Appendix E

Temporally Allocating Emission with CEM Data for Chemical Transport 

and SIP Modeling
		
		



		

	


		
							

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2
Appendix F 

2008 Base Year Emissions Inventory Area (nonpoint) Sources by County 

and SCC
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Ashtabula NOx 0.00029 0.00036 9.4E-05 2.8E-05 0.00038 9.8E-05 2.9E-05 0.00015 0.00387 0.00288 0.0159

VOC 0.0021 0.00684 0.0005 0.00021 0.00711 0.00052 0.00021 1.6E-06 0.02478 0.01844 0.00027

Cuyahoga NOx 0.00444 0.00495 0.00129 0.00038 0.00438 0.00114 0.00033 0.00164 0 0 0.16678

VOC 0.03227 0.09362 0.0068 0.00283 0.083 0.00603 0.00251 1.8E-05 0 0 0.00284

Geauga NOx 0.00027 0.0003 7.7E-05 2.3E-05 0.00026 6.8E-05 2E-05 9.8E-05 0 0 0.02161

VOC 0.00193 0.00559 0.00041 0.00017 0.00497 0.00036 0.00015 1.1E-06 0 0 0.00037

Lake NOx 0.00074 0.00082 0.00021 6.2E-05 0.00073 0.00019 5.5E-05 0.00027 0 0 0.03385

VOC 0.00534 0.0155 0.00112 0.00047 0.01375 0.001 0.00042 2.9E-06 0 0 0.00058

Lorain NOx 0.00091 0.00101 0.00026 7.7E-05 0.0009 0.00023 6.8E-05 0.00034 0 0 0.03724

VOC 0.0066 0.01914 0.00139 0.00058 0.01697 0.00123 0.00051 3.6E-06 0 0 0.00063

Medina NOx 0.0005 0.00056 0.00014 4.2E-05 0.00049 0.00013 3.8E-05 0.00018 0 0 0.01994

VOC 0.00362 0.01051 0.00076 0.00032 0.00932 0.00068 0.00028 2E-06 0 0 0.00034

Portage NOx 0.00043 0.00054 0.00014 4.2E-05 0.00056 0.00015 4.3E-05 0.00022 0 0 0.02442

VOC 0.00314 0.01025 0.00075 0.00031 0.01066 0.00078 0.00032 2.4E-06 0 0 0.00042

Summit NOx 0.00161 0.00202 0.00053 0.00015 0.0021 0.00055 0.00016 0.00083 0 0 0.07233

VOC 0.01174 0.03826 0.00278 0.00116 0.03982 0.00289 0.0012 9E-06 0 0 0.00123

Delaware NOx 0.00053 0.00044 0.00011 3.3E-05 0.0006 0.00016 4.6E-05 0.00021 0 0 0.01239

VOC 0.00387 0.00827 0.0006 0.00025 0.01135 0.00082 0.00034 2.3E-06 0 0 0.00021

Fairfield NOx 0.0005 0.00041 0.00011 3.1E-05 0.00056 0.00015 4.3E-05 0.00019 0 0 0.00934

VOC 0.00363 0.00775 0.00056 0.00023 0.01063 0.00077 0.00032 2.1E-06 0 0 0.00016

Franklin NOx 0.00461 0.00378 0.00099 0.00029 0.00519 0.00136 0.0004 0.00177 0 0 0.06914

VOC 0.03351 0.07164 0.0052 0.00217 0.09828 0.00713 0.00297 1.9E-05 0 0 0.00118

Knox NOx 0.00016 0.0002 5.1E-05 1.5E-05 0.00021 5.4E-05 1.6E-05 8.1E-05 0.00211 0.00157 0.00993

VOC 0.00114 0.00374 0.00027 0.00011 0.00389 0.00028 0.00012 8.7E-07 0.01353 0.01006 0.00017

Licking NOx 0.00058 0.00048 0.00013 3.7E-05 0.00066 0.00017 5.1E-05 0.00023 0 0 0.01682

VOC 0.00425 0.00909 0.00066 0.00028 0.01247 0.00091 0.00038 2.4E-06 0 0 0.00029

Madison NOx 0.00014 0.00011 3E-05 8.7E-06 0.00016 4.1E-05 1.2E-05 5.3E-05 0 0 0.00586

VOC 0.001 0.00214 0.00016 6.5E-05 0.00294 0.00021 8.8E-05 5.8E-07 0 0 1E-04

Butler NOx 0.00095 0.00109 0.00028 8.3E-05 0.00129 0.00034 9.8E-05 0.00045 0 0 0.03888

VOC 0.00688 0.02055 0.00149 0.00062 0.02434 0.00177 0.00073 4.8E-06 0 0 0.00066

Clermont NOx 0.00052 0.00059 0.00016 4.5E-05 0.0007 0.00018 5.4E-05 0.00024 0 0 0

VOC 0.00377 0.01125 0.00082 0.00034 0.01332 0.00097 0.0004 2.6E-06 0 0 0

Clinton NOx 0.00012 0.00015 4E-05 1.2E-05 0.00016 4.2E-05 1.2E-05 6.1E-05 0.00164 0.00122 0.00875

VOC 0.00089 0.00289 0.00021 9E-05 0.00302 0.00022 9.3E-05 6.6E-07 0.01051 0.00781 0.00015

Hamilton NOx 0.00248 0.00284 0.00074 0.00022 0.00336 0.00088 0.00026 0.00117 0 0 0.09854

VOC 0.01799 0.05375 0.0039 0.00162 0.06368 0.00462 0.00193 1.3E-05 0 0 0.00168

Warren NOx 0.00051 0.00058 0.00015 4.5E-05 0.00069 0.00018 5.3E-05 0.00024 0 0 0.02434

VOC 0.00369 0.01103 0.0008 0.00033 0.01308 0.00095 0.00039 2.6E-06 0 0 0.00041

Area SCC list and descriptions: http://www.epa.gov/ttn/chief/net/2011nei/2011_neiv1_tsd_draft.pdf

Area SCCs

Emissions (tons per day)

Appendix F - Page 1
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Ashtabula NOx 0.01479 0.00188 0.04394 0.0062 0.00687 0.06207 0.00211 0.00407 0.00439 0.0001 0.00315

VOC 0.0003 0.0001 0.0034 0.00011 0.00012 0.00341 0.00012 0.00031 7.5E-05 0.00011 0.00012

Cuyahoga NOx 0.13662 0.01987 0.46548 0.06571 0.20634 1.843 0.06357 0.1225 0.13211 0.00017 0.00138

VOC 0.00281 0.00109 0.03597 0.00112 0.00351 0.10137 0.00348 0.00947 0.00226 0.00019 5.4E-05

Geauga NOx 0.0201 0.00255 0.05972 0.00843 0.00658 0.05947 0.00203 0.0039 0.00421 0.00071 0.00468

VOC 0.00041 0.00014 0.00461 0.00014 0.00011 0.00327 0.00011 0.0003 7.2E-05 0.00078 0.00018

Lake NOx 0.03869 0.00491 0.11496 0.01623 0.02294 0.20673 0.00706 0.01361 0.01468 1.6E-05 0.00183

VOC 0.00079 0.00027 0.00888 0.00028 0.00039 0.01137 0.00039 0.00105 0.00025 1.7E-05 7.1E-05

Lorain NOx 0.03464 0.00439 0.10294 0.01453 0.02405 0.21738 0.0074 0.01426 0.01538 1E-05 0.0012

VOC 0.00071 0.00024 0.00795 0.00025 0.00041 0.01196 0.00041 0.0011 0.00026 1.1E-05 4.7E-05

Medina NOx 0.01854 0.00235 0.05511 0.00778 0.0146 0.12856 0.0045 0.00868 0.00936 3.6E-05 0.00199

VOC 0.00038 0.00013 0.00426 0.00013 0.00025 0.00707 0.00025 0.00067 0.00016 4E-05 7.8E-05

Portage NOx 0.02271 0.00288 0.06749 0.00953 0.0112 0.07435 0.00345 0.00664 0.00716 0.00015 0.00417

VOC 0.00047 0.00016 0.00522 0.00016 0.00019 0.00409 0.00019 0.00051 0.00012 0.00016 0.00016

Summit NOx 0.06728 0.00853 0.19993 0.02822 0.07012 0.61577 0.02159 0.0416 0.04486 4.5E-05 0.00212

VOC 0.00138 0.00047 0.01545 0.00048 0.00119 0.03387 0.00118 0.00321 0.00077 5E-05 8.2E-05

Delaware NOx 0.01152 0.00146 0.03424 0.00483 0.01819 0.16388 0.0056 0.01079 0.01163 3.1E-05 0.00165

VOC 0.00024 8E-05 0.00265 8.3E-05 0.00031 0.00901 0.00031 0.00083 0.0002 3.4E-05 6.4E-05

Fairfield NOx 0.00868 0.0011 0.02581 0.00364 0.0091 0.08228 0.0028 0.0054 0.00582 3.8E-05 0.00165

VOC 0.00018 6E-05 0.00199 6.2E-05 0.00015 0.00453 0.00015 0.00042 1E-04 4.2E-05 6.4E-05

Franklin NOx 0 0.00842 0.19737 0.02786 0.17597 1.3826 0.05524 0.10645 0.1148 6.8E-05 0.0027

VOC 0 0.00046 0.01525 0.00048 0.00299 0.07604 0.00303 0.00823 0.00196 7.4E-05 0.0001

Knox NOx 0.00924 0.00117 0.02745 0.00388 0.00458 0.04144 0.00141 0.00272 0.00293 0 0.0008

VOC 0.00019 6.4E-05 0.00212 6.6E-05 7.8E-05 0.00228 7.7E-05 0.00021 5E-05 0 3.1E-05

Licking NOx 0.01565 0.00198 0.0465 0.00656 0.01342 0.07281 0.00413 0.00796 0.00859 3.3E-05 0.00189

VOC 0.00032 0.00011 0.00359 0.00011 0.00023 0.004 0.00023 0.00062 0.00015 3.6E-05 7.4E-05

Madison NOx 0.00545 0.00069 0.01619 0.00229 0.00287 0.02596 0.00088 0.0017 0.00184 0 0.00085

VOC 0.00011 3.8E-05 0.00125 3.9E-05 4.9E-05 0.00143 4.8E-05 0.00013 3.1E-05 0 3.3E-05

Butler NOx 0.03715 0.00469 0.11041 0.01559 0.03524 0 0.01085 0.02091 0.02255 4.9E-05 0.00678

VOC 0.00076 0.00026 0.00853 0.00027 0.0006 0 0.00059 0.00162 0.00039 5.3E-05 0.00026

Clermont NOx 0.0121 0.00153 0.03595 0.00508 0.01507 0.13625 0.00464 0.00894 0.00964 2.6E-05 0.00625

VOC 0.00025 8.4E-05 0.00278 8.7E-05 0.00026 0.00749 0.00025 0.00069 0.00016 2.9E-05 0.00024

Clinton NOx 0.00814 0.00103 0.02419 0.00342 0.00699 0.06322 0.00215 0.00415 0.00447 1E-05 0.00129

VOC 0.00017 5.7E-05 0.00187 5.8E-05 0.00012 0.00348 0.00012 0.00032 7.7E-05 1.1E-05 5E-05

Hamilton NOx 0.04975 0.01353 0.31698 0.04475 0.13642 1.15921 0.04213 0.08119 0.08756 8.3E-05 0.00589

VOC 0.00102 0.00074 0.02449 0.00077 0.00232 0.06376 0.00231 0.00627 0.0015 9.2E-05 0.00023

Warren NOx 0.02333 0.00295 0.06932 0.00979 0.0187 0.1248 0.00576 0.0111 0.01197 0 0.00393

VOC 0.00048 0.00016 0.00536 0.00017 0.00032 0.00686 0.00032 0.00086 0.0002 0 0.00015

Area SCCs

Area SCC list and descriptions: http://www.epa.gov/ttn/chief/net/2011nei/2011_neiv1_tsd_draft.pdf

Emissions (tons per day)

Appendix F - Page 2
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Ashtabula NOx 0.01717 0.03527 0.00288 0.00847 0 0 0 0.00294 0.00237 0.0386 0.06551

VOC 0.001 0.00137 0.01482 0.00033 0.00166 0.00572 0.00082 0.01326 0.009 0.08956 0.09345

Cuyahoga NOx 0.33962 0.07789 0.0452 0.00372 0 0 0 0 0 0 0

VOC 0.01987 0.00303 0.23272 0.00014 0.0212 0.07294 0.01045 0 0 0 0

Geauga NOx 0.01056 0.02039 0.00271 0.01259 0 0 0 0.00386 0.00311 0.08294 0.08602

VOC 0.00062 0.00079 0.01393 0.00049 0.00156 0.00538 0.00077 0.01741 0.01182 0.19241 0.12272

Lake NOx 0.0513 0.01136 0.00748 0.00493 0 0 0 0 0 0 0

VOC 0.003 0.00044 0.0385 0.00019 0.00386 0.0133 0.00191 0 0 0 0

Lorain NOx 0.05531 0.05709 0.00923 0.00322 0 0 0 0 0 0 0

VOC 0.00324 0.00222 0.04752 0.00013 0.00503 0.01729 0.00248 0 0 0 0

Medina NOx 0.02676 0.04234 0.00507 0.00537 0 0 0 0.00373 0.00301 0.12038 0.08321

VOC 0.00157 0.00165 0.02612 0.00021 0.00283 0.00973 0.00139 0.01685 0.01143 0.27928 0.11871

Portage NOx 0.02467 0.05396 0.00432 0.01122 0 0 0 0.00411 0.00332 0.08802 0.09176

VOC 0.00144 0.0021 0.02222 0.00044 0.00258 0.00886 0.00127 0.01858 0.01261 0.2042 0.13091

Summit NOx 0.13128 0.02582 0.01609 0.0057 0 0 0 0 0 0 0

VOC 0.00768 0.00101 0.08284 0.00022 0.00896 0.03082 0.00442 0 0 0 0

Delaware NOx 0.01708 0.04714 0.00553 0.00445 0 0 0 0.00169 0.00137 0.07544 0.07557

VOC 0.001 0.00184 0.02849 0.00017 0.00272 0.00938 0.00134 0.00765 0.00519 0.17503 0.10781

Fairfield NOx 0.01853 0.05605 0.00504 0.00443 0 0 0 0.00355 0.00286 0.03651 0.07921

VOC 0.00108 0.00218 0.02597 0.00017 0.00235 0.00808 0.00116 0.01604 0.01088 0.0847 0.113

Franklin NOx 0.23408 0.07647 0.0462 0.00726 0 0 0 0 0 0 0

VOC 0.0137 0.00298 0.23788 0.00028 0.01864 0.06415 0.00919 0 0 0 0

Knox NOx 0.00724 0.04726 0.00154 0.00215 0 0 0 0.00223 0.0018 0.01306 0.04968

VOC 0.00042 0.00184 0.00794 8.3E-05 0.00098 0.00337 0.00048 0.01006 0.00682 0.0303 0.07088

Licking NOx 0.02433 0.07104 0.00592 0.00509 0 0 0 0.00389 0.00314 0.06495 0.08675

VOC 0.00142 0.00277 0.03049 0.0002 0.0026 0.00896 0.00128 0.01756 0.01192 0.15069 0.12376

Madison NOx 0.00469 0.02843 0.00139 0.0023 0 0 0 0.00065 0.00052 0.0082 0.02884

VOC 0.00027 0.00111 0.00717 8.9E-05 0.00069 0.00238 0.00034 0.00292 0.00198 0.01903 0.04114

Butler NOx 0.04677 0.06173 0.01162 0.01824 0 0 0 0 0 0 0

VOC 0.00274 0.0024 0.05984 0.00071 0.00596 0.0205 0.00294 0 0 0 0

Clermont NOx 0.0152 0.07669 0.00633 0.01682 0 0 0 0.00357 0.00288 0.10113 0.07974

VOC 0.00089 0.00299 0.0326 0.00065 0.00323 0.0111 0.00159 0.01614 0.01095 0.23461 0.11376

Clinton NOx 0.00358 0.03707 0.00117 0.00346 0 0 0 0.00152 0.00122 0.00799 0.03387

VOC 0.00021 0.00144 0.00602 0.00013 0.00071 0.00245 0.00035 0.00686 0.00465 0.01853 0.04832

Hamilton NOx 0.16818 0.07177 0.03035 0.01583 0 0 0 0 0 0 0

VOC 0.00984 0.00279 0.15624 0.00062 0.01406 0.04838 0.00693 0 0 0 0

Warren NOx 0.01857 0.04901 0.00623 0.01057 0 0 0 0.003 0.00242 0.10826 0.067

VOC 0.00109 0.00191 0.0321 0.00041 0.00342 0.01178 0.00169 0.01356 0.0092 0.25116 0.09559

Area SCCs

Area SCC list and descriptions: http://www.epa.gov/ttn/chief/net/2011nei/2011_neiv1_tsd_draft.pdf

Emissions (tons per day)

Appendix F - Page 3
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Ashtabula NOx 0.00047 0 0 0 0.0004 0 0 0 0 0 0

VOC 0.00373 0 0 0.00342 0 0 0 3.2E-05 0 0 0

Cuyahoga NOx 0.00507 0 1.41793 0 0.00609 0 0 0 0 0 0

VOC 0.03987 0 0.07799 0.11073 0 0 0 0.00041 0 0 0

Geauga NOx 0.00043 0 0.32891 0 0.00032 0 0 0 0 0 0

VOC 0.00336 0 0.01809 0.00154 0 0 0 3E-05 0 0 0

Lake NOx 0.0007 0 0.62168 0 0.00081 0 0 0 0 0 0

VOC 0.00547 0 0.03419 0.01002 0 0 0 7.4E-05 0 0 0

Lorain NOx 0.00086 0 0.33394 0 0.00082 0 0 0 0 0 0

VOC 0.00679 0 0.01837 0.01448 0 0 0 9.7E-05 0 0 0

Medina NOx 0.00037 0 0.33836 0 0.00038 0 0 0 0 0 0

VOC 0.00288 0 0.01861 0.00578 0 0 0 5.4E-05 0 0 0

Portage NOx 0.00052 0 0.33945 0 0.00045 0 0 0 0 0 0

VOC 0.00412 0 0.01867 0.00462 0 0 0 4.9E-05 0 0 0

Summit NOx 0.00178 0 1.2253 0 0.00231 0 0 0 0 0 0

VOC 0.01402 0 0.06739 0.03379 0 0 0 0.00017 0 0 0

Delaware NOx 0.00035 0 0.12652 0 0.00024 0 0 0 0 0 0

VOC 0.00272 0 0.00696 0.00466 0 0 0 5.2E-05 0 0 0

Fairfield NOx 0.00051 0 0.14811 0 0.00033 0 0 0 0 0 0

VOC 0.00402 0 0.00815 0.00555 0 0 0 4.5E-05 0 0 0

Franklin NOx 0.0033 0 1.24672 0 0.00424 0 0 0 0 0 0

VOC 0.02594 0 0.06857 0.06627 0 0 0 0.00036 0 0 0

Knox NOx 0.00023 0 0 0 0.0002 0 0 0 0 0 0

VOC 0.00184 0 0 0.00175 0 0 0 1.9E-05 0 0 0

Licking NOx 0.00068 0 0.15983 0 0.00045 0 0 0 0 0 0

VOC 0.00537 0 0.00879 0.00683 0 0 0 5E-05 0 0 0

Madison NOx 0.00014 0 0.09919 0 7.8E-05 0 0 0 0 0 0

VOC 0.00113 0 0.00546 0.00168 0 0 0 1.3E-05 0 0 0

Butler NOx 0.0012 0 0.54383 0 0.00064 0 0 0 0 0 0

VOC 0.00943 0 0.02991 0.02226 0 0 0 0.00011 0 0 0

Clermont NOx 0.00064 0 0.21877 0 0.00025 0 0 0 0 0 0

VOC 0.00499 0 0.01203 0.0055 0 0 0 6.2E-05 0 0 0

Clinton NOx 0.00017 0 0.13997 0 7.9E-05 0 0 0 0 0 0

VOC 0.00135 0 0.0077 0.00119 0 0 0 1.4E-05 0 0 0

Hamilton NOx 0.0032 0 1.84575 0 0.00281 0 0 0 0 0 0

VOC 0.02511 0 0.10152 0.06132 0 0 0 0.00027 0 0 0

Warren NOx 0.00053 0 0.29401 0 0.00029 0 0 0 0 0 0

VOC 0.00414 0 0.01617 0.00838 0 0 0 6.6E-05 0 0 0

Area SCCs

Area SCC list and descriptions: http://www.epa.gov/ttn/chief/net/2011nei/2011_neiv1_tsd_draft.pdf

Emissions (tons per day)

Appendix F - Page 4
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Ashtabula NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00174 0.38832 0.04754 0.05092 0.00468 0.00423 0.00257 0.01739 0.13325 0.00097 0.06904

Cuyahoga NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.02217 4.95367 0.81903 0.14518 0.14284 0.44137 0.40006 0.10743 1.6998 0.01239 3.18833

Geauga NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00164 0.36558 0.04912 0.03259 1.21 0.02646 0.0657 0 0.12544 0.00091 0.28694

Lake NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00404 0.90294 0.24318 0.03725 0.08062 0.0815 0.12413 0 0.30983 0.00226 0.6944

Lorain NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00526 1.17434 0.17273 0.05678 0.03011 0.03069 0.07379 0 0.40296 0.00294 0.80994

Medina NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00296 0.66057 0.12226 0.04228 0.08564 0.00423 0.02222 0.00273 0.22667 0.00165 0.38898

Portage NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00269 0.60185 0.11117 0.04933 0.00669 0.00423 0.10136 0 0.20652 0.00151 0.36242

