[Code of Federal Regulations]
[Title 40, Volume 19]
[Revised as of July 1, 2002]
From the U.S. Government Printing Office via GPO Access
[CITE: 40CFR146.68]

[Page 720-721]
 
                   TITLE 40--PROTECTION OF ENVIRONMENT
 
         CHAPTER I--ENVIRONMENTAL PROTECTION AGENCY (CONTINUED)
 
PART 146--UNDERGROUND INJECTION CONTROL PROGRAM: CRITERIA AND STANDARDS--Table of Contents
 
Subpart G--Criteria and Standards Applicable to Class I Hazardous Waste 
                             Injection Wells
 
Sec. 146.68  Testing and monitoring requirements.

    Testing and monitoring requirements shall at a minimum include:
    (a) Monitoring of the injected wastes. (1) The owner or operator 
shall develop and follow an approved written waste analysis plan that 
describes the procedures to be carried out to obtain a detailed chemical 
and physical analysis of a representative sample of the waste, including 
the quality assurance procedures used. At a minimum, the plan shall 
specify:
    (i) The paramenters for which the waste will be analyzed and the 
rationale for the selection of these parameters;
    (ii) The test methods that will be used to test for these 
parameters; and
    (iii) The sampling method that will be used to obtain a 
representative sample of the waste to be analyzed.
    (2) The owner or operator shall repeat the analysis of the injected 
wastes as described in the waste analysis plan at frequencies specified 
in the waste analysis plan and when process or operating changes occur 
that may significantly alter the characteristics of the waste stream.
    (3) The owner or operator shall conduct continuous or periodic 
monitoring of selected parameters as required by the Director.
    (4) The owner or operator shall assure that the plan remains 
accurate and the analyses remain representative.
    (b) Hydrogeologic compatibility determination. The owner or operator 
shall submit information demonstrating to the satisfaction of the 
Director that the waste stream and its anticipated reaction products 
will not alter the permeability, thickness or other relevant 
characteristics of the confining or injection zones such that they would 
no longer meet the requirements specified in Sec. 146.62.
    (c) Compatibility of well materials. (1) The owner or operator shall 
demonstrate that the waste stream will be compatible with the well 
materials with which the waste is expected to come into contact, and 
submit to the Director a description of the methodology used to make 
that determination. Compatibility for purposes of this requirement is 
established if contact with injected fluids will not cause the well 
materials to fail to satisfy any design requirement imposed under 
Sec. 146.65(b).
    (2) The Director shall require continuous corrosion monitoring of 
the construction materials used in the well for wells injecting 
corrosive waste, and may require such monitoring for other waste, by:
    (i) Placing coupons of the well construction materials in contact 
with the waste stream; or

[[Page 721]]

    (ii) Routing the waste stream through a loop constructed with the 
material used in the well; or
    (iii) Using an alternative method approved by the Director.
    (3) If a corrosion monitoring program is required:
    (i) The test shall use materials identical to those used in the 
construction of the well, and such materials must be continuously 
exposed to the operating pressures and temperatures (measured at the 
well head) and flow rates of the injection operation; and
    (ii) The owner or operator shall monitor the materials for loss of 
mass, thickness, cracking, pitting and other signs of corrosion on a 
quarterly basis to ensure that the well components meet the minimum 
standards for material strength and performance set forth in 
Sec. 146.65(b).
    (d) Periodic mechanical integrity testing. In fulfilling the 
requirements of Sec. 146.8, the owner or operator of a Class I hazardous 
waste injection well shall conduct the mechanical integrity testing as 
follows:
    (1) The long string casing, injection tube, and annular seal shall 
be tested by means of an approved pressure test with a liquid or gas 
annually and whenever there has been a well workover;
    (2) The bottom-hole cement shall be tested by means of an approved 
radioactive tracer survey annually;
    (3) An approved temperature, noise, or other approved log shall be 
run at least once every five years to test for movement of fluid along 
the borehole. The Director may require such tests whenever the well is 
worked over;
    (4) Casing inspection logs shall be run whenever the owner or 
operator conducts a workover in which the injection string is pulled, 
unless the Director waives this requirement due to well construction or 
other factors which limit the test's reliability, or based upon the 
satisfactory results of a casing inspection log run within the previous 
five years. The Director may require that a casing inspection log be run 
every five years, if he has reason to believe that the integrity of the 
long string casing of the well may be adversely affected by naturally-
occurring or man-made events;
    (5) Any other test approved by the Director in accordance with the 
procedures in Sec. 146.8(d) may also be used.
    (e) Ambient monitoring. (1) Based on a site-specific assessment of 
the potential for fluid movement from the well or injection zone, and on 
the potential value of monitoring wells to detect such movement, the 
Director shall require the owner or operator to develop a monitoring 
program. At a minimum, the Director shall require monitoring of the 
pressure buildup in the injection zone annually, including at a minimum, 
a shut down of the well for a time sufficient to conduct a valid 
observation of the pressure fall-off curve.
    (2) When prescribing a monitoring system the Director may also 
require:
    (i) Continuous monitoring for pressure changes in the first aquifer 
overlying the confining zone. When such a well is installed, the owner 
or operator shall, on a quarterly basis, sample the aquifer and analyze 
for constituents specified by the Director;
    (ii) The use of indirect, geophysical techniques to determine the 
position of the waste front, the water quality in a formation designated 
by the Director, or to provide other site specific data;
    (iii) Periodic monitoring of the ground water quality in the first 
aquifer overlying the injection zone;
    (iv) Periodic monitoring of the ground water quality in the 
lowermost USDW; and
    (v) Any additional monitoring necessary to determine whether fluids 
are moving into or between USDWs.
    (f) The Director may require seismicity monitoring when he has 
reason to believe that the injection activity may have the capacity to 
cause seismic disturbances.

[53 FR 28148, July 26, 1988, as amended at 57 FR 46294, Oct. 7, 1992]