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SU0013451
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SU0013451
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Last modified
5/17/2021 4:00:53 PM
Creation date
6/23/2020 11:17:55 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
RECORD_ID
SU0013451
PE
2600
FACILITY_NAME
WC-90-1
STREET_NUMBER
2248
Direction
W
STREET_NAME
LAKE FOREST
STREET_TYPE
RD
City
ACAMPO
APN
00306001
ENTERED_DATE
6/17/2020 12:00:00 AM
SITE_LOCATION
2248 W LAKE FOREST RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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4.7 BIOLOGICAL RESOURCES <br /> aggressive pioneer weed species such as horseweed (Conyza canadensis)and cocklebur(Xanthium sp.). <br /> The latter species is an extremely successful colonizer of open moist soil and shoreline areas during <br /> drought years when such seasonal wetland sites dry in the early spring. At the beginning of the study <br /> for the DEIR in fall 1991,dense cocklebur stands were found throughoutthe lake basins and broken only <br /> where a tractor had disced random wide swaths through the weed complex. <br /> The return of a near normal rainfall pattern in Central California during the 1991-92 winter resulted in <br /> water impoundment in the lake basins by late December. By mid-January they were filled to near <br /> capacity(Figure 4.7-2). Measurements taken by the EIR biologist found depths at the lake centers ranged <br /> from an average of 7 to 11 feet. The inshore zones exhibited depths of one to two feet over large <br /> horizontal distances, and in many areas stands of last year's annual weed crop extended above the water <br /> surface (Figure 4.7-3). <br /> Lake water levels remained high throughout mid and late spring after the winter rains ceased. By early <br /> June 1992 lake levels had receded only a few feet. Increased evaporation occurred during the warm <br /> periods of late June and July, and by mid-summer the surface areas of the lakes were reduced to about <br /> one-half of their original extent. At the termination of the field work in late August 1992 the water area <br /> was reduced to the middle portion of the cross sectional area of each lake basin and had a surface area <br /> of about one-fourth of that present in late winter. However, this remaining aquatic zone still averaged <br /> four feet in depth and extended nearly the entire length of South Tracy Lake (Figure 4.7-4). In the north <br /> lake it was confined to the southern portion of the lake basin. <br /> By late summer a dense annual weed crop had once again occupied the shallow portions of the now dry <br /> lake basins (Figure 4.7-5). However,unless the onset of the fall-winter rainy season is exceptionally late <br /> this year, it appears that an aquatic zone will persist throughout 1992 and may once again be quite <br /> extensive by the new year. Given this natural, unmodified annual cycle for these old Central Valley <br /> aquatic habitats, the term "permanent wetland" rather than "seasonal wetland" seems far more <br /> appropriate in describing these lakes. <br /> Pond/Stream Habitats <br /> Two additional permanent wetland habitats, the "Beaver Pond" and the Mokelumne River, are situated <br /> on the southern edge of the project site (Figure 4.7-1). The Beaver Pond was formed by damming an <br /> arm of South Tracy Lake and is maintained by waste irrigation water from adjacent vineyards (Figure <br /> 4.7-6). It holds water throughout the year, even during extended drought periods. This statement is <br /> supported by several of the larger fish specimens netted in the fall, 1991,lake survey,which presumably <br /> have lived in the lake for a number of years. <br /> The lake supports a lush inshore aquatic vascular plant stand which extends out to a depth of <br /> approximately 4 feet. Maximum lake depth at several sounding points ranges between 6.5 and 8.5 feet. <br /> 4.7-3 <br />
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