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(1) Arsenic up to 58 -micrograms per liter (ug/L) in groundwater from the southwestern corner of <br />the Property and up to 77-ug/L in groundwater from beneath the northeastern portion of Waste <br />Unit 1. Naturally occurring arsenic is present in the Central Valley and may be contributing to <br />concentrations at the Property. <br />(2) Total dissolved solids (TDS) were found in groundwater in areas across the land application <br />area of the 48 -acre parcel up to I ,400-mgIL. The highest TDS values were found at the <br />southeastern and southwestern corners of the Property. The elevated TDS may have resulted <br />from land application of domestic wastewater or contaminant migration from neighboring <br />commercial/industrial properties. <br />(3) Nitrates upto 1,110-mg/L were found in groundwater in the Property's land application area. <br />The elevated nitrates may have resulted from land application of domestic wastewater or <br />contaminant migration from neighboring commercial/industrial properties. <br />1.03 Concrete Pavement. The excavated waste material from Waste Unit I is stabilized within a <br />mixture of 5 percent Portland cement in the upper 12 -inches of the soil within the westerly <br />portion of the building pad subgrade and covered with a 7 -inch concrete floor slab ("Building <br />Floor Slab") to prevent potential migration of non -hazardous contaminants found in the <br />excavated glass waste material. Some excavated glass waste materiai from Waste Unit I also <br />was placed within the upper 12 -inches of soils within the concrete loading dock area north of <br />the building ("Loading Dock"), stabilized with a mixture of 5 percent Portland cement, and <br />covered with a 6 -inch concrete pavement. The areas of consolidated glass waste from Waste <br />Unit I are depicted on Exhibit A3 attached hereto (the "Consolidated Glass Waste Areas"). <br />The remaining concrete and asphalt pavement areas were treated with 5 percent Portland <br />cement to prevent potential infiltration of surface water, thereby preventing any potential <br />leachate of non -hazardous metals from entering groundwater. <br />1.04 Groundwater Remedial Action. The impacts to soil and groundwater will not pose a future <br />threat to regional groundwater or human health if (1) the Property is restricted to preclude the <br />uses listed in Section 4.01 below, (2) the current Building Floor Slab and concrete Loading <br />Dock is maintained over Consolidated Glass Waste Areas shown on Exhibit A3 to prevent <br />infiltration of surface water, and (3) future development of groundwater beneath the Property is <br />prohibited. These restrictions to eliminate exposure to and use of the groundwater are <br />necessary until the Regional Water Board determines that the potential threat to human health <br />and the environment from groundwater beneath the Property has been defined. <br />ARTICLE li-DEFINITIONS <br />2.01 Regional Water Board or RWQCB. "Regional Water Board" shall mean the Regional Water <br />Quality Control Board, Central Valley Region, and shall include its successor agencies, if any. <br />2.02 Owner. "Owner" means Covenantor, its successors in interest, including heirs and assigns, <br />who at any time hold title to or an ownership interest in all or any portion of the Property, during <br />the time of such ownership. <br />2.03 Occupant. "Occupant" means Owner and any person or entity entitled by ownership, <br />leasehold, or other legal relationship to the right to occupy any portion of the Property.