Laserfiche WebLink
' Phase 11 Environmental Site Assessment <br /> Mountain House Neighborhood G <br /> July 9,2002 <br /> Page 2 <br /> C Commissioner's office regarding potential pesticide use at the site from 1996 through July 2001, indicates <br /> pesticides and herbicides were applied at the site during those years. <br /> 3.0 ENVIRONMENTAL SETTING <br /> The site is located in the Great Valley Geomorphic Province in the northern portion of the San Joaquin <br /> Valley. The San Joaquin Valley is a northwest-trending, fault-bounded syncline tilled with up to six <br /> vertical miles of lithified non-marine and marine sediments and nonlithifted non-marine sediments. <br /> Regionally, the Iithology of the upper 3,000 feet of sediments are derived from theCoast Range Mountains <br /> to the west and the Sierra Nevada Mountains to the east. The Coast Range Mountains are approximately <br /> five miles west of the site and the Sierra Nevada Mountains are approximately 40 miles northeast of the <br /> site. <br /> Vegetative cover consisting primarily of alfalfa was present at the site during soil sample collection <br /> activities conducted as part of the Phase II. Stressed vegetation or stained areas were not observed during <br /> sampling activities conducted at the site. The site and surrounding properties were observed to be generally <br /> level during the sampling activities. The land surface in the vicinity of the site is nearly level with a very <br /> slight slope to the northeast. The elevation of the site ranges from approximately 65 to 75 feet above the <br /> National Geodetic Vertical Datum of 1929. The site is bounded by agricultural land. Surrounding <br /> properties within a mile of the site have historically been used for agricultural purposes. Access to the site <br /> is provided by the dirt roads mentioned in Section 2.0. <br /> Soils encountered in the general vicinity of the site are identified as belonging to the Capay-Stomar <br /> Zacharias general soil map unit. Soils encountered in the immediate vicinity of the site are identified <br /> primarily as Stomar clay loam, 0 to 2 percent slopes. This soil type is characterized by slow permeability, is <br /> well drained, and is typically located on alluvial fans that have nearly level relief and is formed from <br /> alluvium derived from sedimentary rock sources. The surficial soils observed at the site appeared to be <br /> generally similar throughout the site. <br /> Because pesticide and herbicide applications are typically restricted to crops and the soil surface, the <br /> potential for these materials to impact groundwater at the site is considered to be minimal. Residual <br /> concentrations of pesticides and herbicides are likely to be confined to the upper 6 to 12 inches of soil as a <br /> result of surficial application. The scope of work performed by Condor as part of this Phase Il did not <br /> include groundwater investigation activities to accurately determine the potentiometric surface below the <br /> site. No piezometers or groundwater monitoring wells were installed. Pumping of site groundwater for <br /> drinking water or any other purpose is not anticipated in the future. Additionally, there are no natural <br /> surface water bodies at the site. <br /> 4.0 SOIL SAMPLING PROCEDURES <br /> Condor personnel collected soil samples from the site on September 28, 2001. The soil sampling <br /> procedures were conducted in general accordance with the soil sampling plan described in the work plan <br /> and with soil sampling plans developed by Condor and utilized to conduct Preliminary Endangerment <br /> Assessments at similar properties in the San Joaquin Valley. The field sampling plan was developed using <br /> information contained in the DTSC Preliminary Endangerment Assessment Guidance Manual, dated <br /> January 1994 (Second Printing, June 1999) and the Interim Guidance for Sampling Agricultural Soils, <br /> prepared by Mr. Brad Parsons of the DTSC,dated June 2000. <br /> iJ CONDOR <br />