Summit NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00937 2.09332 0.39921 0.09284 0.07126 0.56732 0.23411 0 0.7183 0.00524 1.39412

Delaware NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00285 0.63671 0.03885 0.04321 0.04951 0 0.0183 0 0.21848 0.00159 0.18926

Fairfield NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00246 0.54873 0.0707 0.04314 0.02509 0 0.02735 0 0.18829 0.00137 0.12708

Franklin NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.0195 4.35619 0.95592 0.14123 0.21678 0.2265 0.33122 0.01739 1.49477 0.0109 1.90649

Knox NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00102 0.22889 0.02523 0.04047 0.02442 0 0.00968 0.01739 0.07854 0.00057 0.1921

Licking NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00272 0.60852 0.07765 0.05647 0.00301 0 0.00841 0 0.20881 0.00152 0.25738

Madison NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00072 0.16151 0.02024 0.02234 0.0281 0.0254 0.00132 0 0.05542 0.0004 0.09421

Butler NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00623 1.39191 0.16261 0.06063 0.11408 0.00953 0.11263 0 0.47762 0.00348 0.75909

Clermont NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00337 0.75384 0.13518 0.04366 0.02509 0.00423 0.21553 0 0.25867 0.00189 0.29439

Clinton NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00075 0.16668 0.0171 0.02566 0.00301 0 0.0025 0 0.05719 0.00042 0.22961

Hamilton NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.0147 3.28525 0.63313 0.09793 0.25859 0.34928 0.23219 0.10845 1.1273 0.00822 2.01894

Warren NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00358 0.80001 0.06253 0.04174 0.05252 0.0254 0.01239 0 0.27452 0.002 0.35523

Area SCCs

Emissions (tons per day)

Area SCC list and descriptions: http://www.epa.gov/ttn/chief/net/2011nei/2011_neiv1_tsd_draft.pdf

Appendix F - Page 5
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Ashtabula NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00032 0.24332 0.23051 0.17417 0.12166 0.073 0.22795 0.00896 0.02254 0.0167 0.16188

Cuyahoga NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.0255 3.10393 2.94056 2.22176 1.55197 0.93118 2.9079 0.11436 0.23377 0.1732 0

Geauga NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00059 0.22907 0.21701 0.16396 0.11453 0.06872 0.2146 0.00844 0.01824 0.01351 0.01892

Lake NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00236 0.56578 0.536 0.40498 0.28289 0.16973 0.53004 0.02084 0.03736 0.02768 0

Lorain NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00347 0.73583 0.6971 0.5267 0.36792 0.22075 0.68936 0.02711 0.05125 0.03797 0.26328

Medina NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00115 0.41391 0.39212 0.29627 0.20695 0.12417 0.38776 0.01525 0.03301 0.02446 0.14795

Portage NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00236 0.37711 0.35727 0.26993 0.18856 0.11313 0.3533 0.01389 0.03654 0.02707 0.101

Summit NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00624 1.31166 1.24263 0.93887 0.65583 0.3935 1.22882 0.04832 0.10471 0.07758 0

Delaware NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00106 0.39896 0.37796 0.28557 0.19948 0.11969 0.37376 0.0147 0.02234 0.01655 0.35993

Fairfield NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00126 0.34383 0.32573 0.24611 0.17191 0.10315 0.32211 0.01267 0.02159 0.016 0.39187

Franklin NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.022 2.72956 2.58589 1.95379 1.36477 0.81887 2.55716 0.10056 0.20589 0.15254 0.13238

Knox NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00059 0.14342 0.13587 0.10266 0.07171 0.04303 0.13436 0.00528 0.00959 0.0071 0.33458

Licking NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00071 0.3813 0.36123 0.27293 0.19065 0.11439 0.35721 0.01405 0.02996 0.02219 0.3805

Madison NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 1E-04 0.1012 0.09587 0.07244 0.0506 0.03036 0.09481 0.00373 0.01261 0.00935 0.67083

Butler NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00266 0.87216 0.82626 0.62428 0.43608 0.26165 0.81708 0.03213 0.05304 0.0393 0.20172

Clermont NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00236 0.47235 0.44749 0.3381 0.23618 0.1417 0.44252 0.0174 0.03349 0.02481 0.1798

Clinton NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.0002 0.10444 0.09894 0.07476 0.05222 0.03133 0.09784 0.00385 0.00874 0.00647 0.57035

Hamilton NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.01708 2.05852 1.95017 1.47346 1.02926 0.61755 1.9285 0.07584 0.17177 0.12727 0.02584

Warren NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00139 0.50128 0.4749 0.35881 0.25064 0.15038 0.46962 0.01847 0.02752 0.02039 0.19357

Area SCCs

Emissions (tons per day)

Area SCC list and descriptions: http://www.epa.gov/ttn/chief/net/2011nei/2011_neiv1_tsd_draft.pdf

Appendix F - Page 6
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Ashtabula NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.02667 0.05208 0.00984 0.00405 0.00031 0.00085 0.00166 0.01343 0.00781 0.0006 0.04691

Cuyahoga NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.59958 1.17065 0.22126 0.09105 0.00699 0.01915 0.03739 0.30182 0.17547 0.01344 0.46219

Geauga NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.07276 0.14207 0.02685 0.01105 0.00085 0.00232 0.00454 0.03663 0.02129 0.00163 0.03468

Lake NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.07451 0.14547 0.02749 0.01131 0.00087 0.00238 0.00465 0.03751 0.02181 0.00167 0.08207

Lorain NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.10454 0.2041 0.03858 0.01587 0.00122 0.00334 0.00652 0.05262 0.03059 0.00234 0.12634

Medina NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.06106 0.11923 0.02253 0.00927 0.00071 0.00195 0.00381 0.03074 0.01787 0.00137 0.06725

Portage NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.06438 0.12571 0.02376 0.00978 0.00075 0.00206 0.00402 0.03241 0.01884 0.00144 0.06823

Summit NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.17503 0.34174 0.06459 0.02658 0.00204 0.00559 0.01092 0.08811 0.05122 0.00392 0.19784

Delaware NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.06291 0.12283 0.02322 0.00955 0.00073 0.00201 0.00392 0.03167 0.01841 0.00141 0.05624

Fairfield NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.03353 0.06546 0.01237 0.00509 0.00039 0.00107 0.00209 0.01688 0.00981 0.00075 0.04711

Franklin NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.38538 0.75244 0.14221 0.05852 0.00449 0.01231 0.02403 0.194 0.11278 0.00864 0.41495

Knox NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.0116 0.02264 0.00428 0.00176 0.00014 0.00037 0.00072 0.00584 0.00339 0.00026 0.01841

Licking NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.03681 0.07188 0.01358 0.00559 0.00043 0.00118 0.0023 0.01853 0.01077 0.00083 1.23888

Madison NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.01813 0.03539 0.00669 0.00275 0.00021 0.00058 0.00113 0.00912 0.0053 0.00041 0.02216

Butler NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.11281 0.22026 0.04163 0.01713 0.00131 0.0036 0.00704 0.05679 0.03302 0.00253 0.12067

Clermont NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.06134 0.11976 0.02264 0.00931 0.00071 0.00196 0.00383 0.03088 0.01795 0.00138 0.06974

Clinton NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.00892 0.01741 0.00329 0.00135 0.0001 0.00028 0.00056 0.00449 0.00261 0.0002 0.01708

Hamilton NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.2767 0.54025 0.10211 0.04202 0.00322 0.00884 0.01726 0.13929 0.08098 0.0062 0.31853

Warren NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.05589 0.10911 0.02062 0.00849 0.00065 0.00178 0.00349 0.02813 0.01636 0.00125 0.0657

Area SCCs

Emissions (tons per day)

Area SCC list and descriptions: http://www.epa.gov/ttn/chief/net/2011nei/2011_neiv1_tsd_draft.pdf

Appendix F - Page 7
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Ashtabula NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.06146 0.08888 0.07413 0.03698 0.00192 0.00485 0 0 0 0 0

Cuyahoga NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.60563 0.84268 0.70729 0.14778 0.00767 0.04626 0.09674 0.03714 0.01921 8.8122 0.48439

Geauga NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.04544 0.06023 0.05307 0.04456 0.00231 0.00347 0 0.00115 0 0.10769 0.09807

Lake NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.10754 0.1424 0.12559 0.04702 0.00244 0.00821 0.2741 0.01896 0.05146 2.52358 0

Lorain NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.16555 0.22815 0.19334 0.07989 0.00415 0.01264 0 0.00714 0.01764 0.68271 0.09807

Medina NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.08812 0.12641 0.10291 0.15286 0.00793 0.00673 0.05039 0.00714 0 1.20286 0

Portage NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.0894 0.13167 0.10782 0.01716 0.00089 0.00705 0.03124 0.00019 0 0 0

Summit NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.25924 0.38396 0.31267 0.1002 0.0052 0.02045 0 0.01966 0 4.2405 0.09807

Delaware NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.07369 0.28499 0.08888 0.06616 0.00343 0.00581 0 0 0.00294 0.72944 0

Fairfield NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.08951 0.2843 0.07445 0.02459 0.00128 0.00487 0.03124 0 0 0.94279 0

Franklin NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.54373 2.31255 0.6558 0.14749 0.00765 0.04289 0.00504 0.00115 0 5.24018 0.61296

Knox NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.03497 0.11709 0.02909 0.02181 0.00113 0.0019 0.03124 0 0 0.88386 0.01635

Licking NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0 0.3913 0.0979 0.03059 0.00159 0.0064 0 0 0 0.9631 0.09807

Madison NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.0421 0.13655 0.03501 0.02272 0.00118 0.00229 0 0 0.00294 0.09143 0.01635

Butler NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.15812 0.24496 0.19071 0.07928 0.00411 0.01247 0.10178 0.00714 0.00156 2.66784 0.01635

Clermont NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.09138 0.14346 0.11021 0.04194 0.00218 0.00721 0.00504 0 0 1.11143 0.09807

Clinton NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.03245 0.11254 0.02699 0.02009 0.00104 0.00177 0 0 0.00294 0.36167 0.01635

Hamilton NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.41738 0.64771 0.50341 0.09309 0.00483 0.03292 0 0.15358 0.02734 5.70344 0.34867

Warren NOx 0 0 0 0 0 0 0 0 0 0 0

VOC 0.08609 0.12735 0.10384 0.04153 0.00215 0.00679 0.05744 0.00115 0 0 0.09807

Area SCCs

Emissions (tons per day)

Area SCC list and descriptions: http://www.epa.gov/ttn/chief/net/2011nei/2011_neiv1_tsd_draft.pdf

Appendix F - Page 8
C

o

u

n

t

y

p

o

l

l

u

t

a

n

t

2

5

0

5

0

4

0

1

2

0

2

4

0

1

0

6

5

0

0

0

2

4

0

1

0

8

5

0

0

0

Ashtabula NOx 0 0 0

VOC 0 0 0

Cuyahoga NOx 0 0 0

VOC 0.5331081 0.014362 0.0182936

Geauga NOx 0 0 0

VOC 0.1079362 0 0

Lake NOx 0 0 0

VOC 0 0.0037718 0

Lorain NOx 0 0 0

VOC 0.1079362 0.0071242 0

Medina NOx 0 0 0

VOC 0 0 0

Portage NOx 0 0 0

VOC 0 0.0063663 0

Summit NOx 0 0 0

VOC 0.1079362 0 0

Delaware NOx 0 0 0

VOC 0 0 0

Fairfield NOx 0 0 0

VOC 0 0 0

Franklin NOx 0 0 0

VOC 0.6746014 0.0002822 0

Knox NOx 0 0 0

VOC 0.0179894 0 0

Licking NOx 0 0 0

VOC 0.1079362 0 0

Madison NOx 0 0 0

VOC 0.0179894 0 0

Butler NOx 0 0 0

VOC 0.0179894 0 0

Clermont NOx 0 0 0

VOC 0.1079362 0.000288 0

Clinton NOx 0 0 0

VOC 0.0179894 0 0

Hamilton NOx 0 0 0

VOC 0.3837348 0.0003386 0

Warren NOx 0 0 0

VOC 0.1079362 0 0

Emissions (tons per day)

Area SCCs

Area SCC list and descriptions: http://www.epa.gov/ttn/chief/net/2011nei/2011_neiv1_tsd_draft.pdf

Appendix F - Page 9
Appendix F - Page 10
Appendix G

2008 Ozone Mobile Sources Emissions Inventory for Ohio Portion of the 

Cincinnati Ozone Nonattainment Area
2008	Ozone	Mobile	Source	Emissions	

Inventory	for	Ohio	Portion	of	the	

Cincinnati	Ozone	Nonattainment	Area	

Includes the counties of Butler, Clermont, Clinton, Hamilton, and Warren in Ohio. 

Emission estimates for the Year 2008 

Revised	June	2014	

Prepared for the Ohio Environmental Protection Agency by 

OKI Regional Council of Governments
2

 OKI 2008 Ozone Mobile Source Emissions Inventory for Ohio Portion of Cincinnati Ozone 

Nonattainment Area, June 2014 
3

 OKI 2008 Ozone Mobile Source Emissions Inventory for Ohio Portion of Cincinnati Ozone 

Nonattainment Area, June 2014 

Acknowledgments 

Title 2008 Ozone Mobile Source Emissions Inventory for Ohio Portion of 

Cincinnati Ozone Nonattainment Area 

Abstract This report was prepared for the Ohio Environmental Protection Agency. 

The Cincinnati Ozone Nonattainment Area includes a portion of Dearborn 

County Indiana, the counties of Boone, Campbell, Kenton in Kentucky, and 

the counties of Butler, Clermont, Clinton, Hamilton, and Warren in Ohio. 

Clinton County is outside of OKI’s MPO area with emission estimates 

prepared by the Ohio Department of Transportation. This report includes 

emission estimates for year 2008 only and only for the Ohio portion of the 

nonattainment area. EPA’s Motor Vehicle Emission Simulation (MOVES) 

2010b was used to generate the emission inventory. 

Date June 2014 

Agency Ohio-Kentucky-Indiana Regional Council of Governments 

Mark Policinski, Executive Director 

Robert Koehler, P.E., Deputy Director 

Project Manager Andrew J. Reser, AICP 

Project Staff Larry Buckler 

Nino Brunello, P.E., ODOT Division of Planning 

The preparation of this document was financed cooperatively by the Federal Highway Administration, 

the Federal Transit Administration, the Commonwealth of Kentucky Transportation Cabinet, the Ohio 

Department of Transportation, and the units of local and county government in the OKI region. The 

opinions, findings, and conclusions expressed in this document are those of the OKI Regional Council of 

Governments and are not necessarily those of the U.S. Department of Transportation. This report does 

not constitute a standard, specification, or regulation. 
4

 OKI 2008 Ozone Mobile Source Emissions Inventory for Ohio Portion of Cincinnati Ozone 

Nonattainment Area, June 2014 

 
5

 OKI 2008 Ozone Mobile Source Emissions Inventory for Ohio Portion of Cincinnati Ozone 

Nonattainment Area, June 2014 

Year	2008	MOBILE	Source	Ozone	Emissions	

Inventory	for	Ohio	Portion	of	the	Cincinnati	

Ozone	Nonattainment	Area	

This report was prepared for the Ohio Environmental Protection Agency. The Cincinnati nonattainment 

area includes a portion of Dearborn County Indiana, the counties of Boone, Campbell, Kenton in Kentucky, 

and the counties of Butler, Clermont, Clinton, Hamilton, and Warren in Ohio. Clinton County Ohio is 

outside OKI’s MPO boundaries. The Ohio Department of Transportation prepares emission estimates for 

Clinton County. This report includes emission estimates for the year 2008 only. EPA’s Motor Vehicle 

Emissions Simulator (MOVES) 2010b model was used to generate the vehicle emission inventory. Details 

on the various county data inputs used to generate the inventory are described in Table 3. Emissions of 

the ozone precursors, VOC’s, and NOx, were generated. 

Table 1 shows daily mobile source ozone emissions in tons per summer day for each county in the Ohio 

portion of the Cincinnati Nonattainment Area, including Clinton County. Emissions by road type is shown 

in Table 2. 
6

 OKI 2008 Ozone Mobile Source Emissions Inventory for Ohio Portion of Cincinnati Ozone 

Nonattainment Area, June 2014 

Table 1 

Mobile Source Emissions by 

State/County for the Ohio Portion 

of Cincinnati Ozone 

Nonattainment Area (tpsd) 

State 2008

Ohio 

Butler 

VMT 8,218,725

VOC 10.32

NOx 18.76

Clermont 

VMT 5,475,869

VOC 6.88

NOx 12.50

Hamilton 

VMT 24,123,110

VOC 30.30

NOx 55.08

Warren 

VMT 6,192,386

VOC 7.78

NOx 14.14

OKI OH Total 

VMT 44,010,090

VOC 55.28

NOx 100.48

Clinton 

VMT 1,939,190

VOC 2.51

NOx 5.50

OH NA Area VOC Total 57.79

OH NA Area NOx Total 105.98
7

 OKI 2008 Ozone Mobile Source Emissions Inventory for Ohio Portion of Cincinnati Ozone 

Nonattainment Area, June 2014 

Table 2 

VOC and NOx Emissions by Road Type (tons per summer day) 

Butler RoadTypeID RoadDescription VOC NOx 

 1 Off-Network 7.20 4.21

 2 Rural Restricted Access 0.06 0.40

 3 Rural Unrestricted Access 0.29 1.50

 4 Urban Restricted Access 1.11 6.13

 5 Urban Unrestricted Access 1.67 6.52

Butler Total 10.32 18.76

Clermont RoadTypeID RoadDescription VOC NOx 

 1 Off-Network 4.79 2.81

 2 Rural Restricted Access 0.04 0.27

 3 Rural Unrestricted Access 0.19 1.00

 4 Urban Restricted Access 0.74 4.09

 5 Urban Unrestricted Access 1.11 4.34

Clermont Total 6.88 12.50

Hamilton RoadTypeID RoadDescription VOC NOx 

 1 Off-Network 21.12 12.36

 2 Rural Restricted Access 0.18 1.18

 3 Rural Unrestricted Access 0.85 4.41

 4 Urban Restricted Access 3.25 18.00

 5 Urban Unrestricted Access 4.90 19.12

Hamilton Total 30.30 55.08

Warren RoadTypeID RoadDescription VOC NOx 

 1 Off-Network 5.42 3.17

 2 Rural Restricted Access 0.05 0.30

 3 Rural Unrestricted Access 0.22 1.13

 4 Urban Restricted Access 0.83 4.62

 5 Urban Unrestricted Access 1.26 4.91

Warren Total 7.78 14.14

Clinton RoadTypeID RoadDescription VOC NOx 

 1 Off-Network 1.28 0.76

 2 Rural Restricted Access 0.05 0.24

 3 Rural Unrestricted Access 0.18 0.61

 4 Urban Restricted Access 0.25 1.28

 5 Urban Unrestricted Access 0.76 2.61

Clinton Total 2.51 5.50
8

 OKI 2008 Ozone Mobile Source Emissions Inventory for Ohio Portion of Cincinnati Ozone 

Nonattainment Area, June 2014 

Mobile Source Emission Forecast Process 

Emission Factor Model 

OKI’s inventory assessment utilized U.S.EPA’s emissions model MOVES 2010b to generate VOC and NOX

emissions. Table 3 summarizes the settings used in the MOVES run specification file. Table 4 lists the data 

used in the MOVES County-Data Manager. Further technical details on the use of MOVES are found in 

the appendix to the OKI report “Mobile Source Emissions Inventory for Cincinnati PM2.5 Nonattainment 

Area”, revised December 2010.

Table 3 

MOVES RunSpec Parameter Settings

MOVES 2010b, default database 20121030

Scale County, Inventory

Time Span Time aggregation = Hour

July weekday, July meteorological data 

All hours of day selected 

Weekdays only 

Geographic Bounds Custom Domains 1) 4 Ohio counties and 

Lawrenceburg IN 

Vehicles/Equipment All source types, gasoline and diesel

Road Type All road types including off-network

Pollutants and Processes Total gaseous hydrocarbons, non-methane 

hydrocarbons, volatile organic compounds, 

carbon monoxide, oxides of nitrogen 

Strategies none

General Output Units= U.S. ton, joules and miles

Output Emissions Time = 24-hour day, Location =county, on-road 

emission by road type 

Advanced Performance none

Table 4 

County Data Manager Data Source

Source Type Population Local and default. Local data from ODOT (2010) motor vehicle 

registration data. Default data used for source types 

11,41,51,52,53,54,61 and 62. Annual growth rates used to adjust to 

2008 analysis year. 

Vehicle Type VMT Local and default. HPMSVTypeYear VMT=AADVMT from OKI travel 

demand model with EPA’s daily to annual VMT converter applied. 

monthVMTFraction = default. dayVMTFraction=default, 

hourVMTFraction=local. 

I/M Programs Default
9

 OKI 2008 Ozone Mobile Source Emissions Inventory for Ohio Portion of Cincinnati Ozone 

Nonattainment Area, June 2014 

Fuel Formulation Default

Fuel Supply Default

Meteorology Data Default

Ramp Fraction Local. OKI travel demand model.

Road Type Distribution Local. OKI travel demand model.

Age Distribution Local and default. Local data from ODOT (2010) motor vehicle 

registration data. Default data used for source types 

11,41,51,52,53,54,61 and 62. 

Average Speed Distribution Local. OKI travel demand model.

OKI Travel Demand Model 

Vehicle miles traveled, vehicle hours and average speeds were estimated using the OKI Travel Demand 

Model Version 7.6. The OKI Travel Demand Model is composed of CUBE Voyager programs and a series 

of FORTRAN programs written by OKI. It is a state of the practice model that uses the standard 4 phase 

sequential modeling approach of trip generation, distribution, modal choice and assignment. The model 

uses demographic and land use data and capacity and free-flow speed characteristics for each roadway 

segment in the network to produce a “loaded” highway network with forecasted traffic volumes with 

revised speeds based on specified speed/capacity relationships. 

