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have an outsized effect on potential forcing(CC2 is 99.9 percent+of COze). Due to this fact, BLM Colorado <br /> is limiting further downstream combustion estimates to COz only for the remainder of this report. <br /> BLM Colorado's approach for assessing climate impacts in NEPA has been to use the decision scope <br /> emissions as a surrogate (or proxy) for describing the known (modeled) climate impacts associated the <br /> with various global emissions scenarios. This approach has been adopted specifically because there are <br /> presently no climate analysis tools or techniques that lend themselves to describing any actual climate or <br /> earth system response (such as changes to sea level, average surface temperatures or regional <br /> precipitation rates) that would be attributable to the quantized emissions associated with any single <br /> action,decision, or scope. Contrasting proxy emissions at various scales relative to a quantity of emissions <br /> analyzed to have a definitive climate impact allows BLM to provide a relative sense for the intensity of the <br /> proxy emissions. <br /> Proxy emissions are estimated by projecting all of the reasonably foreseeable direct and indirect GHGs <br /> associated with the CARMMS scenarios(low and high)forward to two specific future years(Table 2.2-20). <br /> The study analyzed linear rates of oil, gas, and coal exploration and development (upstream) over a ten- <br /> year period which allowed for the annual average rates of emissions from the associated activities to be <br /> extracted and used in the projection calculations. Indirect downstream emissions(from product end use) <br /> are calculated for the same projection periods by applying EPA combustion emissions factors to the <br /> cumulative production estimates for each scenario. Projected production estimates are derived by <br /> applying the annualized AEO reference case growth rates for each mineral resource to the current <br /> resource production values obtained from ONRR. For the low scenario, the result should be consistent <br /> with the development projections made for CARMMS, which assumed an average development rate <br /> based on five years of historical data and captures recent technology advancements and current laws and <br /> regulations, similar to the AEC's reference case scenario. For the high scenario,the production estimates <br /> require an additional scaling factor based on the ratio of development between the low and high scenario <br /> such that BLM can account for the additional production that would be associated with higher annual <br /> average rates of oil and gas development. Coal production in CARMMS was held static across all scenarios <br /> for operational mines, and thus no additional scaling is required.The first projection period is being made <br /> for 2018 to 2032,and is designed to approximate a no growth, no reduction emissions scenario where the <br /> carbon budget is consumed in 14 years (based on current global emissions rates). The second projection <br /> period assumes steep emission declines to net zero in 2050, which also assumes the entire budget is <br /> consumed. <br /> Dunn Ranch Area LBA and Mining Plan Modification 44 <br /> Technical Resources Report <br />