Erekson v. United States Steel Corp.

260 F.2d 423, 1958 U.S. App. LEXIS 3110
CourtCourt of Appeals for the Tenth Circuit
DecidedSeptember 26, 1958
DocketNos. 5811-5816
StatusPublished
Cited by4 cases

This text of 260 F.2d 423 (Erekson v. United States Steel Corp.) is published on Counsel Stack Legal Research, covering Court of Appeals for the Tenth Circuit primary law. Counsel Stack provides free access to over 12 million legal documents including statutes, case law, regulations, and constitutions.

Bluebook
Erekson v. United States Steel Corp., 260 F.2d 423, 1958 U.S. App. LEXIS 3110 (10th Cir. 1958).

Opinion

MURRAH, Circuit Judge.

These consolidated cases involve claims for damages to livestock in Salt Lake and Utah Counties, Utah, allegedly caused by the emission of gaseous and miniscular [424]*424particles of fluorine from the United States Steel furnaces at Geneva, Utah. The three hundred claims of livestock owners involving common questions of law and similar facts, were grouped into these cases and others unappealed.

Each of the claims charged that since 1950, the appellee had knowingly permitted large quantities of fluorine gases to be emitted from its Geneva plant; that these gases, borne by prevailing winds, contaminated the vegetation growing upon the respective appellants’ land; and that such vegetation was consumed by the livestock in sufficient quantities to cause a disease called fluorosis, with subsequent physical damage to all of the livestock and milk loss from the dairy cattle. Injunctive relief against the operation of the plant was originally sought, but during the pendency, of the litigation, corrective measures reduced the rate of fluorine emission to the point of admittedly harmless result. Injunc-tive relief was thereupon abandoned, but each of the separate claims for damages state the jurisdictional amount in controversy and requisite diversity of citizenship.

Issues having been joined on liability and extent of damage, if any, the trial court sitting without a jury heard 260 witnesses, including the claimants and experts for both the plaintiff-appellants and appellee-defendant. Reports of some 100,000 chemical analyses of vegetation for fluorine, and diagnoses of about 12,-000 cattle and thousands of sheep were received in evidence.

At the conclusion of all the evidence, the trial court by agreement of the parties appointed a medical doctor and former Dean of the University of Utah School of Medicine, as a neutral expert and referee, to “marshal the evidence [from 6,622 pages of testimony and 1,-267 exhibits], discuss it with counsel, case by case and cow by cow, hear them out and report his findings to the court.” And, thereafter, as the court stated, “counsel presented ‘brochures’ containing 10,000 pages summarizing the evidence for the referee, setting forth their respective views supported by extensive briefs and months of oral argument.” The referee’s report in the several cases, consisting of 347 pages, was adopted and incorporated by the trial court in its extensive opinion, in which it directed the entry of judgment generally for the defendant, but granted recovery to some of the claimants in varying amounts. At the same time, the court entered findings of fact in substantial conformity to the referee’s recommendations, which findings, together with conclusions of law were in accordance with those previously suggested by the appellee.

From the scientific proof, the referee found, and the appellee concedes, that during the years complained of, potentially harmful quantities of fluorine gases did emanate from the appellee’s Geneva plant; that it did fall upon the appellants’ lands and vegetation in varying quantities; and that such vegetation was consumed by the appellants’ livestock. And, the appellee further concedes its legal liability for any substantial harm caused thereby. And see Reynolds Metals Co. v. Yturbide, 9 Cir., 258 F.2d 321; E. Rauh & Sons Fertilizer Co. v. Shreffler, 6 Cir., 139 F.2d 38; Anderson v. American Smelting & Refining Co., D.C., 265 F. 928.

Based upon controlled experiments and other scientific analysis, the referee established a “tolerance level” below which the ingestion of fluorine by livestock was found to be harmless and above which there was a possibility, and then a probability of harm. Specifically, the referee and the trial court found that, with respect to cattle, continued ingestion at the rate of 30 parts fluorine per million parts total intake was below the tolerance level; that 30 to 50 ppm created a possibility of harm; and, levels above 50 ppm, injury was probable. The critical level of continued fluorine intake for sheep was found to be 70 ppm. From evidence of scientific forage sampling and atmospheric tests, the referee suggested, and the trial court found, that in a number of areas involved, fluorine in forage reached the border line level of [425]*425harmful concentrations. And, it was therefore necessary to consider the available data relating to specific levels of exposure in connection with the claims of each claimant.

In addition to the forage exposure levels, the scientific proof developed reliable diagnostic aids in determining the damaging effects of fluorine intake on livestock. The first, and most sensitive, is condition of teeth erupting during exposure. The teeth were generally classified as numbers 0 to 5, and it seems to be generally agreed that the teeth classified as 1, 2 and 3 do not indicate any harmful effects, while teeth classified 4 and 5 indicate some fluorine injury. Second, the fluorine content of the hones, which may gradually build up during periods of excessive fluorine ingestion, with symptoms of fluorosis appearing at levels of 4000 to 5000 parts fluorine per million content. Third, urinalysis with 5 ppm as the normal level and 10 ppm as an elevated fluorine systemic content, and consistent levels above 25 ppm suggesting definite fluorosis.1 Fourth, clinical symptoms, such as lameness, poor nutrition, small stature, rough hair coat, tight skin, loss of milk production, lapping of water, and reproductive difficulties. These clinical conditions are generally considered secondary or non-specific evidence of systemic fluorosis. And, it is generally conceded such conditions may arise from other and independent causes. Though it seems to be well established that none of the diagnostic aids are in and of themselves conclusive2, the parties apparently accept these combined factors as standards for the determination of fluorine injury to livestock. Indeed, the burden of the appellants’ contention on appeal is that the referee and the trial court utterly failed to apply these accepted standards in determining' damage to the livestock of the respective claimants. We look, therefore, to the referee’s consideration of livestock injury in the respective herds of each group of cases to determine whether his report and the findings of the court thereon are compatible with these standards and substantially supported by the record. In consideration of this decisive issue, it seems almost superfluous for us. to reiterate the time-honored and oft repeated canon for the interpretation of Rule 52, F.R.C.P., 28 U.S.C.A., to the effect that in determining whether the judgment of the trial court is reversibly erroneous, we will not weigh the evidence or judge the credibility of witnesses. The appellate function is to determine whether the challenged judgment finds support in the facts and warrant in the law — in sum, whether there is a rational basis for what the trial court did. See United States v. Oregon State Medical Society, 343 U.S. 326, 72 S.Ct. 690, 96 L.Ed. 978; Skinner v. Parnell, 10 Cir., 257 F.2d 345; Fuller v. C. M. & W. Drilling Co., 10 Cir., 243 F.2d 862

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Bluebook (online)
260 F.2d 423, 1958 U.S. App. LEXIS 3110, Counsel Stack Legal Research, https://law.counselstack.com/opinion/erekson-v-united-states-steel-corp-ca10-1958.