SMC Martin Inc.
T ' i \
I
EVALUATION OF THE INVENTORY
AND ASSESSMENT OF CLASS V
INJECTION WELLS IN
NORTH DAKOTA
A Subsidiary of Science Management Corporation
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EVALUATION OF THE INVENTORY
AND ASSESSMENT OF CLASS V
INJECTION WELLS IN
NORTH DAKOTA
Submitted to:
Angus Campbell, Project Officer
Water Management Division 8WM-DW
U.S. EPA Region VIII
1860 Lincoln Street
Denver, CO 80295
Prepared by:
SMC MARTIN INC.
900 W. Valley Forge Road
P. 0. Box 859
Valley Forge, PA 19482
Contract No. 68-01-6288
Ref: #8425-040-94001
March 1985
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TABLE OF CONTENTS
Page
Executive Summary 1
Introduction 2
Methodology 4
Results 6
Procedures to Maintain a Current Inventory 11
Environmental Assessment 13
Summary 20
Appendix A Inventory Forms for Those Class V
Injection Wells in North Dakota which
were verified by SMC Martin
Appendix B North Dakota Administrative Code
Governing Class V Injection Wells
Appendix C State of North Dakota Well Drillers
Report Form
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TABLE OF CONTENTS
Page
Executive Summary 1
Introduction 2
Methodology 4
Results 6
Procedures to Maintain a Current Inventory 11
Environmental Assessment 13
Summary 20
Appendix Inventory Forms for All Class V Injection
Wells in North Dakota
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EXECUTIVE SUMMARY
An inventory of Class V injection wells in the State of
North Dakota by Don Richard and G. Padmanabhan of the North
Dakota State University was reviewed and evaluated in accordance
with EPA Contract #68-01-6288. One-hundred eleven Class V
injection wells were identified and located during the North
Dakota State University inventory. Of these, 94 were
ground-water heat pump return wells, 10 were abandoned wells
used for geophysical exploration, 1 was used for disposal of
sanitary wastes, 5 were soil backfill wells, and 1 was used for
cooling water disposal. SMC-Martin contacted 35 percent of the
inventory entries to verify the information on the inventory.
Class V injection wells have the potential to affect
aquifers by causing temperature fluctuations and introducing
contaminants into an aquifer. These problems can surface or be
exacerbated when the waters are being injected or returned to an
aquifer other that that from which it was withdrawn. No
problems associated with return wells have been reported in
North Dakota. Because all wells, including injection wells,
must be permitted by the State, a current inventory can most
effectively be maintained if the North Dakota State Water
Department requires that wells be categorized as "injection" or
"extraction" wells on the drilling permits.
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INTRODUCTION
According to the regulations of the Underground Injection
Control (UIC) program, an injection well is a drilled, driven,
or dug hole whose depth is greater than the largest surface
dimensions and which is used for the subsurface emplacement of
fluids. These wells are used for a variety of purposes,
including aquifer recharge, drainage, the production of oil,
gas, and minerals, and waste disposal. Misuse and/or improper
design, construction, operation, or abandonment of injection
wells may pose a significant threat to ground-water drinking
sources. The aim of the UIC program is to prevent or diminish
deterioration of the quality of potential underground sources of
drinking water.
EPA has defined Class V wells as "All other injection wells
not incorporated in Classes I through IV." Examples of Class V
wells include:
o
Air conditioning/cooling water return wells
o
Storm water drainage wells
o
Agricultural drainage wells
o
Other drainage wells
o
Recharge wells
o
Subsidence control wells
o
Waste disposal wells
Class V wells are reported to account for more than 61 percent
of the total number of injection wells in the country. These
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wells are of particular concern since they represent an unknown
problem due to their number and the current lack of information
on them. The purpose of this study was to review and evaluate
the existing inventory completed by the North Dakota State
University and to make specific suggestions on how North Dakota
can complete and update their own inventory using in-house
staff.
Under EPA Contract #68-01-6288, SMC Martin reviewed and
evaluated all the inventory work conducted to date by the North
Dakota State University (MAn Inventory and Assessment of Class V
Injection Wells in North Dakota," for the North Dakota State
Health Department, 1983).
