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Agenda - 11-03-2004-10a
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Agenda - 11-03-2004-10a
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Last modified
9/2/2008 1:20:29 AM
Creation date
8/29/2008 10:25:27 AM
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BOCC
Date
11/3/2004
Document Type
Agenda
Agenda Item
10a
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Minutes - 20041103
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\Board of County Commissioners\Minutes - Approved\2000's\2004
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Update on .Jordan Lake Nutrient Management Strategy <br />September 17, 2004 <br />Page 2 of 5 <br />standards and (b) nutrient reduction targets to be achieved through a combination of point <br />and nonpoint management practices. <br />Based on available information, point sources account for about 45 percent of the TN <br />load and 18 percent of the TP load to the Upper New Hope Arm of .Jordan Lake. It is <br />cleaz that the success of any nutrient management strategy will depend on meaningful <br />control ofnutrient loads from nonpoint as well as point sources. Because most ofthe <br />Upper New Hope Arm nonpoint load comes from developed (urban azrd suburban) land <br />surfaces, it will be importazrt that the nonpoint management strategy address both existing <br />and new development in the Canboro-Chapel Hill-Durhazn-Research Triangle Park area.. <br />It is notable that the potential for .lordazr Lake nutrient problems has been a water quality <br />concern for more than 30 years, pre-dating the dam's construction in the early 1970s and <br />the lake's eventual impoundment in 1981. The lake was designated Nutrient Sensitive <br />Waters (NSW) by the EMC in 198.3, and all point sources received concentration limits <br />for allowable total phosphorus (TP) discharges. OWASA's TP limit has been 0,6 mg/L. <br />Historically, no TN limits had been imposed in the .Iordan Lake watershed; however, in <br />1997 the NC General Assembly enacted HB 515, which required that all wastewater <br />dischargers in NSW watersheds (such as .Jordan Lalce) meet a TN limit of 5,5 mg/L - <br />unless a nutrient response model indicated that alternative nutrient limits would be more <br />appropriate. <br />To assure that regulatory requirements were based on the best available technical <br />information, OWASA and several local goverrunents contributed to the development of <br />the .Tordan Lake Nutrient Response Model, as noted above, which has been a key tool of <br />the evolving management strategy, <br />Management Implications <br />The outcome of this process may have important effects on local stormwater programs, <br />agricultural practices, development requirements, and on wastewater treatment discharge <br />limits. A similar regulatory initiative has been completed in North Carolina for the <br />Neuse River Basin. <br />Recent Activities <br />Representatives from more than three dozen stakeholder groups, including local <br />governments, envirorunental groups, agriculture, and the business community, have <br />participated in a series of more than 15 meetings held from May 2003 tlu-ough August <br />2004, but achieved little consensus.. In early .July, OWASAstaff co-signed a letter to <br />DWQ (attached) outlining a series of technical concerns and proposing a phased or <br />incremental approach to nutrient reduction strategies. DWQ staff provided a written <br />response to the technical issues, but did not continent on the phased proposal with the <br />S <br />
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