommended Improvement Program Vll viii CHAPTER 1 INTRODUCTION On July 1, 1986, the City Council of Carlsbad adopted a Growth Management Plan designed to insure provision of adequate facilities to accommodate future development. Implementation of the Growth Management Program was envisioned as a three level system involving a Citywide Facilities and Improvement Plan, the preparation of 25 Zone Facilities Plans and individual project approvals. The Citywide Plan established performance standards for eleven critical services. Subsequent zone plans are to show how each area of the City of Carlsbad proposes to meet those standards. The Sewer Collection System and Wastewater Treatment Capacity were two key elements in the Growth Management Plan. The Citywide Facilities and Improvement Plan established the following standards for sewer collection and wastewater treatment: SEWER COLLECTION SYSTEM PERFORMANCE STANDARD - Trunk line capacity to meet demand as determined by the appropriate sewer district must be provided concurrent with development. WASTEWATER TREATMENT CAPACITY PERFORMANCE STANDARD - Sewer plant capacity is adequate for at least a five year period. As a further implementation of the Growth Management Program, the voters of the City of Carlsbad in November of 1986 passed Proposition E approving the Growth Management Program and establishing a cap on total buildout dwelling units of 54,599. These units were assigned to quadrants of the City of Carlsbad. This current revision of the Sewer Master Plan is required to reflect the changes necessitated by the Growth Management Program and is designed to effectively assist in the administration of that program. To accomplish this task the sewer basins identified in previous master plans have been redefined consistent with zone boundaries. Interceptor and trunk systems are evaluated in terms of conformance with standards over time related to each growth management zone. Appendix B contains an analysis of each interceptor sewer keyed to development in each growth management zone. By maintaining records of development and flow data within each sewer subbasin, the City of Carlsbad staff will be able to insure adequate capacity to meet the sewer collection standards concurrent with development activities. Master Plan Modification Two significant changes in sewer system design are incorporated into the current master plan: 1. The Lake Calavera Hills Water Reclamation Plant Service Area has been redesigned such that the sewer system can function with or without the operation of the reclamation plant. Policies related to plant operation are detailed in Chapter 5 and Appendix D. 2. The Palomar Oaks Business Park Area located north of Palomar Airport Road and east of El Camino Real has been diverted from the South Agua Hedionda Drainage Basin into the Buena Outfall serving the Encina Canyon Drainage Basin. With minor exceptions, the current master plan follows and builds upon previous master plan data and systems. HISTORY The first sewer service in the City of Carlsbad area was provided by the Carlsbad Sanitary District. The Carlsbad Sanitary District was formed in 1929. During the same year, a sewage treatment plant and a system of sewer lines covering the northwest corner of the present downtown area of the City of Carlsbad were constructed. Thus, portions of the City of Carlsbad's existing conveyance system date back as far as 1929. The original treatment plant location was on the south shore of the Buena Vista Lagoon adjacent to Carlsbad Boulevard. This is the present location of the Home Plant Lift Station which pumps flow from the old treatment plant site into the Vista/Carlsbad Interceptor. The Carlsbad Sanitary District provided sewer service until the City of Carlsbad incorporated in 1952. When the City of Carlsbad incorporated, there were approximately 600 parcels of property being served by the Carlsbad Sanitary District. The City of Carlsbad expanded the sewer system and the number of connections continued to grow. In 1960, the old treatment plant site adjacent to Carlsbad Boulevard was heavily taxed and new facilities were needed. This led to the planning and construction of the Encina Water Pollution Control Facility by the City of Carlsbad and the Vista Sanitation District. The Encina Water Pollution Control Facility was put into operation in 1965 and all flows to the old Carlsbad Sanitary District plant were diverted to the new facility which has been utilized by the City of Carlsbad to treat all of their flows since that time. SUMMARY Chapter 2 - Description of Study Area The study area consists of about 70 percent of the City of Carlsbad and contains 19,221 acres. There are five major sewage drainage basins within the study area and these are shown on Figure 2-1. Chapter 3 - Land Use and Population Planning in Study Area The present population of the study area is 39,000. The ultimate population of the study area is projected to be 95,700, but will not be reached until well after the year 2000. The majority of the development in the City of Carlsbad is currently in the coastal strip and is predominantly residential development. Development will proceed inland and the percentage of commercial and industrial development will increase. Chapter 4 - Existing Sewerage System The City of Carlsbad wastewater collection system utilizes about 100 miles of sanitary sewers, 15 sewage lift stations and 2 -treatment plants. There are currently four major wastewater interceptor systems within the City of Carlsbad. These interceptors are the Vista/Carlsbad Interceptor, the North Agua Hedionda Interceptor, the Buena/San Marcos Interceptor System and the North Batiquitos Interceptor. The City of Carlsbad is a part owner of the Encina Water Pollution Control Facility, which is located within the study area. The City of Carlsbad also owns the Lake Calavera Hills Water Reclamation Plant. The Lake Calavera Hills Water Reclamation Plant is currently not being operated and major improvements would be needed to make it operational. Chapter 5 - Wastewater Flow Projection Criteria Average wastewater flows from the City of Carlsbad were projected using 220 gallons per day per equivalent dwelling unit. All industrial and commercial development was projected based on estimated equivalent dwelling units and converted to projected flows utilizing the same 220 gallons per day per equivalent dwelling unit figure. The average flow was converted to peak flow utilizing the sliding scale contained in Figure 5-1. The ultimate average flow from the City of Carlsbad was estimated to be 13.41 million gallons per day. Chapter 6 - Design Criteria and Unit Construction Costs The City of Carlsbad design criteria and standards of the industry were utilized to design facilities in this report. Cost estimates were based on present unit costs for pipelines and force mains and lump sums for sewage lift stations. Chapter 7 - Improvement Program Table 1-1 provides a summary of the recommended improvement program for the City of Carlsbad wastewater system. This program provides for a total expenditure of $56,824,000. Of this total, $49,126,000 is to be funded through connection fees and will be constructed by the City of Carlsbad. The remaining $7,698,000 will be funded through development. When this system is in place, it will provide a sewer to each of the sewer drainage basins developed in this report. Chapter 8 - Revenue Program Requirements There are $49,126,000 worth of improvements to be funded by the City of Carlsbad recommended in this report. These facilities will serve an additional 39,380 equivalent dwelling units. Thus, the cost per equivalent dwelling unit for the facilities recommended in this report is $1,247. This amount should be adjusted annually to keep up with inflation. Chapter 9 - Reclamation Program The costs and regulations associated with the use of reclaimed water make its use prohibitively expensive at the present time. Facilities are in place which could provide the backbone of the reclaimed water production and distribution system if there were users. No additional monies should be spent on the reclaimed water program until a user base has been developed. Table 1-1. Suimnary of Recommended Improvements Item C ost.-j, thousands of dollars 1987-1989 1990-1994 1995-1999 Beyond 2000 When Needed for Development Total Encina Water Pollution Control Facility Improvements 11,011 12,492 1,950 0 0 25,453 Ocean Outfall 97 0 9,825 0 0 9,922 Lake Calavera Hills Water Reclamation Plant 0 0 0 2,633 0 2,633 Interceptor System Vista/Carlsbad Interceptors Lift Stations Trunkal 1,270 945 0 0 38 0 985 0 0 1,350 442 0 0 0 388 3,605 1,425 388 North Agua Hedionda Trunks' 0 0 0 0 660 660 South Agua Hedionda Interceptors Lift Stations Trunks' 0 0 0 0 0 0 1,083 850 0 0 850 0 0 0 3,760 1,083 1, 700 3,760 Buena/San Marcos Interceptors Lift Stations Trunks' 0 0 0 0 0 0 0 1,250 0 122 0 0 0 0 1,465 122 1,250 1,465 North Batiquitos Lift Stations Trunks' 0 0 833 0 0 0 0 0 0 1,425 833 1,425 City Maintenance Facility 0 0 500 0 0 500 Monitoring Program 60 100 100 340 0 600 TOTAL 13,383 13,463 16,543 5,737 7,698 56,824 1. Developer Funded Facility. CONCLUSIONS 2, 3, The major interceptor system is in place, with the exception of the South Agua Hedionda Interceptor. The South Agua Hedionda Interceptor is included as a City of Carlsbad funded facility west of El Camino Real. Timing and phasing of this facility requires further study to insure compatibility with the Growth Management Plan. Several improvements will be needed to the Vista/Carlsbad Interceptor within five years. The Home Plant Lift Station should be replaced. 