Joy Technologies, Inc. v. Flakt, Inc.

954 F. Supp. 796, 42 U.S.P.Q. 2d (BNA) 1042, 1996 U.S. Dist. LEXIS 20879, 1996 WL 756758
CourtDistrict Court, D. Delaware
DecidedMarch 30, 1996
DocketCivil Action 89-533-JJF
StatusPublished
Cited by7 cases

This text of 954 F. Supp. 796 (Joy Technologies, Inc. v. Flakt, Inc.) is published on Counsel Stack Legal Research, covering District Court, D. Delaware primary law. Counsel Stack provides free access to over 12 million legal documents including statutes, case law, regulations, and constitutions.

Bluebook
Joy Technologies, Inc. v. Flakt, Inc., 954 F. Supp. 796, 42 U.S.P.Q. 2d (BNA) 1042, 1996 U.S. Dist. LEXIS 20879, 1996 WL 756758 (D. Del. 1996).

Opinion

MEMORANDUM OPINION

FARNAN, Chief Judge.

The court held a bench trial in this matter on the issue of damages and, at the close of the evidence, the parties were given an opportunity to submit post trial briefing. The Court has considered and weighed the evidence adduced at the damages trial and reviewed the post trial submissions. This Memorandum Opinion shall constitute the Court’s Findings of Fact and Conclusions of Law.

I. BACKGROUND

A Procedural History

In 1989, Plaintiff Joy Technology Inc. (“Joy”) sued Flakt Inc. (“Flakt”) for infringement of United States Patent No. 4,279,873, entitled Process for Flue Gas Desulfurization (“the ’873 patent”). In 1991, Niro A/S (“Niro”) was joined as an involuntary Plaintiff. The case was bifurcated into liability and damages phases, and in December 1991 through January 1992 the liability issues were tried to a jury. On January 24, 1992, the jury returned a verdict in favor of Plaintiffs and against Defendant on the issue of infringement, and the Court entered judgment on the jury’s verdict by Order dated February 3,1992.

Subsequently, the Court denied Flakt’s Post Trial Motions for Judgment As A Matter Of Law and for a New Trial. See Joy Technologies Inc. v. Flakt Inc., 820 F.Supp. 802 (D.Del.1993). Flakt appealed the liability determination to the United States Court of Appeals for the Federal Circuit which affirmed the decision in favor of the Plaintiffs.

B. Flue Gas Desulfurization Technology

In 1982, Joy and Flakt were competing bidders for contracts to be let by the Grand River Dam Authority (“GRDA”) for a flue gas desulfurization (“FGD”) system for use in connection with a coal-burning electric power generation plant it had decided to build, known as Unit No. 2. The GRDA was created by state statute in 1935 to provide wholesale electric power to Northeastern Oklahoma. (Plaintiff Damages Trial Exhibits, Vol. 12, Px 711, p. JO 9462). GRDA undertook to build two thermal generating units, GRDA1 and GRDA2, with a combined output of 1,010,00 kilowatts. (Id. at JO 94655). GRDA1 and 2 were designed to meet the Environmental Protection Agency’s (EPA) rigid emissions standards and to be compatible with the environment. 1 Id. As *799 such, the plants are equipped with a scrubber device used to clean the sulfur-laden flue gas before the gas enters the atmosphere. Id.

In 1982, when Joy and Flakt were competitively bidding for the GRDA contracts, essentially three types of FGD processes were available to remove sulfur dioxide from coal: 1) a wet scrubbing process, 2) a dry scrubbing, single pass process and 3) a dry scrubbing process with recycle. Plaintiffs expert, Mr. Karsten Felsvang, a chemical engineer specializing in the field of spray drying and particularly the use of spray drying for air pollution control, identified several important characteristics used to determine which FGD process to use at a particular site. (Trial Transcript, Felsvang, Vol. 1, p. 11). These characteristics include “the sulfur content of the coal, the availability of lime and other reagents at the location and also the disposal problems associated with that location”. Id. As a general principle, Mr. Felsvang testified that “wet FGD systems are more suitable for the higher sulfur coals”. (Id.; Trial Transcript, Neuscheler, Vol. 2, p. 358).

The primary difference between the two types of dry scrubbing processes is the amount of lime needed to run each process. (Trial Transcript, Felsvang, Vol. 1, p. 15). A single pass process consists of mixing the flue gas with a lime slurry. The lime slurry is sprayed into the flue gas where the lime reacts with the sulfur dioxide, removing the sulfur dioxide from the gas. The desulfurizied gas consisting of fly ash, unreacted lime and other material is" then emitted into the atmosphere. The process is referred to as “single pass” because the lime slurry is used once and unreacted lime is not recaptured and reused. Conversely, a recycle process attempts to conserve the amount of lime used by continually recycling the unreacted lime in the fly ash back into the lime slurry. Consequently, recycle processes tend to require less lime and can be more cost effective. (Trial Transcript, Felsvang, Vol. 1, pp. 14-19).

For a plant the siz:e of GRDA, Mr. Felsvang stated that a single pass system would be more costly than a recycle system because it would use approximately three times more lime. Id. at 15. Mr. Felsvang also testified that a recycle system is more cost effective with respect to capital and electrical power consumption than a single pass system. However, he conceded that these costs were relatively insignificant compared to the cost of lime. Id. at 15. Moreover, Mr. Felsvang admitted that some single pass systems are less costly than some recycle processes. (Trial Transcript, Felsvang, Vol. 1, pp. 111-13,127).

C. The GRDA Specification

The GRDA bid preferred a recycle process in which “recycle material (consisting of fly ash, unreacted lime, calcium sulfite and calcium sulfate) ... [is] added to the slurry mixture to reduce lime consumption.” (Defendant Exhibit 1065 at 2t42). However, Mr. Robert Morford, Joy’s Senior Vice President of Business Development, testified that although the GRDA bid specification contained several references to recycle, he believed that the bid left an option for single pass process bids as well. (Trial Transcript, Morford, Vol. 1, p. 157). GRDA also provided its bidders with a comprehensive specification for the air quality control system to be used at GRDA1 and 2. (See Defendant’s Exhibit 1065). Benham-Hollway (BH), the architectural and engineering company hired by GRDA who wrote the specification for the FGD system, stated in the specification that:

“Designing, furnishing, delivering, storing, erecting and start up of a complete air quality control (AQC) system consisting of, but not limited to, a lime spray dryer scrubber; electrostatic precipitator; fly ash handling; lime unloading, storage, handling and preparation; interconnecting flue gas duct work; a complete stack monitoring system for EPA compliance; and all related auxiliary systems and structures”. (Defendant Exhibit 1065 at 2-1).

The BH specification also identifies the detailed functional requirements for the dry scrubbing particulate removal system. (De *800 fendant Exhibit 1065 at 2-32 — 2-50). The BH specification references a system which “shall include all necessary equipment for preparing and supplying the reagent slurry to the rotary spray atomizers in the scrubber modules ... recycle material (consisting of fly ash, unreaeted lime, calcium sulfite, and calcium sulfate) may as an option be added to the slurry mixture to reduce lime consumption. (Defendant Exhibit 1065, p. 2-42 — 2—43). (Emphasis added). The specification further provides that “solids collected in the absorber modules and the precipitator may be recycled to the slurry as required to minimize lime consumption while maintaining required S02 and particulate removal. The recycle system

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954 F. Supp. 796, 42 U.S.P.Q. 2d (BNA) 1042, 1996 U.S. Dist. LEXIS 20879, 1996 WL 756758, Counsel Stack Legal Research, https://law.counselstack.com/opinion/joy-technologies-inc-v-flakt-inc-ded-1996.