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METHODOLOGY
To evaluate the accuracy and completeness of the inventory,
SMC Martin carefully examined the inventory and assessment
report prepared for the state of North Dakota, the methodology
used by the North Dakota State University to conduct the
inventory, and the inventory data base. A telephone survey was
conducted of a representative sample of the inventory entries,
including:
o Private residences
o Industrial and commercial sites
o Municipal and other governmental operations
o Various public facilities including schools,
churches, etc.
For each entry in the inventory, the information was
verified by contacting the party legally responsible for the
well. This information was compared to the data required by
the EPA:
1. Facility name and location.
2. Name and address of a legal contact.
3. Ownership of facility.
4. General nature, type, and number of injection wells.
5. Operational status of the injection wells.
In each case, all the information was either confirmed, updated,
or corrected and an individual inventory sheet was completed.
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Upon completion of the inventory verification phase of the
study, a representative sample of commercial and industrial
installers and dealers of heat pumps was contacted. These
included:
o All North Dakota members of the Contractor Division of
the National Water Well Association;
o Water well drillers;
o Heating contractors;
o Water treatment contractors;
o Heat pump dealers, distributors, and installers;
o Utility companies; and
o Governmental agencies on all levels (federal, state,
county, and municipal).
These sources were asked to identify known owners of heat pumps,
which were then checked against the inventory to verify that
these businesses had been contacted during the previous state
effort. All new heat pump installations that were identified
were contacted and added to the inventory.
Efforts to acquire data on non-heat pump return wells were
geared toward contacting people in various government agencies
and private industries. These industrial contacts included
mining companies, testing labs, and septic tank installers.
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RESULTS
Thirty-five percent of all the inventoried facilities were
contacted and all information was verified. It was not
necessary to contact all facilities on the inventory, as the
data was generally accurate. Small discrepancies did occur but
most manifested themselves as errors in zip codes, the inclusion
of water supply wells, and name misspellings. These
discrepancies were corrected on revised inventory forms, which
are compiled in the Appendix. The North Dakota State University
inventory provided sufficiently accurate information to contact
and identify every facility. The information collected during
the North Dakota State University inventory was found to be
generally correct, and further facility contacts were deemed
unnecessary.
To evaluate the completeness of the inventory, heating
contractors, water well drillers, pump dealers, and septic tank
installers were contacted. Only 70 percent could actually be
reached in our effort, as the remaining 30 percent were found to
no longer exist. Government agencies that were contacted
included county sanitarians, county and municipal engineers,
North Dakota Water Commission, North Dakota Health Department,
the State Geological Survey, the State Land Department, and the
U.S. Geological Survey. All of the government agencies and
businesses were asked to what extent heat pumps are used and to
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estimate, in their opinions, the number of heat pump return
wells in North Dakota. Almost all of the people contacted
estimated that approximately 100 ground-water heat pump recharge
wells exist in the entire state, with one estimate placing the
number as high as 500. North Dakota State University
inventoried 94 ground-water heat pump recharge wells.
Therefore, based on the information provided by the telephone
survey of the various establishments and residences, it is
concluded that the inventory of Class VA wells for the State of
North Dakota is fairly accurate and complete. The number of
heat pump wells estimated by the heat pump dealers, water well
drillers, etc., would indicate that the State of North Dakota
was thoroughly inventoried for such wells.
In addition to the ground-water heat pump recharge wells,
North Dakota State University inventoried 17 other Class V
wells, including:
o 10 geophysical exploration wells abandoned after
plugging;
o 1 cesspool;
o 1 community mound (septic waste disposal); and
o 5 sand backfill facilities (subsidence control).
In order to determine the completeness of the inventory
regarding these other Class V injection wells the State Health
Department, State Public Service Commission, and the Office of
Surface Mines of the Federal Department of the Interior were
contacted. Seven of the wells were verified and inventoried.