5 4. The Lake Calavera Hills Water Reclamation Plant should not be activated at the present time. The plant should only be utilized if there is a use for reclaimed water or if the City of Carlsbad has insufficient capacity at the Encina Water Pollution Control Facility. There is approximately a two year start up time to put the improvements in place which would be needed to operate the Lake Calavera Hills Water Reclamation Plant. 5. Gravity sewer lines should be installed to all sewage lift stations in Zone 2 and Zone 7. These stations are currently used to direct flows toward the Lake Calavera Hills Water Reclamation Plant. These gravity interceptors should be constructed in conjuction with development where possible. 6. The Lake Calavera Hills Water Reclamation Plant and all lift stations which direct sewage toward it should be mothballed but maintained so they can be utilized at a future date. 7. The City of Carlsbad should obtain 13.41 million gallons per day average flow of treatment capacity at the Encina Water Pollution Control Facility. 8. The current connection fees should be increased to assure that adequate funds will be available to meet the capital improvement program recommended in this report. 9. An annual monitoring program should be adopted as described in Appendix C. ACKNOWLEDGMENTS For their capable assistance during the course of this study, we wish to express our appreciation to the following people: Lloyd Hubbs, City of Carlsbad; Steve Jantz, City of Carlsbad; and Phillip Carter, City of Carlsbad. CHAPTER 2 DESCRIPTION OF STUDY AREA The study area and major sewage drainage basin areas are shown in Figure 2-1. STUDY AREA The study area is the sewer service area of the City of Carlsbad. About 70 percent of the City of Carlsbad is contained within the study area. The remainder of the City of Carlsbad is sewered by the Leucadia County Water District and the San Marcos County Water District. There are 19,221 total acres in the study area. The study area is bounded on the north by the City of Oceanside. The eastern border is formed by the City of Vista, the Buena Sanitation District and the San Marcos County Water District. The Leucadia County Water District provides the southern boundary of the study area and the Pacific Ocean provides the western boundary. Figure 2-1 also shows the location of the Encina Water Pollution Control Facility. The Encina Water Pollution Control Facility is a regional wastewater treatment plant and provides sewer service to the City of Carlsbad, the City of Vista, the Buena Sanitation District, the San Marcos County Water District, the Leucadia County Water District and the Encinitas Sanitary District. Since this facility is located in the City of Carlsbad, major interceptor sewers from all the other agencies served by this plant transport wastewater through the City of Carlsbad to this facility. The City of Carlsbad owns or leases capacity in all of the interceptors serving the other agencies. TOPOGRAPHY In general, the least costly and most efficient operation of sewage systems requires that planning and construction be dictated by watershed or topographic boundaries. There are five major sewage drainage basins within the study area. These sewage drainage basins are defined by the existing and planned interceptors within the City of Carlsbad. The most northerly of the sewage drainage basins is the Vista/Carlsbad Interceptor drainage basin. This sewer drainage basin begins at the eastern Carlsbad boundary along Highway 78 and generally follows Highway 78 to the Buena Vista Lagoon. At the Buena Vista Lagoon, the basin turns south along the coast and follows the railroad tracks past the Agua Hedionda Lagoon to the Encina Water Pollution Control Facility. The next sewer drainage basin to the south is the North Agua Hed ionda Interceptor drainage basin. This sewer drainage basin begins in Growth Management Zone 7 and follows westerly along the north shore of the Agua Hedionda Lagoon to the Vista/Carlsbad Interceptor. The next basin to the south is the South Agua Hedionda Interceptor sewer drainage basin. This basin generally follows the Agua Hedionda Creek from the City of Vista boundary to the Agua Hedionda Lagoon. The basin then follows the south shore of the Agua Hedionda Lagoon to the Vista/Carlsbad Interceptor basin. The Encina Canyon area is served by two major interceptors. These interceptors are the Buena Interceptor and the San Marcos Interceptor. This sewer drainage basin is called the Buena/San Marcos Interceptor basin since it is served by two interceptors. This basin also contains a portion of the Batiquitos Lagoon drainage area. This is also known as the North La Costa area. This area is planned to be pumped up to El Camino Real and flow into the San Marcos Interceptor. Thus, this drainage basin begins at the eastern boundary of the study area adjacent to the San Marcos County Water District and crosses the study area ending at the Encina Water Pollution Control Facility. The most southerly sewer drainage basin is the North Batiquitos Interceptor drainage basin. This basin starts at El Cami no Real and flows westerly along the north shore of the Batiquitos Lagoon to Interstate 5. At Interstate 5, this basin turns north and follows along Interstate 5 to the Encina Water Pollution Control Facility. The elevation of the study area varies from sea level along the coast and lagoon shores to just under 600 feet at the eastern boundary of the study area. This provides a substantial slope which aids in the design of an efficient sewage system. Since sewer lines generally follow the low areas of a watershed, there are a number of gravity sewers in the City of Carlsbad which end at lagoons or near the ocean. In order to convey these lines to a single location, lift stations are required. Thus, the study area sewer system is complicated by the fact that it is adjacent to the ocean and a number of lift stations and force mains are necessary to collect all the wastewater and convey it to the Encina Water Pollution Control Facility. CHAPTER 3 LAND USE AND POPULATION PLANNING IN STUDY AREA The study area has reached approximately 40 percent of its ultimate population. The present estimated population of the study area is 39,000. The ultimate population of the study area is projected to be 95,700. The ultimate population will not be reached until well after the year 2000. Table 3-1 provides the projected population and number of equivalent dwelling units through the year 2010 as well as the ultimate population and equivalent dwelling units of the study area. This table will be used to project growth trends for the study area. Table 3-1. Population Estimates for Study Area Year Population Equivalent Dwelling Units^ Present 39,000 21,555 1990 56,500 25,680 1995 69,000 31,360 2000 81,500 37,050 2005 86,200 42,730 2010 90,900 48,410 Ultimate 95,700 60,935 1. Includes commercial/industrial Equivalent Dwelling Units. See Appendix A and E for details. As part of the Growth Management Plan, the City of Carlsbad has been split into 25 planning areas. Some of these planning areas fall into more than one sewer drainage basin. Thus, these planning areas have been further split in this report in order to project flows from specific sewer drainage basins. Figure 3-1 shows the sewer drainage zones used to project flows. 11 LAND USE The land use in an area profoundly affects the amount of sewage generated by that area. In order to project sewage flows, the land use designation from the City of Carlsbad's general plan has been used to establish industrial and commercial square footages. Appendix A provides a summary of land use by zones. Current Land Use Most of the development in the City of Carlsbad is along the coastal strip. In the northern portion of the City of Carlsbad, development has proceeded eastward and is nearing the eastern boundary of the City of Carlsbad. This is the only portion of the study area which has residential development east of the coastal strip. There is also substantial industrial and commercial development within the City of Carlsbad including a regional shopping center and the Palomar Airport Business Park. Projected Land Use The projected land use of the study area shows greater commercial and industrial activity than presently found within the study area. Present commercial and industrial sewage flows represent only 15 percent of the total sewage flow from the study area. At build out it is estimated that these flows will account for one third of the flows from the study area. Thus, the mixture of development in the study area should change over time from mostly residential to an area which has a significant industrial and commercial contribution. This could affect sewage projections and peaking factors in the study area. POPULATION PROJECTIONS The population projections for the study area were based on the Comprehensive Planning Organization of the San Diego Region, Series 6 population projections. The projections were converted to residential dwelling units based on information prepared by the City of Carlsbad Planning Department. These residential dwelling units were divided into the individual zones shown on Figure 3-1. Appendix A provides present, approved and future residential dwelling units for each of the zones. 