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HISTORY OF DARE COUNTY WATER NORTHERN BEACHES No water system developed through this avenue. Nags Head and Kill Devil Hills both incorporated and developed the Dare Beaches Water Authority. Financing difficulty eventually led to the dissolution of this Authority with the emerging of Dare County taking the lead to develop a water supply for the beaches. Under a new arrangement, Dare County, Nags Head and Kill Devil Hills agreed to jointly pay for new treatment improvements. Although these Authorities were created in the early 1950's, a Public Water System was not developed until the early 1960's after the Ash Wednesday Storm of 1962 because of salt water intruding into private wells that were drilled down 15-20 feet below the ground level. Both Kill Devil Hills and Nags Head constructed water treatment plants using the Fresh Pond (27 acre surface water supply). Although extensive studies were conducted to find a drinking water source, it soon became obvious that the Fresh Pond was the only source of "fresh water" available. Low solids and iron content of this pond led to the development of the pond as the source of water supply. Both towns utilized the Fresh Pond with
micro-strainers, primarily for algae and suspended matter removal. This
treatment lasted for years until algae blooms and high iron
concentrations from low pond levels led to further treatment with alum
flocculation and settling basins. Concerns of financing through revenue
bonds led NC Local Government Commission to recommend that Dare County
be responsible for the development of an adequate water supply for the
northern beaches in Dare County. The county involvement led to the
construction of the Skyco WTP at the intersection of US Rte. 64 and NC
Rte. 345 with wells being located along the road south to Wanchese on
Roanoke Island. Presently, 10 wells are drilled to a depth of 200-250
feet in the upper Yorktowne aquifer. With Chloride levels less than 70
mg/l treatment required would be only Ion Exchange Softening. Raw Total
Hardness is between 150-170 mg/l. So in 1983, the County Commissioners authorized a study of additional sources of water. This was at the time of the summer when water demand was at its highest, with some days the Skyco plant running at maximum production - 5.0 MGD. Shortly afterwards, the County decided to
use a brackish water source found in the water supply Due to proposed EPA regulations lowering
the acceptable Trihalomethane limits from 100 µg/l down to 80 µg/l
beginning January 2004 and a proposition to eventually drop the maximum
contaminant level to 40 µg/l, the search for additional methods of
treatment for the Skyco Plant began. Pilot testing performed in 1998,
using different types of anion resin for organic removal, proved that
this method of treatment would work for the Skyco plant needs. The
expansion project consisted of installing five (5) new vessels, which
contain 680 cubic feet each of organic removal resin. Each vessel was
placed in the treatment scheme after the existing cation resin softening
units. The expansion began in August 2001, with the project being
completed in May 2003.
Three major conclusions from that report were summarized as follows:
Eight production wells were placed on the Baum Tract in 1988 and 1989. These wells were drilled to 425' with 100' of intake screen. We have a total of five monitor wells
that we use to monitor the changing conditions, if any, in the adjacent
water strata. These wells are located at levels of 310, 410, 510 & 610
feet below the ground. The fifth monitor well is located at the ocean
interface, 425 feet below the ground and best represents water quality
between the RO well field and the ocean at the level we draw water from.
Although this horizontal migration did not happen, we now know that high salinity waters have migrated vertically. This is obvious because of the consistent chloride levels from the Ocean Monitor Well. This indicates no horizontal salt intrusion from the ocean. It would have caused an increase in chlorides at this ocean monitor well first. Vertical migration of higher salinity waters is obvious by the chloride level increases of monitor wells #410 and #510, which monitor well water quality at 410 and 510 feet below the surface. Expanding the well field towards the south was strongly recommended by Missimer and Associates in their conclusions and recommendations in the Hydrogeology study of 1992. In the fall of 1994, wells 9 and 10 came on-line. These wells are located near the Nags Head Fresh Pond, south of the Baum Tract. Two monitor wells were added to each well at 40' and 400'. Two ocean monitor wells are added at Albatross and Abalone Streets. In the year 2000, the EPA mandated a change in the Drinking Water Standard for Arsenic. The maximum contamination level for Arsenic was lowered from 50 PPB (parts per billion) to 10 PPB, effective in January of 2006. The NRO WTP has approximately 45 PPB Arsenic in eight (8) of its 10 production wells. The RO process removes approximately half, leaving about 20 PPB in the product water. This was a problem! In the Spring of 2003, the NRO ran five (5) arsenic pilot units, all removed Arsenic to some degree. An adsorption method was chosen by, Ian Watson, RO Consultant from Rostec and Associates. Four new RO wells have been designed and are under construction. These wells will provide water to the expanded NRO WTP (expansion includes: two (2) new RO units at 1 mgd each). These extensive upgrades will allow the NRO WTP to produce over five (5) mgd (million gallons per day) of arsenic free water. HATTERAS ISLAND RODANTHE, WAVES & SALVO DESALINATION PLANT
Ground breaking for the construction of the plant occurred on October 25, 1994. The completion and start up of the plant occurred March 7, 1996. Prior to March 1996 the citizens of Rodanthe, Waves & Salvo obtained their water from individual private wells. These wells were often unreliable and untested. After completion of the plant and system, most citizens elected to change their water supply from their old wells to our system. This provides them with a 24 hour per day water supply that is tested regularly and certified safe to drink. The system also provides them water for fire fighting protection.
The Cape Hatteras Water Association, Inc.
was established in 1965 as private and non-profit. The Association was a
membership coop established to provide a potable water system for the
southern villages of Hatteras Island. Hatteras, Frisco and Buxton. STUMPY POINT REVERSE OSMOSIS PLANT
In January 1998, a 300' test well was drilled on property owned by Dare County. Based on the test well results, a study was prepared in June 1998 to analyze the feasibility of constructing a community water system. The report recommended construction of a community water system with approximately 14,000 feet of 8-inch water main and 4,100 feet of 6-inch water main. A Reverse Osmosis water treatment facility and storage facilities were recommended to be constructed on Dare County property at the intersection of Stumpy Point Road and NC Highway 64. A house count in 1998 indicated there were presently 110 residences and eight (8) businesses in the Stumpy Point Community. In the summer of 1998, the individual wells were sampled for coliform bacteria. Twenty-five percent (25%) of the wells were sampled for a total of 28 samples. Of these samples, 51% tested positive for total coliform and 5% tested positive for fecal coliform. These results reinforced the need for a community water system and was a large determining factor in the receipt of the Clean Water Bond Grant. Funding was applied for through USDA - Rural Economic Development Center - Supplemental Grants, and 1998 Clean Water Bonds - DENR High Unit Cost Grant/Loan Funds. On March 10, 2000, a 100% grant in the amount of $1,901,845 was received from the Clean Water Bond Fund for the construction of the system. The new system began providing the village of Stumpy Point with a clean and safe drinking water supply in December 2002. |