Consol Pennsylvania Coal Co. v. Department of Environmental Protection

129 A.3d 28, 2015 Pa. Commw. LEXIS 544, 2015 WL 8718217
CourtCommonwealth Court of Pennsylvania
DecidedDecember 15, 2015
Docket351 C.D. 2015
StatusPublished
Cited by9 cases

This text of 129 A.3d 28 (Consol Pennsylvania Coal Co. v. Department of Environmental Protection) is published on Counsel Stack Legal Research, covering Commonwealth Court of Pennsylvania primary law. Counsel Stack provides free access to over 12 million legal documents including statutes, case law, regulations, and constitutions.

Bluebook
Consol Pennsylvania Coal Co. v. Department of Environmental Protection, 129 A.3d 28, 2015 Pa. Commw. LEXIS 544, 2015 WL 8718217 (Pa. Ct. App. 2015).

Opinion

OPINION BY

President Judge DAN PELLEGRINI.

Consol Pennsylvania Coal Company, LLC (Consol) petitions for review of the order of the Environmental Hearing Board (Board) granting the Department of Environmental Protection’s (Department) motion to dismiss as moot Consol’s appeal from the Department’s issuance of a permit revision. For the reasons that follow, we affirm the Board’s order.

I.

In connection with its operation of an underground bituminous coal mine formerly known as the Bailey Mine 1 in Greene County, Pennsylvania, Consol applied to the Department for a permit revision seeking to conduct longwall mining activities on 2,438.54 acres not covered by the initial permit.

A.

The permit application is góverned by requirements developed by the Department, including standards under the Department’s Module 8 regarding “Hydrology/Baseline Biology” to ensure : that streams which may be undermined by applicants’ proposed mining activities are not adversely affected. (Reproduced Record [R.R.] at 188a.) “Adverse effect” is a term of art meaning “mining induced changes that may impair surface water quality.” (Id. at 85a.) With regard to streams, such impairment includes loss of flow, more than 12% reduction in the average biological score of a stream reach based on a comparison of pre- and post-mining biological scores, and reductions in the length of certain intermittent or perennial streams.

Section 8.9 of the Module concerns “Potential Areas of Flow Loss within the Stream” and instructs as follows:

b. Using Form 8.8B, (Stream Delineation and Bioassessment Summary), include baseline information on fish and macroinvertebrate. communities sufficient to delineate stream segments that qualify as “biologically diverse”,, “biologically variable”, and point of first use based on,.the- criteria and procedures outlined in Appendix A of the Technical Guidance Document “563-2000-655”.
c. Provide -an assessment of the condition of the macroinvertebrate community in each stream augment identified as “biologically diverse” in item b above, using Form 8.8C (Quantitative Multi-Habitat Bioassessment Of Diverse Community) and,8.8D (Biometric And Total Biological Score Summary). Each assessment should consist of Form 8.8C documenting the results of each sampling event (minimum of two) and Form *32 8.8D documenting biometric calculations and calculation of the “Mean Total Biological Score,” . (Additional information on performing aquatic life use .assessment is found in the Technical Guidance Document 568-2000-655.)

(R.R. at 202a.) 2 Section 8.10 of Module 8 imposes substantially similar requirements with regard to streams having gradients of 2% or less that will undergo subsidence as a result of mining and therefore may result in pooling.

Further, the Department’s Bureau of Mining Programs issued Technical Guidance .Document 563-2000-655, entitled “Surface Water Protection — Underground Bituminous Coal Mining Operations” 0Guide) to assist the Bureau’s staff in reviewing underground mining applications and to “provide[] guidance to the regulated community regarding how to comply with existing legal requirements.” (Id. at 84a.) To this extent, the Guide provides procedures governing “the Department’s manner'of interpreting the existing legal requirements applicable to surface water protection, and its recommended approach for mine operators to comply with these existing requirements, in the context of impacts on streams ... caused by underground mining operations.” (Id. at 89a.)

Appendix B to the Guide discusses the Department’s Low Gradient Stream Assessment Protocol which governs the sampling of biologically diverse stream segments. Under the protocol, pre-mining sampling is performed to “assess a stream’s level of use of attainment” and yields an aquatic life use attainment score (biological score) that can be compared with post-mining samplings from the same biological monitoring point to “assess the magnitude of mining-induced change.” (Id. at 113a.)

Among other requirements, the Guide mandates that the following data be included in applications:

(A) Delineation of all biologically diverse and biologically variable segments which are likely to experience mining induced changes during the five-year term of the permit.
(B) At least 12 months of flow data for each stream that may be susceptible to mining induced flow loss within the first two years of the permit term.
(C) At least one total biological score for each stream reach that is likely to experience mining induced flow loss or pooling within the first two years of the permit term.
(D) At least one Wolman Pebble Count for each stream reach that is likely to experience mining induced pooling within the first two years of the permit term.
(E) The identification of wetlands in ar- ‘ eas that will be subsided or undermined at depths of less than 100 feet during the five-year term of the permit.

(Id. at 106a-107a.) The Guide cautions, “Permits that are issued with incomplete sets of pre-mining data pursuant to ... this section will normally include conditions requiring permittees to complete data collection prior to the time a stream or wetland is susceptible to mining induced changes.” (Id. at 107a.)

B.

Following Consol’s submission of its application for a permit revision, the Department advised Consol by letter dated January 13, 2014, that its application contained *33 numerous deficiencies, including its failure to identify nine stream segments for which biological monitoring points and biological data were required. On January 23, 2014, Joel C. Folman, a Water Pollutant Biologist in the Department’s District Mining Office, performed a site inspection of the expanded mining área, after which he determined that information regarding four of the nine missing segments should be included in the application.

Accordingly, in February 2Q14, the Department issued a revised permit granting Consol’s request to conduct longwall mining activities in the expanded area subject to Special Condition No. 77, which stated: “The company shall submit two Biological Monitoring (Appendix B) scores within 16 percent-in accordance to. [the Guide ]” with respect to the subject streams. (Id. at 13a.) .

By letter dated March'5, 2014, Consol satisfied Special Condition No. 77, submitting the required pre-mining biological data for the subject streams. Nonetheless, on March 24, 2014, Consol filed an appeal asserting the following grounds:

[Consol] is aggrieved by, objects to and appeals from the Department’s action because the action is arbitrary, capricious, contrary to law and constitutes an abuse Of discretion,' in that, inter alia:

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Bluebook (online)
129 A.3d 28, 2015 Pa. Commw. LEXIS 544, 2015 WL 8718217, Counsel Stack Legal Research, https://law.counselstack.com/opinion/consol-pennsylvania-coal-co-v-department-of-environmental-protection-pacommwct-2015.