12 Present Population At the present time, approximately 60 percent of the population in the study area resides in the northwest quadrant. This quadrant is north of Palomar Airport Road and west of El Camino Real. Development has proceeded from this quadrant to the east across El Camino Real in the northern area of the City of Carlsbad and south along the coast. Future Population At build out, the northwest quadrant of the City of Carlsbad will contain approximately 40 percent of the population of the study area. Thus, the population will shift both easterly and southerly from the present center of population of the study area. 15 16 CHAPTER 4 EXISTING SEWERAGE SYSTEM The City of Carlsbad wastewater collection system utilizes about 100 miles of sanitary sewers ranging in size from 6 inches to 54 inches in diameter and 15 lift stations. The system has generally been laid out to conform to the watersheds of the Buena Vista, Agua Hedionda, Encina and San Marcos Creeks and to drain in a westerly direction thereby allowing the majority of the wastewater to be collected and transported by gravity. Since the City of Carlsbad is adjacent to the coast, a large number of lift stations are required to collect sewage from individual watersheds and convey it to a wastewater treatment facility. The City of Carlsbad has two wastewater treatment facilities that it can utilize. Currently all sewage from the City of Carlsbad is being treated at the Encina Water Pollution Control Facility. This facility is jointly owned by six agencies and has a current design capacity of 22.5 million gallons per day. The other facility which the City of Carlsbad could utilize if capital improvements were made is the Lake Calavera Hills Water Reclamation Plant. This facility has a design capacity of 1.2 mgd but cannot be utilized until a connection to the Encina Ocean Outfall is made. DESCRIPTION OF EXISTING CONVEYANCE SYSTEM At ultimate development, there will be five major interceptors within the City of Carlsbad. Four of these interceptor systems have been constructed and are now in use. Each of these existing interceptor systems will be described in this chapter. There are two categories of sewers other than interceptor sewers. They are trunk sewers and collector sewers. Trunk sewers are defined as sewers serving more than one growth management zone which have not been previously designated as interceptor sewers. Collector sewers are sewers which convey sewage from a single growth management zone. Trunk sewers are analyzed and described in this chapter. For information on collector sewers consult individual Growth Management Zone reports. 17 18 Vista/Carlsbad Interceptor The Vista/Carlsbad Interceptor starts just west of College Boulevard along Highway 78 at the Vista Meter. This interceptor serves all or portions of Growth Management Zones 1, 2, 3, 7, 22 and 25 and also intercepts flows from the North and South Agua Hedionda Interceptor systems. This interceptor is jointly owned by the City of Vista and the City of Carlsbad. The City of Carlsbad ownership rights in the interceptor increase in the direction of flow reaching greater than 50 percent ownership in the most downstream reaches of the interceptor. Table 4-1 provides engineering data for the gravity portions of this interceptor. Figure 4-1 shows the location of the interceptor. The interceptor parallels Highway 78 from College Boulevard to Jefferson Street. The Buena Vista Lift Station is located near the intersection of Jefferson Street and Highway 78. The force main from this lift station conveys the sewage along Jefferson Street, crosses Interstate 5, and empties into a gravity system. The gravity system then follows Jefferson Street to Grand Avenue and then follows Grand Avenue to the railroad easement. The interceptor then turns south and follows the railroad easement to the Agua Hedionda Lagoon. The Agua Hedionda Lift Station is located on the south side of the lagoon and lifts the sewage up to the gravity interceptor which follows the railroad easement to the Encina Water Pollution Control Facility. Buena Vista Lift Station (Unit C). The Buena Vista Lift Station is located on Jefferson Street at the head of the Buena Vista Lagoon and contains three wastewater pumps. All three pumps are capable of operating at variable speeds by means of an eddy current coupling between the pump and the electric motor. The lift station has a capacity of 17 mgd at the present time. There is a space to add two additional pumps to the station providing for an ultimate capacity of 26.3 mgd. Agua Hedionda Lift Station (Unit G). The Agua Hedionda Lift Station, located on the south side of Agua Hedionda Lagoon, contains four wastewater pumps. Two of these pumps are relatively new 12" x 12" x 21" pumps and there are two older, smaller pumps. All pumps are capable of operating at variable speeds by means of either an eddy current coupling or a variable frequency drive. The present capacity of the station is 24.5 million gallons per day. With the replacement of the two smaller pumps with larger pumping units, the capacity of the station could be expanded to 34.5 mgd. 19 Table 4-1. Engineering Data for the Vista/Carlsbad Interceptor Reach Engineering Data City of Carlsbad Ownership. Minimum Size, in. Minimum Slope, % Length, feet Full Pipe Capacity, mgd Percent Full Pipe Capacity, mgd Full Pipe Available Capacity,^ mgd VCl 36 0.50 6,690 30.0 0 0 0 VC2 42 0.28 2,790 34.0 15.5 5.3 4.7 VC3 36 0.20 3,170 19.5 15.5 3.0 1.6 VC5 27 (24) 0.36 2,500 12.0 27.3 2.6 0.9 VC6 30 0.24 1,180 13.0 27.3 3.3 1.6 VC7 27 1.64 760 25.0 27.3 6.8 4.4 VC8 36 0.10 720 13.8 27.3 3.8 1.0 VC9 36 0.10 1,940 13.8 37.3 5.1 1.5 VCIO 36 0.10 4,330 13.8 37.3 5.1 0.5 VCll 42 0.10 1,370 20.5 37.3 7.6 0.8 VC13 42 0.10 3,520 20.5 51.7 10.6 3.8 VCU 42 0.10 5,080 20.5 51.7 10.6 3.1 VC15 42 0.12 1,760 22.8 51.7 11.8 4.3 VC16 54 0.28 310 67.2 45.24 30.4 22.0 1. Available capacity as of January 1, 1987. 20 BUENA VISTA LIFT STATION VISTA METER STATION VCI5- 22A ^ ENCINA WATER POLLUTION CONTROL FACILITY LEGEND EXISTING SEWERAGE FACILITIES VISTA/CARLSBAD INTERCEPTOR BASIN BOUNDARY SEWER DRAINAGE ZONE BOUNDARY FIGURE 4-1 VISTA/CARLSBAD INTERCEPTOR SYSTEM 2! North Agua Hedionda Interceptor The North Agua Hedionda Interceptor was constructed in 1966. The interceptor starts at El Camino Real and flows westerly along the north shores of the Agua Hedionda Lagoon to the Foxes Landing Lift Station. The Foxes Landing Lift Station pumps the sewage up and across Interstate 5 into a short gravity interceptor which flows to the Vista/Carlsbad Interceptor. The North Agua Hedionda Interceptor enters the Vista/Carlsbad Interceptor just upstream of the Agua Hedionda Lift Station. This interceptor is entirely owned by the City of Carlsbad and conveys only the City of Carlsbad's sewage. Table 4-2 provides engineering data for the gravity portions of this interceptor and Figure 4-2 shows its location. This interceptor serves parts of Growth Management Zones 1, 2, 7 and 14. Foxes Landing Lift Station. The Foxes Landing Lift Station contains three pumps. Two of the pumps are the original units. The third, larger pump has recently been installed. The present capacity of this station is 3.3 mgd. The capacity of the station could be increased by replacing the two smaller, older pumps with larger units. Trunk Sewers. Figure 4-2 shows the existing trunk sewers in this basin. Trunk NAHTIB serves parts of Growth Management Zones 1, 2, 7 and 14. 23 Table 4-2. Engineering Data for the North Agua Hedionda Interceptor Reach Minimum Size, in. Minimum Slope, % Length, feet Full Pipe Capacity,^ mgd Full Pipe Available Capacity, 2 mgd NAHl 21 0.36 1,710 6.14 5.81 NAH2 24 0.10 4,570 4.62 4.07 NAH3 24 oao 4,680 4.62 2.66 NAH4 Siphons --200 6.29 4.33 NAH5 24 0.15 3,940 5.66 3.28 NAH7 18 1.0 1,360 6.79 4.41 NAHTIB 8 1.4 4,000 0.93 -0.533 1. 2. 3. City of Carlsbad retains 100 percent ownership of all reaches. Available capacity as of January 1, 1987. This pipe is in the process of being replaced. ro Ul LEGEND EXISTING SEWERAGE FACILITIES NORTH AGUA HEDIONDA BASIN BOUNDARY SEWER DRAINAGE ZONE BOUNDARY o VISTA/CARLSBAD INTERCEPTOR AGUA HEDIONDA LIFT STATION N N.T.S. FIGURE 4-2 NORTH AGUA HEDIONDA INTERCEPTOR SYSTEM Buena/San Marcos Interceptor System There are two major interceptors which follow the Encina Canyon to the Encina Water Pollution Control Facility. These are the Buena Interceptor and the San Marcos Interceptor. Both of these interceptors serve the Buena/San Marcos Interceptor drainage basin. All portions of Growth Management Zones 4, 5, 6, 10, 13, 17, 18 and 20 are served by these interceptors. Buena Interceptor. The Buena Interceptor flows through the Encina Canyon to the Encina Water Pollution Control Facility. This interceptor is owned by the Buena Sanitation District and was constructed in 1964. The City of Carlsbad has a lease of capacity in this line. The amount of leased capacity increases in the downstream reaches of this interceptor. Table 4-3 provides engineering data for the interceptor and a description of the City of Carlsbad's capacity rights in the interceptor. Figure 4-3 shows the location of the interceptor. The Buena Interceptor begins at the corner of El Camino Real and Palomar Airport Road at the discharge of the Buena force main and flows through the City of Carlsbad's industrial park. The interceptor then parallels Palomar Airport Road until just before Interstate 5, where the interceptor turns away from the road and crosses the freeway to the Encina Water Pollution Control Facility. San Marcos Interceptor. The San Marcos Interceptor is owned by the San Marcos County Water District, but the City of Carlsbad has capacity rights of 5 mgd throughout the length of the interceptor. The interceptor begins at the end of the San Marcos siphon near the intersection of Camino Vida Roble and El Camino Real. It then flows westerly through the industrial park. The interceptor then follows Palomar Airport Road westerly adjacent to the Buena Interceptor. Table 4-4 provides a description of the reaches and the City of Carlsbad ownership in the San Marcos Interceptor. 