West Bay Exploration Co. (Board decision, September 22, 2014)
In re West Bay Exploration Co. (EAB UIC Appeal No. 14-66): permit review denied
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Plain-English summary
Peter Bormuth challenged EPA Region 5’s permit allowing West Bay Exploration Company to construct and operate an injection well for brine wastewater from oil and gas operations in Jackson County, Michigan. He argued that the well could threaten underground drinking water supplies and endangered species. The Board deferred to the Region’s technical findings, which were supported by the administrative record, and concluded that the permit would not endanger the Marshall Sandstone aquifer or affect the identified species. The Board denied the petition for review.
Decision snapshot
- Cited authorities: 42 U.S.C. §§ 300h-300h-8, 1536(a)(2); 40 C.F.R. §§ 144.12(a), 124.19(a)(1), 124.19(a)(4)(i)(A); 50 C.F.R. §§ 402.02, 402.14(a)
- Outcome: The petition for review was denied.
- Key point: A permit challenger bears a heavy burden to show clear error in the Region’s technical findings.
Full text (EPA EAB public release)
BEFORE THE ENVIRONMENTAL APPEALS BO~A~"----------,
UNITED STATES ENVIRONMENTAL PROTECTION fENCl
WASHINGTON, DC
SEP 2 2 2014
)
In re: )
)
West Bay Exploration Co. ) UIC Appeal No. 14-66
)
UIC Permit No. MI-075-2D-0010 )
)
____)
ORDER DENYING REVIEW
I. STATEMENT OF THE CASE
Mr. Peter Bormuth petitions for review of U.S. Environmental Protection Agency
("EPA") Region 5 ("Region")' s decision to grant an Underground Injection Control ("UIC")
permit ("Permit") to West Bay Exploration Company ("West Bay") under Part C of the Safe
Drinking Water Act ("SDWA"), 42 U.S.C. §§ 300h- 300h-8. The Permit allows West Bay to
construct and operate an injection well for the noncommercial disposal of brine waste water from
oil and gas operations. UIC Permit No. MI-075-2D-0010 ("Permit"), at 1 (Apr. 9, 2014)
(Administrative Record ("A.R.") Index No. 171). The well is designated as Haystead #9 SWD
("Haystead") and will be located in Jackson County, Michigan, near the town of Brooklyn. Id.
Mr. Bormuth claims that the injection well will threaten underground drinking water supplies and
harm two endangered species. However, he has failed to demonstrate that the Region's decision
to grant the permit was based on a clearly erroneous finding of fact or conclusion oflaw.
Accordingly, the Environmental Appeals Board ("Board") denies the petition for review.
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II. STATUTORY AND REGULATORY HISTORY
The UIC permit program was established pursuant to SDWA section 1421, 42 U.S.C.
§ 300h, and regulations promulgated by EPA at 40 C.F.R. parts 144 through 148, to protect
underground sources of drinking water. Under this program, a permit for a proposed injection
well may not be granted ifthe well would "allow[] the movement of fluid containing any
contaminant into underground sources of drinking water," and "the presence of that contaminant
may cause a violation of any primary drinking water regulation under 40 C.F .R. part 142 or may
otherwise adversely affect health of persons." 40 C.F.R. § 144.12(a).
III. FACTUAL HISTORY
The Haystead well will be located in a rural part of Jackson County, Michigan. The
actual well placement is in an agricultural field approximately 90 feet from an oil production
well. U.S. EPA Region 5, Response to Public Comments ("RTC") at 50 (Apr. 9, 2014)
(A.R. 68); West Bay, UIC Permit Application ("Permit Appl.") at 1, app. 4, fig.3 (April27,
2011) (A.R. 1). Under the Permit, West Bay may use this well only to inject brine into the
Niagaran Group, a collection of rock formations which, at the location of the Haystead well, are
present at the depth of2,870 to 3,100 feet below ground surface. Permit at 1. The deepest
underground source of drinking water at this location is the Marshall Sandstone aquifer. U.S.
EPA Region 5, Statement of Basis for Issuance ofUIC Permit ("Stmt. Basis") at 1 (March 27,
2013) (A.R. 26). Drilling records indicate that the base of the aquifer in the vicinity of the
Haystead well is approximately 217 feet below ground. Id.
