If properly developed, water from wells may be suitable for culinary use without treatment. A determination concerning whether treatment may be required can only be made after the source has been developed and evaluated.
Water suppliers shall assess the capability of their system in the event of a power outage. If a community water system has no naturally flowing water sources such as springs or flowing wells, one or more of the system's sources shall be equipped for operation during power outages. In this event:
The Utah Division of Water Rights, State Engineer's Office, regulates the drilling of water wells. Before the drilling of a well commences, the well driller must receive a start card from the State Engineer's Office. For public drinking water supply wells, Rule R655-4 applies and shall be followed in addition to this rule.
Public drinking water systems are responsible for protecting their sources from contamination. The selection of a well location shall only be made after consideration of the requirements of Rule R309-600. Sources shall be located in an area that will minimize threats from existing or potential sources of pollution.
Interior surfaces must consist of products complying with ANSI/NSF Standard 61. This requirement applies to drop pipes, well screens, coatings, adhesives, solders, fluxes, pumps, switches, electrical wire, sensors, and any other equipment or surfaces which may contact the drinking water.
Substances introduced into the well during construction or development shall be certified to comply with ANSI/NSF Standard 60. This requirement applies to drilling fluids, including biocides, clay thinners, defoamers, foamers, loss circulation materials, lubricants, oxygen scavengers, viscosifiers, weighting agents, and regenerants.
The use of any non-ferrous material for a well casing shall receive prior approval of the Director based on the ability of the material to perform its desired function. Thermoplastic water well casing pipe shall meet AWWA Standard A100-06 and shall bear the logo NSF-wc indicating compliance with NSF Standard 14 for use as well casing.
Cuttings and waste from well drilling operations shall not be discharged into a waterway, lake, or reservoir. The rules of the Utah Division of Water Quality must be observed with respect to these discharges.
Packers, if used, shall be of material that will not impart taste, odor, toxic substances, or bacterial contamination to the well water. Lead or partial lead packers are specifically prohibited.
The use of well screens is recommended where appropriate and, if used, they shall:
Every well shall be tested for plumbness and vertical alignment in accordance with AWWA Standard A100. Plans and specifications submitted for review shall:
The placement of perforations in the well casing shall:
For each public drinking water well, the annulus between the outermost well casing and the borehole wall shall be sealed with grout to a depth of at least 100 feet below the ground surface unless an exception is issued by the Director, see Subsection R309-500-4(1). If more than one casing is used, including a conductor casing, the annulus between the outermost casing and the next inner casing shall be sealed with grout, meeting the sealing materials requirements of Subsection R309-515-6(i)(ii) or with a water tight steel ring having a thickness equal to that of the permanent well casing and continuously welded to both casings. If a public drinking water well will be equipped with a pitless adapter or unit, a well seal shall be installed to a minimum depth of 110 feet to account for the top 10 feet of compromised seal interval.
The following shall apply to each drinking water well:
Cement, conforming to ASTM Standard C150, and water, with no more than six gallons of water per sack of cement, shall be used for two-inch openings. Additives may be used to increase fluidity subject to approval by the Director.
Equal parts of cement conforming to ASTM Standard C150, and sand, with no more than six gallons of water per sack of cement, may be used for openings larger than two inches.
Where an annular opening greater than six inches is available, a seal of swelling bentonite meeting the requirements of Subsection R655-4-11 (11.4.2) may be used when approved by the Director.
Any water entering a well during construction shall not be contaminated and should be obtained from a chlorinated municipal system. Where this is not possible, the water must be treated to produce a 100 mg/l free chlorine residual in accordance with Subsection R655-4-11 (11.6.5).
The following shall apply to gravel packed wells:
Preliminary to the constant-rate test required in Subsection R309-515-6(10)(b), it is recommended that a stepdrawdown test, which is uniform increases in pumping rates over uniform time intervals with single drawdown measurements taken at the end of the intervals, be conducted to determine the maximum pumping rate for the desired intake setting.
A constant-rate yield and drawdown test shall:
If the aquifer drawdown test data show that the drawdown has stabilized, the Director will consider 2/3 of the pumping rate used in the constant-rate test as the safe yield of the well. The safe yield is used to determine the number of permanent residential connections or ERCs that a well source can support.
Every new, modified, or reconditioned well including pumping equipment shall be disinfected before being placed into service for drinking water use. These shall be disinfected according to AWWA Standards C654-03 and A100-06 as modified to incorporate the following as a minimum standard:
Naturally flowing wells shall:
If the excavation surrounding the well casing allowing installation of the pitless unit compromises the surface seal, the competency of the surface seal shall be restored. Torch-cut holes in the well casing shall be neat lines closely following the outline of the pitless adapter and entirely filled with a competent weld with burrs and fins removed before the installation of the pitless unit and adapter.
Pitless well units and adapters shall:
Observation wells shall be:
Sufficient electrical controls shall be placed on every pump motor to eliminate electrical problems due to phase shifts, surges, or lightning.
The use of a well house is strongly recommended, particularly in installations utilizing above ground motors.
Well pump houses shall conform to the following:
The permanent casing for any groundwater well shall project at least 12 inches above the pump house floor or concrete apron surface and at least 18 inches above the final ground surface. However, casings terminated in underground vaults may be permitted if the vault is provided with a drain-to-daylight sized to handle more than the well flow and surface runoff and is directed away from the vault access.
Where a well house is constructed, the floor surface shall be at least six inches above the final ground elevation and shall be sloped to provide drainage. A drain-to-daylight shall be provided unless highly impractical.
Sites subject to flooding shall be provided with an earth berm terminating at an elevation at least two feet above the highest known flood elevation or other suitable protection as determined by the Director.
The top of the well casing at sites subject to flooding shall terminate at least three feet above the 100-year flood level or the highest known flood elevation, whichever is higher, refer to Subsection R309-515-6(6)(b)(vi).
The well house shall be ventilated, heated, and lighted in such a manner as to assure adequate operation of the equipment.
Where necessary to protect the quality of the well water, the Director may require that certain wells be fenced in a manner similar to fencing required around spring areas.
An access shall be provided either through the well house roof or sidewalls in the event the pump must be pulled for replacement or servicing the well.
Utah Admin. Code R309-515-6