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Environmental Health - Public
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VIA NICOLO
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2900 - Site Mitigation Program
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PR0516772
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
6/1/2020 12:44:39 PM
Creation date
6/1/2020 12:23:17 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0516772
PE
2965
FACILITY_ID
FA0012793
FACILITY_NAME
MUSCO OLIVE LAND APP/TITLE 27
STREET_NUMBER
17950
Direction
W
STREET_NAME
VIA NICOLO
STREET_TYPE
RD
City
TRACY
Zip
95377
APN
20911032
CURRENT_STATUS
01
SITE_LOCATION
17950 W VIA NICOLO RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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Bert E. Van Voris • - 15 - 17 September 2004 <br /> Supervising Engineer <br /> management,18 yet recommends application of sulfuric acid to improve process water penetration, soil <br /> aeration, and crop growth. The RWD strongly recommends that`Bermuda grass be established and <br /> permeability maintained with gypsum and sulfuric acid treatment, if necessary."19 It states, "with <br /> improved management of salt tolerant crops,the land application system areas will satisfactorily <br /> accommodate the period of phasing out process wastewater application as Musco,implements its long- <br /> term compliance plan.i20 <br /> Comment. The RWD does not cite the technical report describing the soil sampling results <br /> obtained in 2003 by Kennedy/Jenks. Soil sampling results presented in Dellavalle's <br /> reports, and summarized in the RWD, do not include SAR as required by the MRP. <br /> The RWD characterizes site soils as containing very little nitrogen,yet data show <br /> instances where soil nitrate concentrations were very high(e.g.,two profiles in Field 95 <br /> and profiles in Park West). <br /> Most significantly, the RWD does not, but should, utilize in its analysis soil data collected <br /> prior to 2000 (e.g., 1999 Annual Monitoring Summary Report dated 31 January 2000). <br /> Comparison of recent data with pre-2000 data clearly shows the extent to which Musco's <br /> discharge has degraded the quality of site soils. Compared to soil not influenced by the <br /> discharge sampled in 1999 in the vicinity of what was then called Field 1 (now called <br /> South Ridge), the upper profile of site soils now contain extremely high concentrations of <br /> sodium, chloride, and other IDS constituents.21 The impact of salt loading to site soils is <br /> summarized below: <br /> pH EC Sodium ESP SAR <br /> (x 103 ms/cm) (meq/L) <br /> Upper profile' <br /> 1999 6.5 1.3 1.5 < 0.1 0. 6 <br /> 2003 9.0 12.73 107.2 39.2 44 .5 <br /> Mid-profile2 <br /> 1999 7. 9 0.4 4.0 4. 6 4.1 <br /> 2003 8 .2 2.73 20.4 16.2 13. 9 <br /> Bottom profile' <br /> 1999 7 .4 1.7 12. 8 7. 9 6.7 <br /> 2003 8.1 1.47 10. 10 10.0 8.9 <br /> Upper profile collected at 0" in 1999 and 0-6" in 2003 <br /> 2 Mid-profile collected at 36" in 1999 and 27-39" in 2003 <br /> 3 Bottom profile collected at 60" in 1999 and 60-72" in 2003 <br /> The RWD should provide data on infiltration rates in the various application fields. <br /> Tailwater collection occurs either in constructed channels or, as in the case of Field 95, in <br /> natural surface water drainage ways. Discharge Prohibition A.2 prohibits the direct or <br /> indirect discharge of wastes within 100 feet of a surface water or surface water drainage <br /> course unless such discharge has been authorized by the Executive Officer. Staff will <br /> research the case file to determine whether such authorization was provided. In any event, <br /> even if it was authorized,the conveyance of tailwater in surface water drainage ways has <br />
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