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CJ "o >> 4J 4J c o CTV c^ c^ in CM •rt 03 u O cn CM CM CM o Ll CM CM CM CM CM rH 03 CL 03 » ca, >, •rt 4J rs. 00 oo 00 cn CM CL •rt -O O 00 OV rH CO E CM cs CM CM CM rH a. 3 (0 fc. U o o o o o O CO 4J 4-1 vo rH rs. o cn IS. 4-1 00 0) CM in vo rH 00 CO e 03 a 03 <4H cn vo rH cn CM 00 c •rt LH 01 E - 03 3 01 s o. CO 00 00 VO in •rt •rt O »•« vo vo vO vo rH rH 00 C rH a •rt CO o o O o o o w s s 3 -E 03 . •rt N e o o O o CJV C •rt •rt cn cn cn cn cn m •rt CO JS o cn m vo rs oo (0 s s s Z 03 CO CO CO CO CO CO CtS aa OQ CQ 03 CQ CQ r^ 00 Ov u CO 3 B trt o CO (0 o CO Q. CO U to rH •rt to > < 28 BSM8 ENCINA WATER POLLUTION CONTROL FACILITY EXISTING SEWERAGE FACILITIES BUENA/SAN MARCOS INTERCEPTOR BASIN BOUNDARY SEWER DRAINAGE ZONE BOUNDARY FIGURE 4-3 BUENA/SAN MARCOS INTERCEPTOR SYSTEM North Batiquitos Interceptor The majority of the North Batiquitos Interceptor is owned 100 percent by the City of Carlsbad. The downstream reaches of this interceptor are owned jointly by the City of Carlsbad, the Leucadia County Water District and the Encinitas Sanitary District. Table 4-5 provides a description of the reaches and ownerships in the North Batiquitos Interceptor. Figure 4-4 shows the location of the interceptor. This interceptor serves all or portions of Growth Management Zones 4, 6, 9, 19, 20, 21 and 22. The North Batiquitos Interceptor begins on the north shore of the Batiquitos Lag oon near El Camino Real. The interceptor follows the north shore of the lagoon to the North Batiquitos Lift Station. This lift station pumps the sewage up and across Interstate 5. The interceptor then continues in a northerly direction and reaches the railroad easement near Poinsettia Lane. The interceptor then follows northerly along the railroad easement to an intersection point with the Vista/Carlsbad Interceptor outside of the Encina Water Pollution Control Facility. North Batiquitos Lift Station. The North Batiquitos Lift Station is currently a package Smith and Loveless lift station. This package lift station was installed in 1976. This sewage lift station cannot be expanded effectively and is scheduled to be replaced when additional capacity is needed. The present capacity of this station is 900 gallons per minute. Trunk Sewers. Table 4-5 provides a description of the existing trunk sewer in this basin. Trunk sewer NBT3B serves parts of Growth Management Zones 4 and 20. Other Existing Lift Stations There are nine lift stations which serve individual Growth Management Zones in the City of Carlsbad. Some of these sewage lift stations are permanent and some will eventually be abandoned. Appendix F provides information on each of these stations. 31 Table 4-5. Engineering Data for the North Batiquitos Interceptor Reach Engineering Data City of Carlsbad Ownership Minimum Size, in. Minimum Slope, % Length, feet Full Pipe Capacity, mgd Percent Full Pipe Capacity, mgd Full Pipe Available Capacity,^ mgd NBl 15 0.15 2,450 1.62 100 1.62 1.40 NB2 18 0.10 2, 180 2.14 100 2.14 1.92 NB3 21 0.10 1,970 3.24 100 3.24 3.02 NB4 24 0.10 4,430 4.62 100 4.62 4.40 NB6 18 0.80 1,930 6.07 100 6.07 5.39 NB7 21 0.20 3,300 4.57 100 4.57 3.77 NB8 27 0.16 3,100 8.00 100 8.00 7.02 NB9 39 0.16 1,430 21.3 40 8.52 7.54 NBIO 48 0.09 1,000 27.8 40 11.12 10.14 NBT3B 8 0.40 5,000 0.49 100 0.49 0.02 S5 1. Available capacity as of January 1, 1987. OJ OJ LEGEND EXISTING SEWERAGE FACILITIES NORTH BATIQUITOS INTERCEPTOR BASIN BOUNDARY SEWER DRAINAGE ZONE BOUNDARY FIGURE 4-4 NORTH BATIQUITOS INTERCEPTOR SYSTEM WASTEWATER TREATMENT FACILITIES The two treatment facilities which may be utilized by the City of Carlsbad are the Encina Water Pollution Control Facility and the Lake Calavera Hills Water Reclamation Plant. The present capacity of the Encina Water Pollution Control Facility is 22.5 million gallons per day and the City of Carlsbad owns 5.716 million gallons per day of this capacity. The capacity of the Lake Calavera Hills Water Reclamation Plant is 1.2 million gallons per day. Encina Water Pollution Control Facility (Unit I) In September, 1965, the Encina Water Pollution Control Facility commenced operation. The original primary treatment capacity, on the average dry weather flow basis, was 4.5 million gallons per day. Primary treatment capacity has been subsequently increased to 13.75 million gallons per day during three major enlargement phases referred to as Phase I, II, and IIA. Phases III and IIIA enlarged and upgraded the facility providing for full secondary treatment of 22.5 million gallons per day, with provisions for expansion to an ultimate average dry weather flow of 45 million gallons per day through modular addition to the basic unit processes. A Phase IV project report is currently being prepared to investigate the need for an expansion beyond 22.5 million gallons per day. The treatment processes consist of screening, grit removal, primary sedimentation, activated sludge secondary treatment, secondary sedimentation, anaerobic sludge digestion and belt press sludge dewatering. At the present time the plant is operated as an advanced Primary Treatment Plant. Treatment Plant Ownership and Capacity (Unit I). Table 4-6 shows the percentage of ownership and capacity in million gallons per day for each of the agencies in the Encina Water Pollution Control Facility. The City of Carlsbad owns 25.4 percent of the plant for a capacity of 5.716 million gallons per day. 35 Table 4-6. Current Encina Water Pollution Control Facility Ownership and Capacity Participant 2 Capacity, mgd Ownership, percent Vista 6.75 30.00 Carlsbad 5.716 25.40 Buena 1.034 4.59 San Marcos 4.00 17.78 Leucadia 3.75 16.67 Encinitas 1.25 5.56 Total 22.50 100.00 1. Section 6 - Seventeenth Supplement, 2. Average daily flow. Encina Ocean Outfall System (Unit J). The original outfall began operation concurrently with the plant in September, 1965. At that time, the entire outfall was 48-inch diameter reinforced concrete pipe. The outfall was 6,600 feet long; 1,100 feet was land outfall and 5,500 feet was ocean outfall. The outfall ended in approximately 100 feet of water. The last 325 feet of the outfall was the diffuser section, which originally contained 27 ports, each 6 inches in diameter. The ports were spaced at 12.5-foot centers on alternate sides of the pipe. In 1973, the ocean section of the outfall was extended 2,300 feet using 72-inch diameter reinforced concrete pipe. A new diffuser section was installed in the final 800 feet of the extension and the 27 ports in the old diffuser section were plugged. The average water depth in the new diffuser section is 159 feet, and water discharged through the outfall remains submerged under almost all conditions. The new diffuser section contains 138 ports. Table 4-7 provides and capacity. a breakdown of ocean outfall ownership 36 Table 4-7. Current Encina Ocean Outfall Ownership and Capacity Rights Agency Ownership, Capacity Rights,^ percent mgd Vista 16.67 6.75 Carlsbad 28.66 11.61 Buena 13.00 5.27 San Marcos 16.67 6.75 Leucadia 16.67 6.75 Encini tas 8.33 — _ 3.37 1. Capacity rights are for peak wet weather flow and based on an outfall capacity of 40.5 mgd. Lake Calavera Hills Water Reclamation Plant Construction of the Lake Calavera Hills Water Reclamation Plant as it now exists was completed in 1981. Since that time, the plant has been turned over to the City of Carlsbad for operation and maintenance. The plant is now owned entirely by the City of Carlsbad and all future upgrades and all costs for operation and maintenance of the plant are borne by the City of Carlsbad. A detailed description of this plant can be found in Appendix D. The design capacity of the plant is 1.2 million gallons per day. Table 4-8 provides a description of the major unit processes at the plant. Table 4-8. Lake Calavera Hills Water Reclamation Plant Capacity of Major Process Units Process Quantity Size Capacity Each Comminutor 1 2 mgd Peak Oxidation Ditch Reactors 2 650,000 gallons 0.6 mgd Average Clarifiers 2 113,700 gallons 0.6 mgd Average Chlorination Tanks 1 43,000 gallons 2 mgd (30 minutes) Aerobic Digester 1 75,000 gallons Belt Press Sludge Dewa taring 1 1/2 meter Emergency Power 1 300 KV 37 38 CHAPTER 5 WASTEWATER FLOW PROJECTION CRITERIA In order to determine deficiencies in the existing system and size future wastewater facilities, it is necessary to establish existing flows and project future flows. Flow estimates are based on either population or equivalent dwelling units. To ensure compatibility with the City of Carlsbad's Growth Management Plan, equivalent dwelling units have been used to project flows. FLOW FACTORS Some elements of the wastewater collection, treatment and disposal system are sized based on average flow. Other elements are sized based on peak flows. Thus, both average daily flow and peak flow must be projected in order to size all elements of the wastewater collection, treatment and disposal system. Average Daily Flow The average daily flow from the City of Carlsbad was projected using 220 gallons per day per equivalent dwelling unit. Three land use categories were adopted for the City of Carlsbad to project future flows. These categories are residential, commercial and industrial. Table 5-1 provides a summary of the unit flow generation factors used to project average daily flows in this report. Appendix E provides backup material showing how these generation factors were derived. Flow generation factors should be evaluated periodically as a part of the flow monitoring program. Peak Flows The ratio of the peak flow to the average flow varies with the number of equivalent dwelling units being projected. The larger the number of equivalent dwelling units, the smaller the peaking factor. Figure 5-1 was utilized to convert average flows to peak flows. 