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The ten geophysical exploration wells were not located during
the initial inventory and were not traceable through contacts
with various governmental agencies and commercial
establishments. As a result, the exact nature or duration of
the wells remains indeterminate, though an extensive record
search of well logs in the State files may disclose the purpose
and ownership of the wells.
SMC Martin surveyed potential installers of other types of
injection wells to evaluate the completeness of the inventory.
Mining companies and testing labs indicated that their firms
were not involved with any type of injection wells.
Conversations with numerous septic tank installers disclosed
that the majority of the soils in North Dakota are so highly
permeable that only low volume (single residence) systems can be
used without risking contamination of the water supply.
Information gathered through conversations with people at
the North Dakota Public Service Commission verified that five
backfill projects had been completed and that two additional
projects were proposed for the summer of 1985. The pertinent
information concerning the completed and proposed projects are
listed in Table 1.
Aside from the 17 wells inventoried during the University
survey, no additional non-ground-water heat pump return wells
were located. None of the agencies, businesses, or industries
contacted during this study indicated that any injection wells
were proposed in the near future.
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TABLE 1
SUMMARY OF CLASS V SUBSIDENCE CONTROL
INJECTION WELLS
Completed Projects
North Dakota Public Service Commission
Beulah, ND
Completed: November, 1983
Backfill: 80% sand, 12% fly ash
Volume: 41,150 tons
No.of Wells: 150
Beulah, ND
Completed: November, 1983
Backfill: 80% sand, 12% fly ash
Volume: 10,000 tons
No.of Wells: 75-100
Office Surface Mines
Beulah, ND
Completed: September, 1983
Backfill: Grout and fly ash
Volume: 4,000 tons
No.of Wells: 60
Beulah, ND
Completed: October, 1983
Backfill: Grout and fly ash
Volume: 1,100 tons
No.of Wells: 50
Beulah, ND
Completed: August, 1983
Backfill: 88% sand, 12% fly ash
Volume: 45,000 tons
No.of Wells: 200-250
Proposed Projects
Office of Surface Mines
Beulah, ND
Proposed Completion: summer, 1985
Volume: 50,000 tons
Beulah, ND
Proposed Completion: Summer, 1985
Volume: >50,000 tons
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Similar results were reported by the North Dakota State
University survey. Therefore, the University's inventory
concentrated on groundwater heat pump return wells, as these
facilities appear to be the most prominent type of injection
well in the state.
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PROCEDURES TO MAINTAIN A CURRENT INVENTORY
The inventory of ground-water heat pump return wells
conducted in 1983 by the North Dakota state University is both
thorough and accurate. However, in order to establish a
complete inventory of all Class V injection wells in the entire
State, the other types of Class V wells must also be inventoried
thoroughly. Therefore, additional efforts may be necessary to
achieve a complete inventory of all the Class V injection well
types.
Under Chapter 33-25-01-16 of the North Dakota Administrative
Code, every individual owner (whether residential, commercial,
or industrial) is required to register their injection well with
the State Department of Health. A copy of these regulations is
presented in Appendix B. This rule sets up the ground work
under which the state Class V injection well inventory can be
maintained and updated by the Division of Water Supply and
Pollution of the State Health Department. However, the
compliance of the general public with this regulation is
minimal, as few people are aware of this requirement. Thus,
unless the public is educated about the existence and importance
of UIC Rule #25-01-16 in Chapter 33 of the North Dakota
Administrative Code, the effectiveness of this regulation is
greatly compromised.
It appears that an alternative regulation may in fact be
applicable for inventorying heat pump recharge wells with
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greater effectiveness. Under Chapter 33, Rule 18-01 (Water Well
Construction and Pump Installation), of the North Dakota
Administrative Code, all water well drillers must submit a log
of the wells that have been completed. A copy of a well
driller's report is presented in Appendix C. It is through this
rule that most of the Class V injection wells have been
inventoried. This requirement applies to all wells and is not
limited to ground-water heat pump return wells.
To date, these methods have proved effective as an
additional 52 ground-water heat pump return wells have been
inventoried by the State Health Department. The results of the
updated inventory indicate that 146 ground-water heat pump
return wells exist at 131 facilities in the state.
