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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 />

Table 2-5: Potential <strong>NOx</strong> Emission <strong>Impacts</strong> <strong>from</strong> <strong>CHP</strong> – Exist<strong>in</strong>g Sites HGB Region<br />

Commercial Sector<br />

Total<br />

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

Avg. Annual<br />

(tons/day)<br />

Total<br />

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

Peak Ozone Season<br />

(tons/day)<br />

Case 1: Maximum Electrical Load -9.4 -13.4<br />

Case 3: Optimal Thermal Utilization -2.9 -5.2<br />

A comparison <strong>of</strong> <strong>NOx</strong> emissions reductions is provided <strong>in</strong> Figure 2-1, which breaks down<br />

the data by prototypical build<strong>in</strong>g type and by season. Aga<strong>in</strong>, <strong>of</strong>fice build<strong>in</strong>gs are noted to<br />

<strong>of</strong>fer the most substantial opportunities for <strong>NOx</strong> reductions through <strong>CHP</strong><br />

implementation. By 2020, economic and population growth <strong>in</strong> HGB is anticipated to<br />

create additional <strong>CHP</strong> opportunities <strong>in</strong> the commercial sector, which could result <strong>in</strong> even<br />

greater <strong>NOx</strong> reductions.<br />

Figure 2-1: <strong>NOx</strong> <strong>Emissions</strong> Sav<strong>in</strong>gs <strong>from</strong> the <strong>CHP</strong> Prototype Categories (Case 3)<br />

Tons per day<br />

3.5<br />

3.0<br />

2.5<br />

2.0<br />

1.5<br />

1.0<br />

0.5<br />

0.0<br />

Healthcare Hotel &<br />

Apartments<br />

Retail Schools Office<br />

Build<strong>in</strong>gs<br />

<strong>NOx</strong> Sav<strong>in</strong>gs<br />

<strong>NOx</strong> Sav<strong>in</strong>gs (Ozone Season)<br />

20

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