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WSP09538
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Last modified
1/26/2010 2:54:22 PM
Creation date
10/12/2006 3:41:59 AM
Metadata
Fields
Template:
Water Supply Protection
File Number
8240.300.10
Description
San Juan Recovery Implementation Program
Basin
San Juan/Dolores
Date
10/12/2000
Author
SJRIP
Title
San Juan River Basin Recovery Implementation Program Final Annual Budget and Work Plan Fiscal Year 2001
Water Supply Pro - Doc Type
Publication
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<br />Obiectives: <br /> <br />I. River Geometry Monitoring: Determine short term and long term change in river cross sections at key <br />locations and the relationship of this change to spring runoff and summer/fall storm events. <br /> <br />2, Cobble Bar Monitoring: Determine short term and long term change in cobble bar characteristics in <br />response to spring runoff and summer/fall storm events. <br /> <br />3. Backwater Perturbation Monitoring: Monitor effect of spring runoff and summer/fall storm events on <br />sediment accumulation in backwaters and backwater depth. <br /> <br />Methods: <br /> <br />I. River Geometry Monitoring: The 14 cross-sections identified in 1999 as part of the long term <br />monitoring plan will be surveyed pre- and post-runoff for analysis of annual change and compared to <br />previous surveys to determine trends. Analysis of the change in cross-section geometry and substrate in <br />relation to hydrographic conditions will be completed to monitor response of the system to flow <br />recommendations, <br /> <br />2. Suspended Sediment Analysis: Continuous turbidity monitors are installed at Shiprock, New Mexico <br />and Montezuma Creek Bridge, Utah. The data will be used to qualitatively assess sediment transport in <br />relation to the flow regime, in addition to identification of storm events. <br /> <br />3. Cobble Bar Monitoring: Maintenance of cobble bars with open interstitial space has been determined to <br />be important for spawning of Colorado Pikeminnow. Four sites (RM 173,7, 168.4, 132, 131) have been <br />identified in the San Juan River as having characteristics suitable for spawning. These sites have been <br />monitored since 1995, The results of the surveys at this site were used as part of the basis of the flow <br />recommendation at 8,000 cfs. To verify or adjust this recommendation, these sites will continue to be <br />monitored per the long range monitoring plan. <br /> <br />Topographic surveys will be completed for each of the sites utilizing total station or gps survey <br />equipment with control provided by the established bench marks at each site. Surveys will be <br />completed as soon as practical after spring runoff, usually during the end of July or early August. The <br />same area will be surveyed each year to allow comparison to previous years. <br /> <br />At the same time, the structure of the bar will be assessed by completing point counts of the surface bed <br />material (n=200 per sample or more) at each bar. Particles will be selected by the point count method <br />over the full extent of the bar within the survey boundary. Size is determined by placing the rocks <br />through a square hole in an aluminum plate, cut to represent an equivalent screen size from I cm <br />through 10 cm at I cm increments, then 2 cm increments through 20 cm, Those larger than 20 cm are <br />recorded as greater than 20 em. Interstitial material smaller than I cm is not recorded. <br /> <br />21 <br /> <br />I <br />I <br />I <br />I <br />\ <br />~ <br />I <br />I <br />I <br />\ <br />I <br />I <br />I <br />I <br />I <br />I <br />~ <br />I <br />E <br />
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