310 CMR 30.675
Probable High Groundwater Levels
(1) For areas in Massachusetts other than Cape Cod:
(a) Sand and gravel areas. For estimating the probable high groundwater levels in sand and
gravel areas in Massachusetts except Cape Cod, the following formula shall be used
wherever practicable. Use of this formula allows for the estimation of the potential
groundwater level rise at the facility site by correlation with the potential rise in an off-site
observation well if the climatic trends and hydrogeologic conditions at the site and the well
are similar. For an in-depth discussion of the derivation of this formula and its use see:
Probable High Groundwater Levels in Massachusetts, U.S. Geological Survey, Water
Resources Investigations, Open-File Report 80-1205 by Michael H. Frimpter.
Sh =
Sc - Sr
(OWc - OWmax)
OWr
where:
Sh
= estimated depth to probable high water level at the site;
Sc
= measured depth to water at the site (ground level to water table);
OWc
= measured depth to water in the observation well which is used to correlate with
the water levels at the site (ground level to water table);
OWmax
= depth to recorded maximum water level at the observation well which is used to
correlate with the water levels at the site;
Sr
= range of water level where the site is located; and
OWr
= recorded maximum value of annual range of water level at the observation well
which is used to correlate with the water levels at the site.
In the above equation, Sc and OWc shall be measured in the same month. The observation
well which is chosen to correlate with the water levels at the facility site shall be among those
included in the report Groundwater Levels in Massachusetts, 1936-74: U.S. Geological Survey
Open-File report, Massachusetts Hydrologic-Data Report 17 by Anthony Maevsky. The
observation well shall be located in the same type of climate and hydrogeologic environment as
the facility site.
Values of OWmax and OWr shall be obtained from the chosen observation-well record.
OWmax shall be found by reviewing the historical record of measurements and finding the depth
from ground level to water table level that corresponds to the maximum water level ever
recorded at the observation well site. OWr shall be determined by finding the maximum water
level fluctuation that ever occurred during one year of recordings at the observation well (i.e.,
the "range" or the maximum difference in water table levels ever recorded during a one year
period).
The value of Sr shall be as follows:
Sand and gravel deposits on terraces and hillsides
10 feet
Sand and gravel deposits in valleys
4 feet
These values represent a range of water level at the site that is unlikely to be exceeded.
(b) Areas of till. For estimating the probable high groundwater level in areas of till, a series
of measurements shall be taken to determine the high groundwater level for a particular year,
and the following method shall be used, wherever practicable.
To estimate the maximum water level, a proportion is used. That proportion is: The
potential water-level rise at the site is to the maximum annual water-level range at the site
as the potential water-level rise at an observation well is to the maximum annual water-level
range at the observation well, where the potential rise is the difference between the highest
and current water levels. For the use of the formula below, a value of five feet was chosen
to represent the maximum annual water-level range at the site. Analysis of records of over
5000 water level measurements in 15 wells in till between 1936 and 1982 show that the mean
range of maximum annual water levels is about five feet. For an illustration of the variables
which are used in the formula, see Figure 30.675(1)(b).
Difference between current
Difference between current and
and maximum levels at site
=
maximum levels at observation well
Range of maximum annual
Range of maximum annual level at
level at site
observation well
Sc - Sm
=
OWc - OWm
5
OWr
OWc - OWm
Sm = Sc - 5 x
OWr
Steps in the method are as follows: Measure and record the water level on a weekly basis
from March 15 to May 15.
From the observation well location map select the most
representative observation well on a basis of geographic proximity. From reports of the U.S.
Geological Survey determine the water level (OWc) in that observation well for the concurrent
date, the date closest to the date at which the highest water level was measured at the site.
Determine from Table 30.675(1)(b), provided here, the maximum recorded water
level (OWm) and the range of annual maximum water level (OWr) for the same observation well.
Substitute these values of OWc, OWm and OWr, and the current maximum annual water level
measured at the site (Sc) in the formula and solve for the estimated maximum water level at the
site (Sm).
Based on the small available sample of 10 representative observation wells in till there is a
10% chance that the maximum annual range at a site would exceed the estimate by about one
foot. See the range of OWr in Table 30.675(1)(b).
TABLE 30.675(1)(b)
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Maximum Water Levels and Maimum Annual
Water-Level Ranges for Observation Wells in Till
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LOCATION
NUMBER
OWm
OWr
Andover
AJW-26
Cheshire
CJW-2
East Bridgewater
EBW-30
Great Barrington
GMW-2
Lowell
L2W-14
Middleborough
MTW-82
Northborough
NUW-38
Topsfield
TQW-1
Weymouth
XGW-2
Winchester
XOW-14
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Most, but not all, facility sites will be located in one of the hydrogeologic settings discussed
above. As an example, a surface impoundment might be located on a terrace composed largely
of silt. In such a case, the formula is not valid. The estimation of the probable high groundwater
levels shall be based upon measurements of the water level at the facility site in the months of
March, April and May and a best possible prediction of the highest water table levels that can
reasonably be expected throughout the facility's operating life (and beyond if a land disposal
facility). Soil mottling may help to verify this prediction. In rare instances, long term historical
data (15 years or more) of water levels may actually be available at the facility site. In these
cases, the probable high groundwater levels can be determined directly from this data.