Cesspools and septic tank discharge wells are inventoried by
the State Water Department. Installation of all septic tanks
must be approved by the Water Department. Therefore, all septic
systems qualifying as Class V injection wells are registered
with the State and thus can be inventoried.
Similar permitting and registration requirements can be
imposed upon various other industries (mining companies,
chemical plants, municipalities, etc.) so as to maintain an
updated inventory of all Class V injection wells.
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ENVIRONMENTAL ASSESSMENT
Ground-water Heat Pumps
In general, a ground-water heat pump operates on the same
principles as a refrigerator. Figure 1 is a schematic diagram
of a typical ground-water heat pump. The unit transfers heat
from the ground water to the atmosphere in the heating cycle and
vice versa during the cooling cycle. The transfer of heat takes
place through a refrigerant, generally freon.
The ground water, after exchanging heat with refrigerant, is
injected or returned back into an aquifer. In the subsurface
injection method of disposal, there are several types of
injection systems. One method has separate supply and return
wells (Figure 2). Another method is the twin-purpose well
method (Figure 3). These two methods are the most prevalent
systems employed by owners of heat pumps in North Dakota. The
impact of ground-water heat pump injection wells is discussed in
the following paragraphs.
No pollution or operation problems were reported at any of
the facilities contacted during the inventory verification
process. However, since ground-water heat pumps are becoming
more popular, problems may develop in the future. Recent
legislation which allows tax credits for heat pump installations
has greatly increased the use of such heat pumps in North
Dakota, and these activities must be monitored carefully.
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sin>PLT AIR
WATI'R
IN
Figure 1. Schematic diagram to a ground-water heat pump.
Source: An Inventory and Assessment of Class V Injection
Wells in North Dakota for North Dakota State
Health Department (1983).
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Figure 2. Separate supply and injection well system.
Source: An Inventory and Assessment of Class V Injection
Wells in North Dakota for North Dakota State
Health Department (1983).
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Figure 3. Diagram of a twin-well system.
Source: An Inventory and Assessment of Class V Injection
Wells in North Dakota for North Dakota State
Health Department (1983).
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Several potential problems that may develop as a result of
increasing usage of ground-water heat pumps are:
o Temperature fluctuations
o Mixing of waters from different aquifers
o Entry of freon, additives, or other contaminants into
ground water.
These are discussed briefly below.
Temperature Fluctuations
The effluent from ground-water heat pumps is warmer in
summer and cooler in winter than the normal average temperature
of the ground water. Though the impact of temperature changes
in the aquifer are difficult to estimate, possible complications
may arise. Temperature fluctuations may alter the rates of
chemical reactions, resulting in undesirable precipitation or
corrosion problems. Temperature increases may also increase
biological activity in the affected area. These effects may
lead to plugging of wells, corrosion or precipitation in
plumbing, and other problems that could render the wells (source
and/or recharge) useless.
To date, no instances of well contamination due to
temperature changes were found either by the North Dakota State
University or by SMC Martin.
The utilization of ground-water heat pumps is relatively new
£ind the long-term effects of ground-water temperature changes
have not been studied in detail. However, the results reported
in other studies conducted on the environmental impact of
17
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ground-water heat pumps ("Ground-Water Heat Pumps in the
Tidewater Area of Southeastern Virginia," SMC Martin, 1983)
indicate that the injection of warm or cold water rarely has a
significant effect on the temperature of the supply well.
Mixing of Water from Different Aquifers
The effect of mixing of waters from different aquifers has
not been studied in detail. However, as suggested in the North
Dakota State University inventory report, possible problems may
arise, including precipitation of iron oxide if the appropriate
chemical conditions exist. The likelihood of iron oxide
precipitation is increased if the ground water contains
significant concentrations of iron, if air is able to leak into
the system, or if waters from two different aquifers are mixed.
Chemical Contamination
Freon 22 is the most widely used refrigerant in heat pumps.
It is a clear, colorless, highly volatile gas that, when exposed
to the atmosphere, evaporates as an inert gas. Compressor
cooling oil, which may circulate with freon, is generally a high
grade mineral oil. Freon 22 and mineral oil are of low toxicity
and are generally regarded as safe materials.