39 Table 5-1. Unit Flow Generation Factors General To convert Equivalent Dwelling Units to flow assume 220 gallons per day average flow. Commercial Property To convert raw land to square feet of building space assume 30 percent coverage. To convert improved pads to square feet of building space assume 40 percent coverage. To convert square feet of a building to Equivalent Dwelling Units assume 1,800 square feet per EDU. Industrial Property To convert raw land to square feet of building space assume 30 percent coverage. To convert improved pads to square feet of building space assume 40 percent coverage. To convert square feet of building to Equivalent Dwelling Units assume 60 percent of space is warehouse and 40 percent is office. For warehouse space 5,000 square feet equals one EDU and for office 1,800 square feet equals one EDU. FLOW PROJECTIONS In order to size the conveyance system, flows for each of the sewer drainage basins within Carlsbad. These individual basins were contributions to the conveyance system to conveyance system for deficiencies and future 5-2 provides a summary of the existing, approv flows and equivalent dwelling units for the Appendix A provides the same information for individual sewer drainage basins within Carlsbad. were projected the City of then used as analyze the needs. Table ed and future study area. each of the the City of Table 5-2. Existing and Future Wastewater Flow Estimates Land Use Exis ting Approved Future Totals Land Use EDUs Flow, mgd EDUs Flow, mgd EDUs Flow, mgd EDUs Flow, mgd Residential Commercial Industrial 18,442 1.664 1,835 4.06 0.37 0.40 3,606 779 2,767 0.79 0.17 0.61 20,462 6,462 4,943 4.50 1.42 1.09 42,510 8,905 9,545 9.35 1.96 2.10 Total 21,941 4.83 7,152 1.57 31,867 7.01 60,960 13.41 40 o UJ CD < cr LiJ < UJ 0. < cr. O.OI 0.02 OR LESS 0.0 AVERAGE FLOW (MILLION GALLONS PER DAY) FIGURE 5-1 PEAKING FACTOR CHART Table 5-3 provides an estimate of total flow from the study area in five year increments. This table is based on estimated population growth and industrial growth rates. This table will be used to determine when additional wastewater conveyance and treatment facilities will need to be constructed. Table 5-3. Wastewater Flow Projection Flow, Year mgd Present 4.74 1990 5.65 1995 6.90 2000 8.15 2005 9.40 2010 10.65 Ultimate 13.41 43 44 CHAPTER 6 DESIGN CRITERIA AND UNIT CONSTRUCTION COSTS DESIGN CRITERIA The design criteria for this report were based on the City of Carlsbad standards and standards of the industry. Gravity Sewers All gravity sewers have been designed to convey peak wet weather flow. For pipes with a diameter of 10 inches and smaller, the sewers have been designed to convey this flow when flowing one-half full. For pipes with a diameter of 12 inches and larger, the sewers have been designed to convey peak wet weather flows when flowing three-fourths full by depth. Manning's equation with n = 0.013 was used to size all gravity sewers. When projected flows were found to exceed the full pipe capacity of existing gravity sewers, a replacement sewer was designed per the above criteria. The replacement sewer was designed to convey all sewage generated in its service area and allow the existing sewer to be abandoned. All new sewers were designed to maintain a minimum velocity of 2 feet per second to prevent the deposition of solids. Prior to actual replacement of existing sewers, flow monitoring should be conducted to verify the analyses in this report. Force Mains and Sewage Lift Stations Sewage lift stations and force mains were designed as a unit. In general, all force mains were designed to maintain velocities between 3 and 5 feet per second. Hazen-Williams' equation with c = 120 was used to determine the losses in force mains. When an existing force main was inadequate to convey needed flows, a parallel force main was designed. The new force main was designed to convey only the additional capacity needed. It was assumed that the old force main would remain in service. All lift stations recommended in this report were designed in accordance with the following criteria. Each station was designed with a wet well and a separate dry well with at least two flooded suction centrifugal pumps. Each station was designed with standby pumping capacity so if a station 45 contains only two pumps each should be capable of pumping the total design flow. Each station was also designed with emergency power generation. All of the above parameters should be considered as guidelines and may change substantially during final design. UNIT COSTS The unit costs used to estimate costs in this report were based on recent construction bid prices. The costs in this report are based on an Engineering News Record Los Angeles Construction Cost Index of 5,500. Gravity Sewers and Force Mains Table 6-1 presents the unit costs used to develop costs for gravity sewers and force mains. These costs include a 35 percent allowance for construction contingencies, legal, engineering and administrative costs. The costs per foot include manholes. Table 6-1. Unit Construction Costs 1 Cost Per Foot, Pipe Type/Size-Inches dollars Gravity Sewers 8 65 10 75 12 90 15 105 18 120 21 135 24 150 27 175 30 200 36 225 42 275 48 325 54 375 60 425 66 475 Force Mains 6 45 8 55 10 65 12 80 16 100 18 UO 21 125 24 140 1. ENRLA-CCI 5,500 (10-87) 46 Sewage Lift Stations The cost for each sewage lift station was estimated as a lump sum based on actual construction costs for similar facilities. 47 48 CHAPTER 7 IMPROVEMENT PROGRAM This chapter provides a description of the needed improvements to the conveyance system and treatment plants. CONVEYANCE SYSTEM IMPROVEMENTS There are improvements needed to the existing interceptors and a new interceptor is needed. Tables 7-1 through 7-5 and Figures 7-1 through 7-5 show the recommended improvements to the City of Carlsbad conveyance system. These figures and tables are arranged on the basis of the five sewage drainage basins within the City of Carlsbad. The total estimated costs for improvements to the trunk and interceptor system is $56,824,000. The City of Carlsbad will fund through the connection fee process $49,126,000 of this amount. Developers will fund $7,698,000 of this amount. Facilities shown in yellow in Figure 7-1 through 7-5 are facilities which will be constructed by the City of Carlsbad through the use of connection fees. The developer funded facilities are shown in red. The connection fees are established on the basis of the City of Carlsbad funding only interceptor and interceptor lift station improvements. All improvements to trunk line collector sewers will be borne by the developers. Table 7-1. Improvements to Drainage Basin Vlsta/Carlsbad Interceptor Sewage IMPROVEMENTS TO EXISTING INTERCEPTORS Reach Location Size,^ Length, feet Total CBJI Year Reach Location in. Length, feet Cost, $ Ownership ,^ Z Cost, $ Needed VC3 Highway 78 East of Buena Vista Lagoon 42 3,170 871,750 15.5 135,120 Beyond 2000 VC5 Jefferson Street 36 2. 500 562,500 27.3 153,560 1989 VC6 Jefferson Street Arbuckle to Grand 42 1,180 324,500 27.3 88,590 1989 VC7 Grand Avenue 30 760 152,000 27.3 41,500 1989 VC8 Grand Avenue 48 720 234,000 27.3 63,880 1989 VC9 Washington Street Grand to Oak 48 1.940 630,500 37.3 235,180 1989 VCIO Washington Street Oak to Olive 48 4,330 1,407,250 37.3 524,900 1989 VClOA Chestnut Lateral 12 1,800 162,000 100 162,000 1989 VCll AT & SF R.R. Olive to Agua Hedionda Lagoon 54 1,370 513,750 37.3 191,630 Beyond 2000 49 Table 7-1. Improvements to Vista/Carlsbad Drainage Basin (Continued) Interceptor Sewage IMPROVEMENTS TO EXISTING INTERCEPTORS Reach VC13 VCl 4 VCl 5 Loca tion AT S SF R.R. Agua Hedionda Lagoon to Cannon AT « SF R.R. Cannon to Palomar Airport Road Avenida Encinas Palomar Airport Road to Encina Water Pollution Control Facility Entrance Size, 1 in. 54 54 54 Length, feet 3,520 5,080 1,760 Total Cost, $ 1,320,000 1,905,000 660,000 Ownership X CajlahaH 51.7 51.7 51.7 Subtotal Interceptor Improvements Cost, $ 682,440 984,890 341,220 3,604,910 Year Needed IMPROVEMENTS TO LIFT STATIONS Beyond 2000 1997 Beyond 2000 Description of Improvements Size, Length, Total Carlsbad Year in. feet Cost, $ Ownership, % Cost, $ Needed Buena Vista Lift Station Add Fourth Pump — 128,000 15.5 20,000 1989 Add Fifth Pump and Force Main Improvements — 531,000 15.5 82,000 Beyond 2000 Agua Hedionda Lift Station Add Third Pump and Miscellaneous Improvements — — 110,000 40.5 45,000 1989 Add Fourth Pump — 95,000 40.5 38,000 1990 Relocate Station — — 888,000 40.5 360,000 Beyond 2000 Home Plant Lift Station Relocate Station — 750,000 100 750,000 1989 Force Main 10 2,000 130,000 100 130,000 1989 Subtotal Lift Station Improvements 1,425,000 Subtotal City of Carlsbad Funded Improvements 5,029,910 CONSTRU CTION OF NEW TRUNK SEWERS Reach Location Size, ' Length, Total Carl shad Year in. feet Cost, $ Ownership ,^ % Cost, $ Needed VCTIA Buena Vista Creek 8 1,500 97,500 100 97,500 (3) VCTIB Buena Vista Creek 8 1,000 65,000 100 65,000 (3) VCTIC Buena Vista Creek 10 3,000 225,000 100 225,000 (3) Subtotal Developer Funded Improvements 387,500 TOTAL 5,417,410 Sizes recommended are based on ultimate flows from the City of Vista and the City of Carlsbad. Note: -Reaches VC3, VC5, VC6, VC7 and VC13 are recommended for improvements because of projected Vista flows exceeding full pipe capacity, Carlsbad does not exceed existing capacity rights. -Reaches VC8, VC9, VCIO, VCll, VCU and VC15 are recommended for improvements due to both the City of Vista and the City of Carlsbad exceeding existing capacity rights. These are current Carlsbad ownership percentages. They may change to reflect a larger need by Carlsbad or Vista when upgrading of the sewers is done. As required for development. 