The rate and duration of the aquifer test will depend upon the size of the proposed subdivision and expected average and peak daily demands for all wells. The aquifer test shall be conducted at a location most representative of site geologic conditions. For residential subdivisions, biasing of testing toward areas of increased fracture density may result in the Township requiring additional testing in areas of lower fracture density to ensure that adequate yield is available throughout the proposed subdivision.
If the proposed site is underlain by two or more geologic zones (Precambrian Metamorphic & Igneous Zone, Cambrian-Ordovician Limestone/Dolomite Zone, or Jurassic-Triassic Conglomerate Zone as defined in the "Evaluation of Groundwater Resources of Union Township, Hunterdon County, New Jersey"), then an aquifer test will be required for each zone. The test requirements for each zone will depend on the number of lots and size of units per zone.
In the event that the preliminary hydrogeologic evaluation indicates that a surface-water and/or groundwater divide separates the subdivision, an aquifer test will be required for each side of the divide.
The average daily, peak day, and average yearly water demand for the subdivision must be determined according to the guidelines in N.J.A.C. 7:10-12.7. The peak day demand is twice the average daily demand.
To ensure that the pumping test adequately stresses the aquifer, the length of the pumping test will be equal to the greater of the following: 1) the volume of water removed from the aquifer is equal to the number of dwelling units multiplied by the peak day demand (e.g. 10 dwelling units times a peak day demand of 450 gallons equals 4,500 gallons); or b) four hours. At a minimum, the pumping rate for the test should be equivalent to 120% of the expected long-term rate (e.g. if the expected rate for a dwelling is five gallons per minute, then the minimum rate for the test is six gallons per minute).
For nonresidential use, demand should be determined based on N.J.A.C. 7:10-12.6. If the demand exceeds 100,000 gallons per day, a New Jersey Water Allocation Permit must be obtained from the New Jersey Department of Environmental Protection. For demands less than 100,000 gallons per day, the length of the pumping test will equal the greater of the following: a) the volume of water removed from the aquifer is equal to the peak demand; or b) four hours. The peak demand should be assumed to equal twice the average daily demand. At a minimum, the pumping rate for the test should equal 120% of the expected long-term rate.
For mixed developments containing both residential and nonresidential properties, the residential portion will be tested as described above for residential developments. Each proposed well for the commercial portions will be tested as described in §
30-6.8e3(a) for nonresidential use. In addition, wells installed for the residential portion should be used as observation wells for the nonresidential testing and wells installed for nonresidential use should be used as observation wells for the residential testing.
The number of observation wells required per aquifer test will depend on the number of dwelling units and/or commercial units for the subdivision. New and existing monitoring wells may be located such that they can be used as future water-supply wells but they shall be located in such a manner that will yield the most accurate information concerning the aquifer. Observation wells should be located parallel and perpendicular to strike of the primary fractures intersected by the tested well.
All wells must be located in accordance with the minimum distances required by N.J.A.C. 7:10-12.12. For nonresidential developments with an expected average daily demand less than 2,000 gallons per day, one observation well is required. This well should be within 500 feet of the pumping well. For all other nonresidential developments, two or more observation wells are required. At a minimum, one of these observation wells must be within 200 feet of the pumping well. A second observation well must be within 200 feet and 500 feet of the pumping well. These two wells should be located along strike of the major water-bearing fractures intersected by the well. If additional observation wells are necessary, these wells should be located parallel to secondary and tertiary fracture sets.
Major subdivisions of five lots or less to be used for single-family dwelling purposes shall conduct a pumping test on each well as outlined in §
30-6.8e2. All the wells in a major subdivision of five lots or less shall be installed and used as observation wells as each individual well test is conducted. For major subdivisions of six or more lots to be used for single-family homes, the recommended number of observation wells shall be as shown in Table 1.
Table 1: Number of Observation Wells Required for Residential Subdivisions |
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No. of Proposed Lots | No. of Observation Wells |
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5 or less | 1 adjacent well |
6 to 25 | (minimum of 2 new wells within proposed subdivision) |
25 to 49 | (minimum of 4 new wells within proposed subdivision) |
50 or more | Test proposal submitted to Board and NJDEP for review and approval |
The observation wells and test well must have a geologic log describing the depth and types of soils and rocks encountered and the depth and approximate yields of water-bearing fracture zones. The observation wells should be completed to a similar depth as the test well. At least one of the observation wells shall be within 200 feet of the test well and at least one observation well must be located along the preferential fracture direction between 200 feet and 500 feet of the pumping well. Additional observation wells should be located to evaluate potential secondary fractures and impacts to adjacent properties. |
The design of the aquifer test shall be developed using the applicable guidance from "Guidelines for Preparing Hydrogeologic Reports for Water Allocation Permit Application with an Appendix on Aquifer - Test analysis Procedures" NJGS GSR 29, 1992. The aquifer test shall be conducted according to the following procedures: |
(1) Owners of existing wells on lots located within 500 feet of the subdivision boundary shall be given an opportunity to have their wells monitored during the aquifer test. Such opportunity shall be given by the applicant by notice via certified mail and shall give the time and place of the well pumping test. Furthermore, the notice shall indicate that such existing well may be monitored if agreed to by the well owner provided the well is readily accessible. Such notice shall indicate that the existing well owner must respond within seven days and the applicant's responsibility is to monitor up to three wells on properties within 500 feet of the subdivision boundaries. If the owner of the lot within 500 feet of the subdivision boundaries decides to participate by agreeing to have their existing well monitored, they shall notify the applicant by certified mail. Such response shall be provided within seven days of receipt of the certified notice from the applicant. If the applicant receives no response within the time provided, the response shall be deemed to be negative.
