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2900 - Site Mitigation Program
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PR0524783
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Entry Properties
Last modified
2/24/2026 4:22:45 PM
Creation date
11/1/2021 4:44:45 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0524783
PE
2960 - RWQCB LEAD AGENCY CLEAN UP SITE
FACILITY_ID
FA0016638
FACILITY_NAME
GREIF STOCKTON
STREET_NUMBER
800
Direction
W
STREET_NAME
CHURCH
STREET_TYPE
ST
City
STOCKTON
Zip
95203
APN
14523004
CURRENT_STATUS
Active, billable
QC Status
Approved
Scanner
SJGOV\gmartinez
Supplemental fields
Site Address
800 W CHURCH ST STOCKTON 95203
Tags
EHD - Public
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TABLE 4 maintenance and operating costs over the long run, although <br /> VOLUME OF WATER PUMPED CONTINUOUSLY it should be recognized that there is a limit to what can be <br /> FROM SMALL CAPACITY WELLS achieved when compared to expenditure. Current design and <br /> construction technology is capable of producing wells with <br /> efficiencies of 80 to 90 percent. Pumping-plant or "wire-to- <br /> Pumping Rate Total Pumped in 24-Hours water" efficiency is currently at 65-70 percent. <br /> Gallons (litres) per minute Gallons Litres Sandia <br /> 0.25 ( ) 0 1 7360 20 <br /> Irrespective of size or composition, any loose <br /> 0.5 (22 72 720) 720 2 material entering a well is usually called "sand", and wells <br /> 5 that regularly produce significant quantities of loose <br /> 1 4 2900 5 00 0 material are termed "sanders". The continued influx of sand <br /> 2 8 900 11 0 to a well results in damage to pumps and leads eventually to <br /> 3 (11) 4,300 16 300 decreased capacity, and thus a reduction in well efficiency. <br /> 5 (19) 7,200 27,200 Further, enough sand may pass through the well to create <br /> 10 (38) 14,400 54 500 cavities in the aquifer around the intake section of the <br /> 50 (190) 72,000 273 000 well. As a result, such cavities can collapse and damage the <br /> well casing or screen. While most wells pump a minor amount <br /> of sand, excessive sanding is usually caused by poor well <br /> of the aquifer(s) in which the well is situated.. The design or inadequate development. <br /> discharge rate and drawdown established should be maintained Uncased ("Open-bottom"). Wells. Casing serves to <br /> for a specified time period. The ratio of the discharge rate hold up the walls of the borehole and provide a path for the <br /> to the drawdown is called the specific capacity of the well movement of the water. In formations with material that will <br /> for that time period. The units for specific capacity are not loosen and be carried away by the inflowing water, such <br /> gallons per minute per foot (litres per minute per metre) of as crystalline rock and other "hard rock" formations, the <br /> drawdown. Static water levels must be measured in advance of practice is to leave the intake sections Uncased. (Theoreti- <br /> the test and after the test during recovery. tally in such instances, well efficiency would be <br /> Detailed descriptions of procedures and methods 100 percent.) Unfortunately, in certain areas some drillers, <br /> believing the underlying material to be fully consolidated or <br /> used in conducting pump tests for large capacity wells and <br /> attempting <br /> for analyzing and interpreting the results are too lengthy to r save on costs, have drilled open-bottom wells <br /> p <br /> be included in this publication. Such information will be that later produced sand. Furthermore, as pumps lowered <br /> found in literature on ground water and on the design of following declining water levels, such wells developed <br /> water wells. sanding problems. This occurred in several areas in the <br /> Central Valley during the 1976-77 drought. In such instances, <br /> Well Efficiency the wells should have been completely cased to prevent caving <br /> and the intake section screened to prevent the entrance of <br /> Well efficiency is defined as the ratio of the sand. <br /> theoretical drawdown in the formation to the actual drawdown Inadequately Designed Intake Sections. Sanding is <br /> in the well. The difference between the two is caused by often the result of poor selection of screen size or perfora- <br /> frictional energy losses of the water as it moves from within tion dimensions and/or, where used, filter material (the <br /> the formation to the pump intake. Thus, well efficiency "gravel pack"). The well screen aperture (slot) openings or <br /> describes the effectiveness of a well in yielding water. the perforation size, together with the length of screen or <br /> Well efficiency should not be confused with pumping-plant <br /> (motor and pump) or "wire-to-water" efficiency used to perforated section, should be selected to provide sufficient <br /> measure um lant erformance open area to allow the desired quantity of water to enter <br /> pumping-plant p with minimal friction losses while keeping out 90 to 95 per- <br /> It should be obvious that well efficiency is cent of the natural aquifer material or filter material. <br /> related to the cost of pumping and the use of energy. If Artificial filter materials perform a similar <br /> efficiency improves, pumping costs and energy consumption function. In addition to allowing the water to enter the <br /> will drop. Thus, optimum well design is no less important well openings and preventing the entrance of fine-grained <br /> where a small capacity well is concerned than it is for one material, artificial filters are also used to increase the <br /> with a large capacity. Unfortunately, design and construction effective diameter of the well and increase the yield of <br /> practices that produce efficient wells are often sacrificed in certain wells by allowing numerous thin aquifers to produce <br /> order to save on the cost of constructing a well, particularly water. On the other hand they need not be used unless there <br /> in the case of small capacity wells. However, the increased are conditions that make their use desirable or necessary. <br /> cost of design and construction can be offset by decreased <br />
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