Travel analysis zones are the basic geographic unit for estimating travel in the OKI model. The OKI region 

is subdivided into 1608 traffic analysis zones to permit detail as well as manageability. A variety of 

socioeconomic data items are used in the OKI transportation planning process. These data are used 

primarily to forecast future travel patterns by serving as independent variables in OKI trip generation 

equations. The following categories of planning data are utilized: 

• Population (household and group quarter) 

• Households 

• Household vehicles 

• Employment (by employment category and zone of work) 

• Labor force participation (by zone of residence) 

• Area type 

The principal data requirements of the OKI travel demand forecasting model are population and 

employment. From these variables, other characteristics including households, labor force, and personal 

vehicles may be derived. Chapter 5 of OKI 2030 Regional Transportation Plan 2008 Update provides a 

complete demographic overview of the region. 

OKI utilizes both base year (2005) and future year data (2010, 2020 and 2030) in the planning process. 

Planning data are maintained at the Traffic Analysis Zone (TAZ) level, and originate in the 2000 Census of 

Population and Housing. Base year 2005 and future year data for each variable are developed through 

various methods. More detailed explanation of base year and future year data generation for each of the 
10 OKI 2008 Ozone Mobile Source Emissions Inventory for Ohio Portion of Cincinnati Ozone 

Nonattainment Area, June 2014 

above-mentioned categories of planning data follows. All of the variables represent the latest OKI 

planning assumptions. 

Population 

Base and Future Year Data: Population data for base year 2005 and future years 2010, 2020 and 2030 

originate with the 2000 Census of Population and Housing. Utilizing ArcView GIS, population data at the 

zonal level for 2000 was derived from the area proportion allocation of block level population. 

As a tri-state regional planning agency, OKI uses county level projections as prepared by the respective 

state data centers (Ohio Department of Development Office of Strategic Research, Kentucky State Data 

Center and Indiana Business Research Center) as control totals. The most current projections (years 2005 

to 2030) were released by the Ohio and Indiana state data centers in 2003 and the Kentucky State Data 

Center in 2004. Population projections at the zonal level are calculated by multiplying household size by 

the projected zonal households. Household size is factored so that, in each county, the sum of the zonal 

populations equals the control total. 

Households 

Base Year Data: Household data for base year 2005 originates with the 2000 Census of Population and 

Housing. Utilizing the geographic information system ArcMap, household data at the zonal level for 2000 

was derived from the area proportion allocation of block level households. Year 2000 household data was 

updated to 2005 with residential building permits issued between January 2000 and December 2004. The 

residential building locations were geo-coded in ArcMap, then aggregated to the TAZs. The housing unit 

totals for each TAZ were converted to households by applying a vacancy rate, an adjustment for permitted 

but unbuilt units, and subtracting demolitions (where data was available). These households were then 

added to the year Census 2000 zonal household total to arrive at 2005 households for each TAZ. 

Future Year Data: The preparation of household projections was accomplished by calculating the number 

of households for a projected county population using ratios of householders to total population by age 

specific cohorts derived from the 2000 Census for each analysis year. Disaggregation to TAZs was 

determined by historical trends, existing and future land use, topography, flood plain information, 

availability of land, local knowledge and other factors. 

Household Vehicles 

Base and Future Year Data: Base and future year household vehicle data were obtained from the 2000 

Census of Population and Housing. The 2000 Census is the only source of household vehicle data available 

at the block group level. Average vehicles per household were calculated for block groups then applied to 

the TAZs associated with each block group. The 2005, 2010, 2020 and 2030 vehicles per household level 

was held at the 2000 level based on the fact that, since 2002, the number of vehicles per household has 

exceeded the number of drivers per household. 
11 OKI 2008 Ozone Mobile Source Emissions Inventory for Ohio Portion of Cincinnati Ozone 

Nonattainment Area, June 2014 

Labor Force 

Base and Future Year Data: The OKI labor force is a function of the population as determined by a labor 

force participation ratio (the number of employed persons in the labor force per persons 16 and over). 

Household data for base year 2005 originates with the 2000 Census of Population and Housing. Utilizing 

the geographic information system ArcMap, household data at the zonal level for 2000 was derived from 

the area proportion allocation of block group level employed labor force. The labor force projections for 

2005, 2010, 2020 and 2030 were based on the most recent projections of national labor force 

participation rates by age and sex cohorts from the U.S. Department of Labor, Bureau of Labor Statistics 

for each of those years. These rates were then applied to the projected county age/sex cohorts and 

adjusted to eliminate the unemployed to arrive at a county employed labor force control total. Employed 

labor force at the zonal level is calculated by multiplying the labor force participation rate by the zonal 

population. The labor force participation rate is adjusted so that, in each county, the sum of the zonal 

labor force counts equals the control total. 

Employment 

Base Year Data: Quarterly Census of Employment and Wages (QCEW or ES202) data for 2005 was utilized 

as the primary tool to calculate employment at the zonal level. Individual business records containing 

physical location, number of employees and SIC code were geocoded through ArcMap and aggregated to 

the TAZ level. This data set was supplemented by other sources of data to complete the commuting 

employment picture in the OKI region. Each zone’s employment was divided according to the SIC code 

into three classes (retail, office, industrial) based upon the potential for generating trips. 

Future Year Data: For future year employment projection, calculation was first made of the employment 

at the regional level. At the regional level, employment is a calculation of the region’s employed labor 

force minus workers who live in the region but commute out to work, plus workers who live outside the 

region but commute in to work. The regional total was disaggregated first to the county level based on 

historic trends and expected changes in the county’s share of the region’s employment and then to the 

TAZ level. Disaggregation to TAZs was determined by historical trends, existing and future land use, 

topography, flood plain information, availability of land, local knowledge and other factors. 

Area Type 

Base and Future Year Data: For each analysis year, each TAZ is assigned an area type designation as CBD, 

Urban, Suburban or Rural based on population and employment densities. 

Model Calibration 

OKI’s Travel Demand Model has been validated to observed traffic volumes for the model base year 2005. 

The modeling network encompasses the entire ozone Maintenance area with the exception of Clinton 

County, Ohio. The modeling network also includes Greene, Miami and Montgomery counties in Ohio and 

the remainder of Dearborn County Indiana. The difference between estimated vehicle miles traveled 

(VMT) and 2005 observed VMT is less than 1%. A highway screenline analysis compares the screenline 
12 OKI 2008 Ozone Mobile Source Emissions Inventory for Ohio Portion of Cincinnati Ozone 

Nonattainment Area, June 2014 

observed and simulated traffic volume discrepancies with the ODOT standard of maximum desirable 

deviation. The comparison shows that the model performs at a satisfactory level and all the errors were 

under the ODOT curve. Further information can be found in OKI’s 2007 report, “OKI/MVRPC Travel 

Demand Model Methodology/ Validation Report”. For the calibration, OKI used over 3000 traffic counts 

collected through 2006 by the Ohio Department of Transportation (ODOT), the Kentucky Transportation 

Cabinet, many county and local governments, transportation engineering consultants, and OKI. These 

traffic counts cover nearly 50% percent of the links in the OKI portion of the modeling network. The 

methodology provides consistency with past emission inventory and conformity analysis work performed 

by OKI. 

Local Inputs and Post-Model Processing 

OKI incorporates a variety of sources of local data to both improve and confirm the accuracy of VMT, as 

well as other travel-related parameters. Free flow speeds used on the highway and transit networks are 

based on travel time studies performed locally. The OKI post-processing program, IMPACT, uses the 

loaded highway network to generate VMT by hour, VMT by speed distribution and VMT by facility type. 

These tables are then included as input into MOVES. Two separate sets of VMT tables are generated: one 

for the four Ohio counties plus Dearborn County Indiana, and a second for the three Kentucky counties. 

The VMT by hour tables utilize hourly traffic distribution and directional split factors for different roadway 

types as developed by OKI. The main source of the data was the permanent traffic counting stations 

located throughout the OKI region for the years of 2004-2006. This data was supplemented with data 

collected at coverage count stations (locations with counts taken on only one-two days). The stations 

were classified by area type: urban and rural, and functional classification: freeway, arterial and collector. 

Speeds representing various “loaded” conditions (with traffic volumes) are estimated using techniques 

from the 1997 Highway Capacity Manual. This permits the estimation of speeds as conditions vary from 

hour to hour on the different facility types throughout the region. The IMPACT program performs the 

appropriate summation by area and roadway type as well as regional totals. OKI has also developed 

seasonal conversion factors to adjust traffic volumes to summer conditions. The factors were derived 

from local data collected at permanent traffic counting stations during 1994-1997 utilizing the average 

daily traffic monthly conversion factors for June, July and August. Further information on OKI’s IMPACT 

program is documented in the report, “Travel Demand Model Summary Reporting and Impact Summary 

Reporting: OKI/MVRPC Travel Demand Model User’s Guide”, OKI 2003.
Appendix H 

Central Ohio On-Road Mobile Emission Estimates 

 
CENTRAL OHIO ON-ROAD MOBILE EMISSION ESTIMATES

PREPARED FOR 

OHIO ENVIRONMENTAL PROTECTION AGENCY

CENTRAL OHIO YEAR 2008 INVENTORY FOR THE 

8-HOUR OZONE STANDARD

JULY, 2014 

111 Liberty Street

Columbus, Ohio 43215

614-228-2663 

www.morpc.org
Central Ohio On-Road Mobile Emission Estimates ii July, 2014 

TABLE OF CONTENTS 

1.0 INTRODUCTION & BACKGROUND ........................................................................................................... 1

1.1 INTRODUCTION ...................................................................................................................................................... 1

1.2 BACKGROUND ....................................................................................................................................................... 1

1.3 GEOGRAPHIC AREA OF ANALYSIS ......................................................................................................................... 2

2.0 QUANTITATIVE ANALYSIS ......................................................................................................................... 3

2.1 ANALYSIS YEARS .................................................................................................................................................. 3

2.2 GENERAL METHODOLOGY .................................................................................................................................... 3

2.3 TRAVEL DEMAND MODEL ..................................................................................................................................... 4

2.3.1 INDEPENDENT VARIABLES ................................................................................................................................... 4

2.3.2 MODEL NETWORKS .............................................................................................................................................. 4

2.3.3 LOADED HIGHWAY NETWORKS ........................................................................................................................... 5

2.3.4 INTRAZONAL TRIPS.............................................................................................................................................. 5

2.4 EMISSION FACTOR GENERATION ........................................................................................................................... 5

2.4.1 VEHICLE AGE DISTRIBUTION ............................................................................................................................. 20

2.4.2 TEMPERATURES ................................................................................................................................................. 20

2.5 COMPUTATIONS METHODOLOGY ........................................................................................................................ 20

2.5.1 AREAS WITH REGIONAL MODEL ........................................................................................................................ 20

2.5.2 AREAS WITHOUT REGIONAL MODEL .................................................................................................................. 21

3.0 SUMMARY OF RESULTS ............................................................................................................................ 22

3.1.1 AREAS WITHIN THE REGIONAL TRAVEL DEMAND MODEL ................................................................................ 22

3.1.2 AREAS PARTIALLY WITHIN THE REGIONAL TRAVEL DEMAND MODEL .............................................................. 22

3.1.3 AREA OUTSIDE REGIONAL TRAVEL DEMAND MODEL ........................................................................................ 24

3.1.4 TOTAL EMISSIONS FOR THE COLUMBUS/CENTRAL OHIO AREA .......................................................................... 24

3.2 EMISSIONS SUMMARY FOR THE COLUMBUS/CENTRAL OHIO AREA .................................................................... 25

APPENDIX ................................................................................................................................................................ 26

LIST OF TABLES 

TABLE 1 – MOVES INPUTS ............................................................................................................................................ 6

TABLE 2 – TEMPERATURE AND RELATIVE HUMIDITY DATA .......................................................................................... 8

TABLE 3 – RAMP FRACTIONS ......................................................................................................................................... 8

TABLE 4 – SOURCE TYPE POPULATION FOR YEAR 2008 ................................................................................................. 9

TABLE 5 – VEHICLE AGE DISTRIBUTION ...................................................................................................................... 10

TABLE 6 – ROAD TYPE DISTRIBUTION .......................................................................................................................... 14

TABLE 7 – YEARLY HPMS VMT FOR 2008.................................................................................................................. 15

TABLE 8 – HOURLY VMT FRACTIONS .......................................................................................................................... 15

TABLE 9 – SAMPLE EMISSION FILE (RATE PER DISTANCE) FOR YEAR 2008 .................................................................. 19

TABLE 10 – SAMPLE EMISSION FILE (RATE PER VEHICLE) FOR YEAR 2008 .................................................................. 19

TABLE 11: EMISSION ESTIMATIONS FOR ON-ROAD MOBILE SOURCES - FRANKLIN COUNTY ...................................... 22

TABLE 12: EMISSION ESTIMATIONS FOR ON-ROAD MOBILE SOURCES - DELAWARE COUNTY .................................... 22

TABLE 13: EMISSION ESTIMATIONS FOR ON-ROAD MOBILE SOURCES - LICKING COUNTY ......................................... 22

TABLE 14A: EMISSION ESTIMATIONS FOR FAIRFIELD COUNTY WITHIN THE TRAVEL DEMAND MODEL AREA ............ 22

TABLE 14B: EMISSION ESTIMATIONS FOR FAIRFIELD COUNTY OUTSIDE OF THE TRAVEL DEMAND MODEL AREAUSING HPMS DATA............................................................................................................................................. 23

TABLE 14C: EMISSION ESTIMATIONS FOR FAIRFIELD COUNTY .................................................................................... 23

TABLE 15A: EMISSION ESTIMATIONS FOR MADISON COUNTY WITHIN THE TRAVEL DEMAND MODEL AREA ............. 23

TABLE 15B: EMISSION ESTIMATIONS FOR MADISON COUNTY OUTSIDE OF THE TRAVEL DEMAND MODEL AREA -

USING HPMS DATA............................................................................................................................................. 23

TABLE 15C: EMISSION ESTIMATIONS FOR MADISON COUNTY ..................................................................................... 24

TABLE 16: EMISSION ESTIMATIONS FOR KNOX COUNTY – USING ONLY HPMS .......................................................... 24

TABLE 17: EMISSION ESTIMATIONS FOR ON-ROAD MOBILE SOURCES FOR COLUMBUS/CENTRAL OHIO .................... 24

TABLE 18: VOC EMISSION INVENTORY SUMMARY ..................................................................................................... 25

TABLE 19: NOX EMISSION INVENTORY SUMMARY ............................................... ERROR! BOOKMARK NOT DEFINED.
Central Ohio On-Road Mobile Emission Estimates iii July, 2014 

LIST OF FIGURES

FIGURE 1: COLUMBUS, CENTRAL OHIO, 8-HOUR MARGINAL NON-ATTAINMENT AREA......................................... 2
Central Ohio On-Road Mobile Emission Estimates 1 July, 2014 

1.0 Introduction & Background 

1.1 Introduction

This Report documents the on-road mobile emission estimates for the Columbus and Central 

Ohio area, in conjunction with the Ohio Environmental Protection Agency (OEPA) State 

Implementation Plan (SIP) update for Central Ohio area, primarily to establish base year 

inventory for the ozone marginal nonattainment area. Currently the region is designated as 

marginal nonattainment for 2008 Ozone National Ambient Air Quality Standards (NAAQS), 

Federal Register Vol. 77, No. 98, FR 30141, May 21, 2012.This report presents the summary of 

on road mobile emissions for the analysis year 2008 as the base year. Year 2008 computations 

for VOC (volatile organic compounds, gaseous compounds made of carbon and hydrogen) and 

NOx (Oxides of Nitrogen), are presented in this report. VOC and NOx interacting with sunlight 

in the lower atmosphere develops the primary constituent of smog, Ozone, a criteria pollutant. 

These emissions documented here are the emissions due to on-road vehicles for the counties in 

the marginal nonattainment area of Central Ohio. The methodologies in computing emissions 

and forecasting models used are also summarized in this report. 

1.2 Background

Under the 1990 Clean Air Act Amendments (CAAA), because of the 1997 eight-hour ozone 

standard, on April 15, 2004, U.S. EPA issued final designations with regard to the 8-hour ozone 

standard, designating the central Ohio basic non-attainment area to be the six counties of 

Franklin, Delaware, Licking, Madison, Fairfield and Knox counties were designated as a basic 

nonattainment area for ozone. The CAAA defines nonattainment areas as geographic regions 

of the country that do not meet the National Ambient Air Quality Standards (NAAQS). In 

nonattainment areas, air quality implementation plans must be developed that identify strategies 

and programs that nonattainment areas will implement to provide the emission reductions 

needed for the areas to meet the NAAQS. In Ohio, OEPA is the lead agency for coordinating 

development of the SIP. The SIP includes actions done on a statewide basis as well as actions 

done within each specific nonattainment area of the state to achieve the air quality standards. 

Re-designation of an area from ‘eight-hour ozone basic non-attainment’ to attainment is based 

on criteria and guidance set forth by U.S. EPA. Re-designation requests to attainment include 

SIP revisions that document that the NAAQS have been met and provide a maintenance plan to 

ensure meeting the standards for the next ten years. One of the items of documentation 

contained in a re-designation request is three consecutive years of air quality monitoring data 

that meet the NAAQS. A Re-designation request to attainment was submitted to EPA in March 

2009. This re-designation request to attainment was approved on September 15, 2009, based 

on 1997 eight-hour ozone standard, which is 80 ppb (0.08 ppm). 

In September 2009, Central Ohio area reached attainment, by re-designation, based on 1997 

eight-hour ozone standard. However on May 21, 2012 US EPA’s Federal Register notice 

designated Columbus Central Ohio area as marginal nonattainment area for the 2008 eighthour ozone standard, Federal Register Vol. 77, No. 98, FR 30141. Thus SIP update is required 

to establish base year as 2008 for Ozone. This report updates ozone emissions inventory using 

MOVES software program. 
Central Ohio On-Road Mobile Emission Estimates 2 July, 2014 

1.3 Geographic Area of Analysis 

The six-county marginal non-attainment areas consist of two metropolitan planning 

organizations (MPOs), MORPC and LCATS and also areas outside of the two MPO’s in 

Fairfield, Madison, and Knox Counties, illustrated in Figure 1. The MORPC transportation 

planning area consists of Franklin County, Delaware County, Pataskala and Etna Township in 

Licking County, and Violet and Bloom Townships in Fairfield County. The LCATS transportation 

planning area covers the remainder of Licking County. The travel demand model area 

comprising MORPC and LCATS transportation planning areas is illustrated in Figure 1. Donut 

areas, referring to Figure 1, are the counties or portions of counties that are outside of the travel 

demand model area. As illustrated, these are portions of Fairfield and Madison counties and all 

of Knox county. On-road mobile emissions analysis methodologies for counties within the travel 

demand area, as well as for counties outside the model area are discussed in the next sections. 

The geographic area of re-designation request for the Columbus, Central Ohio area, comprises 

of six-counties: Franklin county, Delaware county, Licking county, Fairfield county, Madison 

county, and Knox county. 

FIGURE 1: COLUMBUS, CENTRAL OHIO, 8-HOUR MARGINAL NON-ATTAINMENT AREA
Central Ohio On-Road Mobile Emission Estimates 3 July, 2014 

2.0 QUANTITATIVE ANALYSIS 

The methodologies used and background information for estimating on-road mobile emissions 

are discussed in the foregoing sections for the geographic area of 8-hour ozone non-attainment 

area. 

2.1 Analysis Years

Analysis year used in this documentation is 2008 since the need for establishing the base year 

as 2008 for the region's ozone National Ambient Air Quality Standards (NAAQS). Methodology 

for emissions analysis is presented next in this document for year 2008. 

2.2 General Methodology

Evaluating emissions for year 2008 analysis requires several data inputs, discussed in the 

foregoing sections. Among these, vehicle travel characteristics data can be obtained from 

regionally maintained travel demand model. Travel demand model provides daily traffic 

volumes, congested travel times, speeds, v/c (volume to capacity ratios), VMT (vehicle miles 

traveled), VHT (vehicle hours traveled) among other input travel characteristics data used in 

evaluating emissions in this report. Areas that are not within the regional travel demand model 

boundary utilized HPMS (Highway Performance Monitoring Systems) based travel 

characteristics data. Thus, the travel demand model is used in evaluating emissions for 

Franklin county, Delaware county, and Licking county. Both the travel demand model as well as 

HPMS is used in evaluating emissions for Fairfield county and Madison county. HPMS only is 

used for the Knox county, in evaluating emissions. Each of the aforementioned process is 

detailed further in sections 2.5.1 and 2.5.2. 
Central Ohio On-Road Mobile Emission Estimates 4 July, 2014 

2.3 Travel Demand Model

For these analyses the latest planning assumptions available for the Central Ohio area were 

used. For the travel demand model, model validation is a joint process between MORPC, 

LCATS and the ODOT Office of Technical Services. In December 2004, a new model was 

accepted and installed for use at MORPC. The new model covers all of the MORPC and 

LCATS area including portions of Pickaway, Madison and Union Counties along with additional 

portions of Fairfield County outside of the MORPC MPO area. Further, MORPC continuously 

updates the highway and transit network information and maintains accurate networks for future 

year analysis. The new model used is a multi-step tour-based model, incorporating more 

advanced simulation methods than compared to traditional four step model. Thus model inputs 

were tested for quality control and quality assurance. Forecasted variables such as population, 

employment, traffic counts, roadway network, etc. were developed by MORPC in coordination 

with LCATS and used for the analysis. 

