Tuley v. Kansas City Power & Light Co.

843 P.2d 248, 252 Kan. 205, 1992 Kan. LEXIS 198
CourtSupreme Court of Kansas
DecidedDecember 11, 1992
Docket67,445
StatusPublished
Cited by14 cases

This text of 843 P.2d 248 (Tuley v. Kansas City Power & Light Co.) is published on Counsel Stack Legal Research, covering Supreme Court of Kansas primary law. Counsel Stack provides free access to over 12 million legal documents including statutes, case law, regulations, and constitutions.

Bluebook
Tuley v. Kansas City Power & Light Co., 843 P.2d 248, 252 Kan. 205, 1992 Kan. LEXIS 198 (kan 1992).

Opinion

The opinion of the court was delivered by

Abbott, J.:

This is an appeal from the trial court’s grant of summary judgment in favor of Kansas City Power & Light Company (KCPL). This is a class action negligence suit on behalf of current and former employees of KCPL, alleging property damage to their vehicles because of exposure to acidic particulate emissions (acid rain) from the plant. The plaintiffs also appeal from the trial court’s denial of class certification to the plaintiffs’ spouses.

KCPL is a public utility that owns and operates the LaCygne Generating Station, a two-unit coal-fired electric generation facility located near LaCygne, Kansas, in Linn County. -

To generate electric energy, both units at the LaCygne plant bum coal as fuel. To remove a percentage of the particulates, including fly ash, sulphur dioxide (SOa), and sulphur trioxide (S03), from the combustion gases emitted from the boiler and discharged into the stack, Unit No. 1 employs a limestone wet slurry scrubber, which uses a mixture of water and ground limestone. Unit No. 2 employs an electrostatic precipitator to remove a percentage of the particulates (fly ash) from the combustion gases emitted from the boiler and discharged into the stack. No pollution control equipment is used to remove sulphur compounds from the combustion gases in Unit No. 2 because a better grade of coal with a low sulphur content was burned. Unit No. 1 bums a lower grade of coal and has design features and prob *207 lems unique to it. When combined with water, S02 forms sulphurous acid and S03 forms sulphuric acid. These acids corrode the exterior surfaces of vehicles.

The substances emitted from the stacks of the two units are governed by federal and state air quality control laws. Congress enacted the Clean Air Act to regulate and control air pollution. The Act enables the Environmental Protection Agency (EPA) to identify air pollutants posing a hazard to public health and welfare and to promulgate the National Ambient Air Quality Standards (NAAQS) for those pollutants. Such a standard has been promulgated for S02. To comply with the NAAQS, Kansas has developed a State Implementation Plan (SIP), which the EPA has approved. K.A.R. 28-19-31(C), part of the Kansas SIP, provides:

“A person responsible for operation of any indirect heating equipment having a heat input of 250 million BTU/hr or greater shall not cause or permit the emission or more than 1.5 pounds of sulfur per million BTU of heat input per hour.”

Both parties agree this regulation governs the emissions from Unit No. 1, which has indirect heating equipment with a heat input of 250 million BTU/hr or greater.

In August 1977, KCPL hired Bums & McDonnell to conduct emissions tests. Bums & McDonnell reported that Unit No. 1 was emitting less than the legal limit, which is three pounds of S02 per million BTU. The record is not clear how the “1.5 pounds of sulfur per million BTU of heat input per hour” language of K.A.R. 28-19-31(C) translates into the “three pounds of S02 per million BTU” that the parties agree is the legal limit.

In 1987, Bums & McDonnell again conducted emissions tests at the request of KCPL. On June 24, 1987, the tests performed reflected S02 emissions of 3.12, 3.71, 3.65, and 5.68 pounds per million BTUs. The average test ran was 3.49. In December 1987, two of the seven tests performed were under the three-pound limit, reflecting S02 emissions of 2.98 and 2.89 pounds per million BTU. The other five tests performed were above the three-pound limit. KCPL did not inform employees of any of the 1987 test results.

In December 1975, at the LaCygne Generating Station, KCPL posted written notices disclaiming responsibility for damage to vehicles.

*208 The notice read:

“NOTICE TO ALL EMPLOYEES OF KANSAS CITY POWER & LIGHT COMPANY ....
Within the past several weeks, Kansas City Power & Light Company has received numerous damage claims by insurance companies which have paid losses to their insureds for damage to motor vehicle finishes allegedly the result of stack emissions. These claims have all been denied by the Company due to the fact that stack emissions are a normal result of day-to-day operations and are not the result of any negligent activity by the Company or its employees.
PLEASE BE ADVISED THAT THE COMPANY WILL CONTINUE TO DENY THESE TYPES OF CLAIMS, AND THAT PARKING YOUR MOTOR VEHICLE AT OR NEAR THE PLANT SITE IS AT YOUR RISK.”

James A. Tuley, who filed the original petition, denied ever seeing or being aware of this notice.

In February 1976, KCPL erected a permanent outdoor sign that reads as follows:

“NOTICE TO PARKING LOT USERS - AIRBORNE MATERIALS FROM CONSTRUCTION ACTIVITIES AND FROM INTERMITTENT STACK EMISSIONS MAY CAUSE DAMAGE TO VEHICLES - USE OF THIS LOT IS AT YOUR OWN RISK.”

The sign is eight by four feet with the top of the sign eight feet above the ground. The sign is located 1,136 feet from the main gate and 851 feet from the entrance to the parking shelter. Tuley and Angela Hatfield, the plaintiffs representing the class, admitted to reading the sign and being aware of its warning.

Beginning in 1978, KCPL constructed four separate covered parking lots to provide parking for its employees. After these four lots were constructed, there were no major incidents involving paint damage to employees’ vehicles parked at the LaCygne plant until 1987. That does not mean there was no damage. The record shows there was damage to at least some vehicles. In fact, Tuley testified he had been an employee of KCPL for 18 years and that “[ejvery vehicle [he has] ever owned and driven in the power plant has been damaged.”

From December 1987 to February 1988, Unit No. 1 operated with severe problems. The unit’s steam generator and AQC system were designed to bum coal containing a higher thermal content and a significantly lower ash and sulphur content than the coal actually burned from 1987 to 1989. The change in coal *209 quality had a negative effect on the performance of the unit’s steam generator and AQC system. The type of emissions released by a unit depends upon the quality of the coal burned. In 1977, because of historically poor coal quality, KCPL had agreed to adjust the contract with the coal supplier and accept coal with a lower thermal content and a higher ash content. By or before the spring of 1988, KCPL concluded Unit No. 1 could not comply with the air quality control regulation on SOz emissions because of the type of coal being burned in the unit. KCPL did not inform the plaintiffs that it was in violation of and could not comply with the applicable air quality control standards.

It is undisputed that the risk of particulate emission damage to employees’ vehicles, which were parked in the parking lot KCPL provided, was increased because KCPL did not comply with the air quality control standards, particularly the regulation limiting SOz emissions.

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Bluebook (online)
843 P.2d 248, 252 Kan. 205, 1992 Kan. LEXIS 198, Counsel Stack Legal Research, https://law.counselstack.com/opinion/tuley-v-kansas-city-power-light-co-kan-1992.