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

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

To assess the <strong>NOx</strong> emissions impacts <strong>of</strong> potential <strong>CHP</strong> applications with<strong>in</strong> the HGB<br />

commercial and <strong>in</strong>stitutional build<strong>in</strong>g sector, the base case (non-<strong>CHP</strong>) was modeled <strong>in</strong><br />

B<strong>CHP</strong> for each prototypical build<strong>in</strong>g type and compared to the correspond<strong>in</strong>g <strong>CHP</strong> cases.<br />

The B<strong>CHP</strong> model output <strong>in</strong>cludes calculations <strong>of</strong> the on-site <strong>NOx</strong> emissions and the<br />

amount <strong>of</strong> electricity supplied by the utility grid. On-site emissions were calculated based<br />

on each build<strong>in</strong>g cluster’s general build<strong>in</strong>g characteristics and energy demands while the<br />

<strong>of</strong>f-site <strong>NOx</strong> emissions were estimated <strong>from</strong> eGRID. The assumptions used to calculate<br />

the <strong>NOx</strong> impacts are summarized <strong>in</strong> Table 2-2.<br />

Table 2-2: <strong>NOx</strong> <strong>Emissions</strong> Assumptions<br />

Source<br />

<strong>NOx</strong><br />

Production<br />

Unit<br />

Commercial Boilers a 0.074 lbs per MMBtu<br />

Reciprocat<strong>in</strong>g Eng<strong>in</strong>e Generator (< 2 MW) b 0.14 lbs per MWh<br />

Microturb<strong>in</strong>e c 0.036 lbs per MMBtu<br />

Combustion Turb<strong>in</strong>e (< 10 MW) c 0.167 lbs per MMBtu<br />

Combustion Turb<strong>in</strong>e (> 10 MW) c 0.099 lbs per MMBtu<br />

Reciprocat<strong>in</strong>g Eng<strong>in</strong>e Generator (> 3MW) c 0.039 lbs per MMBtu<br />

ERCOT Grid Electricity d Notes:<br />

1.07 lbs per MWh<br />

a) EPA report #AP-42 which assumes 50% <strong>of</strong> boilers are uncontrolled and 50% are controlled<br />

b) Assumes <strong>NOx</strong> controls are implemented to meet current HGB standard permit level, <strong>in</strong>clud<strong>in</strong>g<br />

value <strong>of</strong> thermal energy captured.<br />

c) EPA <strong>CHP</strong> <strong>Emissions</strong> Calculator v1.1<br />

d) EPA eGRID for ERCOT (2007)<br />

In calculat<strong>in</strong>g <strong>of</strong>f-site <strong>NOx</strong> emissions <strong>from</strong> utility generated electricity, a 7% factor is<br />

used to account for transmission and distribution losses. <strong>NOx</strong> impacts were calculated<br />

with respect to ERCOT-only utilities <strong>in</strong> the eight county HGB region. Generally, <strong>NOx</strong><br />

production rate assumptions for prime movers used <strong>in</strong> commercial <strong>CHP</strong> systems were<br />

derived <strong>from</strong> the default values provided <strong>in</strong> the EPA <strong>CHP</strong> <strong>Emissions</strong> Calculator tool and<br />

those provided <strong>in</strong> the B<strong>CHP</strong> model, although <strong>CHP</strong> systems were forced to meet an<br />

emissions level <strong>of</strong> 0.14 lbs/MWh established <strong>in</strong> the standard permit. To establish the<br />

regional <strong>NOx</strong> impact, the total <strong>NOx</strong> emissions change for each build<strong>in</strong>g prototype and<br />

<strong>CHP</strong> case were multiplied by the actual number <strong>of</strong> exist<strong>in</strong>g build<strong>in</strong>gs correspond<strong>in</strong>g to<br />

the specific prototype.<br />

2.4.1 <strong>CHP</strong> Operat<strong>in</strong>g Strategies<br />

While <strong>CHP</strong> systems provide a number <strong>of</strong> benefits to host facilities, <strong>in</strong>clud<strong>in</strong>g for example<br />

improved power reliability, the decision to adopt <strong>CHP</strong> is most <strong>of</strong>ten based upon purely<br />

economic considerations. Acceptable payback periods rang<strong>in</strong>g between 3-10 years are<br />

common, although <strong>in</strong>stitutional build<strong>in</strong>g owners are thought to have the longest time<br />

horizon. As a result <strong>of</strong> the short payback periods, the <strong>CHP</strong> design and operat<strong>in</strong>g strategy<br />

most likely to be implemented <strong>in</strong> commercial and <strong>in</strong>stitutional build<strong>in</strong>gs is “Case 3:<br />

17

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