Due to the advance simulation methods incorporated, there is some variation in model results 

from one complete model run to another with all of the same input data. MORPC performed a 

check on this variability with regard to on-road mobile emission estimates. The emission 

estimates for several 2002 model runs were calculated. The variation in the emission estimates 

were less than one-tenth of one percent (0.1%). Thus it was determined that the variability due 

to the simulation is insignificant. 

2.3.1 Independent Variables

Independent variables (land use/socio-economic data) were developed as well as interpolated 

for year 2008 analysis. Trip tables for the analysis year 2008 were interpolated. MORPC 

continually monitors land use, population and employment information. MORPC performs 

complete land use inventories every five years. The complete documentation of the process 

and future forecasts is provided in 2012-2035 Transportation Plans completed in May 2012 by 

MOPRC and LCATS. 

2.3.2 Model Networks

MORPC staff in conjunction with LCATS and ODOT continuously update the model networks to 

accurately reflect projects in the current TIP and Metropolitan Transportation Plan. The 

Transportation Plan horizon year for MORPC and LCATS is 2035. The model networks 

developed for this emission estimates is for the analysis year 2008. 
Central Ohio On-Road Mobile Emission Estimates 5 July, 2014 

2.3.3 Loaded Highway Networks

Trip assignment was run for model year 2008 using CUBE. The assignment produced a loaded 

highway network for the analysis year. This loaded network files includes total volume for each 

link in the network. Programming scripts in CUBE (a model software), illustrated in Appendix A, 

incorporate ODOT’s CMAQ process, discussed in more detail in Section 2.5.1. The loaded 

highway network for the analysis year was split into separate files for each county. Each county 

network was run independently through the CMAQ process for each analysis year, which 

combined the volumes and emission factors for computing VOC and NOx emissions for the 

entire county. 

2.3.4 IntraZonal Trips

Intrazonal trips are the trips that are generated within a traffic analysis zone (TAZ), that use 

local roads. Intrazonal trips do not get loaded onto the highway networks so Cube/Voyager 

emission calculation script requires a separate input file to account for these trips. Input files for 

evaluating intrazonal emissions are intrazonal trips file, intrazonal area file, and intrazonal 

emissions factor file. These input files for the areas within the travel demand model area are for 

Franklin county, Licking county, Delaware county, as well as for partial areas of Fairfield county 

and Madison county. The intrazonal trips were extracted from the trip tables using a 

Cube/Voyager script. 

2.4 Emission Factor Generation

Base Year 2008 

Using MOVES, emission factor files were generated for year-2008. Programs and 

corresponding MOVES parameters were developed in consultation with OEPA. 

Technical Details 

Table 1 summarizes the settings used in the MOVES run specification file and the MOVES 

County-Data Manager. Further details in specific inputs that are not using default values are 

provided below. 
Central Ohio On-Road Mobile Emission Estimates 6 July, 2014 

Table 1 – MOVES Inputs 

RunSpec Parameter Settings 

MOVES Version MOVES2010b 

Scale Custom Domain 

MOVES Modeling Technique Emission Factor Method 

Rates per Profile (grams/vehicle) 

Rates per Distance (grams/mile) 

Rates per Vehicle (grams/vehicle)

Time Span Time Aggregation: Hour 

1 Month representing average annual temperatures

All hours of day selected

16 speed bins

Weekdays only 

Geographic Bounds Franklin, Delaware, Licking, Fairfield, Madison & Knox 

Counties. 

Vehicles/Equipment All source types, gasoline and diesel 

Road Type All road types including off-network 

Pollutants and Processes Total Gaseous Hydrocarbons, Non-Methane Hydrocarbons, 

Volitile Organic Compounds, NOx, NO, NO2, Total Energy 

Consumption 

Strategies None 

General Output Units = grams, joules and miles 

Output Emissions Time = hour, Location = custom area, on-road emission rates 

by road type and source use type. 

Advance Performance None 

County Data Manager Sources 

Source Type Population Combination of local and default data 

Local data (2010) ODOT from motor vehicle registration 

Default data used for source types 41, 51, 54, 61, and 62

Future year growth rate based on MPO model Household 

growth rate. 

Vehicle Type VMT Combination of local and default data 

HPMSVTypeYear VMT = daily VMT from travel demand 

model 

monthVMTFraction = default 

dayVMTFraction=default 

hourVMTFraction=local 

I/M Program None 

Fuel Formulation Default 

Fuel Supply Default 

Future runs modified for reformulated gas, RVP, etc. for summer 

analyses 

Metereology Data Local data obtained from NOAA National Climatic Data Center. 

Data consist of monthly high and low temperatures and daily 

relative humidity for 2002. 

Ramp Fraction Using the base year travel demand model for VHT fractions. 

Future fractions assumed constant 
Central Ohio On-Road Mobile Emission Estimates 7 July, 2014 

Road Type Distribution Use ODOT county summary VMT categorized by federal 

functional classes 

Age Distribution Combination of local and default data. 

Local data (2010) ODOT from motor vehicle registration 

Default data used for source types 41, 51, 54, 61, and 62

The same age distribution used for all analysis years 

Average Speed Distribution Default 

Alternative Fuel Type Default 
Central Ohio On-Road Mobile Emission Estimates 8 July, 2014 

Temperature and Relative Humidity 

Temperatures used for the single season approach are representative of 12 months in 

2002 based on NOAA data from the National Climate Data Center website. Data for 

Port Columbus International Airport was used because it was the most complete 

compared to other airports in the non-attainment area. To get the correct format for 

MOVES, the data was entered into a spreadsheet provided by EPA which was designed 

to convert Mobile6 data to MOVES. An average annual hourly temperature and relative 

humidity distribution profile can be seen in Table 2. 

Table 2 – Temperature and Relative Humidity Data 

Hour 

Average 

Temperature 

Average 

Relative Humidity 

1 48.9 73.0 

2 47.8 75.0 

3 46.9 77.0 

4 46.2 80.0 

5 45.7 81.0 

6 45.1 81.0 

7 44.6 80.0 

8 45.0 77.0 

9 47.5 73.0 

10 51.5 67.0 

11 55.6 64.0 

12 59.1 61.0 

13 62.2 57.0 

14 63.9 56.0 

15 64.4 53.0 

16 64.6 53.0 

17 64.2 54.0 

18 63.0 55.0 

19 61.0 57.0 

20 58.4 63.0 

21 55.9 67.0 

22 53.6 70.0 

23 52.0 72.0 

24 50.4 75.0 

Ramp Fraction 

Ramp fractions were derived using the base year travel demand model VHT fractions. 

Ramp fractions can be seen in Table 3. Base year fractions were assumed to apply to 

future years. 

Table 3 – Ramp Fractions 

RoadTypeID Road Description Ramp Fraction 

2 Rural Restricted Access 0.02 

4 Urban Restricted Access 0.13 
Central Ohio On-Road Mobile Emission Estimates 9 July, 2014 

Source Type Population 

Source type population is based on a combination of local and MOVES default data. 

Local data was provided by ODOT based on 2010 motor vehicle registration. Default 

data is used for source types 41, 51, 54, 61, and 62. Future year growth rate is based 

on MPO model growth in cars which is an independent variable to the travel demand 

model. Table 4 shows source type population for the analyzed counties in 2008. 

Table 4 – Source Type Population for year 2008 

Source 

Type 

ID sourceTypeName 

Franklin 

Delaware Licking Fairfield 

Madison & 

Knox 

11 MotorCycle 55,222 6,868 8,999 2,444 3,565 

21 Passenger Car 878,901 97,120 128,334 35,905 43,829 

31 Passenger Truck 383,900 44,774 58,759 16,550 31,914 

32 Light Commercial Truck 11,553 1,348 1,768 498 1,280 

41 Intercity Bus 294 66 83 23 66 

42 Transit Bus 79 18 22 6 35 

43 School Bus 1,582 357 446 126 405 

51 Refuse truck 228 39 49 13 37 

52 Single Unit Short-haul Truck 205 35 44 12 1,553 

53 Single Unit Long-haul Truck 264 44 57 15 198 

54 Motor Home 1,102 184 235 65 181 

61 Comb Short-haul Truck 3,144 653 905 154 780 

62 Comb Long-haul Truck 3,616 750 1,040 178 897 

Vehicle Age Distribution 

Vehicle age distribution information was derived using Ohio Bureau of Motor Vehicle 

registration data for year 2010. The data was given to OEPA who supplied a VIN 

decoder that allowed ODOT to create correctly formatted MOVES inputs. MOVES 

default data is used for source types 41, 51, 54, 61, and 62. The registration data for 

most populous four counties were obtained in the non-attainment area and combined to 

create a regional vehicle age distribution file, see Table 5. This data is applied to all six 

counties in the region. The same age distribution will be used for all analysis years 
Central Ohio On-Road Mobile Emission Estimates 10 July, 2014 

Table 5 – Vehicle Age Distribution 

Year 

ID 

Source 

Type ID 

Age 

ID 

Age 

Fraction 

Source 

Type ID 

Age 

ID 

Age 

Fraction 

Source 

Type ID 

Age 

ID 

Age 

Fraction 

2008 11 0 0.0017 21 8 0.0599 31 16 0.0300 

2008 11 1 0.0228 21 9 0.0580 31 17 0.0256 

2008 11 2 0.0552 21 10 0.0634 31 18 0.0157 

2008 11 3 0.0765 21 11 0.0615 31 19 0.0118 

2008 11 4 0.0864 21 12 0.0562 31 20 0.0084 

2008 11 5 0.0820 21 13 0.0527 31 21 0.0077 

2008 11 6 0.0664 21 14 0.0460 31 22 0.0062 

2008 11 7 0.0839 21 15 0.0465 31 23 0.0048 

2008 11 8 0.0584 21 16 0.0383 31 24 0.0031 

2008 11 9 0.0540 21 17 0.0318 31 25 0.0024 

2008 11 10 0.0442 21 18 0.0269 31 26 0.0015 

2008 11 11 0.0333 21 19 0.0209 31 27 0.0009 

2008 11 12 0.0260 21 20 0.0162 31 28 0.0005 

2008 11 13 0.0204 21 21 0.0127 31 29 0.0003 

2008 11 14 0.0195 21 22 0.0092 31 30 0.0037 

2008 11 15 0.0188 21 23 0.0069 32 0 0.0059 

2008 11 16 0.0153 21 24 0.0057 32 1 0.0452 

2008 11 17 0.0128 21 25 0.0042 32 2 0.1089 

2008 11 18 0.0091 21 26 0.0031 32 3 0.0740 

2008 11 19 0.0085 21 27 0.0017 32 4 0.0699 

2008 11 20 0.0078 21 28 0.0011 32 5 0.0388 

2008 11 21 0.0078 21 29 0.0010 32 6 0.0331 

2008 11 22 0.0074 21 30 0.0321 32 7 0.0376 

2008 11 23 0.0106 31 0 0.0071 32 8 0.0370 

2008 11 24 0.0156 31 1 0.0277 32 9 0.0441 

2008 11 25 0.0144 31 2 0.0494 32 10 0.0557 

2008 11 26 0.0126 31 3 0.0584 32 11 0.0557 

2008 11 27 0.0163 31 4 0.0676 32 12 0.0472 

2008 11 28 0.0237 31 5 0.0828 32 13 0.0456 

2008 11 29 0.0163 31 6 0.0800 32 14 0.0385 

2008 11 30 0.0723 31 7 0.0727 32 15 0.0609 

2008 21 0 0.0075 31 8 0.0752 32 16 0.0476 

2008 21 1 0.0279 31 9 0.0613 32 17 0.0340 

2008 21 2 0.0396 31 10 0.0647 32 18 0.0273 

2008 21 3 0.0489 31 11 0.0622 32 19 0.0155 

2008 21 4 0.0508 31 12 0.0515 32 20 0.0156 

2008 21 5 0.0537 31 13 0.0433 32 21 0.0156 

2008 21 6 0.0561 31 14 0.0373 32 22 0.0118 

2008 21 7 0.0595 31 15 0.0362 32 23 0.0095 
Central Ohio On-Road Mobile Emission Estimates 11 July, 2014 

Year 

ID 

Source 

Type ID 

Age 

ID 

Age 

Fraction 

Source 

Type ID 

Age 

ID 

Age 

Fraction 

Source 

Type ID 

Age 

ID 

Age 

Fraction 

2008 32 24 0.0045 42 2 0.0592 43 11 0.0557 

2008 32 25 0.0057 42 3 0.0592 43 12 0.0843 

2008 32 26 0.0044 42 4 0.0592 43 13 0.0484 

2008 32 27 0.0019 42 5 0.0395 43 14 0.0178 

2008 32 28 0.0010 42 6 0.0724 43 15 0.0192 

2008 32 29 0.0007 42 7 0.0461 43 16 0.0129 

2008 32 30 0.0068 42 8 0.0592 43 17 0.0132 

2008 41 0 0.0013 42 9 0.0855 43 18 0.0181 

2008 41 1 0.0344 42 10 0.0592 43 19 0.0213 

2008 41 2 0.0607 42 11 0.1316 43 20 0.0139 

2008 41 3 0.0837 42 12 0.0395 43 21 0.0087 

2008 41 4 0.1005 42 13 0.0329 43 22 0.0077 

2008 41 5 0.0870 42 14 0.0263 43 23 0.0087 

2008 41 6 0.0972 42 15 0.0395 43 24 0.0056 

2008 41 7 0.0607 42 16 0.0461 43 25 0.0066 

2008 41 8 0.0742 42 17 0.0132 43 26 0.0049 

2008 41 9 0.0472 42 18 0.0197 43 27 0.0024 

2008 41 10 0.0466 42 19 0.0197 43 28 0.0017 

2008 41 11 0.0614 42 20 0.0000 43 29 0.0038 

2008 41 12 0.0290 42 21 0.0132 43 30 0.0064 

2008 41 13 0.0263 42 22 0.0066 51 0 0.0097 

2008 41 14 0.0189 42 23 0.0132 51 1 0.0290 

2008 41 15 0.0162 42 24 0.0000 51 2 0.0258 

2008 41 16 0.0229 42 25 0.0329 51 3 0.0839 

2008 41 17 0.0142 42 26 0.0000 51 4 0.0968 

2008 41 18 0.0081 42 27 0.0129 51 5 0.0226 

2008 41 19 0.0175 42 28 0.0000 51 6 0.0677 

2008 41 20 0.0101 42 29 0.0000 51 7 0.0774 

2008 41 21 0.0101 42 30 0.0000 51 8 0.0419 

2008 41 22 0.0121 43 0 0.0561 51 9 0.0323 

2008 41 23 0.0094 43 1 0.0411 51 10 0.0710 

2008 41 24 0.0061 43 2 0.0491 51 11 0.0710 

2008 41 25 0.0034 43 3 0.0655 51 12 0.0613 

2008 41 26 0.0081 43 4 0.0564 51 13 0.0516 

2008 41 27 0.0020 43 5 0.0516 51 14 0.0387 

2008 41 28 0.0000 43 6 0.0627 51 15 0.0419 

2008 41 29 0.0034 43 7 0.0537 51 16 0.0355 

2008 41 30 0.0273 43 8 0.0666 51 17 0.0161 

2008 42 0 0.0000 43 9 0.0603 51 18 0.0258 

2008 42 1 0.0132 43 10 0.0756 51 19 0.0129 
Central Ohio On-Road Mobile Emission Estimates 12 July, 2014 

Year 

ID 

Source 

Type ID 

Age 

ID 

Age 

Fraction 

Source 

Type ID 

Age 

ID 

Age 

Fraction 

Source 

Type ID 

Age 

ID 

Age 

Fraction 

2008 51 20 0.0000 52 29 0.0032 54 7 0.0450 

2008 51 21 0.0032 52 30 0.0484 54 8 0.0417 

2008 51 22 0.0065 53 0 0.0097 54 9 0.0414 

2008 51 23 0.0032 53 1 0.0290 54 10 0.0524 

2008 51 24 0.0032 53 2 0.0258 54 11 0.0482 

2008 51 25 0.0065 53 3 0.0839 54 12 0.0409 

2008 51 26 0.0032 53 4 0.0968 54 13 0.0334 

2008 51 27 0.0000 53 5 0.0226 54 14 0.0356 

2008 51 28 0.0097 53 6 0.0677 54 15 0.0315 

2008 51 29 0.0032 53 7 0.0774 54 16 0.0285 

2008 51 30 0.0484 53 8 0.0419 54 17 0.0254 

2008 52 0 0.0097 53 9 0.0323 54 18 0.0197 

2008 52 1 0.0290 53 10 0.0710 54 19 0.0177 

2008 52 2 0.0258 53 11 0.0710 54 20 0.0180 

2008 52 3 0.0839 53 12 0.0613 54 21 0.0263 

2008 52 4 0.0968 53 13 0.0516 54 22 0.0243 

2008 52 5 0.0226 53 14 0.0387 54 23 0.0230 

2008 52 6 0.0677 53 15 0.0419 54 24 0.0166 

2008 52 7 0.0774 53 16 0.0355 54 25 0.0193 

2008 52 8 0.0419 53 17 0.0161 54 26 0.0208 

2008 52 9 0.0323 53 18 0.0258 54 27 0.0130 

2008 52 10 0.0710 53 19 0.0129 54 28 0.0089 

2008 52 11 0.0710 53 20 0.0000 54 29 0.0074 

2008 52 12 0.0613 53 21 0.0032 54 30 0.1404 

2008 52 13 0.0516 53 22 0.0065 61 0 0.0021 

2008 52 14 0.0387 53 23 0.0032 61 1 0.0135 

2008 52 15 0.0419 53 24 0.0032 61 2 0.0306 

2008 52 16 0.0355 53 25 0.0065 61 3 0.0385 

2008 52 17 0.0161 53 26 0.0032 61 4 0.0509 

2008 52 18 0.0258 53 27 0.0000 61 5 0.0527 

2008 52 19 0.0129 53 28 0.0097 61 6 0.0590 

2008 52 20 0.0000 53 29 0.0032 61 7 0.0584 

2008 52 21 0.0032 53 30 0.0484 61 8 0.0571 

2008 52 22 0.0065 54 0 0.0051 61 9 0.0551 

2008 52 23 0.0032 54 1 0.0130 61 10 0.0628 

2008 52 24 0.0032 54 2 0.0257 61 11 0.0608 

2008 52 25 0.0065 54 3 0.0382 61 12 0.0501 

2008 52 26 0.0032 54 4 0.0413 61 13 0.0542 

2008 52 27 0.0000 54 5 0.0472 61 14 0.0390 

2008 52 28 0.0097 54 6 0.0501 61 15 0.0435 
Central Ohio On-Road Mobile Emission Estimates 13 July, 2014 

Year 

ID 

Source 

Type ID 

Age 

ID 

Age 

Fraction 

Source 

Type ID 

Age 

ID 

Age 

Fraction 

Source 

Type ID 

Age 

ID 

Age 

Fraction 

2008 61 16 0.0430 62 1 0.0485 62 17 0.0079 

2008 61 17 0.0314 62 2 0.0193 62 18 0.0039 

2008 61 18 0.0269 62 3 0.1651 62 19 0.0026 

2008 61 19 0.0228 62 4 0.0912 62 20 0.0032 

2008 61 20 0.0192 62 5 0.1263 62 21 0.0034 

2008 61 21 0.0217 62 6 0.0858 62 22 0.0027 

2008 61 22 0.0203 62 7 0.0529 62 23 0.0013 

2008 61 23 0.0144 62 8 0.0286 62 24 0.0008 

2008 61 24 0.0135 62 9 0.0663 62 25 0.0008 

2008 61 25 0.0099 62 10 0.1102 62 26 0.0006 

2008 61 26 0.0069 62 11 0.0600 62 27 0.0002 

2008 61 27 0.0036 62 12 0.0353 62 28 0.0001 

2008 61 28 0.0032 62 13 0.0186 62 29 0.0003 

2008 61 29 0.0028 62 14 0.0196 62 30 0.0001 

2008 61 30 0.0321 62 15 0.0208 

2008 62 0 0.0076 62 16 0.0160 

2008

 
Central Ohio On-Road Mobile Emission Estimates 14 July, 2014 

Road Type Distribution 

Road type distribution is based on the 2008 ODOT, county summary, HPMS VMT data 

categorized by federal functional class obtained for the most populous four counties, 

and is applied to the region, similar to development of vehicle age distribution data used 

for the region. Road type distribution can be seen in Table 6.

Table 6 – Road Type Distribution 

Source 

Type ID 

Road 

Type ID 

Road Type VMT 

Fraction 

Source Type 

ID 

Road 

Type ID 

Road Type VMT 

Fraction 

11 1 0 43 4 0.37 

11 2 0.05 43 5 0.46 

11 3 0.12 51 1 0 

11 4 0.37 51 2 0.05 

11 5 0.46 51 3 0.12 

21 1 0 51 4 0.37 

21 2 0.05 51 5 0.46 

21 3 0.12 52 1 0 

21 4 0.37 52 2 0.05 

21 5 0.46 52 3 0.12 

31 1 0 52 4 0.37 

31 2 0.05 52 5 0.46 

31 3 0.12 53 1 0 

31 4 0.37 53 2 0.05 

31 5 0.46 53 3 0.12 

32 1 0 53 4 0.37 

32 2 0.05 53 5 0.46 

32 3 0.12 54 1 0 

32 4 0.37 54 2 0.05 

32 5 0.46 54 3 0.12 

41 1 0 54 4 0.37 

41 2 0.05 54 5 0.46 

41 3 0.12 61 1 0 

41 4 0.37 61 2 0.05 

41 5 0.46 61 3 0.12 

42 1 0 61 4 0.37 

42 2 0.05 61 5 0.46 

42 3 0.12 62 1 0 

42 4 0.37 62 2 0.05 

42 5 0.46 62 3 0.12 

43 1 0 62 4 0.37 

43 2 0.05 62 5 0.46 

43 3 0.12 
Central Ohio On-Road Mobile Emission Estimates 15 July, 2014 

Vehicle Type VMT and VMT Fractions

The first component of the VMT inputs is the Yearly HPMS VMT, but the travel demand 

model was used instead of ODOT’s HMPS data since it was felt that the model would 

better predict future year VMT. ODOT’s CMS post-processor was run for each year to 

generate congestion reports, which includes total daily VMT. The vehicle type 

percentages of the total VMT were based on ODOT’s weigh-in-motion (WIM) data. 

