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SU0005871
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SU0005871
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Last modified
8/5/2026 3:12:15 PM
Creation date
10/27/2025 3:44:10 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
File Section
RECORDED DOCUMENTS
RECORD_ID
SU0005871
STREET_NUMBER
34443
Direction
S
STREET_NAME
BIRD
STREET_TYPE
RD
APN
25328002
CURRENT_STATUS
In Review
QC Status
Approved
Scanner
SJGOV\gmartinez
Supplemental fields
Site Address
34443 S BIRD RD
Tags
EHD - Public
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2024 ANNUAL GROUNDWATER MONITORING REPORT <br /> TEICHERT AGGREGATES AND GRANITE CONSTRUCTION <br /> VERNALIS AREA <br /> tabulated in Attachment 2.Water levels in the South Tracy#3 production well were also monitored at a <br /> higher frequency. However, up until spring 2021,the sounding of water levels below a depth of <br /> approximately 271 feet was not successful due to an obstruction at this depth. Since spring 2021,the <br /> obstruction is no longer present,and water levels have been obtained. <br /> The Petz irrigation well, located west of the Teichert Vernalis plant, is completed in both the shallow and <br /> deep zones of the underlying aquifer system, and its water level hydrograph reflects a composite of <br /> these shallow and deep zones(see Attachment 1).The early water level record of this well (prior to <br /> 2000)shows groundwater level elevations between those observed in the discussed shallow and deep <br /> wells in the area. Similarly,seasonal fluctuations prior to 2000 appear to be a composite of observations <br /> made in the shallow and deep network wells. Specifically,seasonally high-water levels in this well rose <br /> from 72.46 to 86.58 feet (msl) between March 1994 and 1998,with seasonal fluctuations of almost 15 <br /> feet. Since then,water levels have been very similar to those observed in the shallow network wells.As <br /> of August 2022,this well is no longer accessible and has been removed from the monitoring network. <br /> Contours of equal groundwater elevations prepared with data from the shallow network wells show that <br /> the general direction of groundwater flow during times of seasonally high-water levels was typically to <br /> the east-southeast and east. This includes the first monitoring event in spring 1994 with comparatively <br /> high-water levels (Figure 10) and the period of the highest historically recorded groundwater elevations <br /> in spring 1998(Figure 11).The water level elevations in spring 2000 were relatively low compared to <br /> groundwater conditions observed in previous spring seasons, however,the predominant direction of <br /> flow was also to the east-southeast(Figure 12). In spring 2002, overall groundwater elevations were <br /> very similar to the spring 2000 elevations, but the groundwater flow direction was east-northeasterly as <br /> influenced by a relatively high groundwater level in the Koster irrigation well (Figure 13). <br /> The February 2024(Figure 14)groundwater elevation contour map indicates a predominately <br /> southeasterly groundwater flow condition.The November 2024(Figure 15)groundwater elevation <br /> contour map indicates a predominately easterly groundwater flow condition. <br /> 4.2 Groundwater Quality <br /> The electrical conductivity(EC)of samples retrieved from the shallow network wells(Hall and Faulkner <br /> domestic wells) mostly ranged between 900 and 1,000 VS/cm between 1994 and the mid-2000's when <br /> EC values started to decrease until early 2014(Figure 16).The November 2014 EC measurement in the <br /> Faulkner well was the highest on record (1,130 µS/cm); Hall increased to 1,040 0/cm.Since late 2015, <br /> EC decreased in both the Faulkner and Hall wells to values lower than early 2014. During 2024, EC in the <br /> Hall domestic well was the lowest of the period of record at 732 VS/cm.The EC of samples retrieved <br /> from the deep network wells South Tracy#1,#3, and Brown's New mainly range from 800 to 900 µS/cm <br /> LUHDORFF&SCALMANINI <br /> CONSULTING ENGINEERS 7 <br />
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