Laserfiche WebLink
<br />3.0 Scientific Basis And Underlying Principles <br /> <br />3-2 <br /> <br />April 2004 <br /> <br />3.2 Underlying Principles Of Plan <br /> <br />This Plan is based on five underlying principles: <br /> <br />1. Structure and functiori of the Green River ecosystem are sufficiently intact to <br />support wild self-sustaining populations of razorback sucker and bonytail; <br />2. Floodplain restoration and flow re-regulation will enhance endangered fish <br />habitats; <br />3. Flow recommendations for the Green River will be evaluated through National <br />Environmental Policy Act (NEP A) compliance and implemented accordingly; <br />4. Wild populations of razorback sucker and bonytail must be initiated from hatchery <br />stocks and through habitat restoration to better understand specific life history <br />needs in the wild, including nursery and rearing habitats; <br />5. Young fish remaining in floodplain depressions for 2 years exhibit the best growth <br />and survival before recruiting to mainstem populations; and <br />6. Best management strategy is based on the "reset theory" of inundating floodplains <br />for 2 - 3 years to enhance growth and survival of razorback sucker and bonytail, <br />and allowing floodplains to become desiccated to periodically kill nonnative fish. <br /> <br />The first and second principles state that the Green River Subbasin retains many of its <br />natural ecological aspects and that floodplain restoration, combined with flow re-regulation, can <br />maintain the structure and function of these habitats to assist recovery of razorback sucker and <br />possibly bonytail. Although much of the Upper Colorado River Basin is flow-regulated, much of <br />the original structure and function of the ecosystem is intact. The upper basin supports the only <br />remaining wild self-sustaining populations of Colorado pikeminnow and five of the six known <br />wild self-sustaining populations of humpback chub. The upper basin also supports viable self- <br />sustaining populations of the four other native, non-endangered fish species: flannelmouth sucker <br />(Catostomus latipinnis), bluehead sucker (Catostomus discobolus), roundtail chub (Gila <br />robusta), and speckled dace (Rhinichthys osculus). This naturalized system provides the <br />opportunity for recovery of razorback sucker through habitat restoration and flow regulation with <br />the minimum necessary investment of resources. The estimated time to achieve recovery of the <br />razorback sucker is 22 years (U.S. Fish and Wildlife Service 2002a), and is based on the <br />assumption that self-sustaining populations can be established in the first 14 years. <br /> <br />The third principle assumes that flow recommendations for the Green River (Muth et al. <br />2000) will be evaluated through NEP A and ESA compliance and implemented accordingly. <br />Flows provided through this compliance process will insure inundation of floodplains on a <br />regular basis. The fourth principle is that wild populations of razorback sucker must be initiated <br />from hatchery stocks and habitat restoration to better understand specific life history needs, <br />including habitat requirements. Floodplain restoration activities will be conducted simultaneous <br />to releases of hatchery fish in order to better understand life history needs based on fish habitat <br />use and response. Larval entrainment, growth, and survival in floodplains can be confirmed from <br />wild, free-roaming fish. <br />