The owner or operator of a Class VI well must prepare,
maintain, and comply with a testing and monitoring plan to verify that the
geologic sequestration project is operating as permitted and is not endangering
USDWs. The requirement to maintain and implement an approved plan is directly
enforceable regardless of whether the requirement is a condition of the permit.
The testing and monitoring plan must be submitted with the permit application,
for Director approval, and must include a description of how the owner or
operator will meet the requirements of this Section, including accessing sites
for all necessary monitoring and testing during the life of the project.
Testing and monitoring associated with geologic sequestration projects must, at
a minimum, include:
1. Analysis of the
carbon dioxide stream with sufficient frequency to yield data representative of
its chemical and physical characteristics;
2. Installation and use, except during well
workovers as defined in
R18-9-J663, of continuous
recording devices to monitor injection pressure, rate, and volume; the pressure
on the annulus between the tubing and the long string casing; and the annulus
fluid volume added;
3. Corrosion
monitoring of the well materials for loss of mass, thickness, cracking,
pitting, and other signs of corrosion, which must be performed on a quarterly
basis to ensure that the well components meet the minimum standards for
material strength and performance set forth in
R18-9-J661, by:
a. Analyzing coupons of the well construction
materials placed in contact with the carbon dioxide stream; or
b. Routing the carbon dioxide stream through
a loop constructed with the material used in the well and inspecting the
materials in the loop; or
c. Using
an alternative method approved by the Director;
4. Periodic monitoring of the ground water
quality and geochemical changes above the confining zone or zones that may be a
result of carbon dioxide movement through the confining zone or zones or
additional identified zones including:
a. The
location and number of monitoring wells based on specific information about the
geologic sequestration project, including injection rate and volume, geology,
the presence of artificial penetrations, and other factors; and
b. The monitoring frequency and spatial
distribution of monitoring wells based on baseline geochemical data that has
been collected under
R18-9-J657 and on any modeling
results in the area of review evaluation required by
R18-9-J659(C).
5. A demonstration of external
mechanical integrity pursuant to
R18-9-J664(C) at
least once per year until the injection well is plugged; and, if required by
the Director, a casing inspection log pursuant to requirements under
R18-9-J664(D) at
a frequency established in the testing and monitoring plan;
6. A pressure fall-off test at least once
every five years unless more frequent testing is required by the Director based
on site-specific information;
7.
Testing and monitoring to track the extent of the carbon dioxide plume and the
presence or absence of elevated pressure (e.g., the pressure front) by using:
a. Direct methods in the injection zone or
zones; and,
b. Indirect methods
(e.g., seismic, electrical, gravity, or electromagnetic surveys and/or
down-hole carbon dioxide detection tools), unless the Director determines,
based on site-specific geology, that such methods are not
appropriate;
8. The
Director may require surface air monitoring and/or soil gas monitoring to
detect movement of carbon dioxide that could endanger a USDW.
a. Design of Class VI surface air and/or soil
gas monitoring must be based on potential risks to USDWs within the area of
review;
b. The monitoring frequency
and spatial distribution of surface air monitoring and/or soil gas monitoring
must be decided using baseline data, and the monitoring plan must describe how
the proposed monitoring will yield useful information on the area of review
delineation and/or compliance with standards under
R18-9-B608;
c. If an owner or operator demonstrates that
monitoring employed under
40 CFR §§
98.440 to
98.449 (Clean Air
Act,
42 U.S.C.
7401 et seq.) accomplishes the goals of
subsections (A)(8)(a) and (b) of this Section, and meets the requirements
pursuant to
R18-9-J666(3)(e),
a Director that requires surface air/soil gas monitoring must approve the use
of monitoring employed under
40 CFR §§
98.440 to
98.449. Compliance
with
40 CFR §§
98.440 to
98.449 pursuant to
this provision is considered a condition of the Class VI permit;
9. Any additional monitoring, as
required by the Director, necessary to support, upgrade, and improve
computational modeling of the area of review evaluation required under
R18-9-J659(C) and
to determine compliance with standards under
R18-9-B608;
10. The owner or operator shall periodically
review the testing and monitoring plan to incorporate monitoring data collected
under this Part, operational data collected under
R18-9-J663, and the most recent
area of review reevaluation performed under
R18-9-J659(E) .
In no case shall the owner or operator review the testing and monitoring plan
less often than once every five years. Based on this review, the owner or
operator shall submit an amended testing and monitoring plan or demonstrate to
the Director that no amendment to the testing and monitoring plan is needed.
Any amendments to the testing and monitoring plan must be approved by the
Director, must be incorporated into the permit, and are subject to the permit
modification requirements under
R18-9-C632 or
R18-9-C633, as appropriate.
Amended plans or demonstrations shall be submitted to the Director as follows:
a. Within one year of an area of review
reevaluation;
b. Following any
significant changes to the facility, such as addition of monitoring wells or
newly permitted injection wells within the area of review, on a schedule
determined by the Director; or
c.
When required by the Director.
11. A quality assurance and surveillance plan
for all testing and monitoring requirements.