The Region determined that brine waste water injected into the Niagaran Group would
not endanger the Marshall Sandstone aquifer because the brine would be confined by the
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"approximately 2,653 feet of rock strata" separating the top of the Niagaran Group from the base
of the Marshall Sandstone aquifer. 1 Id. at 2; Transcript of EPA Public Hearing ("Transcript") at
8 (A.R. 65). These rock strata include layers of anhydrite, shale, and salt in the Salina Group,
and evaporite and shale layers in other geological groups, particularly a formation known as the
Coldwater Shale. R TC at 2. The Salina Group is immediately above the Niagaran at a depth of
approximately 2,782 to 2,352 feet. Id. at 5. The roughly 2,100 feet between the Salina Group
and the Marshall Sandstone aquifer consists mostly of layers of shale and evaporites. Id. at 2.
Following consultation with the U.S. Fish and Wildlife Service, the Region also determined that
construction of the Haystead well would not impact any endangered species. Id at 50. Final
determinations on these points were made only after the Region gave public notice of West Bay's
permit application, held a public hearing, and accepted written public comments. Id. at 1.
IV. ANALYSIS
In his petition, Mr. Bormuth challenges the technical determinations made by the Region
concerning the impact of the Haystead well on underground sources of drinking water and
endangered species. As the petitioner, Mr. Bormuth bears the burden of showing the Region's
decision was "based on * * * [a] finding of fact or conclusion of law that is clearly erroneous."
40 C.F.R. § 124.19(a)(4)(i)(A). On technical or scientific issues such as those raised by Mr.
Bormuth, the Board will typically defer to a permit issuer's technical expertise and experience, as
1
The Region provided the following background information on the geologic terms
"formation" and "group": '"A formation is a rock unit that is distinctive enough in appearance that a geologic mapper can tell it apart from the surrounding rock layers. It must also be thick enough and extensive enough to plot on a map. * Formations can be lumped together into larger rock units called groups, and divided into smaller units called members."' RTC at 32 quoting Utah Geologic Survey, What is a Formation?
· http://geology.utah.gov/surveynotes/gladasked/gladformation.htm (last visited Sept. 18, 2014).
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long as the permit issuer adequately explains its rationale and supports its reasoning in the
administrative record. See In re Dominion Energy Brayton Point, LLC, 12 E.A.D. 490, 510
(EAB 2006); see also, e.g., In re Russell City Energy Ctr., LLC, PSD Appeal Nos. 10-01 to 10-
05, slip op. at 88 (EAB Nov. 18, 2010), 15 E.A.D. _,petition denied sub nom. Chabot-Las
Positas Cmty. Call. Dist. v. EPA, No. 10-73870 (9th Cir. May 4, 2012). Accordingly, it is
particularly important for petitioners challenging technical determinations to address the
Region's rationale for its decision. In re City of Pittsfield, NPDES Appeal No. 08-19, at 8 & n.6
(EAB Mar. 4, 2009) (Order Denying Review), aff'd, 614 F.3d 7 (1st Cir. 2010); see also, e.g., In
re Town of Westborough, 10 E.A.D. 297,311-12 (EAB 2001). It is not sufficient, however, for a
petitioner to show merely that there is a "difference of opinion or an alternative theory regarding
a technical matter." Dominion,I2 E.A.D. at 510. Thus, in challenging technical determinations,
a petitioner bears a "particularly heavy burden" to show that the permit issuer has clearly erred.
In re Peabody W Coal Co., 12 E.A.D. 22, 41, 46, 51 (EAB 2005).
A. Underground Drinking Water Supplies
1. Petitioner's Challenge to the Region's No Endangerment Finding
After reviewing the permit application, all public comments, and the scientific data in the
record, the Region concluded that "there should be no impact to the drinking water supplies as a
result of injection into [the Haystead] well." RTC at 3. The Region based this conclusion on the
following findings:
(1) The Niagaran Group will accept the injected fluids. As the Region explained, the
Niagaran Group is a "vast limestone and dolomite rock structure" that "has been
documented in the Michigan Hydrologic Atlas (1981) to be permeable and very capable
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of accepting fluid." RTC at 2, 10, 66. These characteristics, the Region concluded,
indicate that only relatively low pressure will be required to operate the Haystead #9
SWD well. Id. at 10. Nonetheless, the Region noted that the Permit imposes a maximum
injection pressure that "prevents formations from fracturing and creating migration
pathways," id., and thus makes it "unlikely that injected fluid will leave the injection
zone." Id. at 31.