Since there are not enough WIM stations for lower class facilities in the non-attainment 

area, a statewide average of all ODOT WIM data collectors was used. Daily VMT was 

then converted to yearly. Yearly HPMS VMT for 2008 can be seen in Table 7. The 

same method was used to generate all other analysis years 

Table 7 – Yearly HPMS VMT for 2008 

HPMS 

VtypeID Year ID HPMS BaseYear VMT 

10 2008 65,724,689 

20 2008 11,721,479,841 

30 2008 3,616,636,813 

40 2008 36,966,843 

50 2008 273,279,798 

60 2008 648,816,441 

Monthly and daily VMT fractions used MOVES default data. The hourly VMT fractions 

were derived from ODOT WIM data. Hourly VMT fractions vary for each of the five 

MOVES road types but do not change for each of the 16 MOVES source types. A 

representative sample of the hour VMT fraction input file can be seen in Table 8, the 

entire file is too large to include in this document. 

Table 8 – Hourly VMT Fractions 

Source 

TypeID 

Road 

TypeID DayID HourID 

Hour 

VMTFraction 

11 1 2 1 0.0089 

11 1 2 2 0.00564 

11 1 2 3 0.00424 

11 1 2 4 0.00427 

11 1 2 5 0.00695 

11 1 2 6 0.01798 

11 1 2 7 0.03806 

11 1 2 8 0.057 

11 1 2 9 0.05773 

11 1 2 10 0.05538 
Central Ohio On-Road Mobile Emission Estimates 16 July, 2014 

Source 

TypeID 

Road 

TypeID DayID HourID 

Hour 

VMTFraction 

11 1 2 11 0.05554 

11 1 2 12 0.05558 

11 1 2 13 0.05584 

11 1 2 14 0.06051 

11 1 2 15 0.06765 

11 1 2 16 0.07755 

11 1 2 17 0.08428 

11 1 2 18 0.0797 

11 1 2 19 0.06012 

11 1 2 20 0.04522 

11 1 2 21 0.03646 

11 1 2 22 0.02912 

11 1 2 23 0.02142 

11 1 2 24 0.01486 

11 2 2 1 0.0089 

11 2 2 2 0.00564 

11 2 2 3 0.00424 

11 2 2 4 0.00427 

11 2 2 5 0.00695 

11 2 2 6 0.01798 

11 2 2 7 0.03806 

11 2 2 8 0.057 

11 2 2 9 0.05773 

11 2 2 10 0.05538 

11 2 2 11 0.05554 

11 2 2 12 0.05558 

11 2 2 13 0.05584 

11 2 2 14 0.06051 

11 2 2 15 0.06765 

11 2 2 16 0.07755 

11 2 2 17 0.08428 

11 2 2 18 0.0797 

11 2 2 19 0.06012 

11 2 2 20 0.04522 

11 2 2 21 0.03646 

11 2 2 22 0.02912 

11 2 2 23 0.02142 

11 2 2 24 0.01486 
Central Ohio On-Road Mobile Emission Estimates 17 July, 2014 

Source 

TypeID 

Road 

TypeID DayID HourID 

Hour 

VMTFraction 

11 3 2 1 0.00655 

11 3 2 2 0.0037 

11 3 2 3 0.00304 

11 3 2 4 0.00363 

11 3 2 5 0.00792 

11 3 2 6 0.02343 

11 3 2 7 0.04899 

11 3 2 8 0.06319 

11 3 2 9 0.05402 

11 3 2 10 0.05121 

11 3 2 11 0.0528 

11 3 2 12 0.05608 

11 3 2 13 0.05814 

11 3 2 14 0.05875 

11 3 2 15 0.06676 

11 3 2 16 0.07812 

11 3 2 17 0.08469 

11 3 2 18 0.08152 

11 3 2 19 0.05852 

11 3 2 20 0.04343 

11 3 2 21 0.03606 

11 3 2 22 0.02829 

11 3 2 23 0.01883 

11 3 2 24 0.01233 

11 4 2 1 0.00752 

11 4 2 2 0.0044 

11 4 2 3 0.00354 

11 4 2 4 0.00374 

11 4 2 5 0.00705 

11 4 2 6 0.02123 

11 4 2 7 0.054 

11 4 2 8 0.0768 

11 4 2 9 0.06545 

11 4 2 10 0.05114 

11 4 2 11 0.04692 

11 4 2 12 0.04916 

11 4 2 13 0.05112 

11 4 2 14 0.0534 

11 4 2 15 0.06105 
Central Ohio On-Road Mobile Emission Estimates 18 July, 2014 

Source 

TypeID 

Road 

TypeID DayID HourID 

Hour 

VMTFraction 

11 4 2 16 0.07421 

11 4 2 17 0.08321 

11 4 2 18 0.08385 

11 4 2 19 0.06062 

11 4 2 20 0.04229 

11 4 2 21 0.03442 

11 4 2 22 0.0292 

11 4 2 23 0.02137 

11 4 2 24 0.01431 

11 5 2 1 0.00678 

11 5 2 2 0.00378 

11 5 2 3 0.00295 

11 5 2 4 0.0029 

11 5 2 5 0.00498 

11 5 2 6 0.01422 

11 5 2 7 0.03449 

11 5 2 8 0.05728 

11 5 2 9 0.05435 

11 5 2 10 0.04991 

11 5 2 11 0.05261 

11 5 2 12 0.06098 

11 5 2 13 0.06457 

11 5 2 14 0.06387 

11 5 2 15 0.06812 

11 5 2 16 0.07672 

11 5 2 17 0.08274 

11 5 2 18 0.08284 

11 5 2 19 0.06344 

11 5 2 20 0.04866 

11 5 2 21 0.0407 

11 5 2 22 0.03083 

11 5 2 23 0.01966 

11 5 2 24 0.01262 
Central Ohio On-Road Mobile Emission Estimates 19 July, 2014 

Output Emission Factors 

Table 9 shows the first record in a MOVES sample output (rate per distance) emission 

file for year 2008. For any given month, day of week, hour of the day, pollutant, and 

process; the rate per distance varies by road type, and speed bin. Rates per distance 

emissions are applied to link and intrazonal VMT. 

Table 9 – Sample Emission File (Rate per Distance) for year 2008 

Heading: MOVESScenarioID MOVESRunID yearID monthID dayID hourID

Record: OhioCustomDomain 6 2008 7 5 1 

Heading: linkID pollutantID processID sourceTypeID SCC fuelTypeID

Record: 990250201 3 0 1 0 

Heading: modelYearID roadTypeID avgSpeedBinID temperature relHumidity ratePerDistance

Record: 0 2 1 48.9333 73 12.9489 

Table 10 shows the first record in a MOVES sample output (rate per vehicle) emission 

file for year 2008. The rate per vehicle varies for any combinations of month, day of 

week, hour of the day, pollutant, and process. Rates per vehicle emissions are applied 

to the vehicle source type population. 

Table 10 – Sample Emission File (Rate per Vehicle) for year 2008 

Heading: MOVESScenarioID MOVESRunID yearID monthID dayID

Record: OhioCustomDomain 6 2008 7 5 

Heading: hourID zoneID pollutantID processID sourceTypeID

Record: 1 990250 3 0 2 

Heading: SCC fuelTypeID modelYearID temperature ratePerVehicle

Record: 0 0 48.9333 0.054967 

 Air Quality Consultation Process

The 1990 Clean Air Act amendments required identification of the consultation 

procedures that Ohio's air quality and transportation agencies will follow in the 

conformity process. To fulfill this requirement, the Ohio EPA has adopted Ohio 

Administrative Code 3745-101-04 to define the interagency consultation procedures 

used on air quality issues. These rules define a "straw man" process, whereby the lead 

agencies in the conformity process assume responsibility for preparing and distributing 

draft documents, with supporting information, and ensuring that each affected party 

involved in the conformity process is included in the consultation process. In addition, a 

Memorandum of Understanding (MOU) between MORPC, LCATS, ODOT and Ohio 

EPA has been signed to clarify OAC 3745-101-04 for the Columbus maintenance area. 

As a result of SAFETEA-LU Ohio EPA led the process to update MOU. This process is 

concluding with signatures from all parties obtained in February/March 2008. 
Central Ohio On-Road Mobile Emission Estimates 20 July, 2014 

The Columbus non-attainment area SIP development process employed the 

consultation procedures embodied in the rules. The procedures used in the current air 

quality analysis are comparable to the previous on road emission inventory and 

forecasting process. In addition, MORPC has had various telephone conversations and 

e-mail correspondence with Ohio EPA, ODOT and FHWA. Ohio EPA has also 

discussed various issues with U.S. EPA. 

2.4.1 Vehicle Age Distribution

OEPA provided vehicle age distribution information that was derived using USEPAs VIN 

decoder and Ohio Bureau of Motor Vehicle registration data. The registration data for 

Central Ohio area, Vehicle age distribution used to represent the MORPC/LCATS area 

is listed in Table 5. 

2.4.2 Temperatures

The low and high input temperatures used for MORPC area was given by OEPA. 

ODOT developed an average daily temperature distribution profile to derive the hourly 

temperature values. Temperature data input used is shown in table 2. 

2.5 Computations Methodology

2.5.1 Areas with Regional Model

Post Processing

Custom programs developed by ODOT in conjunction with MPO models, were used in 

computing total emissions. The process uses data on daily and directional traffic 

distributions as well as more up to date volume/delay functions from the 2000 Highway 

Capacity Manual (HCM). This process, described below, uses rewritten code able to 

handle the newer model network formats and MOVES generated emission factors. 

The first step in the process involves running postcms10.exe to calculate hourly link 

volumes based on the percentage of the daily volume (travel demand model output) 

determined by a link’s facility and area type. Link speeds from the travel demand model 

are not used in the analysis. The speeds are estimated as a post-process to the model 

based on HCM methods using a link’s volume-to-capacity ratio and link group code. 

The daily to hourly volume conversion percentages and speed tables can be seen in 

Appendix A, model script.

The second step (movesnet.exe) uses a combination of the MOVES emission factors 

and the hourly link volumes that are output of the postcms10.exe program. The hourly 

volumes are multiplied by the MOVES emission factor for the corresponding hour of 

day, speed bin, and roadtype to calculate emissions for every network link for each 
Central Ohio On-Road Mobile Emission Estimates 21 July, 2014 

hour. The final link on road vehicle emissions for the area is the sum of all individual 

link-hour emissions. 

The third step, (movesveh.exe), calculates vehicle-based emissions for each source 

type for each hour of the day. The vehicle source type is based on a combination of 

local and default data. The final vehicle emissions for each county are the sum of all 

individual hourly emissions for all vehicle types. 

Intrazonal trips do not get loaded onto the network, so the fourth step in the process 

requires a separate method to account for those trips that use local roads to travel 

within a zone. The intracalc2.exe program uses intrazonal trips to estimate VMT using 

the area in square miles and intrazonal trips of each zone. The zone is assumed 

circular and the radius of the circle is used as the average trip length for these 

intrazonal trips. Intrazonal emissions are then calculated by combining MOVES 

generated emissions with estimated intrazonal VMT. The emission rates are the same 

as those used to calculated link based emissions. 

The final step is to summarize link, vehicle, and intrazonal emissions for each county, 

pollutant, and analyzed year, and to multiply annual average daily emissions by 365 to 

produce an annual estimate. Daily summary emissions for each pollutant, county, and 

scenario year in the Central Ohio Region can be found in Appendix B through G. A 

summary of these emissions are tabulated in Sections 3.1.1 and 3.1.2 

2.5.2 Areas without Regional Model

The travel demand forecasting model discussed in the preceding sections does not 

cover the entire non-attainment area. Therefore, a standard process based on HPMS 

VMT was employed for the rest of the area which includes portions of Fairfield County, 

Madison County, and Knox County. This process first requires estimating the 

proportion of county VMT covered by the model and not covered by the model. This 

was accomplished using a GIS procedure, whereby, the proportion of the number of 

vehicles from census data, inside and outside of the model boundary, was calculated. 

This information was then combined with countywide average volumes by functional 

class to obtain the proportion of VMT inside and outside of the model. This computation 

yields 47% of the Fairfield county VMT, being inside the model area. Thus 53% of the 

HPMS VMT is used as the basis of the off-model computation for Fairfield County. For 

Madison County 71% HPMS VMT is used as the basis of the off-model computation of 

emissions. HPMS VMT data is used for all of Knox County. 

VMT by functional classification obtained for outside regional model area, also provides 

speed data based on the type of facility. MOVES generated factors of rate per distance 

as well as rate per vehicle were used to generate emissions for VOC, and NOx. A 

summary of these emissions are tabulated in Sections 3.1.2 and 3.1.3 
Central Ohio On-Road Mobile Emission Estimates 22 July, 2014 

3.0 SUMMARY OF RESULTS 

Emission estimates summary of results is presented in the next sections. 

3.1.1 Areas within The Regional Travel Demand Model

Table 11: Emission Estimations for On-Road Mobile Sources - Franklin County 

Franklin County 2008 

VMT (miles/day) 33,674,281 

VOC (tons/day) 94.250 

NOx (tons/day) 168.462 

Table 12: Emission Estimations for On-Road Mobile Sources - Delaware County 

Delaware County 2008 

VMT (miles/day) 5,163,945 

VOC (tons/day) 8.742 

NOx (tons/day) 18.995 

Table 13: Emission Estimations for On-Road Mobile Sources - Licking County 

Licking County 2008 

VMT (miles/day) 5,269,914 

VOC (tons/day) 10.034 

NOx (tons/day) 20.839 

3.1.2 Areas partially within The Regional Travel Demand Model

Counties that are partially within regional travel demand model are Fairfield county, and 

Madison county. 

Tables 14a, and 14b, summarize emissions estimates for Fairfield county, for the areas within 

and outside travel demand model area, respectively. Results presented in Table 14a is for the 

area covered by the travel demand model. Table 14b is for the area not covered by the travel 

demand model. These are derived by using 53% of the total county HPMS based VMT as 

described in section 2.5.2. Table 14c presents the emissions for the entire Fairfield county, 

which is simply sum of emissions from Tables 14a, and 14b. 

Table 14a: Emission Estimations for Fairfield County within the Travel Demand Model 

Area 

Fairfield County 2008 

VMT (miles/day) 1,762,320 

VOC (tons/day) 2.711 

NOx (tons/day) 6.126 
Central Ohio On-Road Mobile Emission Estimates 23 July, 2014 

Table 14b: Emission Estimations for Fairfield County outside of the Travel Demand 

Model Area- using HPMS data 

Fairfield County 2008 

VMT (miles/day) 1,674,173 

VOC (tons/day) 2.411 

NOx (tons/day) 5.393 

Table 14c: Emission Estimations for Fairfield County 

 sum of emissions from both the Travel Demand Model area as well as the HPMS area 

Tables 15a, and 15b, summarize emissions estimates for Madison county, for the areas within 

and outside travel demand area, respectively. Results presented in Table 15a is for the area 

covered by the travel demand model. Table 15b is for the area not covered by the travel 

demand model. These are derived by using 71% of the Madison county HPMS based VMT as 

described in section 2.5.2. Table 15c presents the emissions for the entire Madison county, 

which is simply sum of emissions from Tables 15a, and 15b. 

Table 15a: Emission Estimations for Madison County within the Travel Demand Model 

Area 

Table 15b: Emission Estimations for Madison County outside of the Travel Demand 

Model Area - using HPMS data 

Fairfield County 2008 

VMT (miles/day) 3,436,493 

VOC (tons/day) 5.122 

NOx (tons/day) 11.519 

Madison County 2008 

VMT (miles/day) 902,205 

VOC (tons/day) 1.319 

NOx (tons/day) 3.056 

Madison County 2008 

VMT (miles/day) 1,521,185 

VOC (tons/day) 2.191 

NOx (tons/day) 4.900 
Central Ohio On-Road Mobile Emission Estimates 24 July, 2014 

Table 15c: Emission Estimations for Madison County 

sum of emissions from both the Travel Demand Model area as well as the HPMS area 

3.1.3 Area outside Regional Travel Demand Model

Tables 16, summarizes emissions estimates for Knox county, and the results presented in this 

Table used methodology based on HPMS data. 

Table 16: Emission Estimations for Knox County – using only HPMS 

3.1.4 Total Emissions for the Columbus/Central Ohio area

Table 17, summarizes emissions estimates for the entire six county area. These emissions 

presented here is simply sum of all emissions in six counties summarized in Tables 11 through 

16. 

Table 17: Emission Estimations for On-Road Mobile Sources for Columbus/Central Ohio 

Madison County 2008 

VMT (miles/day) 2,423,389 

VOC (tons/day) 3.510 

NOx (tons/day) 7.956 

Knox County 2008 

VMT (miles/day) 1,221,494 

VOC (tons/day) 1.759 

NOx (tons/day) 3.935 

Central Ohio Area 2008 

VMT (miles/day) 51,189,516 

VOC (tons/day) 123.416 

NOx (tons/day) 231.706 
Central Ohio On-Road Mobile Emission Estimates 25 July, 2014 

3.2 Emissions Summary for the Columbus/Central Ohio Area

Tables 18 and 19, summarize VOC and NOx emissions estimates respectively for the analysis 

years. The summary presented in the following tables is from the aforementioned in Tables 11 

through 16. 

In addition, these emissions are also tabulated based on RoadTypeID, as follows 

RoadTypeID # RoadTypeID - Description

1 Off-Network- all locations where the predominant activity is vehicle starts, 

parking and idling (parking lots, truck stops, rest areas, freight or bus 

terminals)

2 Rural Restricted Access - rural highways that can only be accessed by an onramp

3 Rural Unrestricted Access- all other rural roads (arterials, connectors, and 

local streets) 

4 Urban Restricted Access - urban highways that can only be accessed by an 

on-ramp 

5 Urban Unrestricted Access - all other urban roads (arterials, connectors, and 

local streets)

Table 18: VOC Emission Inventory Summary 

- Year 2008, (tons/day) 

 RoadTypeID # 

VOC 2008 1 2 3 4 5 

Franklin 94.25 59.444 1.093 4.750 9.453 19.510 

Delaware 8.742 5.514 0.101 0.441 0.877 1.810 

Licking 10.034 6.329 0.116 0.506 1.006 2.077 

Fairfield 5.122 3.230 0.059 0.258 0.514 1.060 

Madison 3.51 2.214 0.041 0.177 0.352 0.727 

Knox 1.759 1.109 0.020 0.089 0.176 0.364 

Total 123.416 77.840 1.432 6.220 12.379 25.547 

Table 19: NOx Emission Inventory Summary 

- Year 2008, (tons/per day) 

 Total RoadTypeID #

NOx 2008 1 2 3 4 5 

Franklin 168.462 31.472 5.620 16.528 47.262 67.580 

Delaware 18.995 3.549 0.634 1.864 5.329 7.620 

Licking 20.839 3.893 0.695 2.045 5.846 8.360 

Fairfield 11.519 2.152 0.384 1.130 3.232 4.621 

Madison 7.956 1.486 0.265 0.781 2.232 3.192 

Knox 3.935 0.735 0.131 0.386 1.104 1.579 

Total 231.706 43.287 7.730 22.733 65.005 92.951 
Central Ohio On-Road Mobile Emission Estimates 26 July, 2014 

APPENDIX 

· Appendix A –Model Script for computing emissions 

· Appendix B – MORPC Travel Demand Model Emission Run Report for 2008 

· Appendix C – MORPC HPMS VMT and Emissions 
Central Ohio On-Road Mobile Emission Estimates July, 2014 27 

Appendix A – Model Script, Figures illustrating Data

CUBE VOYAGER PROGRAM SCRIPT FOR COMPUTING VOC & NOx EMISSIONS 

;[CMS (AQ), Produce Viper Network Output] ;;<<Process Template>>;; 

;Input Network File: {cm3neti,filename,"Input Network File Name",x,"N:\AQ\MOVES\morpc\Ozone\2014_04\model\AQ\Network\AQ_asgn_2008.net","Network File (*.net)|*.net"} ;Output Network File: {cm3neto,filename,"Output Network File Name",x,"N:\AQ\MOVES\morpc\Ozone\2014_04\model\AQ\Network\fra_out\AQ_2008out.net","Network File (*.net)|*.net"} ;Output CSV Summary File: {cm3sumo,filename,"Output CSV Summary File",x,"N:\AQ\MOVES\morpc\Ozone\2014_04\model\AQ\Network\fra_out\fra2008.csv","Report File (*.csv;*.txt)|*.csv;*.txt"} ;Output TXT Report File: {cm3rpto,filename,"Output TXT Report File",x,"N:\AQ\MOVES\morpc\Ozone\2014_04\model\AQ\Network\fra_out\fra2008.rpt","Report File (*.rpt;*.txt)|*.rpt;*.txt"} ;Output CSV Hourly File: {cm3hro,filename,"Output CSV Hourly File (Needed for benefits calc but very big)",x,"NONE","Report File (*.csv;*.txt)|*.csv;*.txt"} ;Note: {cm3junkname,note,"Optional Air Quality Files, Leave Blank When Not Doing Air Quality Calculations"} ;AQ Run Type: {cm3aqtype,combolist,"AQ Run Type","MOVES","NONE","MOBILE"} ;AQ Comment Line: {cm3aqcom,editbox,"Optional AQ Report Comment",T,"Ozone Analysis with MOVES - MORPC"} 

