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ARCHIVED REPORTS_DRAFT ENVIRONMENTAL IMPACT REPORT
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ARCHIVED REPORTS_DRAFT ENVIRONMENTAL IMPACT REPORT
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Last modified
7/23/2020 5:02:58 PM
Creation date
7/23/2020 4:33:19 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
DRAFT ENVIRONMENTAL IMPACT REPORT
RECORD_ID
PR0506303
PE
2965
FACILITY_ID
FA0001086
FACILITY_NAME
MANTECA PUBLIC WORKS
STREET_NUMBER
2450
Direction
W
STREET_NAME
YOSEMITE
STREET_TYPE
AVE
City
MANTECA
Zip
95336
APN
24130050
CURRENT_STATUS
01
SITE_LOCATION
2450 W YOSEMITE AVE
P_LOCATION
04
P_DISTRICT
005
QC Status
Approved
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program defined as the primary data source for a site was the program possessing the longest from dry/below normal water years were available for analysis. Data from dry/below normal <br /> monitoring history at the particular location. If data from the primary data source were not water years reflect different water quality conditions in the Delta relative to conditions observed <br /> available for a particular parameter at a particular site,then data from a secondary and/or tertiary during wet or above normal water years. San Joaquin River water quality and flow conditions <br /> data source were used. In an effort to compile as large a data set as possible for a particular characteristic of dry/below normal water years are expected to reflect future San Joaquin River <br /> parameter at a particular monitoring site,data from more than one monitoring program were conditions during rainfall-limited time periods due to the actions set forth in the Water Quality <br /> often combined when appropriate to provide an extended data set. These secondary and tertiary Control Plan for the San Francisco Bay/Sacramento-San Joaquin Delta Estuary(1995 Bay-Delta <br /> data sources acted to"fill in"data gaps that exist in the primary program's monitoring record at a Plan;SWRCB,1995)and the Revised Water Right Decision 1641(SWRCB,2000). <br /> particular location. So as not to unfairly weight certain sample collection dates by including The 1995 Bay-Delta Plan sets forth flow objectives to control declines in aquatic resources— <br /> more than one data point(coming from multiple monitoring programs)for any single calendar namely,fisheries—experienced in the Bay-Delta Estuary in recent decades,in addition to <br /> date,data from non-primary monitoring programs were omitted from the data set used for providing upstream-and within-Delta management strategies for the protection of beneficial uses <br /> statistical analysis. For example,on the occasion that a particular monitoring location possessed that involve salinity,water project operations,and DO. San Joaquin River at Vernalis flow <br /> three DO measurements taken on the same date,only a single DO measurement was included in objectives contained in the 1995 Bay-Delta Plan require spring and fall flows in the river to <br /> the final data set. The single DO measurement chosen for analysis was taken from the support spring out-migration and fall spawning of salmonids,respectively. Information gathered <br /> monitoring program acting as the primary data source for the site. Excluding the other two DO by parties during the limited-term Revised Water Rights Decision 1641(in effect through 20 10) <br /> measurements avoided the skewing of the statistical analysis since most monitoring dates were will allow the State Water Board to further review Vernalis flow objectives in terms of timing <br /> only represented by a single environmental measurement from a single monitoring program. and magnitude during a future review of the 1995 Bay-Delta Plan. Irrespective of final numeric <br /> Data were also excluded from use where analyte detection,analytical method,and detection limit flow objectives for the San Joaquin River at Vernalis that may be set forth in a future Bay-Delta <br /> were not documented sufficiently in a monitoring program's original raw data set. Plan,future flow objectives will provide flows similar to or greater than those observed during <br /> Water Year Hydrologic Classification dry water years,and not typical of those historically experienced during critical water years,as a <br /> means of protecting the aquatic life and water supply beneficial uses of the Bay-Delta Estuary. <br /> Data for the 18 water quality parameters measured at selected sites in the project area(see Table <br /> 7)were compiled and summary statistics calculated to provide historic surface water quality Table 9: Hydrologic Classification of Years 1990 <br /> information for two different water year types:critical years and dry/below normal years. Even through 2006 by Water Year Type <br /> though dry and below normal water years are distinct hydrologic classifications under the <br /> California Department of Water Resources hydrologic classification scheme(see Figure 4),they Water Year <br /> are grouped together in the current analysis as a"dry/below normal"water year type due to the Water Year Type (Oct.1—Sept.30) <br /> grouping of data required to produce as large a water quality data set as possible. The analysis of 1990 <br /> water quality data for two distinct water year hydrologic classifications—critical and dry/below 1991 <br /> normal—provides information upon which to estimate future water quality conditions in the Critical 1992 <br /> project area under the widely variable hydrologic conditions experienced in California's Central 1994 <br /> Valley. Critical and dry/below normal water years represent worse case conditions for most 2001 <br /> parameters as they relate to the impact of WQCF discharge on Delta water quality as compared <br /> to impacts measured during a wet or above normal water year. The current near-and far-field Dry 2002 <br /> water quality impacts assessments were designed to estimate the incremental change in water 2004 <br /> quality within the project area with an increase in WQCF effluent flowrate from the current Below Normal 2003 <br /> permitted 9.87 MGD(ADWF)to the proposed 27 MGD(ADWF). The greatest incremental 1999 <br /> change in surface water quality conditions in the San Joaquin River and Delta would likely occur Above Normal 2000 <br /> when WQCF effluent is discharged to a system with comparatively lower ambient pollutant 1993 <br /> concentrations and diminished flows such as those observed during critical and dry/below 1995 <br /> normal water years. <br /> 1996 <br /> Using California Department of Water Resources water year hydrologic classifications for the Wet 1997 <br /> San Joaquin Valley(see Figure 4),water quality data collected during specific water years were <br /> selected to determine baseline surface water quality in the project area during critical and 1995 <br /> dry/below normal water years. Table 9 lists the water year designations and relevant time 2005 <br /> periods for the years 1990 through 2006. With regard to the constituents selected for near-field 2006 <br /> impact assessments in the project area(see Table 7),only San Joaquin River water quality data <br /> City of Manteca Antidegradation Analysis 27 June 2007 City of Manteca Antidegradation Analysis 28 June 2007 <br />
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