(2) The Salina Group is impermeable. The Region relied on the Michigan Hydrologic
Atlas to support its conclusion that the Salina Group, the rock formation directly above
the Niagaran Group, "is an approximately 430 foot thick sequence of carbonate,
anhydrite, shale, and salt which will act as a confining layer to prevent flow out of the
injection zone." Id. at 2, 66. In fact, as noted by the Region, the Hydrologic Atlas
documents at least six rock formations within the Salina Group that are either
"impermeable" or have "extremely low permeability." EPA Region 5 Response to
Petition for Review ("Region's Resp. ") at 17-18. Three examples from the Hydrologic
Atlas suffice to demonstrate this:
The A-2 Evaporite is an excellent confining layer. It is the seal
over the pinnacle reefs that developed in the shelf facies of the
Niagaran and has the properties necessary to confine fluids under
Pressure. * * * Porosity. Extremely low. Permeability. Extremely
low.
***
The B-salt and the B-Unit are excellent confining layers. The thick
salt section in the central part of the basin would be most effective,
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but the presence of either salt or anydrite should indicate that the
member is an aquiclude. l2l
***
The C-Shale is a plastic shale and should not maintain open
fractures at depth. Thus, it is considered to be an excellent
confining layer. * * * Porosity. Effective porosity is essentially
zero. * * * Permeability. Essentially impermeableYl
Dep't of Geology, W. Mich. Univ., Michigan Hydrologic Atlas, Part I (Hydrology for
Underground Injection Control in Michigan) ("Hydrologic Atlas") at II-46, 1!.49, II-51
(1981) (A.R. 28).
(3) Impermeable shales separate the Salina Group from Underground Drinking
Water Supplies. The Region also noted that the underground drinking water supplies in
the Marshall Sandstone are protected not only by the Salina Group but also by many
impermeable layers of shale and evaporites in the over two thousand feet between the top
of the Salina Group and the base of the Marshall Sandstone aquifer. Region's Resp.
at 22; RTC at 2. According to the Region, these layers include the Antrim Formation, the
Bedford Shale, the Bell Shale, the Sunbury Shale, and the Coldwater Shale. RTC at 2,
68. The Region laid special emphasis on the Coldwater Shale layer that is present at the
site of the Haystead well at a depth of approximately 217 to 1,200 feet below ground
2
An aquiclude is "a geologic formation or stratum that confines water in an adjacent
aquifer." Webster's Third New Int'l Dictionary 108 (1993).
3
The Region also cites the following additional rock layers in the Salina Group: the A-1
Evaporite, the D-unit salts, and the shales and anhydrite beds in the E-Unit. The Hydrologic Atlas describes these layers as having low or zero permeability. Hydrologic Atlas at II-43, II-51, 11-55.
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level. Id. The thickness of this impermeable layer is documented by drilling records
from the immediate vicinity of the Haystead well. Region's Resp. at 22; RTC at 2, 68.
· (4) Seismic data show no faults or fractures. After reviewing seismic data and
geophysical profiles submitted by West Bay, the Region concluded that there are no
fractures or faults present within the vicinity of the Haystead well in the Niagaran Group
injection zone, RTC at 9, the Salina Group, id. at 66, or the Coldwater Shale, id. at 17.
(5) The steel well casings will be cemented to prevent movement of fluids. The
Permit requires that the Haystead well consist of three steel casing strings set to 350, 930,
and 2,780 feet. Permit at 15, B-2 of2. Each casing, the Region explained, will be
encased in cement "to preclude the movement of fluids into and between [underground
sources of drinking water] due to injection operations." RTC at 66.
Mr. Bormuth has a far different view of the risk posed to underground sources of drinking
water by injection of brine at the Haystead well. He disputes the Region's conclusion that the
injected brine will be confined to the Niagaran Group by the Salina Group and the other rock
strata overlying the injection zone. Mr. Bormuth's theory runs as follows: first, the injected
brine will convert the anhydrite in the Salina Group into gypsum, and this conversion process
will cause the converted anhydrite to swell and fracture. Petition for Review, Appeal No.
UIC 14-66 ("Pet."), at 2; Transcript at 39-41. Then, the brine will saturate the Salina Group and
dissolve the salt layers in the Group. Petitioner Peter Bormuth's Reply to EPA response to
Petition for Review UIC 14-66 ("Reply") at 4-5. Finally, with the layers of the Salina Group
fractured or dissolved, the brine will be forced upward by "a known vertical component to the
Michigan hydraulic gradient * * * through pre-existing fractures in the overburden rock
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formation" until it reaches the near surface aquifers. Pet. at 7. Mr. Bormuth's petition is replete
with citations to scientific articles, which he claims substantiate his thesis. Mr. Bormuth labels
the Region's conclusion that the injected waste will be confined to the Niagaran Group as "a joke
and contrary to all known scientific theory and current technological practices."4 Reply at 5.