;Input Network Emissions Factors: {cm3effile,filename,"Input Network (per distance)Emissions Factors",x,"N:\AQ\MOVES\morpc\Ozone\2014_04\model\factors\2008MORPC_ozone_3source_rpd.csv","Emissions File (*.fac;*.csv)|*.fac;*.csv"} ;Input Vehicle (MOV) or Intrazonal (MOB) Emissions Factors: {cm3ieffile,filename,"Input Vehicle (MOV) or Intrazonal (MOB) Emissions Factors",x,"N:\AQ\MOVES\morpc\Ozone\2014_04\model\factors\2008MORPC_ozone_3source_rpv.csv","Emissions File (*.crd; *.csv)|*.crd; *.csv"} ;Input area file: {cm3afile,filename,"Input Area File",x,"N:\AQ\MOVES\morpc\Ozone\2014_04\model\AQ\area_taz\TAZ_areain.txt","Text File (*.txt; *.prn)|*.txt; *.prn"} ;Input Intrazonal Trips File: {cm3ifile,filename,"Input Intrazonal Trips (Matrix must be OMS format else use text)",x,"N:\AQ\MOVES\morpc\Ozone\2014_04\model\AQ\intra_z\county\fra08.txt","Matrix or Text File (*.txt; *.prn; *.mat; *.trp)|*.txt; *.prn; *.mat; *.trp"} ;Intrazonal File Type: {cm3iztype,combolist,"Intrazonal File Type","TEXT","NONE","OMSTABLE"} ;Input vehicle file: {cm3vfile,filename,"Input Vehicle File (Moves Only)",x,"N:\AQ\MOVES\morpc\Ozone\2014_04\model\factors\Source_Type_Pop_2008_MORPC_on-Model.csv","Text File (*.csv)|*.csv"} ;Space: {cm3space,note,"Parameters"} 
Central Ohio On-Road Mobile Emission Estimates July, 2014 28 

;Truck PCE: {cm3tpce,editbox,"Truck PCE",N,"2.0"} ;Capacity Field: {cm3capf,comboedit,"Capacity Field","CAP24","CAP1","CAP2","CAP3","CAP4"} ;Hourly/Model Capacity Factor: {cm3kfact,editbox,"Hourly/Model(usually daily) Capacity Factor",N,"0.10"} 

;AQ Season Factor: {cm3aqfact,comboedit,"AQ Season Factor (Ozone Only)","1.08","1.00"} ;Set Priority Code from ADMCLASS?:{cm3pri,combolist,"Set Priority Code from ADMCLASS? (CMSCOST can use)","NO","SW","OMS"} ;Run Mode: {cm3rmode,combolist,"Run Mode (usually use Normal for AQ)","NORMAL","4PERIOD_OMS","4PERIOD_SW","4PERIOD_MARKETSEGMENTS_SW"} ;Note: {cm3junkname2,note,"Normal Mode Inputs (if you specify another mode the fields are predetermined)"} ;Volume Field: {cm3volf,comboedit,"Volume Field", "VOL24_TOT","V_1", "LOADEDVOL","WINTERVOL","SUMMERVOL"} ;Truck Volume Field: {cm3trkf,comboedit,"Truck Volume Field (leave to NONE for AQ unless EFs generated by source)", "NONE","VOL24_TRK","VOL24_TRKHV","V2_1"} ;;<<End Parameters>>;; 

*if exist tempcms.txt DEL tempcms.txt *if exist summary.rpt DEL summary.rpt *if exist hourly.rpt DEL hourly.rpt *if exist cmstext.rpt DEL cmstext.rpt COPY FILE=county.dat ADA 1 4 ALL 2 3 ASD 3 4 ATB 4 4 ATH 5 4 AUG 6 4 BEL 7 3 BRO 8 4 BUT 9 2 CAR10 4 CHP11 4 CLA12 3 CLE13 2 CLI14 4 COL15 4 COS16 4 CRA17 4 CUY18 1 DAR19 4 DEF20 4 DEL21 2 ERI22 3 FAI23 4 
Central Ohio On-Road Mobile Emission Estimates 

July, 2014 29 

FAY24 4 FRA25 1 FUL26 4 GAL27 4 GEA28 2 GRE29 2 GUE30 4 HAM31 1 HAN32 4 HAR33 4 HAS34 4 HEN35 4 HIG36 4 HOC37 4 HOL38 4 HUR39 4 JAC40 4 JEF41 3 KNO42 4 LAK43 2 LAW44 3 LIC45 3 LOG46 4 LOR47 2 LUC48 2 MAD49 4 MAH50 2 MAR51 4 MED52 2 MEG53 4 MER54 4 MIA55 2 MOE56 4 MOT57 2 MRG58 4 MRW59 4 MUS60 4 NOB61 4 OTT62 4 PAU63 4 PER64 4 
Central Ohio On-Road Mobile Emission Estimates July, 2014 30 

PIC65 4 PIK66 4 POR67 2 PRE68 4 PUT69 4 RIC70 3 ROS71 4 SAN72 4 SCI73 4 SEN74 4 SHE75 4 STA76 2 SUM77 2 TRU78 2 TUS79 4 UNI80 4 VAN81 4 VIN82 4 WAR83 2 WAS84 3 WAY85 4 WIL86 4 WOO87 2 WYA88 4 ENDCOPY COPY FILE=dailya.dat HOUR 0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 PCTADT URB FWY 0.9 0.6 0.5 0.6 0.9 2.2 5.2 7.3 6.4 5.2 4.9 5.1 5.3 5.5 6.1 7.2 8.0 7.9 5.8 4.2 3.4 2.9 2.2 1.5 URB ART 0.7 0.4 0.3 0.3 0.6 1.5 3.5 5.7 5.5 5.1 5.3 6.2 6.5 6.4 6.8 7.6 8.2 8.1 6.2 4.8 4.0 3.0 1.9 1.3 RUR FWY 1.4 1.1 0.9 1.0 1.3 2.2 3.7 5.2 5.4 5.4 5.6 5.6 5.7 6.0 6.5 7.1 7.5 7.0 5.6 4.5 3.8 3.2 2.5 2.0 RUR ART 0.8 0.5 0.4 0.5 1.0 2.4 4.8 6.2 5.5 5.3 5.5 5.8 6.0 6.0 6.7 7.6 8.1 7.7 5.6 4.2 3.5 2.8 1.9 1.3 PCTADT TRK URB FWY 2.1 1.9 1.8 2.0 2.4 3.0 3.9 4.6 5.3 6.0 6.3 6.4 6.4 6.4 6.3 5.8 5.2 4.6 4.1 3.7 3.4 3.1 2.8 2.4 
Central Ohio On-Road Mobile Emission Estimates July, 2014 31 

URB ART 1.1 0.9 1.0 1.2 1.6 2.3 3.9 5.9 6.9 6.7 7.1 7.6 7.4 7.2 7.4 7.2 6.0 5.0 3.7 2.8 2.3 1.9 1.5 1.3 RUR FWY 2.6 2.2 2.1 2.3 2.6 3.1 3.5 4.0 4.5 5.1 5.6 5.8 5.8 5.8 5.8 5.6 5.3 4.9 4.6 4.3 4.0 3.8 3.5 3.1 RUR ART 1.5 1.3 1.4 1.6 2.2 3.0 4.2 5.3 6.1 6.7 7.0 7.1 

7.0 6.9 6.8 6.3 5.5 4.6 3.8 3.1 2.6 2.3 2.1 1.7 PCTDIR URB FWY 38 40 40 46 56 64 70 70 68 62 58 52 52 52 50 46 38 38 46 52 46 42 42 40 URB ART 44 46 44 48 54 62 66 68 64 56 54 52 50 50 50 46 40 38 46 52 48 46 46 46 RUR FWY 44 46 48 54 60 68 68 64 58 54 52 50 50 52 52 48 42 40 44 48 48 44 46 44 RUR ART 40 42 44 48 58 66 72 68 60 56 54 50 50 50 50 46 40 38 46 50 46 44 44 44 LOS E VC 0 0.625 1.25 1.875 2.5 3.125 3.75 4.375 5 5.625 6.25 6.875 7.5 8.125 8.75 9.375 10 10.625 11.25 11.875 12.5 13.125 13.75 14.375 SPEEDVC curve1 75 75 75 75 75 75 74.9 74.8 74.6 74.2 73.5 72.3 70.5 67.8 64.2 59.5 54 47.7 41.2 34.9 28.9 23.7 19.2 15.5 curve2 70 70 70 70 70 70 70 69.9 69.8 69.6 69.2 68.4 67.1 65.1 62.2 58.2 53 47 40.5 33.9 27.7 22.2 17.6 13.8 curve3 65 65 65 65 65 65 65 65 65 64.9 64.8 64.4 63.8 62.6 60.5 57 52 45.4 37.8 29.9 22.7 16.7 12.1 8.6 curve4 60 60 60 60 60 60 60 60 60 59.9 59.8 59.6 59.1 58.2 56.7 54.3 50.8 46.1 40.3 33.8 27.3 21.3 16.2 12.2 curve5 55 55 55 55 55 55 55 55 55 55 55 54.9 54.7 54.3 53.6 52.3 50 46.5 41.5 35.3 28.5 21.9 16.1 11.5 curve6 60 60 60 60 60 60 60 60 59.9 59.8 59.7 59.4 59.1 58.5 57.7 56.5 55 53.1 50.7 47.9 44.7 41.1 37.3 33.4 curve7 55 55 55 55 55 55 55 55 54.9 54.9 54.7 54.5 54.2 53.8 53.1 52.2 50.9 49.3 47.3 44.9 42.1 39 35.7 32.2 curve8 50 50 50 50 50 50 50 50 49.9 49.9 49.8 49.6 49.4 49 48.5 47.7 46.7 45.4 43.8 41.8 39.5 36.8 33.9 30.9 curve9 45 45 45 45 45 45 45 45 45 44.9 44.8 44.7 

44.4 44.1 43.6 43 42.1 40.9 39.4 37.6 35.5 33.1 30.5 27.8 curve10 50 50 50 50 49.9 49.8 49.7 49.4 49 48.4 47.5 46.5 45.1 43.5 41.7 39.6 37.3 34.9 32.4 29.8 27.3 24.9 22.6 20.4 curve11 50 50 50 50 50 49.9 49.7 49.4 48.9 48 46.7 44.9 42.5 39.6 36.2 32.6 28.7 25 21.4 18.2 15.3 12.9 10.8 9 
Central Ohio On-Road Mobile Emission Estimates July, 2014 32 

curve12 50 50 50 50 50 49.9 49.8 49.6 49.1 48.2 46.8 44.5 41.4 37.5 32.9 28 23.1 18.7 14.9 11.8 9.2 7.2 5.7 4.5 curve13 40 40 40 40 40 40 39.9 39.8 39.5 39.2 38.6 37.8 36.7 35.3 33.5 31.4 29 26.4 23.7 21.1 18.5 16.1 13.9 12 curve14 40 40 40 40 40 39.9 39.8 39.6 39.1 38.5 37.5 36.1 

34.3 32.1 29.4 26.5 23.5 20.5 17.7 15.1 12.8 10.7 9 7.6 curve15 40 40 40 40 40 39.9 39.7 39.4 38.8 37.9 36.5 34.7 32.3 29.5 26.4 23.2 20 17 14.3 11.9 9.9 8.2 6.8 5.6 curve16 35 35 35 35 35 34.9 34.8 34.5 34 33.2 32.1 30.5 28.5 26.1 23.5 20.6 17.9 15.2 12.8 10.7 8.9 7.4 6.1 5.1 curve17 35 35 35 35 35 34.9 34.7 34.4 33.9 33.1 32 30.3 28.3 25.8 23.1 20.3 17.5 14.9 12.5 10.4 8.6 7.2 5.9 4.9 curve18 35 35 35 35 35 34.9 34.6 34.2 33.5 32.4 30.9 28.8 26.3 23.4 20.4 17.4 14.6 12.1 9.9 8.1 6.6 5.4 4.4 3.6 curve19 30 30 30 30 30 29.9 29.8 29.5 29 28.2 27.1 25.6 23.7 21.5 19.1 16.6 14.2 12 10 8.3 6.8 5.6 4.6 3.8 curve20 30 30 30 30 30 29.9 29.7 29.4 28.9 28.1 26.9 25.3 23.4 21.1 18.6 16.1 13.6 11.4 9.5 7.8 6.4 5.3 4.3 3.6 curve21 30 30 30 30 30 29.9 29.7 29.3 28.7 27.7 26.2 24.4 22.1 19.6 17 14.4 12 9.9 8.1 6.6 5.4 4.4 3.6 2.9 VC RATIO TO LOS CONVERSION (VALUE SHOWN IS LOWER LIMIT FOR THAT LOS)(URBAN ROADS USE SPEED BREAKS BELOW FOR LOS DETERMINATION) (ALL USE THE BASE VC'S TO DETERMINE EXCEEDANCE)  BASE RUR2 FWY A 0.00 0.00 0.00 B 0.30 0.00 0.25 C 0.50 0.10 0.40 D 0.70 0.30 0.60 E 0.90 0.50 0.80 F 1.00 1.00 1.00 F+ 1.10 1.10 1.10 F++ 1.30 1.30 1.30 SPEED VC RATIO BREAKS FOR URBAN STREETS (HIGHEST SPEED FOR GIVEN LOS & FF SPEED) FFS B C D E F >47 42. 34. 27. 21. 16. >37 35. 28. 22. 17. 13. >32 30. 24. 18. 14. 10. <33 25. 19. 13. 9. 7. LEVEL OF SERVICE THRESHOLD BY AREA 
Central Ohio On-Road Mobile Emission Estimates July, 2014 33 

NUM LOS DEFINITION 1 F CINCINNATI,CLEVELAND,COLUMBUS CENTRAL MPO COUNTIES (CUY,FRA,HAM) 2 E OTHER TMA MPOS (AKRON,CANTON,DAYTON,TOLEDO,YOUNGSTOWN + NON-CENTRAL COUNTIES FROM 1) 3 E OTHER MPOS & PARTS OF AREAS 1 & 2 OUTSIDE URBANIZED AREA 4 E RURAL NON MPO COUNTIES PEAK SPREADING MODEL INFO (SET MAX ITERATIONS TO 0 TO DISABLE PEAK SPREADING) MAX VC RATIO FWY: 1.30 MAX VC RATIO ART: 1.30 MAX ITERATIONS : 1000 TRUCK PCE: {cm3tpce} AQ SEASON FACTOR: {cm3aqfact} ENDCOPY rrmode='{cm3rmode}' if(rrmode='NORMAL') COPY FILE=dailyb.dat MODEL CLASS PARAMETERS (MAX 4 CLASSES, HOURS 0-23 W/ NO OVERLAP IN CLASS, ALLOCATE ENTIRE CLASS AS TRUCK(1) OR NOT(0)) CLS TRK 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 CLS BEG 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 CLS END 23 23 0 0 0 0 0 0 0 0 0 0 0 0 0 0 CLS NUM 1 3 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ENDCOPY  volff='li.1.{cm3volf}'  trkfff='{cm3trkf}'  if (trkfff == 'NONE') then  trkff='_zero'  else  trkff='li.1.{cm3trkf}'  endif  vol1s='_zero'  vol2s='_zero'  vol3s='_zero' 
Central Ohio On-Road Mobile Emission Estimates July, 2014 34 

 vol4s='_zero'  vol5s='_zero'  vol6s='_zero'  vol7s='_zero'  vol8s='_zero'  vol9s='_zero'  vol10s='_zero'  vol11s='_zero'  vol12s='_zero'  vol13s='_zero'  vol14s='_zero'  vol15s='_zero'  vol16s='_zero' elseif(rrmode='4PERIOD_OMS') COPY FILE=dailyb.dat MODEL CLASS PARAMETERS (MAX 4 CLASSES, HOURS 0-23 W/ NO OVERLAP IN CLASS, ALLOCATE ENTIRE CLASS AS TRUCK(1) OR NOT(0)) CLS TRK 0 0 0 0 1 1 1 1 0 0 0 0 0 0 0 0 CLS BEG 18 6 9 14 18 6 9 14 0 0 0 0 0 0 0 0 CLS END 5 8 13 17 5 8 13 17 0 0 0 0 0 0 0 0 CLS NUM 1 1 1 1 3 3 3 3 0 0 0 0 0 0 0 0 ENDCOPY  volff='_zero'  trkff='_zero'  vol1s='li.1.volnt_aut'  vol2s='li.1.volam_aut'  vol3s='li.1.volmd_aut'  vol4s='li.1.volpm_aut'  vol5s='li.1.volnt_trk'  vol6s='li.1.volam_trk'  vol7s='li.1.volmd_trk'  vol8s='li.1.volpm_trk'  vol9s='_zero'  vol10s='_zero'  vol11s='_zero'  vol12s='_zero' 
Central Ohio On-Road Mobile Emission Estimates July, 2014 35 

 vol13s='_zero'  vol14s='_zero'  vol15s='_zero'  vol16s='_zero' elseif(rrmode='4PERIOD_SW') COPY FILE=dailyb.dat MODEL CLASS PARAMETERS (MAX 4 CLASSES, HOURS 0-23 W/ NO OVERLAP IN CLASS, ALLOCATE ENTIRE CLASS AS TRUCK(1) OR NOT(0)) CLS TRK 0 0 0 0 1 1 1 1 0 0 0 0 0 0 0 0 CLS BEG 19 7 10 16 19 7 10 16 0 0 0 0 0 0 0 0 CLS END 6 9 15 18 6 9 15 18 0 0 0 0 

0 0 0 0 CLS NUM 1 1 1 1 3 3 3 3 0 0 0 0 0 0 0 0 ENDCOPY  volff='_zero'  trkff='_zero'  vol1s='li.1.evvol_aut'  vol2s='li.1.amvol_aut'  vol3s='li.1.mdvol_aut'  vol4s='li.1.pmvol_aut'  vol5s='li.1.evvol_trk'  vol6s='li.1.amvol_trk'  vol7s='li.1.mdvol_trk'  vol8s='li.1.pmvol_trk'  vol9s='_zero'  vol10s='_zero'  vol11s='_zero'  vol12s='_zero'  vol13s='_zero'  vol14s='_zero'  vol15s='_zero'  vol16s='_zero' elseif(rrmode='4PERIOD_MARKETSEGMENTS_SW') COPY FILE=dailyb.dat MODEL CLASS PARAMETERS (MAX 4 CLASSES, HOURS 0-23 W/ NO OVERLAP IN CLASS, ALLOCATE ENTIRE CLASS AS TRUCK(1) OR NOT(0)) 
Central Ohio On-Road Mobile Emission Estimates July, 2014 36 

CLS TRK 0 0 0 0 1 1 1 1 0 0 0 0 0 0 0 0 CLS BEG 19 7 10 16 19 7 10 16 19 7 10 16 19 7 10 16 CLS END 6 9 15 18 6 9 15 18 6 9 15 18 6 9 15 18 CLS NUM 1 1 1 1 3 3 3 3 2 2 2 2 4 4 4 4 ENDCOPY  volff='_zero'  trkff='_zero'  vol1s='li.1.evvol_autwk'  vol2s='li.1.amvol_autwk'  vol3s='li.1.mdvol_autwk'  vol4s='li.1.pmvol_autwk'  vol5s='li.1.evvol_trkhv'  vol6s='li.1.amvol_trkhv'  vol7s='li.1.mdvol_trkhv'  vol8s='li.1.pmvol_trkhv'  vol9s='li.1.evvol_autnw'  vol10s='li.1.amvol_autnw'  vol11s='li.1.mdvol_autnw'  vol12s='li.1.pmvol_autnw'  vol13s='li.1.evvol_trklt'  vol14s='li.1.amvol_trklt'  vol15s='li.1.mdvol_trklt'  vol16s='li.1.pmvol_trklt' endif *if exist daily.dat del daily.dat *copy dailya.dat+dailyb.dat daily.dat *del dailya.dat *del dailyb.dat RUN PGM=NETWORK

 NETI={cm3neti.q} 

 LINKO=templnk.txt, format = TXT, include = a(6),b(6),junk1(1),junk1(4),junks(1),moffpspd(4),  ctoll(4),junkb(1),lanes(1),twidth(2),junkb(1),terrain(1),junk1(1),junkb(1),  cap(6),vol(6),loneway(1),boffpspd(4),ttoll(4),junkb(1),blanes(1),areatype(1),admclass(1),  junkb(1),bterrain(1),junk1(1),junkb(1),bcap(6),bvol(6),medturn(1),pcttrk(2),junk1(2),  funclass(2),lnkgrp(2),mpostspd(2),jurisdic(1),county(3),rtenumb(5),junk1(7),nhs(1),  fedfunc(2),trkvol(5),junkp(1),junk1(30),junk1(30),junk1(30),junk1(21),mdist(6), 
Central Ohio On-Road Mobile Emission Estimates July, 2014 37 

 vol1(6),vol2(6),vol3(6),vol4(6),vol5(6),vol6(6),vol7(6),vol8(6),vol9(6),vol10(6),vol11(6),  vol12(6),vol13(6),vol14(6),vol15(6),vol16(6)  NODEO=tempnod.txt, format = TXT, include = junkn(1),n(6),x(11),y(11)  PHASE=NODEMERGE  junkn='N'  ENDPHASE  PHASE=LINKMERGE  _zero=0  junk1=0  junks='S'  junkp='P'  fffff='{cm3pri}' /*;commented out 04/02/2012

if(fffff=='SW') 

 if(li.1.admclass==1 && li.1.district <13 && li.1.district>0)  junkp='P' ;state system

 elseif(li.1.district<13 && li.1.district>0) 

 junkp='G' ;non-state

 else 

 junkp='U' ;out of state

 endif 

elseif(fffff='OMS')  if(li.1.admclass<6)  junkp='P'  else  junkp='G'  endif endif */;commented out 04/02/2012jurisdic=' ' nhs=0 fedfunc=li.1.fedfuncl  junkb=' '  ctoll=0; =cartoll*10

 ttoll=0; =trktoll*10 mdist = LI.1.DIST*1000 

 moffpspd=li.1.offpspd*100  mpeakspd=li.1.peakspd*100 
Central Ohio On-Road Mobile Emission Estimates July, 2014 38 

 cap=li.1.{cm3capf}*{cm3kfact}  loneway='1' ; el_oneway change

 bcap=0 

 bvol=0  boffpspd=0  bpeakspd=0  blanes=0  bterrain=0  mpostspd=round(li.1.postspd)  vol=@volff@  trkvol=@trkff@  vol1=@vol1s@  vol2=@vol2s@  vol3=@vol3s@  vol4=@vol4s@  vol5=@vol5s@  vol6=@vol6s@  vol7=@vol7s@  vol8=@vol8s@  vol9=@vol9s@  vol10=@vol10s@  vol11=@vol11s@  vol12=@vol12s@  vol13=@vol13s@  vol14=@vol14s@  vol15=@vol15s@  vol16=@vol16s@  ENDPHASE 

