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CO0052918
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Last modified
7/14/2022 10:51:25 AM
Creation date
3/5/2021 10:16:14 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
RECORD_ID
CO0052918
PE
2900
STREET_NUMBER
0
STREET_NAME
WALNUT GROVE
City
WALNUT GROVE
ENTERED_DATE
11/4/2020 12:00:00 AM
SITE_LOCATION
WALNUT GROVE & OTHERS
RECEIVED_DATE
11/4/2020 12:00:00 AM
P_LOCATION
99
QC Status
Approved
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<br />Soil Investigations for Data Collection in the Delta <br />Initial Study/Proposed Mitigated Negative Declaration 83 <br />metamorphosis from larval to juvenile stages. After approximately 10 days, <br />larvae begin feeding and growing rapidly, and young green sturgeon appear to <br />rear for the first 1 to 2 months in the upper Sacramento River between Keswick <br />Dam and Hamilton City (CDFW 2002). Length measurements estimate juveniles <br />to be 2 weeks old (24 to 34 millimeters [0.95 to 1.34 inch] fork length) when they <br />are captured at the Red Bluff Diversion Dam (CDFW 2002; USFWS 2002), and <br />three weeks old when captured further downstream at the Glenn-Colusa facility <br />(Van Eenennaam et al. 2001). Growth is rapid as juveniles reach up to 30 <br />centimeters (11.8 inches) the first year and over 60 centimeters (24 inches) in the <br />first 2 to 3 years (Nakamoto et al. 1995). Juveniles spend 1 to 4 years in <br />freshwater and estuarine habitats before they enter the ocean (Nakamoto et al. <br />1995). According to Heublein et al. (2009), in 2006 all tagged adult green <br />sturgeon emigrated from the Sacramento River prior to September. Lindley et al. <br />(2008) found frequent large-scale migrations of green sturgeon along the Pacific <br />Coast. Kelly et al. (2007) reported that green sturgeon enter the San Francisco <br />Estuary during the spring and remain until fall. Juvenile and adult green sturgeon <br />enter coastal marine waters after making significant long-distance migrations with <br />distinct directionality thought to be related to resource availability. <br />Overall, designated in-water work windows would reduce exposure of sensitive <br />fish species and life stages to in-water work activities. The activities of the <br />Proposed Project would be minor in scope and would not result in degradation of <br />aquatic habitat or water quality conditions and any potential effects related to <br />potential increase in suspended sediment concentrations and contaminants due <br />to disturbance of the river bed would be negligible. Implementation of Mitigation <br />Measures MM BIO-14, along with MM HYD-1 and MM HAZ-1 through 4 would <br />reduce potential impacts to green sturgeon to: Less than Significant with <br />Mitigation Incorporated. <br />MM-BIO-14: General Fish <br />Over-water activities will be limited to only being conducted during the fish <br />window (August 1 – October 31) to avoid impacts to sensitive fish species <br />that have the potential to occur in the Study Area. <br /> <br />Delta Smelt (Hypomesus transpacificus) <br />Delta Smelt is listed as a threatened species under the FESA and was listed as a <br />threatened species under the CESA in 1993. In 2009, Delta Smelt was <br />reclassified as an endangered species under the CESA. The 2010 5-year status <br />review recommended up-listing Delta Smelt from threatened to endangered <br />status under the FESA (USFWS 2010a). However, as of the time of this writing, <br />Delta Smelt remain listed as threatened under the FESA. <br />Delta Smelt are endemic to the San Francisco Estuary, found nowhere else in <br />the world (Bennett 2005). The Delta functions as a migratory corridor, as rearing <br />habitat, and as spawning habitat for Delta Smelt. Overall, the Delta Smelt life
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