The Region characterizes Mr. Bormuth's scientific arguments as an "extrapolat[ion of]
various arguments from different unrelated publications to loosely frame an argument based on
conjecture." Region's Resp. at 9. The Region does not disagree that anhydrite can be converted
to gypsum by exposure to water. But, according to the Region, anhydrite conversion occurs only
near the surface and would not happen at the depth of the Salina Group. Id. at 23. The Region
also stresses that there are many impermeable rock layers between the Salina Group and the
Marshall Sandstone aquifer. Id. at 21-22. Finally, the Region faults Mr. Bormuth for relying
almost entirely on information and articles not cited or provided to the Region during the public
comment period. Id. at 10.
2. Discussion
The Region concluded that "2,653 feet of rock strata" protect the Marshall Sandstone
aquifer from brine injected to the Niagaran Group. Stmt. Basis at 2; Transcript at 8; RTC at 2.
Yet, Mr. Bormuth focuses his challenge to the Haystead well on a relatively thin layer of those
4
Mr. Bormuth also alleges that the Region's approval of the West Bay permit was
motivated by "Christians in the EPA who deliberately want to destroy the Great Lakes watershed and aquifers," Reply at 9, and that the Board is prejudiced against him because of his religious beliefs, id. ("The assumption seems to be that it is safe to ignore science because the Petitioner is proceeding prose while the Petitioner's hatred of the evil scum Jesus myth will insure that any judicial officer selected to review this case will prejudicially rule against him."). Because Mr. Bormuth offers not a scintilla of evidence to substantiate these allegations, the Board summarily rejects them.
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strata - the anhydrite in the Salina Group. Our discussion of Mr. Bormuth's challenge looks first
at the non-anhydrite strata and then turns to the anhydrite in the Salina Group.
a. Rock Layers Other Than Anhydrite
Mr. Bormuth devotes little attention to the Region's conclusion that the Marshall
Sandstone aquifer is protected from the injected brine by multiple impermeable rock layers, not
just the anhydrite in the Salina Group. As explained below, the Board concludes that
Mr. Bormuth has not shown that the Region clearly erred in its determination that several other
rock layers - principally, the Coldwater Shale - form an impermeable barrier protecting the
Marshall Sandstone aquifer.
In his public comments and his petition, Mr. Bormuth relies on a recently published
stratigraphic map to argue that the Coldwater Shale will not protect the Marshall Sandstone
aquifer from brine injected into the Niagaran Formation. 5 E-mail from Peter Bormuth to
Timothy Elkins, U.S. EPA (Apr. 30,2013, 10:21 pm) (A.R. 54); Pet. at 6-7. He claims that this
map shows that the Coldwater Shale is only 250 feet thick- not almost 1,000 feet as the Region
concluded. He further argues that both this map and the stratigraphic map the Region relied on
show that the Coldwater Shale is layered with sandstone and is therefore permeable. Pet. at 6-7.
Mr. Bormuth ignores, however, that the Region's conclusions regarding the Coldwater Shale are
5
Mr. Bormuth principally insists that no substantive rebuttal is needed to the Region's
reliance on the Coldwater Shale because the Region allegedly has not formally designated the Coldwater Shale as the "confining zone" for brine injected to the Niagaran Group. Pet. at 6. However, Mr. Bormuth acknowledged in comments filed during the public comment period that he was aware of the Region's reliance on the Coldwater Shale as the "ultimate confining zone protecting" underground drinking water supplies. E-mail from Peter Bormuth to Timothy Elkins, U.S. EPA (Apr. 30,2013, 10:21 pm) (A.R. 54). Thus, Mr. Bormuth is in no position to claim he · did not have a full opportunity to contest the Region's reliance on the Coldwater Shale.
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based primarily on drilling records from two wells immediately adjacent to the Haystead wellsite
not general stratigraphic maps. R TC at 7. The records from these wells show the Coldwater
Shale to be nearly 1,000 feet thick and free of sandstone. Id.
Mr. Bormuth also advances a new argument in his Petition as to why the Coldwater Shale
is not impermeable. He claims that the Region has ignored "a known vertical component to the
Michigan hydraulic gradient which will move the injected brine upward naturally through pre-
existing fractures in the overburden rock formations." Pet. at 7. This claim, however, was not
presented to the Region during the public comment period. The Board will not consider issues
raised for the first time on appeal. 6 40 C.F.R. § 124.19(a)(4)(ii); Westborough, 10 E.A.D. at 304,
308-09; In re W Bay Exploration Co., UIC Appeal No. 14-67, at 7-8 (July 3, 2014) (Order
Denying Review) (dismissing claim by another petitioner challenging the permit for the Haystead
.well for failure to specifically raise the claim during the public comment period).