(2) If the owner of a lot within 500 feet of the subdivision boundaries is to have his existing well monitored, such lot owner shall, if requested by the applicant, the applicant's hydrogeologist, and/or well driller, provide in writing a hold harmless agreement to applicant, the applicant's hydrogeologist, and/or well driller. All reasonable efforts shall be made to protect the potability of water from the monitored well.
(3) In the case when more than three property owners within 500 feet of the subdivision boundaries decide to participate to have their existing wells monitored, only the three nearest the test well need be monitored.
(4) Prior to conducting an aquifer test, the applicant shall submit the design of such aquifer test including the location of wells to be monitored on adjacent lots and qualifications of the persons and firm who will be performing the test for review by the Township. The applicant shall submit the application fees and escrow deposits in accord with §
30-11.5d, along with the proposed design of the aquifer test. The purpose of the escrow deposit is to cover the cost of Township review of the proposed aquifer test. Such review may include submission of such design to a qualified hydrogeologist representing the Township for review and recommendation.
(5) The pumping test will be comprised of three phases. The first phase will involve the collection of background water levels prior to the start of the test. The second phase will involve the pumping of water from the well and the monitoring of water-level drawdown in the observation and pumping wells. The third phase will involve the recovery of water levels in the observation and pumping well after the pump has been shutdown. This third phase of the test should be the same length as the pumping phase.
(6) If at all possible, the pumping test (all three phases) should not be conducted during precipitation events.
(7) The background phase includes allowing the test well and observation wells to stabilize for a minimum of three days before the test. Water levels shall be collected from the test well and observation well 24 hours before the test. Barometer measurements and additional water-level measurements can be made by the applicant to evaluate the change in water levels resulting from barometric pressure changes.
(8) On the day of the test, water levels shall be collected from all wells. For those wells showing a change of more than 0.1 foot, a second round of measurements shall be collected before starting the test. Additional rounds of measurements may be necessary to determine that the well is in equilibrium. However, if the applicant has barometric pressure and water-level data to indicate that the change in static levels is due to changes in barometric pressure, the applicant can submit these data in lieu of delaying the pumping test.
(9) The pump and discharge pipe shall be equipped with a flow meter and the discharge shall be directed so that it leaves the site without infiltrating to the aquifer. Any and all permits required by the NJDEP for the discharge of water must be obtained prior to starting the test.
(10) When the pump is started the flow rate shall be adjusted immediately to a uniform pumping rate as required for a constant rate test so that the flow rate varies less than 10% throughout the test. If the flow rate fluctuates more than 10%, the test may be deemed invalid and the applicant required to repeat the notification and testing process. At a minimum, the flow rate for the test should be equal to 120% of the flow rate required to satisfy the average daily demand.
(11) Water-level measurements during the pumping phase of the test shall be collected in accordance with Table 2. This same schedule shall be followed for the recovery phase of testing upon shut down of the pump in the test well.
Table 2: Frequency of Water-Level Measurements in Wells During and After Aquifer Testing |
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Time Since Pumping Began or Stopped | Test Well | Observation Wells |
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0 to 5 minutes | 0.5 minutes | 0.5 minutes |
5 to 10 minutes | 1 minute | 1 minute |
10 to 30 minutes | 2 minutes | 2 minutes |
30 to 60 minutes | 5 minutes | 5 minutes |
60 to 120 minutes | 10 minutes | 10 minutes |
2 to 8 hours | 30 minutes | 30 minutes |
8 to 24 hours | 60 minutes | 60 minutes |
24 or more hours | 120 minutes | 120 minutes |
(12) If the water levels in the observation wells and test well do not fully recover to static (pre-pumping) levels within a length of time since pumping stopped equal to the length of pumping, the test will be deemed to have failed unless adequate data can be provided to ensure the aquifer is of sufficient extent to prevent the mining of groundwater.
(13) Groundwater samples should be collected during the pumping test from the pumping well. The samples should be collected in accordance with the NJDEP Field Procedures Manual. At a minimum, the samples should be analyzed by a NJDEP certified laboratory for pH (field determined), hardness, iron, manganese, nitrate, chloride, and coliform bacteria. If site conditions indicate potential historic uses of pollutants such as, heavy metals, pesticides, herbicides, volatile organic compounds, and/or semivolatile organic compounds, these analyses should be conducted. The results of the water sample analyses will be used to assess background water quality.
(14) The Township may choose to have a person of its choosing monitor the aquifer test.