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addressing uncertainty in oil and natural gas industry greenhouse

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As was shown <strong>in</strong> Table 5-8, emissions from b<strong>oil</strong>ers/heaters, <strong>natural</strong> <strong>gas</strong> eng<strong>in</strong>es <strong>and</strong> flares are ranked <strong>in</strong> the<br />

top ten highest emission sources, with one source, emergency flare, contribut<strong>in</strong>g about 62% of the total.<br />

Uncerta<strong>in</strong>ty associated with the emergency flare was calculated to be 21.1%, or about ±6,500 tonnes CO 2 e/yr.<br />

By exam<strong>in</strong><strong>in</strong>g the calculations used for flar<strong>in</strong>g, the follow<strong>in</strong>g general strategies could be selected by the<br />

operat<strong>in</strong>g company to reduce <strong>uncerta<strong>in</strong>ty</strong> <strong>in</strong> flar<strong>in</strong>g:<br />

• Ref<strong>in</strong>e the measurement of total <strong>gas</strong> flared (the activity factor), to reduce the activity factor<br />

<strong>uncerta<strong>in</strong>ty</strong> from the current value of 15% <strong>and</strong>/or;<br />

• Ref<strong>in</strong>e the <strong>gas</strong> composition measurements to reduce the <strong>uncerta<strong>in</strong>ty</strong> from 4%.<br />

Ref<strong>in</strong><strong>in</strong>g the measurement of total <strong>gas</strong> flared may result from many approaches, such as improv<strong>in</strong>g the meter<br />

quality (even possibly replac<strong>in</strong>g the meter), improv<strong>in</strong>g the quality control of the exist<strong>in</strong>g meter (such as<br />

number of calibrations <strong>and</strong> <strong>in</strong>spections), or improv<strong>in</strong>g the number of measurements taken <strong>and</strong> recorded from<br />

the meter that is used to calculate the total <strong>gas</strong> flared (this assumes measurements were not already<br />

cont<strong>in</strong>uous). These approaches have vary<strong>in</strong>g costs, <strong>and</strong> some may be cost-prohibitive. The company would<br />

have to determ<strong>in</strong>e which approach was the most cost effective.<br />

Ref<strong>in</strong><strong>in</strong>g the <strong>gas</strong> composition data may also come from several methods, such as tak<strong>in</strong>g additional rout<strong>in</strong>e<br />

samples, <strong>in</strong>stall<strong>in</strong>g a cont<strong>in</strong>uous <strong>gas</strong> analyzer, or us<strong>in</strong>g a better analysis method. As with the <strong>gas</strong> flow rate<br />

measurement, these approaches have vary<strong>in</strong>g costs, <strong>and</strong> some may be cost-prohibitive. The company would<br />

have to determ<strong>in</strong>e which approach was the most cost effective.<br />

If the company was effective <strong>in</strong> reduc<strong>in</strong>g the <strong>uncerta<strong>in</strong>ty</strong> <strong>in</strong> flare <strong>gas</strong> CO 2 emissions, it might then elect to<br />

proceed to the next largest CO 2 <strong>uncerta<strong>in</strong>ty</strong> source. The end-user will have to recalculate total emissions for<br />

the company or facility each time, <strong>and</strong> determ<strong>in</strong>e if the <strong>uncerta<strong>in</strong>ty</strong> goal or target has been reached.<br />

Reduction of Uncerta<strong>in</strong>ty <strong>in</strong> Vented CO 2 Sources<br />

If the company decided to take the next step of emission reductions, it may target the next largest category of<br />

<strong>uncerta<strong>in</strong>ty</strong>, which is vented CO 2 sources. Vented CO 2 emissions result from seven sources listed <strong>in</strong><br />

Table F-15. The am<strong>in</strong>e unit accounts for the over 98% of the emissions <strong>in</strong> this category.<br />

Am<strong>in</strong>e unit CO 2 vented emissions have an <strong>uncerta<strong>in</strong>ty</strong> of 4,360 tonnes of CO 2 e <strong>in</strong> a category that only has an<br />

<strong>uncerta<strong>in</strong>ty</strong> of 4,420 tonnes of CO 2 e. Therefore any <strong>uncerta<strong>in</strong>ty</strong> reduction efforts <strong>in</strong> this area should be<br />

directed at the am<strong>in</strong>e unit calculations. However, the calculations used for the am<strong>in</strong>e units reveal that the<br />

<strong>uncerta<strong>in</strong>ty</strong> is actually relatively low. The <strong>uncerta<strong>in</strong>ty</strong> <strong>in</strong> that emission category is less than 7%. It is possible<br />

to reduce this <strong>uncerta<strong>in</strong>ty</strong> by improv<strong>in</strong>g the uncerta<strong>in</strong>ties for <strong>gas</strong> composition, <strong>and</strong> <strong>gas</strong> throughput. While it is<br />

possible to reduce this <strong>uncerta<strong>in</strong>ty</strong>, given the low percentage level of the <strong>uncerta<strong>in</strong>ty</strong>, any improvement may<br />

be small. Therefore this is likely a case where company efforts are best spent on the previous categories.<br />

Pilot Version, September 2009 5-23

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