ENDRUNaqmode='{cm3aqtype}' 

if(aqmode=='MOBILE') *copy {cm3effile.q} tempef.txt *N:\AQ\MOVES\morpc\Ozone\model\AQ\utils\postcms10.exe templnk.txt tempcms.txt N tempef.txt {cm3rmode} *del tempef.txt else *N:\AQ\MOVES\morpc\Ozone\model\AQ\utils\postcms10.exe templnk.txt tempcms.txt N NONE {cm3rmode} endif if(aqmode=='MOVES') *copy {cm3effile.q} tempef.txt if(rrmode='NORMAL' && trkfff == 'NONE')then *N:\AQ\MOVES\morpc\Ozone\model\AQ\utils\movesnet.exe hourly.rpt tempef.txt cmstext.rpt {cm3aqfact} 
Central Ohio On-Road Mobile Emission Estimates July, 2014 39 

else *N:\AQ\MOVES\morpc\Ozone\model\AQ\utils\movesnet.exe hourly.rpt tempef.txt cmstext.rpt {cm3aqfact} 1 {cm3tpce} 3 endif endif RUN PGM=NETWORK

 NETI[1]={cm3neti.q} 

 LINKI[2]=tempcms.txt var=a,1-6,b,8-13,  cVMT,97-111,cTRKVMT,113-128,cVOLPERLANE,130-137,cCONINDEX,139-146,  cVCRATIO,148-155,cPEAKHOUR,157-160,cVHT,162-169,cCONGDELAY,171-178,  cPHYSDELAY,180-187,cSPDLIMDELAY,189-196,cDELAYRATIO,198-205,  cDIR1HRSEXCEED,229-232,cDIR2HRSEXCEED,234-237,cPKVMT,253-267,cEXCEEDVMT,269-283,  cEXCEEDPKVMT,285-299,cLOS,317,1,,,1,  select=(substr(record,1,1)!= 'A')  NODEI[2]=tempnod.txt var=n,2-7, x,8-18, y,19-29  NETO={cm3neto.q}  MERGE RECORD=F ENDRUNiiztype='{cm3iztype}' 

if(iiztype=='TEXT') *copy {cm3ifile.q} tempif.txt elseif(iiztype=='OMSTABLE') RUN PGM=MATRIX 

FILEO PRINTO[1] = tempif.txt 

FILEI MATI[1] = {cm3ifile.q} MW[1]=mi.1.5+mi.1.10+mi.1.15 jloop if(j=i) print list=i(4.0),mw[1][j](6.0),printo=1 endif endjloop ENDRUNendif 

if(iiztype!='NONE') *copy {cm3afile.q} tempaf.txt 
Central Ohio On-Road Mobile Emission Estimates July, 2014 40 

if(aqmode=='MOBILE') *copy {cm3ieffile.q} tempief.txt *N:\AQ\MOVES\morpc\Ozone\model\AQ\utils\intracal2.exe tempif.txt summary.rpt tempaf.txt tempief.txt *del tempief.txt elseif(aqmode=='MOVES') *N:\AQ\MOVES\morpc\Ozone\model\AQ\utils\movesintra.exe tempif.txt tempef.txt tempaf.txt cmstext.rpt {cm3aqfact} *del tempef.txt endif *del tempaf.txt *DEL tempif.txt endif if(aqmode=='MOVES') *copy {cm3ieffile.q} tempief.txt *copy {cm3vfile.q} tempveh.txt *N:\AQ\MOVES\morpc\Ozone\model\AQ\utils\movesveh.exe tempveh.txt tempief.txt cmstext.rpt {cm3aqfact} *del tempveh.txt *del tempief.txt endif if(aqmode=='MOVES') *echo MOVES BASED EMISSIONS REPORT > tempcom.txt elseif(aqmode=='MOBILE') *echo MOBILE BASED EMISSIONS REPORT >> tempcom.txt else *echo NO EMISSIONS ANALYSIS CONDUCTED >> tempcom.txt endif *echo {cm3aqcom} >> tempcom.txt *echo Loaded Network: {cm3neti} >> tempcom.txt *echo Network Emission Factors: {cm3effile} >> tempcom.txt if(aqmode=='MOVES') *echo Vehicle Emission Factors: {cm3ieffile} >> tempcom.txt *echo Vehicle Population : {cm3vfile} >> tempcom.txt else *echo Intrazonal Emission Factors: {cm3ieffile} >> tempcom.txt endif *echo Intrazonal Trips : {cm3ifile} >> tempcom.txt *echo Area File (sq mi): {cm3afile} >> tempcom.txt 
Central Ohio On-Road Mobile Emission Estimates 

July, 2014 41 

*echo Volume Field Used: {cm3volf} >> tempcom.txt *echo Truck Volume Field Used: {cm3trkf} >> tempcom.txt *echo Capacity Field Used: {cm3capf} >> tempcom.txt *echo ----------------------------------------- >> tempcom.txt *copy /B tempcom.txt+cmstext.rpt {cm3rpto.q} *if exist {cm3sumo.q} del {cm3sumo.q} *rename summary.rpt {cm3sumo.q} *del tempcom.txt *del cmstext.rpt *DEL tempnod.txt *DEL templnk.txt *DEL tempcms.txt hhro=rightstr('{cm3hro}',4) if(hhro=='NONE') *del hourly.rpt else *if exist {cm3hro.q} del {cm3hro.q} *rename hourly.rpt {cm3hro.q} endif 
Central Ohio On-Road Mobile Emission Estimates July, 2014 42 

Appendix B – MORPC Travel Demand Model Emission Run Report for 2008

 MOVES BASED EMISSIONS REPORT Ozone Analysis with MOVES - MORPC Loaded Network: N:\AQ\MOVES\morpc\Ozone\2014_04\model\AQ\Network\AQ_asgn_2008.net Network Emission Factors: N:\AQ\MOVES\morpc\Ozone\2014_04\model\factors\2008MORPC_ozone_3source_rpd.csv Vehicle Emission Factors: N:\AQ\MOVES\morpc\Ozone\2014_04\model\factors\2008MORPC_ozone_3source_rpv.csv Vehicle Population : N:\AQ\MOVES\morpc\Ozone\2014_04\model\factors\Source_Type_Pop_2008_MORPC_on-Model.csv Intrazonal Trips : N:\AQ\MOVES\morpc\Ozone\2014_04\model\AQ\intra_z\county\fra08.txt Area File (sq mi): N:\AQ\MOVES\morpc\Ozone\2014_04\model\AQ\area_taz\TAZ_areain.txt Volume Field Used: VOL24_TOT Truck Volume Field Used: NONE Capacity Field Used: CAP24 -----------------------------------------  CMS/AQ REPORT  POSTCMS10, UPDATED DEC 2009, GTG  DATE:04/29/2014 TIME:10:40:49  PARAMETER FILE DUMP (DAILY.DAT FILE) HOUR 0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 

15 16 17 18 19 20 21 22 23 PCTADT URB FWY 0.9 0.6 0.5 0.6 0.9 2.2 5.2 7.3 6.4 5.2 4.9 5.1 5.3 5.5 6.1 7.2 8.0 7.9 5.8 4.2 3.4 2.9 2.2 1.5 URB ART 0.7 0.4 0.3 0.3 0.6 1.5 3.5 5.7 5.5 5.1 5.3 6.2 6.5 6.4 6.8 7.6 8.2 8.1 6.2 4.8 4.0 3.0 1.9 1.3 RUR FWY 1.4 1.1 0.9 1.0 1.3 2.2 3.7 5.2 5.4 5.4 5.6 5.6 5.7 6.0 6.5 7.1 7.5 7.0 5.6 4.5 3.8 3.2 2.5 2.0 RUR ART 0.8 0.5 0.4 0.5 1.0 2.4 4.8 6.2 5.5 5.3 5.5 5.8 6.0 6.0 6.7 7.6 8.1 7.7 5.6 4.2 3.5 2.8 1.9 1.3 PCTADT TRK URB FWY 2.1 1.9 1.8 2.0 2.4 3.0 3.9 4.6 5.3 6.0 6.3 6.4 6.4 6.4 6.3 5.8 5.2 4.6 4.1 3.7 3.4 3.1 2.8 2.4 URB ART 1.1 0.9 1.0 1.2 1.6 2.3 3.9 5.9 6.9 6.7 7.1 7.6 7.4 7.2 7.4 7.2 6.0 5.0 3.7 2.8 2.3 1.9 1.5 1.3 RUR FWY 2.6 2.2 2.1 2.3 2.6 3.1 3.5 4.0 4.5 5.1 5.6 5.8 5.8 5.8 5.8 5.6 5.3 4.9 4.6 4.3 4.0 3.8 3.5 3.1 RUR ART 1.5 1.3 1.4 1.6 2.2 3.0 4.2 5.3 6.1 6.7 7.0 7.1 7.0 6.9 6.8 6.3 5.5 4.6 3.8 3.1 2.6 2.3 2.1 1.7 PCTDIR URB FWY 38 40 40 46 56 64 70 70 68 62 58 52 52 52 50 46 38 38 46 52 46 42 42 40 URB ART 44 46 44 48 54 62 66 68 64 56 54 52 50 50 50 

46 40 38 46 52 48 46 46 46 RUR FWY 44 46 48 54 60 68 68 64 58 54 52 50 50 52 52 

48 42 40 44 48 48 44 46 44 
Central Ohio On-Road Mobile Emission Estimates July, 2014 43 

RUR ART 40 42 44 48 58 66 72 68 60 56 54 50 50 50 50 46 40 38 46 50 46 44 44 44 LOS E VC 0 0.625 1.25 1.875 2.5 3.125 3.75 4.375 5 5.625 6.25 6.875 7.5 8.125 8.75 9.375 10 10.625 11.25 11.875 12.5 13.125 13.75 14.375 SPEEDVC curve1 75 75 75 75 75 75 74.9 74.8 74.6 74.2 73.5 72.3 70.5 67.8 64.2 59.5 54 47.7 41.2 34.9 28.9 23.7 19.2 15.5 curve2 70 70 70 70 70 70 70 69.9 69.8 69.6 69.2 68.4 67.1 65.1 62.2 58.2 53 47 40.5 33.9 27.7 22.2 17.6 13.8 curve3 65 65 65 65 65 65 65 65 65 64.9 64.8 64.4 63.8 62.6 60.5 57 52 45.4 37.8 29.9 22.7 16.7 12.1 8.6 curve4 60 60 60 60 60 60 60 60 60 59.9 59.8 59.6 59.1 58.2 56.7 54.3 50.8 46.1 40.3 33.8 27.3 21.3 16.2 12.2 curve5 55 55 55 55 55 55 55 55 55 55 55 54.9 54.7 54.3 53.6 52.3 50 46.5 41.5 35.3 28.5 21.9 16.1 11.5 curve6 60 60 60 60 60 60 60 60 59.9 59.8 59.7 59.4 59.1 58.5 57.7 56.5 55 53.1 50.7 47.9 44.7 41.1 37.3 33.4 curve7 55 55 55 55 55 55 55 55 54.9 54.9 54.7 54.5 54.2 53.8 53.1 52.2 50.9 49.3 47.3 44.9 42.1 39 35.7 32.2 curve8 50 50 50 50 50 50 50 50 49.9 49.9 49.8 49.6 49.4 49 48.5 47.7 46.7 45.4 43.8 41.8 39.5 36.8 33.9 30.9 curve9 45 45 45 45 45 45 45 45 45 44.9 44.8 44.7 44.4 44.1 43.6 43 42.1 40.9 39.4 37.6 35.5 33.1 30.5 27.8 curve10 50 50 50 50 49.9 49.8 49.7 49.4 49 48.4 47.5 46.5 45.1 43.5 41.7 

39.6 37.3 34.9 32.4 29.8 27.3 24.9 22.6 20.4 curve11 50 50 50 50 50 49.9 49.7 49.4 48.9 48 46.7 44.9 42.5 39.6 36.2 32.6 28.7 25 21.4 18.2 15.3 12.9 10.8 9 curve12 50 50 50 50 50 49.9 49.8 49.6 49.1 48.2 46.8 44.5 41.4 37.5 32.9 28 23.1 18.7 14.9 11.8 9.2 7.2 5.7 4.5 curve13 40 40 40 40 40 40 39.9 39.8 39.5 39.2 38.6 37.8 36.7 35.3 33.5 31.4 29 26.4 23.7 21.1 18.5 16.1 13.9 12 curve14 40 40 40 40 40 39.9 39.8 39.6 39.1 38.5 37.5 36.1 34.3 32.1 29.4 26.5 23.5 20.5 17.7 15.1 12.8 10.7 9 7.6 curve15 40 40 40 40 40 39.9 39.7 39.4 38.8 37.9 36.5 34.7 32.3 29.5 26.4 

23.2 20 17 14.3 11.9 9.9 8.2 6.8 5.6 curve16 35 35 35 35 35 34.9 34.8 34.5 34 33.2 32.1 30.5 28.5 26.1 23.5 20.6 17.9 15.2 12.8 10.7 8.9 7.4 6.1 5.1 curve17 35 35 35 35 35 34.9 34.7 34.4 33.9 33.1 32 30.3 28.3 25.8 23.1 20.3 17.5 14.9 12.5 10.4 8.6 7.2 5.9 4.9 curve18 35 35 35 35 35 34.9 34.6 34.2 33.5 32.4 30.9 28.8 26.3 23.4 20.4 17.4 14.6 12.1 9.9 8.1 6.6 5.4 4.4 3.6 curve19 30 30 30 30 30 29.9 29.8 29.5 29 28.2 27.1 25.6 23.7 21.5 19.1 16.6 14.2 12 10 8.3 6.8 5.6 4.6 3.8 curve20 30 30 30 30 30 29.9 29.7 29.4 28.9 28.1 26.9 25.3 23.4 21.1 18.6 16.1 13.6 11.4 9.5 7.8 6.4 5.3 4.3 3.6 curve21 30 30 30 30 30 29.9 29.7 29.3 28.7 27.7 26.2 24.4 22.1 19.6 17 14.4 12 9.9 8.1 6.6 5.4 4.4 3.6 2.9 VC RATIO TO LOS CONVERSION (VALUE SHOWN IS LOWER LIMIT FOR THAT LOS)(URBAN ROADS USE SPEED BREAKS BELOW FOR LOS DETERMINATION) (ALL USE THE BASE VC'S TO DETERMINE EXCEEDANCE) 
Central Ohio On-Road Mobile Emission Estimates July, 2014 44 

 BASE RUR2 FWY A 0.00 0.00 0.00 

B 0.30 0.00 0.25 

C 0.50 0.10 0.40 D 0.70 0.30 0.60 

E 0.90 0.50 0.80 F 1.00 1.00 1.00 F+ 1.10 1.10 1.10 F++ 1.30 1.30 1.30 SPEED VC RATIO BREAKS FOR URBAN STREETS (HIGHEST SPEED FOR GIVEN LOS & FF SPEED) FFS B C D E F >47 42. 34. 27. 21. 16. >37 35. 28. 22. 17. 13. >32 30. 24. 18. 14. 10. <33 25. 19. 13. 9. 7. 

LEVEL OF SERVICE THRESHOLD BY AREA 

NUM LOS DEFINITION 1 F CINCINNATI,CLEVELAND,COLUMBUS CENTRAL MPO COUNTIES (CUY,FRA,HAM) 

2 E OTHER TMA MPOS (AKRON,CANTON,DAYTON,TOLEDO,YOUNGSTOWN + NON-CENTRAL COUNTIES FROM 1) 3 E OTHER MPOS & PARTS OF AREAS 1 & 2 OUTSIDE URBANIZED AREA 4 E RURAL NON MPO COUNTIES PEAK SPREADING MODEL INFO (SET MAX ITERATIONS TO 0 TO DISABLE PEAK SPREADING) MAX VC RATIO FWY: 1.30 MAX VC RATIO ART: 1.30 MAX ITERATIONS : 1000 TRUCK PCE: 2.0 

AQ SEASON FACTOR: 1.08 

MODEL CLASS PARAMETERS (MAX 4 CLASSES, HOURS 0-23 W/ NO OVERLAP IN CLASS, ALLOCATE ENTIRE CLASS AS TRUCK(1) OR NOT(0)) CLS TRK 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 CLS BEG 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 CLS END 23 23 0 0 0 0 0 0 0 0 0 0 0 0 0 0 CLS NUM 1 3 0 0 0 0 0 0 0 0 0 0 0 0 0 0  MOVES NETWORK LINK EMISSIONS OUTPUT  COUNTY MONTH VMT HC NOX SO2 PM2.5  ADA JANUARY 0. 0.0000 0.0000 0.0000 0.0000  ALL JANUARY 0. 0.0000 0.0000 0.0000 0.0000  ASD JANUARY 0. 0.0000 0.0000 0.0000 0.0000  ATB JANUARY 0. 0.0000 0.0000 0.0000 0.0000  ATH JANUARY 0. 0.0000 0.0000 0.0000 0.0000  AUG JANUARY 0. 0.0000 0.0000 0.0000 0.0000 
Central Ohio On-Road Mobile Emission Estimates 

July, 2014 45 

 BEL JANUARY 0. 0.0000 0.0000 0.0000 0.0000  BRO JANUARY 0. 0.0000 0.0000 0.0000 0.0000  BUT JANUARY 0. 0.0000 0.0000 0.0000 0.0000  CAR JANUARY 0. 0.0000 0.0000 0.0000 0.0000  CHP JANUARY 0. 0.0000 0.0000 0.0000 0.0000  CLA JANUARY 0. 0.0000 0.0000 0.0000 0.0000  CLE JANUARY 0. 0.0000 0.0000 0.0000 0.0000  CLI JANUARY 0. 0.0000 0.0000 0.0000 0.0000  COL JANUARY 0. 0.0000 0.0000 0.0000 0.0000  COS JANUARY 0. 0.0000 0.0000 0.0000 0.0000  CRA JANUARY 0. 0.0000 0.0000 0.0000 0.0000  CUY JANUARY 0. 0.0000 0.0000 0.0000 0.0000  DAR JANUARY 0. 0.0000 0.0000 0.0000 0.0000  DEF JANUARY 0. 0.0000 0.0000 0.0000 0.0000  DEL JANUARY 4593746. 0.0000 0.0000 0.0000 0.0000  ERI JANUARY 0. 0.0000 0.0000 0.0000 0.0000  FAI JANUARY 1564756. 0.0000 0.0000 0.0000 0.0000  FAY JANUARY 0. 0.0000 0.0000 0.0000 0.0000  FRA JANUARY 29955170. 0.0000 0.0000 0.0000 0.0000  FUL JANUARY 0. 0.0000 0.0000 0.0000 0.0000  GAL JANUARY 0. 0.0000 0.0000 0.0000 0.0000  GEA JANUARY 0. 0.0000 0.0000 0.0000 0.0000  GRE JANUARY 0. 0.0000 0.0000 0.0000 0.0000  GUE JANUARY 0. 0.0000 0.0000 0.0000 0.0000  HAM JANUARY 0. 0.0000 0.0000 0.0000 0.0000  HAN JANUARY 0. 0.0000 0.0000 0.0000 0.0000  HAR JANUARY 0. 0.0000 0.0000 0.0000 0.0000  HAS JANUARY 0. 0.0000 0.0000 0.0000 0.0000  HEN JANUARY 0. 0.0000 0.0000 0.0000 0.0000  HIG JANUARY 0. 0.0000 0.0000 0.0000 0.0000  HOC JANUARY 0. 0.0000 0.0000 0.0000 0.0000  HOL JANUARY 0. 0.0000 0.0000 0.0000 0.0000  HUR JANUARY 0. 0.0000 0.0000 0.0000 0.0000  JAC JANUARY 0. 0.0000 0.0000 0.0000 0.0000  JEF JANUARY 0. 0.0000 0.0000 0.0000 0.0000  KNO JANUARY 0. 0.0000 0.0000 0.0000 0.0000  LAK JANUARY 0. 0.0000 0.0000 0.0000 0.0000  LAW JANUARY 0. 0.0000 0.0000 0.0000 0.0000  LIC JANUARY 4683831. 0.0000 0.0000 0.0000 0.0000  LOG JANUARY 0. 0.0000 0.0000 0.0000 0.0000  LOR JANUARY 0. 0.0000 0.0000 0.0000 0.0000  LUC JANUARY 0. 0.0000 0.0000 0.0000 0.0000  MAD JANUARY 802361. 0.0000 0.0000 0.0000 0.0000  MAH JANUARY 0. 0.0000 0.0000 0.0000 0.0000  MAR JANUARY 0. 0.0000 0.0000 0.0000 0.0000  MED JANUARY 0. 0.0000 0.0000 0.0000 0.0000  MEG JANUARY 0. 0.0000 0.0000 0.0000 0.0000  MER JANUARY 0. 0.0000 0.0000 0.0000 0.0000  MIA JANUARY 0. 0.0000 0.0000 0.0000 0.0000  MOE JANUARY 0. 0.0000 0.0000 0.0000 0.0000  MOT JANUARY 0. 0.0000 0.0000 0.0000 0.0000 
Central Ohio On-Road Mobile Emission Estimates 

