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addressing uncertainty in oil and natural gas industry greenhouse

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when plann<strong>in</strong>g the compilation of an emissions <strong>in</strong>ventory <strong>and</strong> could address as part of emission <strong>in</strong>ventory<br />

assurance processes (API/IPIECA, OGP, 2003).<br />

Adher<strong>in</strong>g to appropriate sampl<strong>in</strong>g, measurement, <strong>and</strong> estimation procedures – with applicable quality<br />

control <strong>and</strong> quality assurance measures – can help m<strong>in</strong>imize uncerta<strong>in</strong>ties. Nonetheless, it is the nature of<br />

the measurement process that makes it impossible to measure a physical quantity without error.<br />

It is this collection of measurement errors <strong>and</strong> approximations that contribute largely to overall emission<br />

<strong>in</strong>ventory range of <strong>uncerta<strong>in</strong>ty</strong>. Emission <strong>in</strong>ventory development <strong>and</strong> <strong>uncerta<strong>in</strong>ty</strong> analysis could be<br />

viewed as components of a quality improved management process. Once estimates of <strong>uncerta<strong>in</strong>ty</strong> are<br />

developed, the <strong>in</strong>ventory preparer could review the <strong>in</strong>ventory <strong>and</strong> target the most significant sources –<br />

those exhibit<strong>in</strong>g the largest range of <strong>uncerta<strong>in</strong>ty</strong> – for more research <strong>and</strong> ref<strong>in</strong>ement. Table 2-1 provides<br />

an overview of selected methods recommended by the U.S. Environmental Protection Agency (EPA) for<br />

qualitative <strong>and</strong> quantitative estimation of emissions ranges of <strong>uncerta<strong>in</strong>ty</strong>. The uncerta<strong>in</strong>ties associated<br />

with <strong>natural</strong> variability <strong>in</strong>herent to the emission process <strong>and</strong> its underly<strong>in</strong>g data can be assessed by<br />

statistical analysis methods. Further discussion <strong>and</strong> specific procedures for statistical quantification of<br />

<strong>uncerta<strong>in</strong>ty</strong> <strong>in</strong>tervals are provided <strong>in</strong> Section 4.0.<br />

Table 2-1. Overview of Methods Used to Estimate Emissions Uncerta<strong>in</strong>ty a<br />

METHODOLOGY<br />

Qualitative<br />

Discussion<br />

−<br />

−<br />

DESCRIPTION OF METHOD<br />

Sources of <strong>uncerta<strong>in</strong>ty</strong> are listed <strong>and</strong> discussed.<br />

General direction of bias <strong>and</strong> relative magnitude of imprecision are given<br />

if known.<br />

LEVEL OF<br />

EFFORT<br />

Low<br />

Subjective Data<br />

Quality Rat<strong>in</strong>gs<br />

−<br />

Subjective rank<strong>in</strong>gs based on professional judgment are assigned to each<br />

emission factor or parameter.<br />

Low<br />

Data Attribute<br />

Rat<strong>in</strong>g System<br />

(DARS)<br />

−<br />

Numerical values represent<strong>in</strong>g relative <strong>uncerta<strong>in</strong>ty</strong> are assigned through<br />

objective methods.<br />

Medium<br />

Expert<br />

Estimation<br />

Method<br />

−<br />

−<br />

−<br />

Experts estimate emission distribution parameters (i.e., mean, st<strong>and</strong>ard<br />

deviation, <strong>and</strong> distribution type).<br />

Simple analytical <strong>and</strong> graphical techniques are then used to estimate<br />

confidence limits from the assumed distributional data.<br />

In the Delphi method, expert judgment is used to estimate <strong>uncerta<strong>in</strong>ty</strong><br />

directly.<br />

Medium<br />

Pilot Version, September 2009 2-2

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