You may have heard about
the Daubert legal ruling. It is an attempt to
keep junk science out of the courtroom. The Daubert standard governs the
admissibility of expert witness testimony during all U.S. federal legal
proceedings and over half of state proceedings. It allows for the legal challenge
of any expert witness testimony. In essence, the expert scientific witness has
the burden of proof relative to the validity and acceptability of his or her
scientific conclusions. They can no
longer simply claim that they are an “expert” whose opinions and conclusions
should be accepted without proof.
An example of a
potential Daubert challenge for exposure assessors or industrial hygienists
exists in the use of first principle physical-chemical models of human
exposure. A few years ago we were
subject to a potential Daubert challenge for some modeling work conducted in
anticipation of a court case. In
preparation for this challenge we presented the relevant details of the 2-zone model relative to Daubert in a
draft affidavit for the court. We specifically
elucidated the Daubert criteria to address a potential challenge for the Near
Field/Far Field (two-zone) indoor air model of breathing zone concentration. As often happens, the case was
settled before we had an opportunity to present our arguments. We decided to summarize this work in a paper
for the benefit of other exposure assessors and Industrial Hygienists for
future cases.
My friends and
colleagues Tom Armstrong (fellow modeler) and Michael Taylor (lawyer
specializing in occupational health law) published the paper in the Journal of
Occupational and Environmental Hygiene as a commentary. If you want a PDF of this paper I will be
happy to send it to anyone requesting it of me at mjayjock@gmail.com.
The paper goes into some
considerable detail relative to the two-zone model and the model from which it
was derived, the well-mixed box model.
In the paper we present the model theory and discuss our methods, findings,
and conclusions below following four key Daubert requirements:
1. Testing of the model
2. Status of peer review and acceptance
3. The technique’s rate of error and standards for
the model’s application
4. Personal/professional experience and use of the
model.
With regard to “Testing
of the Model” we conducted a literature search from which we located and
documented multiple studies where the NF/FF technique has been appropriately
used and tested. The testing of the model actually involves several stages:
1. Correctness of the mathematical derivation
2. Implementation of the computations and
verification of the calculations
3. Testing of the model against suitable real world
air concentration data: Verification of model predictions against real world
data needs to include situations for the predicted and measured near field
concentrations.
Regarding the status of
peer review and acceptance, we found and documented multiple peer reviewed
publications on the model, coverage in two editions of the AIHA book: Mathematical
Models for Estimating Occupational Exposure to Chemicals, and coverage in
chapters in two other texts. In
addition, we provided a table that lists numerous studies in a review of the
NF/FF model included in a paper by Jennifer Sahmel et al in 2009. We also included at least 10 others published
peer reviewed journal articles using the model to successfully predict exposures
to various airborne contaminants.
The models rate of error
is actually bound up in its standards for application. Since all models are idealized portrayals of
reality they are accurate to the extent that the reality under investigation conforms with their
assumptions. Indeed, the standards for
the model’s application have been stated as the principle “bounding conditions”
for the model’s use and can be summarized from the various publications and
book chapters as follows:
• The contaminant is instantaneously mixed throughout
the near-field and far-field work space.
• There is limited airflow between the two zones.
• The random air velocity between the two zones is
uniformly distributed across the NF/FF interface surface.
• There are no significant cross drafts.
Testing the model versus
real world concentrations indicates that many scenarios reasonably
conform to the above conditions and model predictions typically come within a
factor of 0.5 to 2 fold of measured values.
This is good performance for any concentration predicting model.
The paper has all the details and as mentioned above is available to all
who ask for it.
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