July, 2014 46 

 MRG JANUARY 0. 0.0000 0.0000 0.0000 0.0000  MRW JANUARY 0. 0.0000 0.0000 0.0000 0.0000  MUS JANUARY 107344. 0.0000 0.0000 0.0000 0.0000  NOB JANUARY 0. 0.0000 0.0000 0.0000 0.0000  OTT JANUARY 0. 0.0000 0.0000 0.0000 0.0000  PAU JANUARY 0. 0.0000 0.0000 0.0000 0.0000  PER JANUARY 0. 0.0000 0.0000 0.0000 0.0000  PIC JANUARY 771943. 0.0000 0.0000 0.0000 0.0000  PIK JANUARY 0. 0.0000 0.0000 0.0000 0.0000  POR JANUARY 0. 0.0000 0.0000 0.0000 0.0000  PRE JANUARY 0. 0.0000 0.0000 0.0000 0.0000  PUT JANUARY 0. 0.0000 0.0000 0.0000 0.0000  RIC JANUARY 0. 0.0000 0.0000 0.0000 0.0000  ROS JANUARY 0. 0.0000 0.0000 0.0000 0.0000  SAN JANUARY 0. 0.0000 0.0000 0.0000 0.0000  SCI JANUARY 0. 0.0000 0.0000 0.0000 0.0000  SEN JANUARY 0. 0.0000 0.0000 0.0000 0.0000  SHE JANUARY 0. 0.0000 0.0000 0.0000 0.0000  STA JANUARY 0. 0.0000 0.0000 0.0000 0.0000  SUM JANUARY 0. 0.0000 0.0000 0.0000 0.0000  TRU JANUARY 0. 0.0000 0.0000 0.0000 0.0000  TUS JANUARY 0. 0.0000 0.0000 0.0000 0.0000  UNI JANUARY 1375900. 0.0000 0.0000 0.0000 0.0000  VAN JANUARY 0. 0.0000 0.0000 0.0000 0.0000  VIN JANUARY 0. 0.0000 0.0000 0.0000 0.0000  WAR JANUARY 0. 0.0000 0.0000 0.0000 0.0000  WAS JANUARY 0. 0.0000 0.0000 0.0000 0.0000  WAY JANUARY 0. 0.0000 0.0000 0.0000 0.0000  WIL JANUARY 0. 0.0000 0.0000 0.0000 0.0000  WOO JANUARY 0. 0.0000 0.0000 0.0000 0.0000  WYA JANUARY 0. 0.0000 0.0000 0.0000 0.0000  XXX JANUARY 34621. 0.0000 0.0000 0.0000 0.0000  TOT JANUARY 43874524. 0.0000 0.0000 0.0000 0.0000  ADA APRIL 0. 0.0000 0.0000 0.0000 0.0000  ALL APRIL 0. 0.0000 0.0000 0.0000 0.0000  ASD APRIL 0. 0.0000 0.0000 0.0000 0.0000  ATB APRIL 0. 0.0000 0.0000 0.0000 0.0000  ATH APRIL 0. 0.0000 0.0000 0.0000 0.0000  AUG APRIL 0. 0.0000 0.0000 0.0000 0.0000  BEL APRIL 0. 0.0000 0.0000 0.0000 0.0000  BRO APRIL 0. 0.0000 0.0000 0.0000 0.0000  BUT APRIL 0. 0.0000 0.0000 0.0000 0.0000  CAR APRIL 0. 0.0000 0.0000 0.0000 0.0000  CHP APRIL 0. 0.0000 0.0000 0.0000 0.0000  CLA APRIL 0. 0.0000 0.0000 0.0000 0.0000  CLE APRIL 0. 0.0000 0.0000 0.0000 0.0000  CLI APRIL 0. 0.0000 0.0000 0.0000 0.0000  COL APRIL 0. 0.0000 0.0000 0.0000 0.0000  COS APRIL 0. 0.0000 0.0000 0.0000 0.0000  CRA APRIL 0. 0.0000 0.0000 0.0000 0.0000  CUY APRIL 0. 0.0000 0.0000 0.0000 0.0000 
Central Ohio On-Road Mobile Emission Estimates 

July, 2014 47 

 DAR APRIL 0. 0.0000 0.0000 0.0000 0.0000  DEF APRIL 0. 0.0000 0.0000 0.0000 0.0000  DEL APRIL 4593746. 0.0000 0.0000 0.0000 0.0000  ERI APRIL 0. 0.0000 0.0000 0.0000 0.0000  FAI APRIL 1564756. 0.0000 0.0000 0.0000 0.0000  FAY APRIL 0. 0.0000 0.0000 0.0000 0.0000  FRA APRIL 29955170. 0.0000 0.0000 0.0000 0.0000  FUL APRIL 0. 0.0000 0.0000 0.0000 0.0000  GAL APRIL 0. 0.0000 0.0000 0.0000 0.0000  GEA APRIL 0. 0.0000 0.0000 0.0000 0.0000  GRE APRIL 0. 0.0000 0.0000 0.0000 0.0000  GUE APRIL 0. 0.0000 0.0000 0.0000 0.0000  HAM APRIL 0. 0.0000 0.0000 0.0000 0.0000  HAN APRIL 0. 0.0000 0.0000 0.0000 0.0000  HAR APRIL 0. 0.0000 0.0000 0.0000 0.0000  HAS APRIL 0. 0.0000 0.0000 0.0000 0.0000  HEN APRIL 0. 0.0000 0.0000 0.0000 0.0000  HIG APRIL 0. 0.0000 0.0000 0.0000 0.0000  HOC APRIL 0. 0.0000 0.0000 0.0000 0.0000  HOL APRIL 0. 0.0000 0.0000 0.0000 0.0000  HUR APRIL 0. 0.0000 0.0000 0.0000 0.0000  JAC APRIL 0. 0.0000 0.0000 0.0000 0.0000  JEF APRIL 0. 0.0000 0.0000 0.0000 0.0000  KNO APRIL 0. 0.0000 0.0000 0.0000 0.0000  LAK APRIL 0. 0.0000 0.0000 0.0000 0.0000  LAW APRIL 0. 0.0000 0.0000 0.0000 0.0000  LIC APRIL 4683831. 0.0000 0.0000 0.0000 0.0000  LOG APRIL 0. 0.0000 0.0000 0.0000 0.0000  LOR APRIL 0. 0.0000 0.0000 0.0000 0.0000  LUC APRIL 0. 0.0000 0.0000 0.0000 0.0000  MAD APRIL 802361. 0.0000 0.0000 0.0000 0.0000  MAH APRIL 0. 0.0000 0.0000 0.0000 0.0000  MAR APRIL 0. 0.0000 0.0000 0.0000 0.0000  MED APRIL 0. 0.0000 0.0000 0.0000 0.0000  MEG APRIL 0. 0.0000 0.0000 0.0000 0.0000  MER APRIL 0. 0.0000 0.0000 0.0000 0.0000  MIA APRIL 0. 0.0000 0.0000 0.0000 0.0000  MOE APRIL 0. 0.0000 0.0000 0.0000 0.0000  MOT APRIL 0. 0.0000 0.0000 0.0000 0.0000  MRG APRIL 0. 0.0000 0.0000 0.0000 0.0000  MRW APRIL 0. 0.0000 0.0000 0.0000 0.0000  MUS APRIL 107344. 0.0000 0.0000 0.0000 0.0000  NOB APRIL 0. 0.0000 0.0000 0.0000 0.0000  OTT APRIL 0. 0.0000 0.0000 0.0000 0.0000  PAU APRIL 0. 0.0000 0.0000 0.0000 0.0000  PER APRIL 0. 0.0000 0.0000 0.0000 0.0000  PIC APRIL 771943. 0.0000 0.0000 0.0000 0.0000  PIK APRIL 0. 0.0000 0.0000 0.0000 0.0000  POR APRIL 0. 0.0000 0.0000 0.0000 0.0000  PRE APRIL 0. 0.0000 0.0000 0.0000 0.0000  PUT APRIL 0. 0.0000 0.0000 0.0000 0.0000 
Central Ohio On-Road Mobile Emission Estimates 

July, 2014 48 

 RIC APRIL 0. 0.0000 0.0000 0.0000 0.0000  ROS APRIL 0. 0.0000 0.0000 0.0000 0.0000  SAN APRIL 0. 0.0000 0.0000 0.0000 0.0000  SCI APRIL 0. 0.0000 0.0000 0.0000 0.0000  SEN APRIL 0. 0.0000 0.0000 0.0000 0.0000  SHE APRIL 0. 0.0000 0.0000 0.0000 0.0000  STA APRIL 0. 0.0000 0.0000 0.0000 0.0000  SUM APRIL 0. 0.0000 0.0000 0.0000 0.0000  TRU APRIL 0. 0.0000 0.0000 0.0000 0.0000  TUS APRIL 0. 0.0000 0.0000 0.0000 0.0000  UNI APRIL 1375900. 0.0000 0.0000 0.0000 0.0000  VAN APRIL 0. 0.0000 0.0000 0.0000 0.0000  VIN APRIL 0. 0.0000 0.0000 0.0000 0.0000  WAR APRIL 0. 0.0000 0.0000 0.0000 0.0000  WAS APRIL 0. 0.0000 0.0000 0.0000 0.0000  WAY APRIL 0. 0.0000 0.0000 0.0000 0.0000  WIL APRIL 0. 0.0000 0.0000 0.0000 0.0000  WOO APRIL 0. 0.0000 0.0000 0.0000 0.0000  WYA APRIL 0. 0.0000 0.0000 0.0000 0.0000  XXX APRIL 34621. 0.0000 0.0000 0.0000 0.0000  TOT APRIL 43874524. 0.0000 0.0000 0.0000 0.0000  ADA JULY 0. 0.0000 0.0000 0.0000 0.0000  ALL JULY 0. 0.0000 0.0000 0.0000 0.0000  ASD JULY 0. 0.0000 0.0000 0.0000 0.0000  ATB JULY 0. 0.0000 0.0000 0.0000 0.0000  ATH JULY 0. 0.0000 0.0000 0.0000 0.0000  AUG JULY 0. 0.0000 0.0000 0.0000 0.0000  BEL JULY 0. 0.0000 0.0000 0.0000 0.0000  BRO JULY 0. 0.0000 0.0000 0.0000 0.0000  BUT JULY 0. 0.0000 0.0000 0.0000 0.0000  CAR JULY 0. 0.0000 0.0000 0.0000 0.0000  CHP JULY 0. 0.0000 0.0000 0.0000 0.0000  CLA JULY 0. 0.0000 0.0000 0.0000 0.0000  CLE JULY 0. 0.0000 0.0000 0.0000 0.0000  CLI JULY 0. 0.0000 0.0000 0.0000 0.0000  COL JULY 0. 0.0000 0.0000 0.0000 0.0000  COS JULY 0. 0.0000 0.0000 0.0000 0.0000  CRA JULY 0. 0.0000 0.0000 0.0000 0.0000  CUY JULY 0. 0.0000 0.0000 0.0000 0.0000  DAR JULY 0. 0.0000 0.0000 0.0000 0.0000  DEF JULY 0. 0.0000 0.0000 0.0000 0.0000  DEL JULY 4961246. 4.9865 14.6985 0.0000 0.0000  ERI JULY 0. 0.0000 0.0000 0.0000 0.0000  FAI JULY 1689937. 1.5448 4.7334 0.0000 0.0000  FAY JULY 0. 0.0000 0.0000 0.0000 0.0000  FRA JULY 32351584. 53.7694 130.3709 0.0000 0.0000  FUL JULY 0. 0.0000 0.0000 0.0000 0.0000  GAL JULY 0. 0.0000 0.0000 0.0000 0.0000  GEA JULY 0. 0.0000 0.0000 0.0000 0.0000  GRE JULY 0. 0.0000 0.0000 0.0000 0.0000  GUE JULY 0. 0.0000 0.0000 0.0000 0.0000 
Central Ohio On-Road Mobile Emission Estimates 

July, 2014 49 

 HAM JULY 0. 0.0000 0.0000 0.0000 0.0000  HAN JULY 0. 0.0000 0.0000 0.0000 0.0000  HAR JULY 0. 0.0000 0.0000 0.0000 0.0000  HAS JULY 0. 0.0000 0.0000 0.0000 0.0000  HEN JULY 0. 0.0000 0.0000 0.0000 0.0000  HIG JULY 0. 0.0000 0.0000 0.0000 0.0000  HOC JULY 0. 0.0000 0.0000 0.0000 0.0000  HOL JULY 0. 0.0000 0.0000 0.0000 0.0000  HUR JULY 0. 0.0000 0.0000 0.0000 0.0000  JAC JULY 0. 0.0000 0.0000 0.0000 0.0000  JEF JULY 0. 0.0000 0.0000 0.0000 0.0000  KNO JULY 0. 0.0000 0.0000 0.0000 0.0000  LAK JULY 0. 0.0000 0.0000 0.0000 0.0000  LAW JULY 0. 0.0000 0.0000 0.0000 0.0000  LIC JULY 5058537. 5.7217 16.1163 0.0000 0.0000  LOG JULY 0. 0.0000 0.0000 0.0000 0.0000  LOR JULY 0. 0.0000 0.0000 0.0000 0.0000  LUC JULY 0. 0.0000 0.0000 0.0000 0.0000  MAD JULY 866550. 0.7521 2.3643 0.0000 0.0000  MAH JULY 0. 0.0000 0.0000 0.0000 0.0000  MAR JULY 0. 0.0000 0.0000 0.0000 0.0000  MED JULY 0. 0.0000 0.0000 0.0000 0.0000  MEG JULY 0. 0.0000 0.0000 0.0000 0.0000  MER JULY 0. 0.0000 0.0000 0.0000 0.0000  MIA JULY 0. 0.0000 0.0000 0.0000 0.0000  MOE JULY 0. 0.0000 0.0000 0.0000 0.0000  MOT JULY 0. 0.0000 0.0000 0.0000 0.0000  MRG JULY 0. 0.0000 0.0000 0.0000 0.0000  MRW JULY 0. 0.0000 0.0000 0.0000 0.0000  MUS JULY 115932. 0.0927 0.2925 0.0000 0.0000  NOB JULY 0. 0.0000 0.0000 0.0000 0.0000  OTT JULY 0. 0.0000 0.0000 0.0000 0.0000  PAU JULY 0. 0.0000 0.0000 0.0000 0.0000  PER JULY 0. 0.0000 0.0000 0.0000 0.0000  PIC JULY 833698. 0.6705 2.2002 0.0000 0.0000  PIK JULY 0. 0.0000 0.0000 0.0000 0.0000  POR JULY 0. 0.0000 0.0000 0.0000 0.0000  PRE JULY 0. 0.0000 0.0000 0.0000 0.0000  PUT JULY 0. 0.0000 0.0000 0.0000 0.0000  RIC JULY 0. 0.0000 0.0000 0.0000 0.0000  ROS JULY 0. 0.0000 0.0000 0.0000 0.0000  SAN JULY 0. 0.0000 0.0000 0.0000 0.0000  SCI JULY 0. 0.0000 0.0000 0.0000 0.0000  SEN JULY 0. 0.0000 0.0000 0.0000 0.0000  SHE JULY 0. 0.0000 0.0000 0.0000 0.0000  STA JULY 0. 0.0000 0.0000 0.0000 0.0000  SUM JULY 0. 0.0000 0.0000 0.0000 0.0000  TRU JULY 0. 0.0000 0.0000 0.0000 0.0000  TUS JULY 0. 0.0000 0.0000 0.0000 0.0000  UNI JULY 1485973. 1.7530 4.8751 0.0000 0.0000  VAN JULY 0. 0.0000 0.0000 0.0000 0.0000 
Central Ohio On-Road Mobile Emission Estimates 

July, 2014 50 

 VIN JULY 0. 0.0000 0.0000 0.0000 0.0000  WAR JULY 0. 0.0000 0.0000 0.0000 0.0000  WAS JULY 0. 0.0000 0.0000 0.0000 0.0000  WAY JULY 0. 0.0000 0.0000 0.0000 0.0000  WIL JULY 0. 0.0000 0.0000 0.0000 0.0000  WOO JULY 0. 0.0000 0.0000 0.0000 0.0000  WYA JULY 0. 0.0000 0.0000 0.0000 0.0000  XXX JULY 37391. 0.0236 0.0867 0.0000 0.0000  TOT JULY 47384488. 69.2779 175.6670 0.0000 0.0000 MOVES INTRAZONAL EMISSIONS OUTPUT FRANKLIN COUNTY  MONTH VMT HC NOX SO2 PM2.5  JANUARY 21378. 0.0000 0.0000 0.0000 0.0000  APRIL 21378. 0.0000 0.0000 0.0000 0.0000  JULY 23088. 0.0175 0.0605 0.0000 0.0000 DELAWARE COUNTY  MONTH VMT HC NOX SO2 PM2.5  JANUARY 3147. 0.0000 0.0000 0.0000 0.0000  APRIL 3147. 0.0000 0.0000 0.0000 0.0000  JULY 3399. 0.0026 0.0089 0.0000 0.0000 LICKING COUNTY  MONTH VMT HC NOX SO2 PM2.5  JANUARY 7563. 0.0000 0.0000 0.0000 0.0000  APRIL 7563. 0.0000 0.0000 0.0000 0.0000  JULY 8168. 0.0062 0.0214 0.0000 0.0000 FAIRFIELD COUNTY  MONTH VMT HC NOX SO2 PM2.5  JANUARY 4163. 0.0000 0.0000 0.0000 0.0000  APRIL 4163. 0.0000 0.0000 0.0000 0.0000  JULY 4496. 0.0034 0.0118 0.0000 0.0000 MADISON COUNTY  MONTH VMT HC NOX SO2 PM2.5  JANUARY 782. 0.0000 0.0000 0.0000 0.0000  APRIL 782. 0.0000 0.0000 0.0000 0.0000  JULY 844. 0.0006 0.0022 0.0000 0.0000  MOVES VEHICLE BASED EMISSIONS OUTPUT  MONTH VEHICLES HC NOX SO2 PM2.5  JANUARY 1763111. 0.0000 0.0000 0.0000 0.0000  APRIL 1763111. 0.0000 0.0000 0.0000 0.0000  JULY 1904160. 52.1614 51.2648 0.0000 0.0000 
Central Ohio On-Road Mobile Emission Estimates July, 2014 51 

Appendix C – MORPC HPMS VMT and Emissions

COMBINED OFF-MODEL AREA EMISSIONS 2008 MOVES BASED HPMS EMISSIONS REPORT MORPC area AQ analysis - Ozone emissions Analysis Input VMT File: N:\AQ\MOVES\morpc\Ozone\2014_04\model\factors\MORPC_All_Off-Model_VMT_2008.csv 

Network Emission Factors: N:\AQ\MOVES\morpc\Ozone\2014_04\model\factors\2008MORPC_ozone_3source_rpd.csv Vehicle Emission Factors: N:\AQ\MOVES\morpc\Ozone\2014_04\model\factors\2008MORPC_ozone_3source_rpv.csv Vehicle Population: N:\AQ\MOVES\morpc\Ozone\2014_04\model\factors\Source_Type_Pop_2008_MORPC_off-model_HPMS.csv -----------------------------------------  DATE:04/29/2014 TIME:12:52:09  PARAMETER FILE DUMP (DAILY.DAT FILE) HOUR 0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 PCTADT 

URB FWY 0.9 0.6 0.5 0.6 0.9 2.2 5.2 7.3 6.4 5.2 4.9 5.1 5.3 5.5 6.1 

7.2 8.0 7.9 5.8 4.2 3.4 2.9 2.2 1.5 URB ART 0.7 0.4 0.3 0.3 0.6 1.5 3.5 5.7 5.5 5.1 5.3 6.2 6.5 6.4 6.8 7.6 8.2 8.1 6.2 4.8 4.0 3.0 1.9 1.3 RUR FWY 1.4 1.1 0.9 1.0 1.3 2.2 3.7 5.2 5.4 5.4 5.6 5.6 5.7 6.0 6.5 7.1 7.5 7.0 5.6 4.5 3.8 3.2 2.5 2.0 RUR ART 0.8 0.5 0.4 0.5 1.0 2.4 4.8 6.2 5.5 5.3 5.5 5.8 6.0 6.0 6.7 7.6 8.1 7.7 5.6 4.2 3.5 2.8 1.9 1.3  AQ SEASON FACTOR: 1.08000004  MOVES HPMS EMISSIONS OUTPUT  MONTH VMT HC NOX SO2 PM2.5  JANUARY 4521707. 0.0000 0.0000 0.0000 0.0000  APRIL 4521707. 0.0000 0.0000 0.0000 0.0000  JULY 4883444. 2.0500 9.6658 0.0000 0.0000  MOVES VEHICLE BASED EMISSIONS OUTPUT  MONTH VEHICLES HC NOX SO2 PM2.5  JANUARY 143274. 0.0000 0.0000 0.0000 0.0000  APRIL 143274. 0.0000 0.0000 0.0000 0.0000  JULY 154736. 4.2387 4.1659 0.0000 0.0000