Locating Your Well and the Illinois State Geological Survey can provide advice on developing new wells and solving problems with old wells. High-Quality Water Are you planning a new home on a site that is not served by a community water sysem? Or are you thinking of replacing your water well with a new well? If so, the importance of having a dependable supply of safe, high-quality water cannot be overstated. Family health is at stake, and the market value of a home will reflect any serious shortcomings in the water supply. The first step in planning a new well is to familiarize yourself with the geologic conditions of your site. If you plan to install a new well, these conditions will influence the kind of well you put in, how deep you will have to drill to obtain a dependable supply, and even the potential for future water contamination. To learn about the condition of your site, you can contact local well drillers, geologists, soil scientists, agricultural and civil engineers, and University of Illinois Extension staff. In addition, specialists at the Illinois State Water Survey How Geology Affects Groundwater Although groundwater occurs everywhere, its quality and the amount available varies from one location to the next. The variation is due to geologic formations underlying different areas, which affect impurities found in the water and the rate of water withdrawal. Some of the geologic factors that affect groundwater are: permeability, depth to aquifer, and type of aquifer. Permeability Clay and Shale. Certain geologic materials, such as clay and shale, may contain abundant supplies of water in their minute pores. However, the movement of water between pores in clay and shale is so restricted that water cannot flow into a well in usable quantities. These formations Figure 1. Groundwater $SFWJDFESPDL 8BUFSOPUHSPVOEXBUFS IFMECZTPJMQBSUJDMFTBOESPDL "JS 4PJM "JS "QQSPYJNBUFMFWFMPGUIFXBUFSUBCMF (SPVOEXBUFS "MMPQFOJOHTCFMPX XBUFSUBCMFGVMMPGXBUFS When water fills all of the spaces between soil particles or rock, it is called groundwater. The upper level of the groundwater is the water table. 1 Figure 2. Aquifers 8FMM 8BUFSUBCMF -BLF 4IBMF (SBOJUF 6ODPOGJOFEBRVJGFS $POGJOFEBRVJGFS An unconfined aquifer a is bounded q by geologic u materials i through f ewhich waterr easily i moves. A confined aquifer a is bounded q on the top u by geologic i materials f e through which r water moves very slowly. Because of pressure inside a confined aquifer, the water level sometimes naturally rises in the well. This is called the “pressure head.” With an unconfined aquifer, however, water in the well remains at the same level as the water table—unless it is being pumped upward. The water table is the upper level of the groundwater. have low water-yielding capability, or what is called low permeability. Sand and Gravel. Other geologic materials capable of transmitting and storing significant quantities of water, such as sand and gravel, are referred to as aquifers. In Illinois, aquifers are commonly found in bedrock (such as sandstone, dolomite, and limestone) and in overlying unconsolidated deposits (such as sand and gravel). These materials have varying degrees of permeability. s i b s If you drill into a deeper aquifer, however, there are no assurances that the quality of water will be good. Some deep aquifers are too highly mineralized or salty for most domestic uses. The best way to determine the aquifer’s depth is to obtain a well log. If there is an existing well on the property, there should be a well log. If you do not have one, check with the previous property owners or the company that dug the well. Otherwise, contact the state geological survey, state water survey, local well drillers, or your nearest Extension office. Depth to Aquifer If the aquifer from which you draw water is within 50 feet of the surface, it is generally considered to be a shallow aquifer. Wells finished in very shallow aquifers may cost less to drill and may require a smaller pump, but they are subject to seasonal variations in precipitation that can cause the water table to rise or drop significantly. They are also more susceptible to surface sources of contamination than wells drawing from deeper aquifers. Type of Aquifer There is a strong association between the detection of agrichemicals in rural wells and the type of aquifer from which water is drawn. The potential for contamination depends a lot on whether the aquifer is “confined” or “unconfined.” 