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values, <strong>gas</strong> density <strong>and</strong> viscosity, hydrocarbon dew po<strong>in</strong>t, <strong>and</strong> compressibility. These analyses are<br />

essential for obta<strong>in</strong><strong>in</strong>g <strong>in</strong>formation about the composition, <strong>in</strong>clud<strong>in</strong>g contam<strong>in</strong>ants <strong>in</strong> the <strong>gas</strong> stream.<br />

Calculations based on these analyses are key to optimization of process conditions, determ<strong>in</strong>ation of<br />

adherence to contractual specifications, or estimation of GHG emissions when such a stream is<br />

combusted.<br />

The API MPMS provides specific details for collect<strong>in</strong>g <strong>and</strong> h<strong>and</strong>l<strong>in</strong>g <strong>natural</strong> <strong>gas</strong> samples for critical<br />

measurements such as custody transfer (API, February 2006). Exhibit 3-4 provides guidance on general<br />

considerations of <strong>in</strong>accuracies that might be <strong>in</strong>troduced <strong>in</strong> the measurement system when collect<strong>in</strong>g<br />

samples that are used for carbon content <strong>and</strong>/or heat<strong>in</strong>g values determ<strong>in</strong>ations for GHG emissions. At the<br />

same time, design<strong>in</strong>g a sampl<strong>in</strong>g <strong>and</strong> analysis system should – <strong>in</strong> all cases – take <strong>in</strong>to account regulatory<br />

requirements <strong>and</strong> contractual obligations.<br />

EXHIBIT 3-4: KEY FACTORS IMPACTING GAS SAMPLING AND ANALYSIS UNCERTAINTY<br />

a) Inappropriate sampl<strong>in</strong>g techniques or equipment<br />

− All sampl<strong>in</strong>g methods would require the use of a sample conta<strong>in</strong>er for transport<strong>in</strong>g the sample from the field<br />

location to the laboratory<br />

− Whenever practical, samples should be collected on a flow proportional or flow weighted basis, s<strong>in</strong>ce spot<br />

samples – by their nature – may not fully represent a <strong>gas</strong> stream of vary<strong>in</strong>g composition.<br />

− Gaseous samples of <strong>in</strong>terest are a mixture of organic <strong>and</strong> <strong>in</strong>organic <strong>gas</strong>es, <strong>and</strong> their <strong>in</strong>tegrity will be<br />

compromised.<br />

b) Inappropriate sample condition<strong>in</strong>g <strong>and</strong> h<strong>and</strong>l<strong>in</strong>g<br />

− Bias could be <strong>in</strong>troduced if any components of a sample are either depleted or augmented dur<strong>in</strong>g the<br />

sampl<strong>in</strong>g, transport, or laboratory h<strong>and</strong>l<strong>in</strong>g phases prior to analyses.<br />

− Condensation <strong>and</strong> revaporization of hydrocarbons can cause significant distortions <strong>in</strong> the <strong>gas</strong> sample.<br />

− Care should be taken to sample above the hydrocarbon dew po<strong>in</strong>t <strong>and</strong>/or to prevent retrograde condensation<br />

when pressure is reduced dur<strong>in</strong>g sampl<strong>in</strong>g.<br />

c) Collection of samples from non-representative locations <strong>and</strong>/or under non-representative operat<strong>in</strong>g<br />

conditions<br />

− Sampl<strong>in</strong>g systems that are used <strong>in</strong> conjunction with on-l<strong>in</strong>e analyzers, such as chromatographs or<br />

gravitometers, are typically designed to extract, condition, <strong>and</strong> deliver a representative sample to the analyzer.<br />

− Sampl<strong>in</strong>g l<strong>in</strong>es are kept as short as possible <strong>in</strong> conjunction with proper heat<strong>in</strong>g <strong>and</strong> <strong>in</strong>sulation to avoid<br />

condensation.<br />

− The flow rate of the sampl<strong>in</strong>g system is adjusted to allow for close to real time data, while at the same time<br />

not <strong>in</strong>creas<strong>in</strong>g the flow to a level that might lead to turbulence.<br />

d) Inappropriate analytical methods<br />

− The threshold sensitivity of the analytical methods used are typically those that are well documented by<br />

<strong>in</strong>dustry recommended practices for sample families<br />

− Analyses are typically limited to the range of mixture concentrations <strong>and</strong> species previously identified<br />

− For complicated sample matrices, the potential for <strong>in</strong>terferences is usually noted.<br />

Pilot Version, September 2009 3-14

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