Importation of chemicals into the aquifer may occur if
chemical additives are used to clean or purge the source or
return well of iron oxide, algae, or to inhibit corrosion.
Processes involving the introduction of chemicals into the
eiquifer, however, do not require sufficient quantities to
significantly alter the ground-water chemistry. None of the
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owners of ground-water heat pumps contacted by SMC Martin
reported having to treat their wells.
Subsidence Control Wells
Mine backfill operations present special problems where
ground water migrates through the backfilled mine voids and
leaches high concentrations of chemical species such as heavy
metals and sulfuric acid from the backfill material itself.
Because stopes or other large mined out areas are typically
backfilled, a large volume of material may be deposited, adding
to the potential for adverse environmental impact.
Generally, subsidence control wells are used to backfill
mine areas underlying roads and construction areas in North
Dakota. The method usually employed includes the installation
of bulkheads at the outer perimeter of the area to be
backfilled. After the installation of the bulkheads, numerous
wells, or holes, are drilled in order to facilitate the
emplacement of the backfill.
Though no instances of ground-water contamination have been
reported as a result of backfilling, the potential threat still
exists. The practice in North Dakota formerly was to mix sand
and fly ash together for backfilling. However, the North Dakota
State Health Department conducted leachate analyses on the fly
ash and discovered that the fly ash contained high amounts of
arsenic and salts (particularly sodium sulfate). As a result of
this study, the practice of adding fly ash to the backfill
material has recently been discontinued in North Dakota.
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SUMMARY
Close examination of the Class V injection well inventory
for the State of North Dakota indicates that the inventory is
accurate and complete. Though minor discrepancies did occur
(missing zip codes, name misspellings, etc.), these were easily
remedied; it was possible to contact all facilities from the
data on the inventory. Contacts with representatives of the
various industries potentially involved with injection wells
indicated that the total number of wells listed on the North
Dakota State University inventory closely approximates the
numbers estimated by these sources.
The methodology employed by the North Dakota State
University proved to be both adequate and comprehensive. This
method of telephone surveys and follow-up letters matched the
challenge at hand with sufficiently good results.
Several methods can be used to maintain an updated
inventory. Regulatory controls (mostly through permitting) seem
to be an efficient means of inventorying the ground-water heat
pump return wells, considering their relative scarcity. It is
possible that with increased popularity of heat pumps, further
regulatory steps may have to be taken in the future.
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APPENDIX A
INVENTORY FORMS FOR THOSE CLASS V INJECTION WELLS
IN NORTH DAKOTA WHICH WERE VERIFIED
BY SMC MARTIN
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U.S. |NVIH0NM(NTH PftOTCCTIOM AGCMCV
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INVENTORY OF INJECTION WELLS
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At least 100 to 150 wells were used to inject
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-------
APPENDIX B
NORTH DAKOTA ADMINISTRATIVE CODE GOVERNING
CLASS V INJECTION WELLS
-------
33-25-01-16. Authorization of Class V underground injection
wells.
1. Authorization of injection into a Class V well is authorized
indefinitely, subject to the requirements of subsections 4, 5,
and 6 of section 33-25-D]-]0 and subsection 3 of section
33-25-03-12.
2. The owner or operator of any existing Class V well shall,
within one year of the effective (Sate of an underground
injection control program, notify the director of the
existence of any well meeting the definitions of Class V uncer
the owner's or operator's control, and submit the following
inventory information:
a. Name of owner or operator of the well and legal contact;
b. Number of wells and location by township, range and
section;
C. Nature and volume of injected fluids;
d. Construction features of the well, including well depth,
screened interval, and casing size and type, and
e. Any other information which the director requests.
3. All new Class V wells shall be in compliance with
article 43-35 and subrr.it to the director a log of format i ens
penetrated and the inventory information requested in
subsection 2.
4. a. The director may require the operator of a Class V well
authorized by rule to apply for and obtain an Individual
or area permit. Cases where permits may be required
Include;
(1) The Injection well 1s not 1n compliance with the
applicable rule.
