(1)
Groundwater level measurements. The elevation of the water
table shall be determined at or near the location of each soil boring which
penetrates the water table. The water table may be determined using a completed
water table monitoring well, or piezometer. The bottom of a piezometer used to
measure water table elevation shall be no more than 5 feet below the water
table. The apparent horizontal groundwater flow direction shall be determined
based on water table measurements. Vertical groundwater flow shall then be
assessed in at least two profiles approximately parallel to the apparent
horizontal flow direction. Vertical groundwater flow shall be assessed using at
least two well clusters per profile. Each well cluster shall contain a water
table monitoring well or piezometer and additional water level monitoring
points based on site conditions as follows:
a.
If the water table is in the uppermost aquifer, one additional water level
monitoring point shall be located near the base of the aquifer or at least 20
feet below the base of the water table monitoring point. This additional
monitoring point may not be required if the aquifer is less than 20 feet
thick.
b. If the uppermost aquifer
is less than 50 feet below the water table, an additional water level
monitoring point shall be located at the top of the aquifer.
c. If the uppermost aquifer is more than 50
feet below the water table, additional water level monitoring points shall be
placed at depths of 30 feet and 50 feet below the water table.
d. If required, the one deeper soil boring
into bedrock shall be used as a site for one well cluster. Water table
monitoring points in this cluster shall correspond to the other well cluster
used for a profile. In addition, water level monitoring points shall be placed
at the bottom of the boring and, if possible, at the top and bottom of the
uppermost aquifer. Groundwater level measurements shall be made after the water
levels have stabilized in the monitoring point; at least 24 hours after
completion and bailing of the monitoring well, or installation of the
piezometer. The water level in existing wells shall be observed and recorded
prior to bailing. Each set of water level measurements shall be made in as
short a time frame as possible not to exceed 8 hours.
(2)
In-situ permeability
tests. In-situ permeability tests shall be conducted on each
monitoring well and piezometer in each well cluster.
a.
Pumping test. If more
than one monitoring point is located in the uppermost aquifer, a pumping test
shall be conducted at one or more upper aquifer monitoring points. A pumping
test involves pumping at a constant rate from one well while observing water
levels in other wells. The pumping rate shall be as high as possible without
dewatering the well. Water level measurements in other uppermost aquifer wells
shall be measured at frequent intervals near the start of the test and then at
progressively longer intervals (e.g., 1-minute intervals to 10 minutes,
5-minute intervals to an hour, 15-minute intervals to 2 hours, and half-hour
intervals thereafter). Continuous water level recording is preferable.
Water levels in wells not located in the uppermost aquifer
shall be recorded throughout the test at regular intervals (e.g., every half
hour). Water levels in all wells shall be measured 24 hours prior to the test
and just before the test. The test duration shall be at least 4 hours and
continue until a stabilized drawdown condition is observed. Longer tests may be
necessary if other uppermost aquifer monitoring points are slow to respond.
Water level readings shall be recorded through the recovery phase of the water
table.
b.
Bail and
slug tests. Monitoring wells and piezometers located in materials with
low permeabilities shall be tested using bail or slug tests. These tests
involve rapidly removing or adding a known volume of water to a well and then
recording water levels in the well as the well recovers to its original level.
Typically, the necessary frequency of measurements will be similar to that
required of pumping tests. In materials of very low permeability, less frequent
measurements are necessary. In materials of higher permeability, more frequent
measurements may be necessary.