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=31 <br /> Two additional sources of nutrient loading affect the lake directly. Atmospheric deposition <br /> contributes nitrogen, phosphorus, and organic carbon directly to the surface of Falls Lake as well as <br /> to the contributing drainage area. Atmospheric deposition data incorporated into the monitoring and <br /> modeling shows total nitrogen loads from atmospheric deposition have declined by approximately <br /> 20 percent since 2006 (DWR 2021). The bottom sediments within Falls Lake accumulate, release, <br /> and cycle nutrients. The UNRBA 2019 monitoring report estimated that lake sediments release <br /> approximately 200,000 pounds of total <br /> nitrogen each year(10 percent to 25 <br /> percent of the watershed load <br /> depending on rainfall and the year The UNRBA 2019 monitoring report estimated that <br /> referenced) and 14,000 pounds of total lake sediments release approximately 200,000 <br /> phosphorus (5 percent to 15 percent of pounds of total nitrogen each year(10 percent to <br /> the watershed load depending on 25 percent of the watershed load depending on <br /> rainfall and the year referenced). rainfall and the year referenced) and 14,000 <br /> These preliminary estimates of lake pounds of total phosphorus (5 percent to 15 <br /> sediment releases have been refined percent of the watershed load depending on <br /> through the UNRBA lake modeling rainfall and the year referenced) <br /> efforts and Collaboratory studies. <br /> To summarize,the hydrology, <br /> morphology, retention time, depth, and characteristics of the different areas of the lake contribute <br /> significantly to nutrient loading and chlorophyll-a levels in the lake. These aspects of the lake are <br /> beyond the control of the regulated entities in the watershed. While the UNRBA aims to manage <br /> nutrient loading in the watershed, it recognizes it is not the only factor to consider in developing a <br /> revised nutrient management strategy. <br /> Many important data results and relationships contribute to an updated and improved <br /> understanding of this lake and watershed. The best way to examine those in detail is to access the <br /> UNRBA 2019 Monitoring Report. <br /> UNRBA Watershed Modeling <br /> The UNRBA has worked extensively with local governments, researchers, state and federal agencies, <br /> and utilities to obtain the most comprehensive and complete data available to develop a revised <br /> watershed model for Falls Lake. The UNRBA selected the Watershed Analysis Risk Management <br /> Framework (WARMF) model partly because it is the same model that DWR used to support <br /> development of the Falls Lake Nutrient Management Strategy. Data summaries and discussions <br /> related to the Falls Lake and watershed WARMF model development are documented in Modeling <br /> and Regulatory Support Workgroup (MRSW) meetin materials and the UNRBA watershed modeling <br /> report(BC and Systech Water Resources 2023, available at https://unrba.org/reexamination). <br /> Development of a watershed model is an essential component of a fully informed management <br /> approach. The UNRBA has invested significant resources into an effective watershed model <br /> development process. The following summary of the watershed modeling effort is provided as <br /> context for the UNRBA recommendations for a revised nutrient management strategy. The modeling <br /> was reviewed extensively by subject matter experts,third-party model reviewers funded by the NC <br /> Collaboratory, and DWR modeling staff. The UNRBA has a high level of confidence in the results of <br /> this modeling. A more complete description of the model and the development process is available <br /> in the UNRBA Watershed Modeling Report(BC and Systech Water Resources 2023, available at <br /> https://unrba.orVreexamination). <br /> 12 <br />