50 BUENA VISTA LIFT STATION VISTA METER STATION HOME PLANT LIFT STATION - /•^ \\\ ej •V \\\^ VC9 CITY OF CARLSBAD FUNDED IMPROVEMENTS DEVELOPER FUNDED MPROVEMENTS EXISTING SEWERAGE FACILITIES VISTA/CARLSBAD NTERCEPTOR BASIN BOUNDARY SEWER DRAINAGE ZONE BOUNDARY ENCINA WATER POLLUTION CONTROL FACILITY FIGURE 7-1 IMPROVEMENTS TO VISTA/CARLSBAD INTERCEPTOR SYSTEM 51 ro LEGEND DEVELOPER FUNDED IMPROVEMENTS EXISTING SEWERAGE FACILITIES NORTH AGUA HEDIONDA BASIN BOUNDARY SEWER DRAINAGE ZONE BOUNDARY VISTA/CARLSBAD INTERCEPTOR AGUA HEDIONDA LIFT STATION N.T.S FIGURE 7-2 IMPROVEMENTS TO NORTH AGUA HEDIONDA INTERCEPTOR SYSTEM Table 7-2. Improvements to North Agua Hedionda Interceptor Sewage Drainage Basin IMPROVEMENTS TO EXISTING TRUNK SEWERS Reach Location Size, in. Length, feet Total Cost, $ Year Needed NAHTIB Kelly Drive 12 4,000 360,000 (1) CONSTRUCTION OF NEW TRUNK SEWERS Reach Location Size, in. Length, feet Total Cost, $ Year Needed NAHTIA Tamarack Ave. 10 4,000 300,000 (1) Total Developer Funded Improvements 660,000 1. As required for development. Table 7-3. Improvements to South Agua Hedionda Interceptor Sewage Drainage Basin CONSTRUCTION OF NEW INTERCEPTORS Reach Location Size, in. Length, feet Total Cost, $ Year Needed SAHl Hidden Valley Road 21 2.320 313,200 1995 SAH2 Hidden Valley Road 21 2,200 297,000 1995 SAH4 Future Cannon Road 21 3,500 472,500 1995 Subtotal for New Interceptors 1,082,700 LIFT STATION IMPROVEMENTS Description of Improvements Size, in. Length feet Total Cost, $ Year Needed South Agua Hedionda Lift Station Stage 1 Lift Station — — 514,000 1995 Sta ge 1 Force Main 24 2,400 336,000 1995 Stage 2 Lift Station — — 550,000 2000 Stage 2 Force Main 21 2,400 300,000 2000 Subtotal Lift Station Improvements 1,700,000 Subtotal City of Carlsbad Funded Improvements 2,782,700 CONSTRUCTION OF NEW TRUNK SEWERS Reach Location Size, in. Length, feet Total Cost, $ Year Needed SAHTIA Carlsbad Raceway 8 1,000 65,000 (1) SAHTIB Agua Hedionda Creek 12 3,500 315,000 (1) SAHTIC Agua Hedionda Creek 15 3, 700 388,500 (1) SAHTID Sunny Creek Road 15 3, 500 367,500 (I) SAHTIE Rancho Carlsbad Sunny Creek 15 4, 540 476,700 (1) SAHTIF Future College Blvd. 8 2,000 130,000 (1) SAHTIG El Camino Real 18 2, 500 300,000 (1) SAHT2A Future Cannon Road 10 6,300 472,500 (1) SAHT2B Future College Blvd. 8 3,000 195,000 (1) SAHT2C Future Cannon Road 15 3,500 367,500 (1) SAHT3A Future Macario Canyon Road 8 1,500 97,500 (1) SAHT3B Future Macario Canyon Road 12 6,500 585,000 (1) Subtotal Developer Funded Improvements 3,760,200 TOTAL 6,542,900 1. As required for development. 54 ENCIN WATER POLLUTI CONTRO FACILITY CITY OF CARLSBAD FUNDED IMPROVEMENTS DEVELOPER FUNDED IMPROVEMENTS EXISTING SEWERAGE FACILITIES BUENA/SAN MARCOS INTERCEPTOR BASIN BOUNDARY SEWER DRAINAGE ZONE BOUNDARY FIGURE 7-4 IMPROVEMENTS TO BUENA/SAN MARCOS INTERCEPTOR SYSTEM Table 7-4. Improvements to Buena/San Marcos Interceptor Sewage Drainage Basin IMPROVEMENTS TO EXISTING INTERCEPTORS Ul CONSTRUCTION OF NEW TRUNK SEWERS Computer runs indicate BSM2 will not exceed capacity in the future; however, flow monitoring indicates future flows will exceed full pipe capacity and therefore a replacement pipe is recommended. Cost based on old-line ownership percent. As required for development. Reach Location Size, Length, Total Carlsbad Year in. feet Cost, $ Ownership, % Cost ,^ $ Needed BSM2 1 Camino Vida Roble 21 4,690 633,150 19.2 121,600 Beyond 2000 LIFT STATION IMPROVEMENTS Description of Improvements Size, Length, Total Carlsbad Year in. feet Cost, $ Ownership, % Cost, $ Needed North La Costa Lift Station Construct Station — — 750,000 100 750,000 1996 Force Main 16 5,000 500,000 100 500,000 1996 Subtotal Lift Station Improvements 1,250,000 Subtotal City of Carlsbad Funded Improvements 1,371,600 Reach Location Size, Length, Total Carlsbad Year i n. feet Cost, $ Ownership, . % Cost, $ Needed BSMTIA Future Carrillo Way 12 2,000 180,000 100 180,000 (3) BSMTIB Serves 6B 8 1,000 65,000 100 65,000 (3) BSMTIC Future Carrillo Way 12 1,000 90,000 100 90,000 (3) BSMTID Future Carrillo Way 15 3,700 388,500 100 388,500 (3) BSMTIE Serves 17A 10 3,400 255,000 100 255,000 (3) BSMTIF North of La Costa Golf Course 15 1. 200 126,000 100 126,000 (3) BSMT2 Laurel Tree Road 12 4,000 360,000 100 360,000 (3) Subtotal Developer Funded Improvements 1,464,500 TOTAL 2,836,100 00 Table 7-5. Improvements to North Batiquitos Interceptor Sewage Drainage Basin LIFT STATION IMPROVEMENTS Description of Improvements Size, in. Length, feet Total Cost, $ Year Needed North Batiquitos Lift Station Reconstruct Station — 750,000 (1) Add ^orce Main 6 1,840 82,800 (1) Subtotal City of Carlsbad Funded Improvements 832,800 IMPROVEMENTS TO EXISTING TRUNK SEWERS Reach Location Size, in. Length, feet Total Cost, $ Year Needed NBT3B Daisy Avenue and Batiquitos Lagoon 12 5,000 450,000 (1) CONSTRUCTION OF NEW TRUNK SEWERS Reach Location Size, in. Length, feet Total Cost, $ Year Needed NBTl 19C 10 3,000 225,000 (1) NBT2 19B 12 7,500 675,000 (1) NBT3A 4B 10 1,000 75,000 (1) Subtotal New Trunk Sewers 975,000 Subtotal Developer Funded Improvements 1,425,000 TOTAL 2,257,800 1. As required for development, LEGEND CITY OF CARLSBAD FUNDED IMPROVEMENTS DEVELOPER FUNDED IMPROVEMENTS EXISTING SEWERAGE FACILITIES NORTH BATIQUITOS INTERCEPTOR BASIN BOUNDARY SEWER DRAINAGE ZONE BOUNDARY FIGURE 7-5 IMPROVEMENTS TO NORTH BATIQUITOS INTERCEPTOR SYSTEM WASTEWATER TREATMENT SYSTEM IMPROVEMENTS The City of Carlsbad has the ability to treat sewage either at the Encina Water Pollution Control Facility or the Lake Calavera Hills Water Reclamation Plant. Recommended improvement programs for both of these facilities are provided. The City of Carlsbad has an ultimate sewage treatment capacity need of 13.41 million gallons per day. For the purposes of cost estimating for future facilities, it is assumed that all 13.41 million gallons per day of capacity will be obtained at the Encina Water Pollution Control Facility. The effluent disposal line and filtration system improvements discussed in this chapter would be added to the Lake Calavera Hills Water Reclamation Plant to allow it to be used as a reclamation facility. In conjunction with the improvements to the Lake Calavera Hills Water Reclamation Plant, gravity outfalls will be provided to all lift stations. This will enable the lift stations to be turned off when the Lake Calavera Hills Water Reclamation Plant is not in operation. Encina Capital Improvement Program The capital improvement program at the Encina Water Pollution Control Facility includes the Phase IV expansion, the Phase V expansion, the solids management program and improvements to the ocean outfall. Table 7-6 provides times and cost estimates for these improvements. For the purposes of estimating the costs for improvements to the Encina Water Pollution Control Facility, the ultimate capacity of the plant has been established as 45 million gallons per day. In order for the City of Carlsbad to obtain 13.41 million gallons per day of capacity, they will have to own 29.8 percent of the plant. At the present time, the City of Carlsbad owns only 25.4 percent of the plant. 