Additionally, Mr. Bormuth fails to adequately contest the Region's reliance on shale and
salt layers in the Salina Group to demonstrate that the injected brine would not escape the
injection zone. Transcript at 8; RTC at 2. Mr. Bormuth either ignores the existence of these
6
In addition, Mr. Bormuth presents no evidence to support his claim of pre-existing
fractures in the rock formations between the Salina Group and the Marshall Sandstone. As noted above, the Region relied on seismic data and geophysical profiles to conclude no such fractures exist.
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formations (the shale layer)7 or makes untimely arguments concerning their permeability (the salt
layers). 8
b. Anhydrite in the Salina Group
Mr. Bormuth's argument that the Haystead well will endanger underground aquifers is
based mainly on his theory that the injected brine will convert the anhydrite layers in the Salina
Group to gypsum, resulting in the breach of these layers. To support this theory, Mr. Bormuth
cites a long list of scientific articles and submits copies of the articles to the Board. However,
Mr. Bormuth has not preserved some aspects of this argument for review because he failed to cite
or provide some of these articles to the Region during the public comment period.
In his testimony at the public hearing, Mr. Bormuth took a very different approach than in
his petition. 9 Although he outlined the basics of his anhydrite conversion theory, he did not
present the list of citations and copies of the cited articles that were included in his petition to the
Board. Transcript at 39-41. Instead, his testimony is filled with claims such as "[l]aboratory
7
Mr. Bormuth's petition and reply brief repeatedly describe the composition of the Salina
Group but omit mention of its shale layer on each occasion. Pet. at 3, 6; Reply at 5.
8
In his reply brief, Mr. Bormuth now claims for the first time that the salt layers in the
Salina group "will dissolve in solution upon receiving the injected fluid." Reply at 4; see In re BP Cherry Point, 12 E.A.D. 209,216 n.l8 (EAB 2005) (rejecting new argument in reply brief as untimely).
9
In addition to his testimony, Mr. Bormuth filed three separate written comments during
the public comment period on discrete subjects. See E-mail from Peter Bormuth to Anna Miller and Timothy Elkins, U.S. EPA (Apr. 16,2013, 8:58pm) (A.R. 52) (expressing displeasure with EPA and suggesting a different injection zone 1500 feet lower); E-mail from Peter Bormuth to Timothy Elkins, U.S. EPA (Apr. 30,2013, 10:21 pm) (A.R. 54) (questioning the thickness and impermeability of the Coldwater Shale); E-mail from Peter Bormuth to Timothy Elkins, U.S. EPA (May 2, 2013, 9:08pm) (A.R. 58) (asking Region to consider the earthquake risk to the Haystead well).
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experiments show," "many researchers are reporting," and"[ o]ther studies show." Id. In effect,
Mr. Bormuth is attempting to use this appeal to bypass the Region, the permit issuing authority
here. He has saved the full elaboration of his argument and the supporting scientific articles for
presentation to the Board in his permit appeal. Allowing this tactic would turn the administrative
permit process on its head. In re BP Cherry Point, 12 E.A.D. 209, 219-20 (EAB 2005) (holding
that resolving newly-raised issues on appeal would be "contrary to the expectation that 'most
permit conditions should be finally determined at the [permit authority] level" (quoting In re
Knauf Fiber Glass, GMBH, 8 E.A.D. 121, 127 (EAB 1999))). The Region, not the Board, has
the technical expertise to grapple with complex scientific questions, such as the geologic
argument Mr. Bormuth presents, as a first line decision-maker. E.g. W. Bay Exploration, UIC
Appeal No. 14-67 at 4. The Board's role is not to make initial scientific findings but to review
the Region's decisions to determine if the Region has based its conclusions on clearly erroneous
conclusions of fact or law. 40 C.F.R. § 124.19(a)(4)(ii).
Consistent with this division of responsibilities, EPA permit regulations require that any
person who believes that a permit condition is inappropriate to raise "all reasonably ascertainable
issues and * * * all reasonably available arguments supporting [petitioner's] position" to the
permitting authority during the comment period on the draft permit. Id. § 124.13. Moreover,
these regulations specifically require that "[ c]ommenters shall make supporting materials not
already included in the administrative record available to EPA as directed by the Regional
Administrator." Id. The Board's regulations require exhaustion of issues before the permit
issuer priot to Board review. Id. § 124.19(a)(4)(ii); see Westborough, 10 E.A.D. at 304, 308-09.
