In Re Armstrong World Industries, Inc.

285 B.R. 864, 60 Fed. R. Serv. 578, 2002 Bankr. LEXIS 1564, 2002 WL 31553862
CourtUnited States Bankruptcy Court, D. Delaware
DecidedOctober 22, 2002
Docket12-11546
StatusPublished
Cited by4 cases

This text of 285 B.R. 864 (In Re Armstrong World Industries, Inc.) is published on Counsel Stack Legal Research, covering United States Bankruptcy Court, D. Delaware primary law. Counsel Stack provides free access to over 12 million legal documents including statutes, case law, regulations, and constitutions.

Bluebook
In Re Armstrong World Industries, Inc., 285 B.R. 864, 60 Fed. R. Serv. 578, 2002 Bankr. LEXIS 1564, 2002 WL 31553862 (Del. 2002).

Opinion

FINDINGS OF FACT AND CONCLUSIONS OF LAW RE: MOTIONS OF THE DEBTORS AND ASBESTOS PROPERTY DAMAGE COMMITTEE TO EXCLUDE EVIDENCE

RANDALL J. NEWSOME, Bankruptcy Judge.

This chapter 11 case is before the court pursuant to motions by the debtors and the Asbestos Property Damage Committee to exclude certain evidence on the grounds that it fails to meet the standards of scientific reliability and validity mandated by Daubert v. Merrell Dow Pharmaceuticals, Inc., 509 U.S. 579, 113 S.Ct. 2786, 125 L.Ed.2d 469 (1993). The only issue before the court is whether the “indirect method” for measuring airborne asbestos expounded in American Society for Testing and Materials D5755 (“D5755”) 1 meets the Daubert test. 2 This issue arises in the context of some 600 claims for damage to buildings from the presence of asbestos-containing floor tile manufactured by debtors Armstrong World Industries, Inc. and affiliates (“AWI”).

A timed hearing was held on September 26 and 27, 2002, at which the debtors and the Asbestos Property Damage Committee (“Committee”) were each given eight hours to present evidence on this issue. Neither side used the full amount of their allotted time. Based on the evidence presented, the court hereby makes the following Findings of Fact and Conclusions of Law.

FINDINGS OF FACT

Although the evidence presented was wide-ranging and voluminous, many of the essential facts are undisputed. From the 1930’s until 1983 AWI incorporated asbestos into certain of its asphalt and vinyl floor tiles. Unlike many other asbestos-containing building products, floor tile is not considered a friable material. When properly maintained and not abused (i.e. by sanding, gouging, scraping etc.), it presents a minimal risk of asbestos release in buildings. See Exh. 21, p. 388.

The long-recognized health risks associated with exposure to asbestos have spurred the search for methods of accurately testing the amount of asbestos in the air inside buildings. It is generally agreed that the risk of harm from asbestos stems from inhaling fibers, not from how *868 much asbestos is on the surfaces of a room. Thus, the focus of testing is not on how much asbestos is present in a room or building, but upon how many respirable asbestos structures are in the air during normal activity.

Measuring airborne asbestos the amount is not an exact science. The nature of the activity in a room at any given time, airflow patterns in the room and a host of other variables can affect the test results. But it is generally recognized that the direct air sampling method for testing airborne asbestos and determining the consequent risk of harm is, in the words of Committee expert Dr. James R. Millette, “the best that we have.” Trial Transcript (“Tr.”) 580. This method is described in Method 7400, Issue 2 of the National Institute of Occupational Safety and Health’s Manual of Analytical Methods. ( Exh. M) A portable, personal sampling pump is calibrated to draw air at an appropriate rate. Attached to the pump is a hose with a filter cassette on the other end. The filter cassette is affixed to the sampler in close proximity to the face. Sampling is then performed for varying amounts of time to obtain optimum fiber loading on the filter, i.e. shorter periods in dusty atmospheres, longer periods in cleaner ones. (Exh. M, “Sampling,” Note 1)

At the end of the sampling period, the cassette is sealed and shipped to a testing laboratory. There, the filter is removed from the cassette, and a wedge is cut from it. The wedge is then “cleared,” or collapsed by applying a small quantity of acetone with a pipet, so that all of the trapped fibers are exposed. The end product is then examined with a microscope and the number of fibers counted.

Method 7400 calls for examination with an optical microscope known as a phase contrast microscope (“PCM”). Only fibers 5 p. greater are counted, and the results are reported as the number of fibers per cubic centimeter of air. A more precise count of even smaller fibers and structures can be obtained by use of a transmission electron microscope (“TEM”) using the same sampling procedure. The number of fibers per cubic centimeter of air are then calculated based on the number of liters of air tested and the number of fibers counted on the filter sample.

The indirect method described in D5755 (Exh. A) has been proposed by Dr. Millette and others as a substitute for the direct method of measuring airborne asbestos. Under this method, a 100-cubic centimeter area of flooring is vacuumed for two minutes using a nozzle made from plastic hose which is attached to a filter cassette, which in turn is attached to a vacuum pump. After the floor is vacuumed, both the nozzle and the cassette are sealed and sent to a testing laboratory. The cassette is opened, and 10 mL of a 50/50 solution of alcohol and water are poured into the cassette, which is resealed and shaken lightly for three seconds. The contents of the cassette are poured through a screen into a 200 mL sample bottle. This procedure is repeated two additional times. The nozzle is washed out with the same 50/50 solution and the contents poured into the sample bottle. Acetic acid is added to bring the contents of the sample bottle to a ph of 3 to 4. The contents of the bottle are passed through a filter and an additional 20 mL of water are added. The contents are shaken again for three seconds and allowed to settle for two minutes. The bottle is put into an ultrasonic bath and sonicated for three minutes. An aliquot of the solution is then withdrawn and deposited onto a filter.

Plugs from the wet filter are placed on a glass slide and dried in a desiccator. The plugs are then cleared and prepared for TEM analysis. All asbestos structures are *869 counted, including matrices (fibers attached to a particle of material, such as asphalt or vinyl), clusters (groupings of fibers), or fibrils (a single fiber). Exh. A, §§ 3.1.3-3.2.10. The results are reported as asbestos structures per square centimeter. By employing a statistical convention known as a K-factor, which is “[t]he ratio between the air level... and the surface loading level...” (Exh. 11 at 371), advocates of this method attempt to predict the amount of asbestos that is entrained into the air from the floor.

The parties seem to agree that the number of asbestos structures, particularly smaller fibers, found through the indirect method is almost always significantly higher than through the direct method. Tr. 532; see also Exh. B, p. 33. A number of theories have been propounded to explain this so-called positive bias. One hypothesis is that debris obscures some particles in the direct method which is cleared away in the indirect method. Exh. B, p. 34. Most theories for the increased count center on the additional steps used to prepare an indirect sample. Some studies suggest that the sonication and shaking steps break larger fibers into smaller ones, or tear apart clusters of fibers, thus exaggerating the total fiber count. Exh. KKK; Exh. b, p. 34.

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Bluebook (online)
285 B.R. 864, 60 Fed. R. Serv. 578, 2002 Bankr. LEXIS 1564, 2002 WL 31553862, Counsel Stack Legal Research, https://law.counselstack.com/opinion/in-re-armstrong-world-industries-inc-deb-2002.