(2) The injection well 1s riot or no longer 1s within the
category of wells and types of well operations
authorized by rule.
(3) Protection of an underground source of drinking water
requires the Injection operation be regulated by
requirements not contained 1n the rules.
b. Any owner/operator authorized by rule may request and be
granted a permit and hence be excluded from coverage by
rul e.
c. All Injection wells regulated by rule shall submit
inventory information to the director.
d. Upon program approval, the director shall notify
owner/operators of injection wells of their duty to submit
inventory information.
e. Failure to submit required inventory information for
Class V well within one year of program approval will
result in authorization removal for that well.
-------
APPENDIX C
STATE OF NORTH DAKOTA WELL DRILLERS
REPORT FORM
-------
•TATE OF NORTH DAKOTA
BOARD OF WATER WELL CONTRACTORS
BOO E BOULEVARD • BISMARCK NORTH DAKOTA SBSOI
WELL DRILLERS REPORT
State law requires that this report be filed with the State Board of Water Well
Contractors within 30 days after completion or abandonment of the well.
1. WELL OWNER
Name
Address,
2. WELL LOCATION
Sketch map location must agree with written location.
HOKTH
County_
Vi_
1 —
1
1
1
1
1
i
1
1
I
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1 Mile
-V4_
_V« Sec._
Twp N. Rg._
_W.
3. PROPOSED USE
~ Domestic
~ Stock
~ Geothermal
~ Irrigation
~ Municipal
~ Industrial
~ Test Hole
4. METHOD DRILLED
~ Cable ~ Reverse Rotary ~ Bored
~ Forward Rotary ~ Jetted ~ Other
If other, specify
5. WATER OUALITY
Was a water sample collected for chemical analysis?
~ Yes ~ No
If so, to what laboratory was it sent
7. WATER LEVEL
Static water level.
If flowing- closed-in pressure
GPM flow through
Controlled by: ~ Valve
If other, specify
feet below land surface
—psi
inch pipe
~ Reducers ~ Other
I. WELL TEST OATA
~ Pump ~ Bailer ~ Other
Pumping level below land surface:
ft after hrs. pumping-
_ft after.
_ft. after-
Jirs. pumping-
_hrs. pumping-
_gpm
_gpm
_gpm
«. WELL LOG
Formation
Depth (ft.T"
From
To
6. WELL CONSTRUCTION
Diameter of hole
Casing. ~ Steel
~ Threaded
If other, specify
Pipe Weight: Diameter:
lb/ft. Inches
lb/ft. inches
lb/ft. inches
lb/ft. inches
Was perforated pipe used?
Length of pipe perforated
Was casing left open end?
Was a well screened installed?
Materia I
—inches. Depth-
~ Plastic
~ Welded
feet.
~ Concrete
~ Other
From:
To:
.feet
_feet
_feet
_feet
~ Yes
-feet
-feet
_feet
-feet
~ Yes
~ Yes
Diameter
~ No
feet
~ No
~ No
inches
(Use separate sheet if necessary.)
10. DATE COMPLETED.
(stainless steel, bronze, etc.)
Slot size set from feet to feet
Slot size set from feet to feet
Slot size set from feet to feet
Slot size set from feet to feet
11. WAS WELL PLUGGED OR ABANDONED?
~ Yes ~ No
If so, how
12. REMARKS:
Was a packer or seal used?
If so, what material
Type of well: Straight screen n
Was the well grouted?
To what depth?
L) Yes LI No
Gravel picked ~
Yes ~ No ~
—feet
1L DRILLER'S CERTIFICATION
This well was drilled under my jurisdiction and this report is
true to the best of my knowledge.
Material used in grouting
Well head completion: Pitless adapter.
12" above grade Other
Driller's or Firm's Name
Certificate No.
If other, specify
Was well disinfected upon completion? ~ Yes ~ No
Address
Signed by
Date
WHITE—OftlLLCR** COPV
VELLOW-eOARO'S COPY
CUSTOMER'S COPY
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