Based on these regulations, the Board has frequently barred petitioners from relying on
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documents on appeal that could have been, but were not, submitted to the permit issuer during
the comment period. See, e.g., In re Chevron Michigan, LLC, UIC Appeal No. 13-03, at 16
(EAB Nov. 7, 2013) (Order Denying Review) (declining to consider article on appeal because,
although article was published prior to comment period, it was not raised during the comment
period); In re Russell City Energy Ctr., LLC, PSD Appeal Nos. 10-01 through 10-05, slip op. at
45 n.35, 57 n.46 (EAB Nov. 18, 2010).
Giving Mr. Bormuth the benefit of the doubt, in light of his lack oflegal counsel, 10 the
Board finds that three of the articles cited in the Petition were at least marginally referenced in
his public comments: articles by Joanna Jaworska, R.C. Murray, and Ingo Sass and Ulrich
Burbaum. 11 See Transcript at 39. The record indicates that the Region understood Mr. Bormuth
to be relying on these articles; the Region addressed them at least generally in the Response to
Comments document. RTC at 67-68. The Board therefore will consider each of these articles to
be included by reference in the record of this case. The Board will not review the other articles
cited in Mr. Bormuth's Petition as they were not raised to the Region's attention during the
public comment period and are thus not properly before the Board. 12
10
See In re Sutter Power Plant, 8 E.A.D. 680, 687 (1998) (noting that the Board broadly
construes arguments from petitioners unrepresented by legal counsel to ensure that "public participation be meaningful and not unduly hampered by process restrictions").
11
Joanna J aworska, Crystallization, Alternation and Recrystallization of Sulphates, in
Advances in Crystallization Processes (Itzhak Mastai ed., 2012); R.C. Murray, Origin and Diagenesis of Gypsum and Anhydrite, 34(3) J. of Sedimentary Petrology 512 (1964); Ingo Sass & Ulrich Burbaum, Damage to the Historic Town ofStaufen (Germany) Caused by Geothermal Drillings Through Anhydrite Formations, 39(2) Acta Carsologica 233 (2010).
12
Mr. Bormuth does not dispute that he did not submit these studies during the public
comment period. He seeks to excuse this omission by claiming that he offered to provide the scientific articles to the Region's permit writer, Mr. Timothy Elkins, but received no response.
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In any event, the Board finds that the Jaworska, Murray, and Sass and Burbaum articles
do not meaningfully support Mr. Bormuth's theory that anhydrite layers at the depth of the Salina
Group would be breached by injected brine. The Jaworksa and Murray articles generally discuss
a geological cycle whereby buried gypsum may be replaced by anhydrite, and, in tum, the
anhydrite may be re-converted to gypsum if the overburden is removed. See Jaworska, supra,
note 11, at 468; Murray, supra note 11, at 522. The Jaworska article, however, does not discuss
in detail whether gypsification of anhydrite can occur at a depth of more than 2,600 below the
surface (the situation presented in this case), and Mr. Bormuth does not cite it for that purpose.
Reply at 5; Transcript at 39. The Murray article does suggest this possibility, but only briefly.
Murray writes:
Although the transition [from anhydrite to gypsum] commonly takes place within a few
hundred feet of the present surface, the replacment of anhydrite by gypsum has been
observed as deep as 3500 feet in the Permian San Andrea Formation, Dune field, Crane
County, Texas.
Murray, supra note 11, at 512. Murray, however, provides no other details about this discovery.
The article contains no information on the thickness of the converted anhydrite or the causative
factors in the anhydrite conversion. Further, the article provides no documentation of the
discovery other than a photograph. Id. at 513 fig.1. This single reference in the Murray article to
Reply at 1-2. However, the public notice initiating this Permitproceeding clearly established how members ofthe public were to submit comments. U.S. EPA, Region 5, New Disposal Well Permit Near Brooklyn, Michigan (April2013) (A.R. 99) (specifying that comments may be submitted "in writing at the public hearing and during the public comment period via standard mail or email, or orally during the formal public meeting"). Offering to submit the articles to the Region did not meet the terms specified by the Region and does not comply with the requirements of 40 C.F.R. § 124.13.
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gypsification of anhydrite at depth of 3,500 feet is a slender reed upon which to construct the
elaborate argument made by Mr. Bormuth.
The Sass and Burbaum article also addresses a situation that is not analogous to the
Haystead well. Sass and Burbaum discuss an incident in Staufen, Germany involving subsurface
conversion of anhydrite to gypsum that resulted in the swelling and fracturing of the anhydrite.
Sass & Burbaum, supra note 11, at 234. But the circumstances in the city of Staufen are far
different than the situation at the Haystead well. In Staufen, borehole heat exchange wells were
drilled through a near-surface anhydrite layer into a confined artesian (i.e. pressurized) aquifer.
