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<br />effects, however, with California experiencing increased economic output relative to baseline by <br />the year 2020 while most of the other states show declines. <br /> <br /> TABLE 4-C <br /> Colorado Study Direct Economic Impacts <br />for Critical Habitat Designation for the Colorado River Basin (1991$ Millions) <br /> Year <br />Sector 1995 2000 2005 2010 2015 2020 <br /> Colorado River Basin <br />Livestock Feed -0.205 -0.882 -1.680 -2.217 -3.022 -3.720 <br />Other Crops 0.552 0.967 1.438 1.372 2.336 3.530 <br />Recreation -0.243 -0.372 -0.409 -0.435 -0.461 -0.487 <br />Electric Power -1. 752 -1.806 -2.372 -1. 961 -2.546 -1.465 <br />Non-petrol Mining 0.277 0.398 0.561 0.433 0.262 0.457 <br />Oil and Gas Mining 0.128 0.093 0.295 0.213 0.688 0.143 <br />Construction 0.788 0.804 0.844 0.844 0.844 0.844 <br />Combined Mfg. 0.753 0.768 0.807 0.807 0.807 0.807 <br />Local Amusements 1.863 1.863 1.863 1.863 1.863 1.863 <br />Total Direct Impacts 2.161 1.833 1.347 0.919 0.771 1.972 <br /> <br />The overall direct and indirect sectorial impacts of the critical habitat designations are presented <br />in Table 5. These impacts include the direct and indirect effects of critical habitat as estimated <br />from an 1-0 model for the seven-state basin. As can be seen the impacts are both positive and <br />negative across sectors reflecting the reallocation process of resources that is required for the <br />recovery of the endangered fishes. Thus, one outcome of the analyses is that there are sectorial <br />distributional consequences. The largest negative impacts were projected for the electric power <br />production sector and the livestock feed sector. The electric power sector must adjust to the <br />changes in the flow regimes of the river system and the livestock feed sector represents a low <br />value of water use so these uses are the first to be retired. <br /> <br />31 <br />