61 Table 7-6. Improvements to the Encina Water Pollution Control Facility Carlsbad Cost.l thousands of dollars Project 1987-1989 1990-1994 1995-1999 Beyond 2000 Total Phase IV 8,995 8,995 17,990 Phase IV 8,995 8,995 17,990 Solids Management Stage 1 2,016 3,497 5,513 Solids Management Stage 1 2,016 3,497 5,513 Solids Management Stage 2 1,950 1,950 Solids Management Stage 2 1,950 1,950 Outfall Pump 3 Outfall Pump 4 and Surge Tower 97 97 140 Outfall Pump 3 Outfall Pump 4 and Surge Tower 97 140 97 140 Outfall Pump 3 Outfall Pump 4 and Surge Tower 140 97 140 Parallel Outfall 9,685 9,685 Parallel Outfall 9,685 9,685 Totals 11,108 12,492 11,775 0 35,375 1. All costs are based on the City of Carlsbad's needed plant ownership of 29.8% and existing outfall ownership of 28.66%. Phase IV Project. The Phase IV project will increase the capacity of the Encina Water Pollution Control Facility from 22.5 million gallons per day to 35.5 million gallons per day. With additional modifications, the Encina Water Pollution Control Facility could be expanded to 45 million gallons per day. The extent of these modifications is not known at the present time, but they are being built into the Phase IV project. The cost estimate for the City of Carlsbad's share of the Phase IV project includes a 20 percent add-on to estimated costs to expand the capacity of the plant from 35.5 million gallons per day to 45 million gallons per day. The cost estimate also includes a buy-in to the present facilities to increase the City of Carlsbad's ownership from 25.4 percent to 29.8 percent. Thus, the total cost for the City of Carlsbad in the Phase IV project is estimated to be $17,990,000 and it will provide the City of Carlsbad with a total of 13.41 million gallons per day of treatment capacity. Solids Management Program. The solids management program is an effort to treat the solids to a level that will permit disposal in a sanitary landfill. Present regulations have moisture content requirements for sewage sludges. The Encina Water Pollution Control Facility's sludge does not meet these requirements at the present time. Phase I of the 62 solids management program is scheduled to be completed by 1991 and will cost the City of Carlsbad $5,513,000. Phase II of the solids management program will be needed around the year 2000 and will cost the City of Carlsbad $1,950,000. All estimates are based on a City of Carlsbad ownership of 29.8 percent, and a solids disposal . solution limited to the Encina Water Pollution Control Facility. Oc ean Outfall Improvements. There are three major improvements needed to the ocean outfall. The first two involve the addition of pumps to the effluent pump station. The addit ion of the third pump to the effluent pump station is scheduled to be completed by 1990 and will cost the City of Carlsbad $97,000. The fourth pump is not scheduled to be needed until the year 2000 and will cost the City of Carlsbad $140,000. Around the year 2000 there will be a need for a parallel ocean outfall and this will cost the City of Carlsbad $9,685,000. All estimates are based on a City of Carlsbad ownership of 29.8 percent. Lake Calavera Hills Water Reclamation Plant The Lake Calavera Hills Water Reclamation Plant was constructed in 1981 to provide sewage treatment for the Lake Calavera Hills planned community and developments east of El Camino Real in the proximity of the Lake Calavera Hills development. This facility has never been operated as a wastewater treatment plant and additional improvements are needed for it to operate. Appendix D to this report provides a detailed discussion of the Lake Calavera Hills Water Reclamation Plant. This plant will only be operated if there is a need for reclaimed water, or if there is a capacity problem at the Encina Water Pollution Control Facility that requires it to operate. For the purposes of estimating costs for the needed improvements to this plant, facilities required to allow this plant to operate as a reclamation plant are included. Although the plant has a design capacity of 1.2 million gallons per day, the maximum flow which can be conveyed to the plant is 0.88 million gallons per day. Improvements to the Lake Calavera Hills Water Reclamation Plant. There are four major improvements which are needed for the Lake Calavera Hills Water Reclamation Plant to operate as a reclamation plant. The costs for these improvements are shown in Table 7-7. The biggest expense would be the construction of missing portions of the 63 effluent disposal line to convey treated effluent from the Lake Calavera Hills Water Reclamation Plant to the Encina Outfall. This improvement would be needed to operate the plant, either as a reclamation plant or as a treatment plant. Table 7-7. Improvements to the Lake Calavera Hills Water Reclamation Plant Item Cost, dollars Completion of Effluent Disposal Line (Lake Calavera Hills Water Reclamation Plant to El Camino Real at College Boulevard) 1,272,000 Solids Disposal Line 293,000 Lift Station Improvements (El Camino Real at Tamarack Avenue) 40,000 Tertiary Facilities 1,028,000 TOTAL 2,633,000 To allow for the efficient operation and maintenance of the Lake Calavera Hills Water Reclamation Plant, a solids disposal line should be installed, and the lift station at the corner of El Camino Real and Tamarack Avenue should be improved. The final improvement to the Lake Calavera Hills Water Reclamation Plant would be the addition of tertiary facilities for water reclamation. These facilities would not be needed if the plant was operated as a treatment plant with effluent disposal through the Encina Ocean Outfall. These improvements are discussed in more detail in Appendix D. Improvements to the Lake Calavera Hills Water Reclamation Plant should begin two years prior to the estimated need for the facility. 64 CHAPTER 8 REVENUE PROGRAM REQUIREMENTS To assure the proper operation of a sewerage enterprise fund, the amount of money taken in must be equal to the amount of money spent. This chapter develops the connection fees needed to fund the improvements to the sewerage facilities. USE OF FUNDS To assure the continued fiscal solvency of the sewer enterprise fund, the use of various sources of revenue to the fund should be restricted. The purpose of these restrictions is to prevent the fund from going bankrupt when growth within the agency ceases. To comply with the guidelines, all sewerage system operations, maintenance and capital replacement costs should be recovered from service charges. Capacity fees should be used to pay only capital costs. Sewer Service Charges Sewer service charges are monthly fees paid by the user for the privilege of using the sewage disposal system. They may be used for any of the district's expenses but they should cover the costs of operation, maintenance and capital replacement. The sewer service charge is to be based on both the quantity and strength of the sewage produced. Strength is normally only a major factor for industrial users. Sewer service charges are not analyzed in this report. Capacity Fees Capacity fees are charged to new users who connect to the system. They are based on the estimated quantity of the discharge and are routinely charged to residential, commercial and industrial builders. These fees are intended to pay for the approximate capital expense for the portion of system used. 65 CAPACITY FEE Based on the capital projects presented in Chapter 7 and estimated costs for a monitoring program and City Maintenance Facility, Table 8-1 projects the capital costs for the listed time periods. The cost per equivalent dwelling unit is $1,247. Table 8-1. Connection Fees Item Costs, thousands of dollars 1987-1989 1990-1994 1995-1999 Beyond 2000 Total Encina Water Pollution Control Facility Improvements 11,108 12,492 11,775 0 35,375 Lake Calavera Hills Water Reclamation Plant 0 0 0 2,633 2,633 Interceptor System 1.270 0 2,068 1,472 4,810 Lift Stations 945 871 2, 100 1,292 5,208 City Maintenance Facility 0 0 500 0 500 Monitoring Program 60 100 100 340 600 Total 13,383 13,463 16,543 5,737 49,126 Increase in EDUs, units 4,125 5,680 5,690 23,885 39,380 The City of Carlsbad funds only improvements to the Encina Water Pollution Control Facility, the Lake Calavera Hills Water Reclamation Plant, designated interceptors, lift stations, maintenance facilities and the growth management monitoring program through the connection fee process. All improvements to trunk and collector sewers, are funded through the development process. 66 CHAPTER 9 RECLAMATION PROGRAM There are a number of reclaimed water lines within the City of Carlsbad. These water lines are currently used as effluent disposal lines from the Gafner Water Reclamation Plant, the Meadowlark Water Reclamation Plant and the Shadow Ridge Water Reclamation Plant. Plans have also been developed to complete the effluent disposal line from the Lake Calavera Hills Water Reclamation Plant to the existing line near Palomar Airport Road. This chapter will discuss the issues involved in water reclamation and then discuss the existing and proposed facilities within the City of Carlsbad. WATER RECLAMATION ISSUES To fully understand the water reclamation potential within the City of Carlsbad, a number of issues must be raised and discussed. These issues relate to the cost, distribution and use of reclaimed water. Cost There are two elements associated with the cost of using reclaimed water. The first is the cost to purchase the reclaimed water; the second is the cost of the reclaimed water distribution system. In order to have a viable market for reclaimed water, the total price for the reclaimed water, including capitalization of improvements, must be less than the cost for potable water. Since the potable water system is in place within the City of Carlsbad, a substantial capital investment difference exists between utilization of potable water versus reclaimed water. Cost of Reclaimed Water. For a user to utilize reclaimed water instead of potable water, it must be financially beneficial for him. If conveyance systems are in place for the user to pick whether he utilizes reclaimed water or potable water, there is still an added cost to the user associated with reclaimed water. For example, if a golf course chooses to use reclaimed water rather than potable water for irrigation, they must post the golf course and will probably be required to print on their scorecards that reclaimed water is being used on the site. They will also have to designate a person on their staff to be responsible for use or misuse of the reclaimed water. The golf course will further have to investigate all of their piping systems 67 to assure that there are no existing