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LAKE MEAD RAZORBACK SUCKER MONITORING AND RESEARCH: They’re Wild and They’re Recruiting!. Brandon Albrecht Ron Kegerries Zach Shattuck. BIO-WEST, Inc. Acknowledgements. Lake Mead Workgroup. Study Area. Background/Objectives. Determine population size of Lake Mead razorback sucker.
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LAKE MEAD RAZORBACK SUCKER MONITORING AND RESEARCH: They’re Wild and They’re Recruiting! Brandon Albrecht Ron Kegerries Zach Shattuck BIO-WEST, Inc.
Acknowledgements Lake Mead Workgroup
Background/Objectives • Determine population size of Lake Mead razorback sucker. • Document Lake Mead habitat use and life history characteristics. • Document use of known spawning sites. • Conduct sampling efforts for all life stages. • Conduct long-term monitoring (1996-2012). • Search for new population concentrations (i.e., Colorado River Inflow Area). • WILD FISH!
Methods • Sonic telemetry (active and passive) • Trammel netting • Larval sampling • Nonlethal age determination (fin rays) • Population estimate
2011 Long-term Monitoring • 67 total net-nights (January–April 2011) • 86 total captures, 14 recaptures (16.3%) = 72 new/wild captures • 600+ captured and tagged to date • 73 individuals aged • 360 aged to date • 72.6% (n = 53) were 7 years or younger • Strong year-class for 2005 • Total of 4,288 larval razorback collected from long-term monitoring sites • 5 wild juveniles
To date: 107 wild, young, sexually immature (subadult) razorback sucker collected at Lake Mead. The trend: 1996–1997 (2 years) = 4 subadults 1998–2005 (8 years) = 17 subadults 2006–2011 (6 years) = 86 subadults
Recruitment nearly every year! Strong recruitment pulse around 2005; these fish are now adults. Expect recruitment to continue past 2008.
Lake Mead Conditions, 2005 and 2011 • Heavy winds and Large woody debris, bad for props
Lake Mead Conditions • Started at 1,092 ft. Jan 2011 and rose to 1,134 ft. • Strong year class for 2011? Hope for the future!
Colorado River Inflow Second Rapid First Rapid 2011 spawning area North Beach 2010 spawning area “Lunch Cove”
Telemetry Summary • Sonic-tagged fish enhanced our ability to capture wild razorback suckers, • helped identify the 2011 spawning area, and • increased our efficiency. • Limited upstream movement - fish stocked upstream returned to the lake. • Radio technology was useful but became irrelevant.
CRI Adult Sampling • Total of 187 net nights (600% increase from 2010). • Total of 15 razorbacks (8 recaptured, 7 new wild fish). • Total of 7 hybrids [razorback x flannelmouth] (1 recaptured, 6 new wild fish). • Total of 112 flannelmouth (39 recaptured, 73 new wild fish). • 0.08 razorback/net night (0.04 new, wild fish/net night). • Single bluehead sucker also captured.
CRI Larval Collections • Total of 265 sampling events for a total of 146 light hours. • First larval razorback sucker collected (Feb 14, 2011; temp 11.5° C). • Total catch of 65 larval razorback suckers (350% increase from 2010). • Captured 11 flannelmouth larvae for a CPM of 0.0013. • Catch per minute (CPM) value for razorback sucker larvae similar to those observed initially at MR/VR inflow. • CRI important spawning location for native suckers.
Razorback Sucker Aging Ages ranged from 6 to 11 (2000–2005)
CRI Conclusions • Successful spawning has been documented and confirmed for the past two field seasons. • Wild, ripe razorback suckers were captured at different locations for two consecutive field seasons in the CRI. • Sonic-telemetry techniques can be used as an effective tool to help document razorback sucker habitat use in understudied areas of Lake Mead. • Hybridization of native sucker species has been documented.
Why Lake Mead? • Unique population • Young, recruiting, resilient • Population estimate ~ 1000 fish • Unique habitat • Inflows – cover • Unique opportunity • Study recruitment (subadult fish) • The importance of cover • Positive outlook for an endangered species