3 Pa. Commw. 110 | Pa. Commw. Ct. | 1971
Opinion by
As the noted legal luminary, Karl Lléwellyn, once said, “Law . . . begins when someone takes to doing something someone else does not like.” These words seem particularly appropriate in this case which is an appeal from an adjudication of the Sanitary Water Board (Board) which,
.The primary contention of appellants is that the proposed K. & J. strip mine operation will cause sedimentation which will degrade the quality of Rogues Harbor Run as a fishing stream and adversely affect it as a domestic water supply for Westover Borough.
Intervening appellee, K. & J., filed a Motion to Quash on April 13, 1971, to which an Answer was filed by appellants on April 27, 1971. We conclude that the contentions made in the Motion are without merit, and therefore it is denied.
Turning to the merits, appellants make the following contentions:
(1) Contrary to the weight of thé evidence, which proved that sedimentation would enter the stream, the Board decided that the proposed operation can be con
(2) The Board erred in finding that KL & J.’s mining operations under another permit at nearby Rock Run Creek do not provide a basis for determining whether it could properly operate the proposed operation.
(3) The Board erred in permitting EL & J. to file less than a complete set of plans.
As to the first contention, appellants acknowledge that “If this sedimentation was excessive, it would be harmful to aquatic life and to the use of the stream as a domestic water supply. Thus, the question is whether the sedimentation that would in fact occur might become excessive." (Emphasis added) On this point, appellants point to the testimony of Mr. David Yost, a soil scientist with the Soil Conservation Service, to the effect that he had made a study of the soils in the Rogues Harbor Run area and had calculated that “for a five year frequency storm, from 93,367 to 107,650 cubic yards of silt loam would be moved into Rogues Harbor Run if no vegetation is planted prior to the storm." (Emphasis added) This study, however, was based on a formula from a technical manual used by the Soil Conservation Service. In applying the formula, which was marked “tentative” and published in
We are hardly stream pollution experts, and, as the Supreme Court’s words in Blumenschein v. Housing Authority of Pittsburgh, 379 Pa. 566, 572-573, 109 A. 2d 331, 334-335 (1954), indicate,
As to the second contention, it would appear that K. & J. has significantly changed its plan of operation for the present tract as opposed to its methods .at the Rock Run Creek location. As appellee points out, “. . . K. .& J.’s proposed operation on Rogues Harbor Run differs in two major particulars: (1) all haul roads are to be constructed on the spoils of the operation or at an elevation higher than the mined areas, whereas in the Rock Run operation there were no conditions on the location of the haul roads. To the extent there was any problem with siltation on that Rock Run operation, it was due to the silt in the drainage from the haul roads, which were constructed below the mined area. This drainage reached the stream without any settling. This situation has been remedied by the building of settling ponds intermittently along the haul roads to direct the drainage in the ditches from the stream temporarily to enable settling of silt to occur. (2) The mining is to progress in a checkerboard fashion, Avhich significantly decreases the possible area exposed at any one time. In any event, K. & J. was never found to be in violation on its Rock Run operation, and the latest biological study of the stream in July of 1970 revealed that Rock Run is progressly improving in its ability to support aquatic life.”
Appellants’ third contention is urged because the plans “did not show the annual waterfall, composition of the soil, slope of the land, or quantity of water which Avill drain over, around and through the proposed min
We applaud the civic spirit demonstrated by the several appellants, but we nevertheless fail to find the requisite “manifest and flagrant abuse of discretion or a purely arbitrary execution of the agency’s duties or functions.”
Order affirmed.
The Sanitary Water Board consisted of the Secretary of Health, who was the chairman, the Secretary of Forests and Waters, the Secretary of Mines, the Executive Director of the Pennsylvania Fish Commission, the Secretary of Commerce, and three members of the general public. See the Administrative Code, the Act of April 9, 1929, P. L. 177, as amended by the Act of August 14, 1963, P. L. 1119, 71 P.S. §149. The Chairman of the State Soil and Water Conservation Commission was added by Section 1 of the Act of July 31, 1970, P. L. , No. 222, 35 P.S. §691.1.
