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<br />2-10 . <br /> <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />0223 <br /> <br />Co Loss of retail and wholesale trade will cause some local businesses to close or <br />relocate outside the study area, redu~ng the vitality of the community and its <br />attractiveness to new economic develoI1ment. <br />, <br />I <br />Financial burdens are imposed upon other water user~. They frequently participate in water court <br />cases for the purpose of protecting supplies, and m~st bear the expense of expert advice from <br />attorneys, hydrologists, agronomists and water quality Consultants. Currently there is no provision <br />for transfer of those expenses to applicants for a transfer, (except C.R.S. 37-92-304(3.5) as to mutual <br />agricultural ditch shareholders) and the burden of ~hose expenses discourages objectors from <br />addressing their concerns in court. An argument in f~vor of the existing process is that it imposes <br />less restraint on the movement of water supplies to ,higher economic uses. Cost protection for <br />objectors would further restrain these changes of use.f <br /> <br />, <br />Water transfers affect the social structure and intera<itions in the community. The overall quality <br />and character of life can be undermined in areas where historical irrigation is suddenly terminated <br />(Shupe, Weatherford and Checchio 1989, 429); the people of the area lose their psychological and <br />cultural "roots" (Weber 1990b, 15); even in highly ~omogeneous communities, proposed water <br />transfers create conflicting interpretations among resid4nts regarding the proper relationship between <br />the physical and social environments and the proper rblationships among themselves (Greider and <br />, <br />Little 1988, 47). ' <br /> <br />If community impacts are to be mitigated there is little consensus as to what would constitute fair <br />and adequate mitigation, and who should judge the adequacy of mitigation. Possibilities include the <br />courts, local government, or state government. Water fourts have a limited role in third party impact <br />mitigation (Pratt 1988). Some mitigation proposa~ raise issues of who pays or who receives <br />payment. Such proposals may include payments hI lieu of taxes; compensation to individuals, <br />businesses or local governments; economicdevelopme~t efforts; "banking" of compensation measures; <br />and requirements for severance-type payments. . <br /> <br />3. Environmental; riparian wetlands and plalhs ecosystems <br /> <br />The ecology of the vicinity of a large ditch is influen~d by the quantity and quality of water, and <br />variability in supply. Water use influences the soil, l>lant, and microclimate characteristics of the <br />land. Irrigated lands and related hedgerows, wetlands, and reservoirs create important ecosystems <br />for the eastern plains. Also derived from the environ~ent are recreation uses and aesthetic beauty, <br />with attendant economic and social benefits. I <br />, <br /> <br />Regional environmental issues include: dryland habitat impacts, including hedgerows and drainage <br />corridors; wetland habitat impacts, including wetlan~ arising from ditch and lateral seepage, surface <br />waste flows and drains, outcrops of underground re~rn flows, tail water ponds, and return flow fed <br />stock ponds; open water areas, including nesting, res~ing, and forage habitat for local and migratory <br />waterfowl; possible influences upon endangered speres habitat. <br />