Ridenour v. Furness

546 N.E.2d 322, 1989 Ind. App. LEXIS 1160, 1989 WL 139770
CourtIndiana Court of Appeals
DecidedNovember 21, 1989
Docket06A01-8903-CV-76
StatusPublished
Cited by12 cases

This text of 546 N.E.2d 322 (Ridenour v. Furness) is published on Counsel Stack Legal Research, covering Indiana Court of Appeals primary law. Counsel Stack provides free access to over 12 million legal documents including statutes, case law, regulations, and constitutions.

Bluebook
Ridenour v. Furness, 546 N.E.2d 322, 1989 Ind. App. LEXIS 1160, 1989 WL 139770 (Ind. Ct. App. 1989).

Opinion

BAKER, Judge.

STATEMENT OF THE CASE

Defendant-appellant, James M. Ridenour, Director of the Indiana Department of Natural Resources (the DNR), appeals from a judgment entered on its action to recover the damages sustained from an injunction erroneously imposed in favor of plaintiff-appellees, Clay, Chris and Jeff Furness, Mike Brzinski, Chris Camalick, Clem Cho, Bill Dickerson, John Hart, Lance Kaeding, Howard Westerman, Phil Smidt, Harold Buey, and Tom Mayoch (the fishermen).

We reverse and remand.

STATEMENT OF THE FACTS

For over two decades, the DNR has been actively involved in enhancing and protect *324 ing the ecology of Lake Michigan. Of the many measures instituted in that regard, the DNR commenced operation of a program which raises various types of fish, including chinook salmon and lake trout, to be stocked in the Indiana waters of Lake Michigan. The purpose of the stocking program is to introduce a new species of fish that will, in time, adapt to the ecosystem and regenerate itself. Chinook salmon are stocked in various Indiana tributaries normally in the spring of the year at which point they are 372 inches long. The salmon are released for stocking at this size because it is at this time that they are in smolt. Smolting is that stage of the fish’s life cycle at which it receives a biological imprint of its place of stocking to which it will return to spawn at the end of its life cycle. The natural mortality rate of the stocking effort ranges as high as 30% of the fish released and is incurred within the first three to four months of stocking. The fish that survive are approximately 9 to 14 inches in length by the following September and October. By the time the individuals of the stocking program achieve this size, mortality is drastically reduced and it is highly likely that they will survive to spawning. Thus, salmon of this size are of great significance to the stocking program.

Another protection effort taken in coordination with the stocking program, involved a monitoring program of the commercial fishing industry on Lake Michigan. The monitoring program was conducted in order to ascertain the effect of gill net fishing on the population of various species of protected sport fish including chinook salmon and lake trout. Gill fishing nets are commonly deployed by commercial fishermen in order to catch perch fish. A gill net also incidentally catches a variety of other fish as well, however. Following several years of study, DNR fisheries biologists concluded that immature chinook salmon and lake trout dominated the catch of fish incidentally caught and destroyed in the gill nets utilized by commercial perch fishermen. As a result of the monitoring studies, the DNR promulgated an emergency order on August 22, 1986, temporarily banning the use of gill fishing nets by commercial fishermen for a 47-day period from September 15 to October 31, 1986. The stated purpose of the ban was to prevent the incidental catch of salmon and trout by commercial fishermen using gill nets.

In response, the fishermen filed suit in Marion Circuit Court seeking to enjoin the DNR from enforcing the emergency order. The fishermen also moved for a temporary restraining order. Following a hearing on the motion for a temporary restraining order, the Marion Circuit Court, on September 12, 1986, enjoined the DNR’s enforcement of the gill net ban. Upon stipulation by the parties, the cause was venued to the Boone Circuit Court which subsequently denied the DNR’s motion to dissolve the preliminary injunction. On appeal, the Indiana Court of Appeals reversed the preliminary injunction entered against the DNR. Ridenour v. Furness (1987), Ind.App., 504 N.E.2d 336. That decision was subsequently approved by the Supreme Court of Indiana on transfer. Ridenour v. Furness (1987), Ind., 514 N.E.2d 273.

The DNR then returned to the trial court seeking to recover damages it suffered because of the erroneous injunction. Specifically, the DNR sought damages for the value of the salmon and trout incidentally caught and destroyed by those fishermen who continued to fish with gill nets during the period of the erroneous injunction. Additionally, the DNR sought as damages the amount of profits on the harvest of perch fish earned by the fishermen while under the protection of the injunction. Thereafter, the fishermen filed a motion for partial summary judgment on the perch profit element of damages sought by the DNR. Following a hearing on the motion, the trial court granted the partial summary judgment.

The cause then proceeded to trial on the issue of the damages sustained from the incidental catch of the protected sport fish. DNR fisheries biologist, Dan Brazo (Bra-zo), testified on behalf of the DNR. Brazo explained that the DNR conducted a monitoring study of the perch harvest and the incidental catch of sport fish in gill nets at the start of the 1986 calendar year before *325 the gill net ban was challenged. During the year, 81 monitoring trips were made, 29 of which were conducted from September 15 through October 31. The study culminated in a report which documented the number of fish and species monitored. Brazo estimated that a total of 6,044 salmon and trout were incidentally caught in gill nets during the period in question. The study also documented the size of each species of fish incidentally caught during the period. On this basis, Brazo determined that the salmon and trout incidentally caught in the gill nets ranged from 9 to 16 inches in length. Brazo also concluded that chinook salmon were juvenile and primarily from the 1986 stocking effort.

The DNR determined to assign a value for the various species of sport fish incidentally caught according to the individual size or weight of the fish as set forth in the American Fisheries Society (AFS), Pub. No. 13. Upon this basis, Brazo testified that the total value for the 6,044 salmon and trout incidentally caught to be $21,383.58. On the other hand, the fishermen argued during their case-in-chief that the DNR’s actual hatchery production cost of producing a 3 ¥2 inch fingerling fish was the appropriate method for assessing the damages incurred by the DNR. The fishermen produced evidence establishing that the DNR’s hatchery production costs for the fish varied between $.09 and $.57 per fish depending upon the species of fish raised. As an alternative method of assessing damages, fishermen, Mayoch and Buey, offered into evidence a contract between the state of Michigan and a private contractor accompanied by a cover letter from an official with the Michigan Department of Natural Resources. That letter explained that Michigan valued maturing salmon at $1 to $3 per pound and permitted a liquidated damage value of the greater of $10 per fish or $10 per pound. In its findings of fact and conclusions of law, the trial court accepted the actual hatchery production cost theory of damages, but permitted allowance for a 50% mortality rate between the time of stocking and the time of the incidental catch. On this basis the trial court assessed damages in favor of the DNR in the amount of $1,906.16. The DNR subsequently instituted this appeal.

ISSUES

The DNR raises the following issues for our review:

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Cite This Page — Counsel Stack

Bluebook (online)
546 N.E.2d 322, 1989 Ind. App. LEXIS 1160, 1989 WL 139770, Counsel Stack Legal Research, https://law.counselstack.com/opinion/ridenour-v-furness-indctapp-1989.