2 o b o Figure 3. Minimum Setbacks #BSOZBSE .BOVSF QJMF 4BOETBMU TUPSBHFQJMF 6OEFSHSPVOE GVFMUBOL 8FMM 4USFBN DBSSZJOHQPMMVUBOUT 'FFU In the illustration above, the well is placed out of reach from several sources of contamination. The well is more than 25 feet from the stream, more than 50 feet from the barnyard, more than 100 feet from the manure pile, and more than 200 feet from the sand/salt storage pile and the underground fuel storage tank. Confined Aquifers. An aquifer is confined when it is bounded on the top by what is called an “aquitard”—geologic materials through which water moves very slowly. This material, such as clay, shales, dense crystalline, and sedimentary bedrock, helps prevent contaminants from entering the aquifer. Unconfined Aquifers. An unconfined aquifer is bounded by permeable layers—geologic material through which water moves rapidly. Generally, confined aquifers offer cleaner, safer water; but if chemicals should enter them, it takes a long time to decontaminate them. Confined aquifers may also be harder to find and can be expensive to tap. Boundaries. The well must be within your property lines. Its exact distance from property lines is governed by local codes. Maintenance. The well must be accessible for maintenance, inspection, and pump replacement. For example, wells should not be located directly under trees or power lines or inside a house or basement. Wells also must be at least 2 feet clear of an overhang. Groundwater Flow. Ideally, the well should be placed on the side of the contaminant source opposite the flow of groundwater. For example, if you know groundwater flows to the south, place the well as far north of the contaminant as possible. To find out the direction of groundwater flow in your area, contact a well driller, an engineering firm, or the Illinois State Water Survey. Contamination Sources. The well must be as far removed as possible from potential contamination sources and routes, such as septic tanks, road salt, underground gas storage tanks, manure piles, fertilized cropland, and solid waste disposal sites. The Illinois Department of Public Health has established the following minimum setbacks for common sources and routes of contamination: • At least 200 feet from potential sources and routes of contamination. However, if What About Surface Water as Drinking Water? Location Requirements When locating a new well, most people do not have a site large enough to offer a wide range of options. This is because a well’s location is expected to meet several requirements. The following specifications are described in the Illinois Water Well Construction Code. Any variances must be approved in writing by the local health department or the Illinois Department of Public Health. 3 Surface waters (lakes, steams, ponds) generally are undesirable sources of drinking water for private water systems because they require a high degree of treatment and are easily contaminated. However, if groundwater is unsuitable for a domestic supply in your area, then you may need to consider this option. For technical assistance and advice on the potential costs and effectiveness of a surface water supply, contact the nearest office of the USDA Natural Resources Conservation Service or University of Illinois Extension. These lateral distances apply to clay- and loam-textured soils; they should be increased for more permeable soils. For example, these distances should be doubled for highly permeable, coarse-textured soils, such as loamy sand. As you evaluate a site for your well, also consider future land uses near the site, as well as pesticides that will be applied nearby. Some pesticides, such as atrazine, require setback zones around wells where the chemical cannot be applied. the owner of the private well is the same as the owner of the potential source or route of contamination, the setback is 75 feet. (For information on sources and routes of contamination, see the sidebar below.) 150 feet from existing cesspools. New installations of cesspools are not approved in Illinois. 100 feet from leaching pits. 75 feet from a pit privy or a septic seepage tile, which should be downslope from a well. 50 feet from a barnyard, animal confinement lot, or septic tank. 25 feet from lakes, ponds, and streams. 10 feet from a sewer with watertight joints. 2 feet from a pump house floor drain 100 feet from a temporary manure stack. (This is an Illinois EPA setback requirement.) • • • • • • • • Sinkholes Regions with shallow limestone or dolomite can be particularly susceptible to groundwater contamination because water may move rapidly through dissolved caverns or sinkholes. Once water enters a sinkhole, it receives little filtration or chance for degaradation of the chemical. Fractured rock systems also allow rapid movement of contaminant-bearing water. Potential Sources of Contamination Potential Routes of Contamination • • • • • Landfills and land disposal areas for municipal, special, and hazardous wastes Underground storage tanks containing more than 500 gallons and aboveground tanks containing more than 25,000 gallons of petroleum products Storage and handling areas for de-icers, hazardous substances, road oils, agricultural chemicals, and animal waste September 20072 • Number 0 15 0 • Abandoned and improperly plugged wells Injection wells (most commonly used to drain surface water and dispose of industrial and municipal waste water) Excavations related to the production of stone, sand, and gravel Sources Bob Frazee, University of Illinois Extension natural resources educator Jerry Dalsin, Illinois Department of Public Health Brian Kaiser, Illinois State Water Survey 7 & Water Coordinator Land Michael C. Hirschi, U of I Extension soil and water specialist 4
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