(2) Probable High Groundwater Levels For Cape Cod. For estimating the probable high water
level in sand and gravel areas of Cape Cod, the following method shall be used wherever
practicable. It cannot be applied in areas where low permeability layers of silt, clay or till are
present. Some parts of Cape Cod show no pattern for annual water level range. In these
locations, soil conditions are unsuitable for water level estimation. In cases where the following
procedure is not applicable, tests for water levels shall be conducted at the site during March,
April and May and a best possible judgment made of the probable high groundwater levels
considering hydro-geologic and climatic trends.
Probable high groundwater levels at a site in Cape Cod shall be made by correlation of a
single water-level measurement from a facility test site with water level records from one of nine
index wells which have been established bythe U.S. Geological Survey. For the rationale behind
the establishment of the estimating procedure, and for an in-depth discussion of its use, see:
Probable High Groundwater Levels on Cape Cod, Massachusetts, U.S. Geological Survey,
Water-Resources Investigations, Open-File Report 80-1008 by Michael H. Frimpter. Also, in
order to estimate the probable high groundwater levels, Plate 1 and Plate 2 from that report will
need to be utilized. These plates subdivide Cape Cod into nine areas in which water level
fluctuations in each area are best represented by a particular index well.
The formula which is used to estimate the depth to the probable high water level at the site
is similar to the formula that is used for finding probable high water levels for areas in
Massachusetts other than Cape Cod:
Sh = Sc - Sr
(OWc - OWmax)
OWr
or
Estimated depth to probable =
measured depth to -
water level
high water table
water at the site
adjustment
where
Sr(OWc - OWmax)
= the water level adjustment
OWr
However, in this case Sr, the maximum value of the annual range of water level at the facility
site, will be one of five values (2, 3, 4, 5 or 6 feet), depending upon the particular geographical
zone in which the facility is situated. In areas of perched groundwater tables, a value Sr = 10 may
be used, but only with written approval of the Department.
In order to simplify the use of this formula, a series of nine tables has been developed. These
tables appear in the Report cited in 310 CMR 30.675(2). One table has been prepared for each
of the nine index observation wells. The water level adjustment value shall be found from these
tables once the geographic zone of the facility site is known and the water levels in the index
well and at a specific site have been measured.
Procedure
1. Measure, to the nearest 1/10th of a foot, the depth to the water table below land surface at
the facility site.
2. Find the location on Plate 1 or Plate 2 of the facility test site. From this Plate determine the
geographical zone in which the facility site exists (Zone A, B, C, D or E). Also determine
the index well which shall be used.
3. Determine the depth to water in the appropriate index well for the month in which the depth
to water was measured at the facility site (or previous month if current data are not yet
available; see the NOTE below). (The U.S. Geological survey reports the index-well
measurements monthly to the Regional Environmental Engineers of the Department and to
the Cape Cod Planning and Economic Development Commission.)
4. Use the appropriate table (See Sample Table 30.675(2)) and find the depth to water level
adjustment value from the Table based upon the geographical zone where the site is located
and the reported depth to water in the index well. (Refer to the U.S.G.S. report for the
complete set of tables).
5. Subtract the water-level adjustment value from the measured depth to water at the facilitysite
to obtain the estimate of depth to the probable high water level.
NOTE:
Because the locations of the boundaries between the areas represented by the index wells are
somewhat inexact, the above-cited report suggests that, when the site being evaluated is within
1,000 feet of such a boundary, estimates should be calculated from both index wells. The higher
of the two groundwater levels calculated would be less likely to be exceeded.
The water level for the month in which the site testing was done should be used in Procedure 3.
However, the water level reported for the index well for the month previous to the month in
which the site was tested may be used, provided that 0.25 feet is subtracted from the depth to the
water level for each week or fraction thereof between the date of the site test and the end of the
previous month. For example, if an estimate for a site test made on the 8th of August (8/7 =
1.14) should be adjusted by subtracting 0.3 feet from the reported July water level for the index
well. This adjustment need only be applied when the test site is measured in the months of May,
June, July, August, September, or October. The adjustment is based on the recorded maximum
water level decline of 0.99 feet over a one month period in all nine index wells and the
observation that groundwater levels on Cape Cod generally decline from May through October.
SAMPLE TABLE 30.675(2)
Water-level Adjustments, in Feet, for Use with
Index Well Barnstable A1W-230 (Located in Zone C)
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Measured water
level (OWc in
Zone A
Zone B
Zone C
Zone D
Zone E
feet below land
surface)
(2/4)1
(3/4)1
(4/4)1
(5/4)1
(6/4)1
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.0
.1
.1
.1
.1
.1
.1
.2
.2
.3
.1
.2
.3
.4
.4
.2
.3
.4
.5
.6
.2
.4
.5
.6
.7
.3
.4
.6
.7
.9
.3
.5
.7
.9
.4
.6
.8
.4
.7
.9
.5
.7
.5
.8
.6
.9
.6
.7
.7
.8
.8
.9
.9
SAMPLE TABLE 30.675(2) (continued)
Water-level Adjustments, in Feet, for Use with
Index Well Barnstable A1W-230 (Located in Zone C)
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Measured water
level (OWc in
Zone A
Zone B
Zone C
Zone D
Zone E
feet below land
surface)
(2/4)1
(3/4)1
(4/4)1
(5/4)1
(6/4)1
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1
Sr /OWr =
2
Recorded highest water level (OWmax).
(3) Alternative Methods. The Department may accept alternative methods for determining
probable high groundwater levels if such methods are demonstrated to give equally reliable
results. For the purposes of 310 CMR 30.000, alternative methods may be used only following
written approval by the Department.