Id. at 238-39. Improper sealing of the boreholes led to groundwater infiltration of the holes and
the subsequent swelling and fracturing of the anhydrite. Id. These wells were drilled to depths
of between 105 and 140 meters (approximately 345 to 460 feet) and the anhydrite layer began
about 60 meters (197 feet) underground. Id. In contrast, the Haystead well will be drilled into a
formation that will readily accept fluids, the well must meet rigorous construction requirements
to prevent fluid infiltration of the borehole, and the anhydrite layer is greater than 2,350 feet
underground.
Mr. Bormuth attempts to buttress his argument for the conversion of the anhydrite layers
in the Salina Group with a flurry of facts, figures, and calculations on temperature, solubility, and
pressure. See Transcript at 39-41; Pet. at 3-5; Reply at 4-5. Mr. Bormuth fails to explain,
however, how these calculations demonstrate that anhydrite will be converted to gypsum at the
depth of the Salina Group. 13 In sum, the only evidence that he provides to support his theory is
13
For example, at the public hearing, Mr. Bormuth stated that (1) "[e]ach 0.01 [pascal]
increase in pressure results in 3 to 5 times increase in solubility" of anhydrite; (2) overburden pressure on the Salina Group anhydrite is "roughly 1,290 [pounds per square inch];" (3) the
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the Murray article's brief mention of a single unexplained incident of anhydrite conversion at the
depth of 3,500 feet. This marginal evidentiary showing falls well short of demonstrating the
Region clearly erred in its technical evaluation of Mr. Bormuth's anhydrite conversion argument
for the Haystead well situation.
4. Conclusion on Petitioner's Groundwater Endangerment Argument
The Board concludes that Mr. Bormuth has failed to demonstrate that the Region made a
clear error of fact or law in finding that the Haystead well does not present an endangerment to
underground supplies of drinking water. The Region is entitled to deference on this technical
issue and has provided a well-reasoned and thoroughly-documented explanation for its
conclusion that the Marshall Sandstone aquifer is protected from contamination by 2,653 feet of
rock strata. In his petition, Mr. Bormuth attempts to shift the focus to a relatively narrow
segment of these rock strata, the anhydrite layers in the Salina Group, and argues that these rock
layers will be breached by the injected brine. As discussed above, however, the Board has
determined that the evidence that Mr. Bormuth has submitted to substantiate this claim is
marginal at best. Mr. Bormuth presents an even less convincing case that the other rock strata
relied upon by the Region will not confine the injected brine. He ignores findings by the Region
that are inconvenient to his argument, and he failed to timely raise or adequately support several
claims critical to his position. For these reasons, the Board defers to the Region's technical
judgment that the Haystead well will not endanger the Marshall Sandstone aquifer.
swelling of hydrated anhydrite will create "pressures of 1.7 to 4.7 [megapascals];" and (4) "(s]alinic pressures as high as 10,000 (pounds per square inch], 70 [megapascals]" have been reported in anhydrite deposits in Texas. Transcript at 40. Based on these abstract calculations, he jumped immediately to the conclusion that "[t]his pressure will rapidly cause a conversion and breaching ofthe anhydrite cap." Id.
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B. Endangered Species
Mr. Bormuth next challenges the Region's compliance with the Endangered Species Act
("ESA"), 16 U.S.C. §§ 1531-1544. Section 144.4 of Title 40 ofthe Code of Federal Regulations
directs that the ESA "may apply to issuance of permits under the [UIC] rules," and that, if it does
apply, "its procedures must be followed." 40 C.F.R. § 144.4. ESA section 7 requires all federal
agencies to ensure, through consultation with the Secretary of the Interior, that their actions are
"not likely to jeopardize the continued existence of any endangered or threatened species or
result in the destruction or adverse modification" of a species' critical habitat. ESA § 7(a)(2),
16 U.S.C. § 1536(a)(2). A federal agency considering taking an action is required to determine
whether a proposed action "may affect," directly or indirectly, species listed as endangered or
threatened or designated critical habitat. 50 C.F .R. § 402.14(a). If this determination is in the
affirmative, then formal consultation on the action is required with the U.S. Fish and Wildlife
Service. However, if an agency determines, on the basis of a biological assessment prepared
under 40 C.F.R. § 402.12 or an informal consultation with the U.S. Fish and Wildlife Service,
that the proposed action is not likely to adversely affect a listed species or critical habitat, no
formal consultation is required and no further action is required under the ESA. 50 C.F.R.
§§ 402.13(a), .14(a).