or potential interties between potable systems and reclaimed water systems. This means that all restrooms and drinking fountains located on the golf course will have to be reviewed to assure that there is no possible way to cross tie the two water systems. All drinking fountains located outdoors where they could be sprayed by the irrigation system would have to be moved. For an existing golf course, the expense associated with relocation of bathroom facilities may be greater than the savings associated with the use of the reclaimed water and the potential user will elect not to use the reclaimed water. Thus, the simple statement that the reclaimed water is 75 percent of the cost of potable water does not make it cost effective to the ultimate user. Capital Costs. In ord er for users to use reclaimed water- it must be made available to them. In most cases, reclaimed water lines are not adjacent to potential users. This is not the case for potable water. Potable water lines are put in with all developments and will continue to be put in as the primary source of water. Small users are not able to install reclaimed water lines to bring the water to their project. It is not cost effective for them to construct these lines for the nominal savings in their water bills. A user must be a substantial water user in order for the savings to offset the capital construction .costs. REGULATIONS There are two agencies which regulate the use of reclaimed water. These agencies are the State Health Department and the Regional Water Quality Control Board. Like all other agencies, these agencies' rules and requirements for the use of reclaimed water change over time. Historically, the rules have gotten more and more restrictive for the use of reclaimed water. Thus, the cost for the use of reclaimed water has increased. It is likely that this increase will continue over time and that the regulation concerning the use of reclaimed water will become more and more restrictive. Regional Water Quality Control Board The Regional Water Quality Control Board sets the treatment and monitoring standards for wastewater reclamation plants. The Regional Water Quality Control Board also reviews the reclaimed water purveyors rules and regulations and issues permits for reclaimed water users. 68 State Health Department The State Health Department sets the levels of treatment required for individual users of reclaimed water. These regulation fall under Title 22 of the Administrative Code of the State of California. Title 22 establishes the treatment level requirements and chlorination requirements based on certain categories of users. EXISTING RECLAIMED WATER FACILITIES There are a number of facilities which have been constructed within the City of Carlsbad in conjuction with water reclamation plants. These facilities could be utilized to provide water to potential users. Figure 9-1 shows these existing facilities. Conveyance System All satellite reclamation plants have a connection to the Encina Ocean Outfall. The lines connecting the satellite plants with the ocean outfall run through the City of Carlsbad and could be utilized as a reclaimed water distribution system. The major line running through the City of Carlsbad connects to the Meadowlark Treatment Plant and the Shadow Ridge Treatment Plant. It will eventually connect to the Lake Calavera Hills Water Reclamation Plant. This line runs parallel to Palomar Airport Road up to College Boulevard. At College Boulevard there is a branch which follows College Boulevard to El Camino Real. This branch will eventually serve the Lake Calavera Hills Water Reclamation Plant. The main line continues to follow Palomar Airport Road to the Palomar Airport Business Park. At this point it branches with one line heading out toward the intersection of El Camino Real and Palomar Airport Road and eventually to the Shadow Ridge Treatment Plant while the other branch crosses El Camino Real and goes down into the Carillo Ranch area to the Meadowlark Treatment Plant. There is also an excess effluent disposal line which runs from the Gafner Treatment Plant along La Costa Avenue and then up the coast to the Encina Water Pollution Control Facility. All of these lines can be operated as pressure pipelines to a certain degree. It is anticipated that these lines would serve as the backbone for any reclaimed water distribution system. 69 Water Reclamation Plants There are four water reclamation plants which could be utilized to produce reclaimed water. The four water reclamation plants are the Lake Calavera Hills Water Reclamation Plant, the Meadowlark Water Reclamation Plant, the Shadow Ridge Water Reclamation Plant and the Gafner Water Reclamation Plant. Each of these plants is discussed below. The Lake Calavera Hills Water Reclamation Plant. The Lake Calavera Hills Water Reclamation Plant can produce 1.2 mgd of secondary quality effluent. However, without major modifications to the existing conveyance system, a maximum flow of 0.88 million gallons per day is all that can reach the Lake Calavera Hills Water Reclamation Plant. Thus, the maximum water available for reclamation at this plant with the facilities recommended in this report is 0.88 million gallons per day. In order to utilize this plant as a reclamation facility, $2,633,000 of improvements would be required. These improvements are discussed in Chapter 7. A detailed discussion of the Lake Calavera Hills Water Reclamation Plant can be found in Appendix D. Meadowlark Water Reclamation Plant. The Meadowlark Water Reclamation Plant is capable of producing 2.0 million gallons per day of tertiary treated water. Water from this plant is currently being delivered to the La Costa Golf Course for irrigation purposes. Shadow Ridge Water Reclamation Plant. The Shadow Ridge Water Reclamation Plant is currently capable of producing 1.0 million gallons per day of filtered chlorinated wastewater. This plant is currently under operation and discharging flows down the fail-safe line. Gafner Water Reclamation Plant. The Gafner Water Reclamation Plant can produce 0.75 million gallons per day of secondary effluent. FACILITIES Figure 9-1 shows existing and proposed facilities for reclaimed water distribution. The figure also shows the location of the major potential reclaimed water users. Parkway irrigation users are not shown on this figure. This 70 STUDY AREA RANCHO CARLSBAD GOLF COURSE POTENTIAL GOLF COURSE ENCINA WATER POLLUTION CONTROL FACILITY POTENTIAL GOLF COURSE EXISTING RECLAIMED WATER LINE FUTURE RECLAIMED WATER LINE FIGURE 9-1 RECLAIMED WATER LINES AND POTENTIAL USE AREAS 71 is because parkway irrigation would require the use of a dual piping system, and dual piping systems are not cost effective. SUMMARY In order to summarize the issues and policies related to the use of reclaimed water, it is best to discuss current reclaimed water users. At the present time the La Costa Golf Course is the only user within the City of Carlsbad which is actively pursuing the use of reclaimed water. The nine hole extension of their golf course north of Alga Road is able to utilize reclaimed water from the Meadowlark Water Reclamation Plant. This project was able to allow for the use of reclaimed water on their golf course because the excess effluent disposal line from the Meadowlark Water Reclamation Plant was adjacent to the golf course and the irrigation system on the golf course was set up as a non-potable system. Since the irrigation system was non-potable, the reclaimed water could be tied directly into the irrigation system. Although the nine holes are set up so they can be irrigated with reclaimed water, the golf course has used the reclaimed water sparingly, due to the high total dissolved solids and the problems these salts cause to the turf. Based on the results at the La Costa Golf Course, the viability of reclaimed water use, even on model projects, is marginal. Projects which would require substantial capital outlay at this time would be prohibitively expensive. Therefore, a regional approach to water reclamation which provides flexibility for the future is the proper path at the present time. This regional approach should incorporate the Encina Water Pollution Control Facility as the regional sewage treatment plant and allow the reclamation program to be built around the existing satellite reclamation plants. Since facilities are now in place to produce reclaimed water and a network of distribution lines could be set up using the existing effluent disposal lines, no additional facilities should be constructed until a strong user base is established for the reclaimed water. 73 74 LIST OF REFERENCES • Algren & Koptionak, Inc. Report on South Agua Hedionda Interceptor for City of Carlsbad. September, 1987. John Carollo Eng ineers, Encina Water Pollution Control Facility 2020 Facility Plan. Draft, August, 1987. John Carollo Engineers, Encina Water Pollution Control Facility Ocean Outfall Facility Plan. August, 1985. Encina Water Pollution Control Facility, Budget Recommendations 1987/88 Fiscal Year. June, 1987. Eraser, Wilson & Associates, Master Plan of Sewerage. Vista Sanitation District. Buena Sanitation District. March, 1982. Neste, Brudin & Stone Incorporated, Sewer Master Plan City of Carlsbad. June, 1984. Wilson Engineering, Evaluation of the Capacity of the Buena Interceptor in the City of Carlsbad. April, 1987. Wilson Engineering, Facilities Plan for Agua Hedionda Pump Station and Buena Vista Pump Station. October, 1987. 75