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1. Well wholly situated in unconsolidated <br /> material in an unconfined ground water zone (Figure 9A). If <br /> the ground water supplies are within 50 feet (15 metres) of <br /> the surface, the upper 20 feet (6 metres) shall be sealed <br /> with impervious material and the remainder of the well shall <br /> be filled with clay, sand, or other suitable inorganic <br /> material (see item D, this section). - <br /> 2. Well penetrating several aquifers or <br /> q <br /> formations. In all cases the upper 20 feet (6 metres) of the 4 : r y EXISTING GROOJT SEAL . .'.;- <br /> well shall be sealed with impervious material. 2d M""` r y gp Ew10t€ <br /> ' 20'min. <br /> In areas where the interchange of water between F. —SEALIIIS YpiER��1L `:;+� �. ' ► =?- <br /> aquifers will result in a significantV deterioration of the ° Q <br /> quality of water in one or more aquifers, or will result in a <br /> loss of artesian pressure, the well shall be filled and <br /> sealed so .as to prevent such interchange. Sand or other CX$ING <br /> suitable inorganic material may be placed opposite the <br /> producing aquifers and other formations where impervious FILLER <br /> sealing material is not required. To prevent the verticalRSk�LIHG <br /> movement of water from the producing formation, impervious <br /> material must be placed opposite confining formations above iIITEJiIIkL <br /> and below the producing formations for a distance of 10 feet <br /> (3 metres) or more. The formation producing the deleterious � RAVEL py <br /> water shall be sealed by placing impervious material <br /> opposite the formation, and opposite the confining formations :* <br /> for a sufficient vertical distance (but no less than 10 feet ' <br /> or 3 metres) in both directions, or in the case of "bottom" A" SHALLOW WELL Ill UNCONSOLIDATED waters, in the upward direction. (See Figure 9B.) TERJ ! <br /> In locations where interchange is in no way detri i:'. _:'o- I': <br /> mental, suitable inorganic material may be placed opposite <br /> the formations penetrated. When the boundaries of the ExiSiING n I-' AQUIFER T4 <br /> various formations are unknown, alternate layers of ACKFILt <br /> impervious and pervious material shall be placed in the well. I r}r RFNE T101�8 #'.�.: � I. SE,S�Ep-pFFI <br /> 5, Max <br /> Determining the significance of interchange of waters 4 Mfl'�tIN <br /> whose qualities vary and of the loss of artesian pressures, <br /> Ap ' .` .:*'. <br /> 'requires extensive knowledge of the ground water basin in . '. FALLER T <br /> question. The Department of Water Resources has over the '�"' ;.' r:: <br /> years, and frequently in cooperation with agencies such as a GR SEALING <br /> the U. S. Geological Survey, undertaken a number of r ' SEALING MATERIAL MATERIAL <br /> water studies and amassed considerable information and ` " 1 <br /> CASlFiG Ex15TIMG � <br /> data about the subject. Although much is known about the :: .' . ERFORATION$ ! M <br /> State's ground water supplies, detailed studies suffi- <br /> ciently accurate to define interchange problems have been EXrSTIIfG GROUT <br /> I I <br /> made only in certain areas. In still other areas, there _ ; ' <br /> is only partial definition of the problem. Examples of '• ExL I r <br /> areas where definition has been made are the coastal plain UPPER J$EALfN� FEATURES g DEEP WELL WITH AQUIFER SE r <br /> of Los Angeles County and the eastern part of the Santa URBAN AREA WELL <br /> Clara Valley in Alameda County. An excellent example of a <br /> "bottom" water is the saline connate water underlying the <br /> Central Valley at varying depths. <br /> Figure 9. PROPERLY DESTROYED WELLS <br />