Based on an ecological assessment submitted by West Bay, the Region identified two
listed endangered species, the Indiana bat and Mitchell's satyr butterfly, and two candidates for
listing, the eastern massasauga (a rattlesnake) and the Poweshiek skipperling (a butterfly), that
may be found in Jackson County. RTC at 49-50; Westshore Consulting, Additional Information
Requested/or the Haystead SWD #9 Injection Well, Permit Application #MI-075-2D-OOIO
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("Westshore Rpt.") at 1 (March 19, 2012) (A.R. 13). However, the Region concluded that the
Haystead well would have no impact on these species because it "will not affect [their] habitat."
RTC at 50. The identified habitat for the four species are upland woods, riparian woods or
woodlots located close to rivers or streams; and wetlands, wet prairies, or fen wetlands.
Westshore Rept. at 2. The Haystead well is proposed to be in constructed in an "open upland
plowed agricultural field." ld. Records indicate that this location has historically been in
agricultural use. RTC at 50. The proposed well will be close to two oil production wells (90 feet
to the closest) and will require only minor clearing and leveling of a relatively small area of a
plowed field (85 x 220 feet). ld. No access roads will be required and construction is planned
for prior to the summer migration period for the Indiana bat. ld. Based on these facts, the
Region found that no impact would occur on any of the four species, and the U.S. Fish and
Wildlife Service, following an informal consultation, concurred in writing. 14 RTC at 50; Letter
from Scott Hicks, Field Supervisor, U.S. Fish and Wildlife Service, to Rebecca L. Harvey, U.S.
EPA, Region 5 (Sept. 4, 2013) (A.R. 82).
Mr. Bormuth argues that the Indiana bat and the eastern massasauga rattlesnake will be
impacted by the Haystead well. Noting that a marsh, a river, and a creek are relatively close to
the well site (within 100 to 1,500 feet), Mr. Bormuth argues that these bats and rattlesnakes will
be present at the construction site. Pet. at 9, fig. 2. He claims that spills of toxic chemicals are
14
The U.S. Fish and Wildlife Service opined that nearby groundwater-dependent
wetlands could be impacted if the injection well leaked and contaminated local aquifers. U.S. Letter from Scott Hicks, Field Supervisor, U.S. Fish and Wildlife Service, to Rebecca L. Harvey, U.S. EPA, Region 5, at 2 (Sept. 4, 2013) (A.R. 82). As discussed above, the Board has concluded that the Region reasonably determined that the Haystead well will not endanger groundwater.
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frequent at injection wells and that insects are likely to be contaminated by these spills and later
consumed by bats.
The Board defers to the Region and to the U.S. Fish and Wildlife Service on this
technical question. The issue is not whether the two endangered species could be present at the
site but whether they will be directly or indirectly impacted or affected. At most, Mr. Bormuth
alleges an indirect impact on the endangered species. ESA regulations require that for an indirect
effect to be cognizable it must be "reasonably certain to occur." 50 C.F.R. § 402.02. To
demonstrate an effect on the Indiana bat, Mr. Bormuth piles speculation (injectate will be spilled)
upon speculation (insects will be contaminated) upon speculation (bats will consume
contaminated insects in sufficient quantities to receive a toxic dose). As to the eastern massasauga
rattlesnake, Mr. Bormuth advances no reason, other than its possible presence in the area, as to
why it would be impacted. Speculation does not meet Mr. Bormuth's heavy burden of showing
the Region clearly erred in resolving this technical question. Accordingly, the Board denies Mr.
Bormuth's endangered species claim. 15
15
The Region also argues, among other things, that Mr. Bormuth's endangered species
claim should be denied because surface activities at the well site, such as spills, are outside the scope ofUIC permit review. Region's Resp. at 27. The Board, however, is uncertain precisely what the legal basis is for the Region's contention, as the Region cites only to a Board decision not involving an ESA claim. Id. (citing In re Presidium Energy, LC, UIC Appeal No. 09-01 (EAB July 27, 2009) (Order Denying Review)).
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V. CONCLUSION
For the foregoing reasons, the Board denies Mr. Bormuth's Petition.
So ordered.
ENVIRONMENTAL APPEALS BOARD 16
By:
Catherine R. McCabe
Environmental Appeals Judge
16
The three-member panel deciding this matter is composed of Leslye M. Fraser,
Catherine R. McCabe, and Kathie A. Stein.
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CERTIFICATE OF SERVICE
I hereby certify that copies of the foregoing Order Denying Review in the matter of
West Bay Exploration Co., UIC Appeal No. 14-66 were sent to the following persons in the manner indicated:
By U.S. First Class Mail:
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