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Agenda 11-02-23; 4-a - Resolution Endorsing Consensus Principles II for Revised Falls Lake Rules
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Agenda 11-02-23; 4-a - Resolution Endorsing Consensus Principles II for Revised Falls Lake Rules
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11/2/2023
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Agenda
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4-a
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Agenda for November 2, 2023 BOCC Meeting
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�n=42 <br /> chlorophyll-a standard 90 percent of the time in the upper part of the lake. A 50 percent reduction in <br /> total nitrogen load from 2014 to 2018 levels translates to a reduction of 825,000 pounds per year <br /> on average. This is a massive reduction goal on top of the reductions already achieved since 2006. <br /> Multiple pump-and-treat type systems would be needed to achieve this level of reduction. Many, if <br /> not all of these systems, would be treating nutrients from unmanaged lands including forests and <br /> wetlands that do not receive watershed-scale human inputs (however, nutrients are "applied"to <br /> these areas from atmospheric deposition). <br /> Implementation <br /> Assuming the highest estimate of nitrogen removal (6,000 pounds per year, which is unlikely), <br /> removing 825,000 pounds of nitrogen per year would require 138 full-scale algal floways. These <br /> floways would generate an estimated 276,000 wet tons of harvested algae, which would need to be <br /> transported to an offsite treatment facility. A rough extrapolation of the pilot study estimates the <br /> cost of 138 algal floways at$1.1 billion for construction and $23.4 million per year for operation and <br /> maintenance. These facilities have an assumed life span of 20 years, meaning that life-time costs <br /> would be approximately$1.6 billion (construction plus 20 years of operational costs). Treatment <br /> beyond 20 years would require additional construction or repair costs. This is a conservative cost <br /> estimate as site selection, land costs, and legal costs are not included. <br /> These costs assume the maximum amount of treatment based on the pilot study. Assuming the low <br /> end of the treatment range (3,000 pounds of nitrogen removed per year per system), construction <br /> costs would double to $2.2 billion, and operation and maintenance would double to $46.9 million for <br /> a total of$2.7 billion for the 20-year life span of the systems. <br /> Feasibility <br /> While hypothetical costs can be estimated for 138 systems,there are many logistical reasons that <br /> warrant this approach infeasible: <br /> • The City of Durham has faced challenges siting even one of these systems, so siting 138 would <br /> be unachievable. <br /> • This number of systems would require treatment of 1.38 billion gallons of water per day <br /> (10 million gallons per day times 138 systems). This is more water than entered Falls Lake <br /> during the average to high precipitation conditions that were evaluated by the UNRBA(only 239 <br /> million gallons per day to 476 million gallons per day). If sufficient water is not present in the <br /> tributary or lake where pumping occurs,the systems cannot fully operate, and pumps may be <br /> stressed. <br /> • More than 276,000 wet tons of algae would have to be harvested, transported, and composted <br /> each year. This would likely require construction of a dedicated composting facility. <br /> • The effectiveness of the floways is estimated based on the results of a pilot study. For the sake <br /> of illustration, constant removal efficiencies for all 138 systems are assumed. However, <br /> cumulative effects for multiple systems are unknown, and removal efficiency for a given floway <br /> could decrease significantly if incoming water had already been treated by an upstream floway. <br /> Similarly, some of these systems would have to be placed in areas that were predominately <br /> forested. Inflow concentrations from these areas would likely be lower than the pilot study, and <br /> removal efficiencies would be lower. <br /> • Processing that volume of water and removing that level of nutrients from the system could have <br /> unknown environmental and ecological impacts. <br /> Addition of 138 algal floway footprints and algal harvest transportation could have negative <br /> environmental impacts such as increased impervious area and greenhouse gas emissions. <br /> 23 <br />
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