“Land affected shall mean the land from which the overburden is removed and-that occupied by the spoil piles.” Section 3 of the. Bituminous Coal Open; Pit Mining Conservation Act, Act of May 31, 1945, P. L. 1198, as amended, 52 P.S. §1396.3.
Section 2(a) of Article 900 of the Rules and Regulations of the Sanitary Water Board provided: “Reporting agency shall mean the Commonwealth agency responsible to the Board for certain investigating, reporting and enforcement duties. In the case of bituminous strip mines the reporting agency shall be the Department of Mines and Mineral Industries. In other eases the reporting agen-, cy shall be the Department of Health.”
Section 1 of the Olean Streams Law, at the time of K. & J.’s application, provided in part: “ ‘Pollution’ shall be construed to mean noxious and deleterious substances rendering unclean the waters of the Commonwealth to the extent of being harmful or inimical to the public health, or to animal or aquatic life, or to the use of such waters for domestic water supply, or industrial purposes, or for recreation. The Sanitary Water Board shall determine when the discharge of any industrial waste, or the effluent therefrom, constitutes pollution, as herein defined, and shall establish standards whereby and wherefrom, so far as reasonably practicable and possible, it can be ascertained and determined whether any such discharge does or does not constitute pollution as herein defined.”
“By a host of authorities in our own and other jurisdictions it has been established as an elementary principle of law that courts will not review the actions of governmental bodies or administrative tribunals involving acts of discretion, in the absence of bad faith, fraud, capricious action or abuse of power; they will not inquire into the wisdom of such actions or into the details of the manner adopted to carry them into execution. It is true that the mere possession of discretionary power by an administrative body does not make it wholly immune from judicial review, but the scope of that review is limited to the determination of whether there. has been a manifest and flagrant abuse of discretion or a purely arbitrary execution of the agency’s duties or functions. That the court might have a different opinion or judgment in regard to the action of the agency is not a sufficient ground for interference; judicial discretion may not be substituted for ad,ministrative discretion.” (Emphasis in original).
Although,for reasons of space we have not included here the elaborate operation plan of Á & J. or the 32 conditions attached to the Board’s approval, we quote'here the Board’s reasoning as to appellants’ third contention:
“First, the quantity of rainfall and the slope of the land are relevant only to the capacity of the settling ponds constrú'etéd to handle surf ace, runoff. However, the water from the-pit-going into settling ponds is pumped. Quantity of water going into these ponds is, therefore, easily regulated,, and any . excess drainage can be retained in the pit until such time as adequate space' is' available in the treatment ponds. The water from- the ditches of the haul roads goes into the pit, and creates no problem' in this regard: The water from the diversion ditches above the highwall is' channeled to the 50 foot barrier areas of undisturbed ground, which will be able to filter substantial quantities of water. In any event, the .location and size of the diversion ditches will be constantly changing. When mining in the first pit is completed, the adjoining highwall area where the first diversion ditch was located is blasted with dynamite, and the overburden therefrom placed in the first pit. Prior thereto another diversion ditch will have been constructed back further on the highwall, so as to divert the surface drainage from the new second pit. Thus, the location and size of the diversion ditches bn the highwall will be constantly changing, if diversion ditches and settling ponds become necessary, to prevent siltation' from the initial spoil pile and the restored areas, these will, of necessity,, be of such size and location as conditions warrant. . .
, “The composition of the soil is relevant to the quantity of silt and sediment that a given area will produce. If the collection and filtration and settling facilities are adequate, the quantity of siltatio'n produced by a given área is relevant only to the -frequency With which the ponds will have to be cleaned or constructed elsewhere. .This will vary with the- peculiar circumstances-of. ,the area.
- “The specific types of grasses, legumes, and trees that .will.-be planted.on the backfilled .areas is highly dependent on the precisé type and composition of the soil on the surface'of thé'baekfill. Accordingly they cannot be designated until the' backfilling has taken place, and then must be approved by the Department of Mines and Mineral Industries (now a part of the Department' of Environmental Resources).’’