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Environmental Impact Statement - Sonoma Land Trust

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California Department of Fish and Game<br />

U.S. Fish and Wildlife Service<br />

Section 3.5. Biological Resources<br />

Table 3.5-3 Species Protection Windows<br />

(Note: The species protection windows may be modified by permits)<br />

Species<br />

California Clapper Rail and Black Rail<br />

Burrowing owls<br />

White-tailed kite, northern harrier, short-eared<br />

owl, tricolored blackbird, San Pablo song sparrow,<br />

and saltmarsh common yellowthroat or other nonspecial<br />

status migratory bird<br />

California red-legged frog<br />

Rearing juvenile salmonids and longfin smelt<br />

Species Protection Window<br />

Avoid construction in tidal marsh habitat during rail<br />

breeding season from February 1 through August 31<br />

if present.<br />

No eviction from burrows.<br />

Restoration construction activities shall not be<br />

conducted during the breeding season (generally<br />

March 1 through September 1) for these species to<br />

the degree feasible to avoid removing or disturbing<br />

any active nests.<br />

Construction that commences in the dry season may<br />

continue into the rainy season if exclusion fencing is<br />

placed. Avoid grading activity within suitable<br />

aquatic and associated upland habitat (within 300<br />

feet of aquatic habitat) between the onset of the<br />

rainy season (generally October 15, whichever<br />

occurs first) to May 1 unless exclusion fencing is<br />

utilized.<br />

Avoid construction activities that could affect tidal<br />

aquatic habitats (e.g., construction associated with<br />

lowering the perimeter levee and excavating tidal<br />

channels through the outboard salt marsh) during<br />

periods when special status fish could be present<br />

(typically August thru November) to the extent<br />

feasible. If hydraulic dredging is used to excavate<br />

the connector channel, a maximum 10-inch pump<br />

would be allowed, and salinity and temperature<br />

considerations would dictate dredge operations.<br />

A major assumption used in this analysis is that the predicted conditions of the<br />

restoration alternatives would actually develop within 50 years of<br />

implementation of the proposed expansion. These predictions are largely based<br />

on estimated rates of sediment accumulation, subsidence of dredged and other fill<br />

material, and colonization of plants, as well as predictions of the effects of wave<br />

action on plant colonization. and the rate of sea level rise. The actual rate at<br />

which nontidal and tidal wetland habitats would evolve and their distribution on<br />

the Project site is speculative because of uncertainties regarding the actual<br />

function and interaction of these parameters in tidal systems. Other assumptions<br />

used to conduct this analysis include the following.<br />

Sears Point Wetland and Watershed Restoration<br />

Project Final <strong>Environmental</strong> <strong>Impact</strong><br />

Report/<strong>Environmental</strong> <strong>Impact</strong> <strong>Statement</strong><br />

3.5-26<br />

April 2012

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