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NOx Emissions Impacts from Widespread Deployment of CHP in ...

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Table 3-4: Ten <strong>CHP</strong> Prototypes and Frequency (by Prime Move Size)<br />

<strong>NOx</strong> <strong>Emissions</strong> Report<br />

Recip Eng<strong>in</strong>e GT*<br />

GT<br />

Prototype Capacity Microturb<strong>in</strong>e (rich burn) (no duct burner) (duct burner)<br />

0.1 MW 100% - - -<br />

0.5 MW 50% 50% - -<br />

2.0 MW - 50% 50% -<br />

10.0 MW - 10% 40% 50%<br />

100 MW<br />

* GT = Gas Turb<strong>in</strong>e<br />

- - 50% 50%<br />

Each <strong>CHP</strong> prototype must have an associated prime mover technology and operat<strong>in</strong>g<br />

strategy to allow effective emissions model<strong>in</strong>g. Prime mover technologies used for <strong>CHP</strong><br />

prototypes <strong>in</strong>clude microturb<strong>in</strong>es, reciprocat<strong>in</strong>g eng<strong>in</strong>es, and gas turb<strong>in</strong>es, with and<br />

without duct burners. Table 3-4 shows the frequency with which the various prime<br />

movers are anticipated to occur for each size <strong>of</strong> prototype.<br />

This breakout <strong>of</strong> the <strong>CHP</strong> potential by prime mover and size creates ten unique prototype<br />

systems. Based upon the technical potential <strong>in</strong> HGB (Table 3-3) and the frequency <strong>of</strong><br />

each prototypical project (Table 3-4), the estimated number <strong>of</strong> projects anticipated for<br />

each <strong>of</strong> the ten prototypes and the total electrical capacity can be calculated. The results,<br />

which are presented <strong>in</strong> Table 3-5, show that <strong>in</strong> 2007, an estimated 946 projects could be<br />

developed <strong>in</strong> the HGB <strong>in</strong>dustrial sector with a comb<strong>in</strong>ed capacity <strong>of</strong> some 1,298 MW.<br />

3.4 System Performance and Potential <strong>NOx</strong> Sav<strong>in</strong>gs<br />

In order to determ<strong>in</strong>e the <strong>NOx</strong> emission impacts <strong>from</strong> each <strong>of</strong> the ten prototypes, six <strong>CHP</strong><br />

templates were developed to reflect the range <strong>of</strong> prime mover technologies employed <strong>in</strong><br />

the ten prototype projects. The six templates <strong>in</strong>clude:<br />

• 250 kW microturb<strong>in</strong>e<br />

• 750 kW rich burn reciprocat<strong>in</strong>g eng<strong>in</strong>e<br />

• 3 MW rich burn reciprocat<strong>in</strong>g eng<strong>in</strong>e<br />

• 3 MW gas turb<strong>in</strong>e<br />

• 10 MW gas turb<strong>in</strong>e without duct burners<br />

• 20 MW gas turb<strong>in</strong>e with duct burners<br />

In order to model the <strong>NOx</strong> emission impacts, <strong>in</strong>formation such as equipment<br />

configurations, performance assumptions, and operat<strong>in</strong>g strategies was needed for each<br />

template: <strong>in</strong> particular, required fuel type, the number <strong>of</strong> generat<strong>in</strong>g units, operat<strong>in</strong>g<br />

hours, heat rate, the use <strong>of</strong> duct burners, and the type <strong>of</strong> absorption chiller used <strong>in</strong> the<br />

project, if any. Templates were developed to align with practices and strategies<br />

commonly applicable for typical <strong>in</strong>dustrial <strong>CHP</strong> facilities. Generally, <strong>CHP</strong> systems with<br />

electrical capacity <strong>of</strong> less than 5 MW were assumed to operate only 5840 hours per year,<br />

while those greater than 5 MW were assumed to operate year round. All <strong>of</strong> the <strong>in</strong>dustrial<br />

25

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