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Appendices The Platinum Triangle Subsequent EIR The Planning Center Appendix D: Air Quality Modeling Output ---PAGE BREAK--- Appendices The Platinum Triangle Subsequent EIR The Planning Center This page intentionally left blank. ---PAGE BREAK--- Page: 1 URBEMIS 2002 For Windows 7.5.0 File Name: C:\Program Files\URBEMIS 2002 For Windows\Projects2k2\Platinum Triangle.urb Project Name: Platinum Triangle Project Location: South Coast Air Basin (Los Angeles area) On-Road Motor Vehicle Emissions Based on EMFAC2002 version 2.2 SUMMARY REPORT (Pounds/Day - Summer) AREA SOURCE EMISSION ESTIMATES ROG NOx CO SO2 PM10 TOTALS (lbs/day,unmitigated) 473.56 115.22 48.74 0.00 0.22 OPERATIONAL (VEHICLE) EMISSION ESTIMATES ROG NOx CO SO2 PM10 TOTALS (lbs/day,unmitigated) 496.30 446.56 5,184.20 11.49 1,973.16 SUM OF AREA AND OPERATIONAL EMISSION ESTIMATES ROG NOx CO SO2 PM10 TOTALS (lbs/day,unmitigated) 969.86 561.78 5,232.93 11.49 1,973.38 Page: 2 URBEMIS 2002 For Windows 7.5.0 File Name: C:\Program Files\URBEMIS 2002 For Windows\Projects2k2\Platinum Triangle.urb Project Name: Platinum Triangle Project Location: South Coast Air Basin (Los Angeles area) On-Road Motor Vehicle Emissions Based on EMFAC2002 version 2.2 SUMMARY REPORT (Pounds/Day - Winter) AREA SOURCE EMISSION ESTIMATES ROG NOx CO SO2 PM10 TOTALS (lbs/day,unmitigated) 473.47 115.20 47.91 0.00 0.22 OPERATIONAL (VEHICLE) EMISSION ESTIMATES ROG NOx CO SO2 PM10 TOTALS (lbs/day,unmitigated) 440.45 638.35 4,818.28 10.31 1,973.16 SUM OF AREA AND OPERATIONAL EMISSION ESTIMATES ROG NOx CO SO2 PM10 TOTALS (lbs/day,unmitigated) 913.91 753.55 4,866.19 10.31 1,973.38 Page: 3 URBEMIS 2002 For Windows 7.5.0 File Name: C:\Program Files\URBEMIS 2002 For Windows\Projects2k2\Platinum Triangle.urb Project Name: Platinum Triangle Project Location: South Coast Air Basin (Los Angeles area) On-Road Motor Vehicle Emissions Based on EMFAC2002 version 2.2 DETAIL REPORT (Pounds/Day - Winter) AREA SOURCE EMISSION ESTIMATES (Winter Pounds per Day, Unmitigated) Source ROG NOx CO SO2 PM10 Natural Gas 8.70 115.20 47.91 - 0.22 Wood Stoves 0.00 0.00 0.00 0.00 0.00 ---PAGE BREAK--- Fireplaces 0.00 0.00 0.00 0.00 0.00 Landscaping - No winter emissions Consumer 464.77 - - - - TOTALS(lbs/day,unmitigated) 473.47 115.20 47.91 0.00 0.22 Page: 4 UNMITIGATED OPERATIONAL EMISSIONS ROG NOx CO SO2 PM10 Apartments high rise 134.19 182.61 1,413.90 3.05 568.05 Retail 192.40 285.02 2,132.26 4.48 869.63 General office building 113.86 170.72 1,272.11 2.78 535.48 TOTAL EMISSIONS (lbs/day) 440.45 638.35 4,818.28 10.31 1,973.16 Does not include correction for passby trips. Does not include double counting adjustment for internal trips. OPERATIONAL (Vehicle) EMISSION ESTIMATES Analysis Year: 2025 Temperature 50 Season: Winter EMFAC Version: EMFAC2002 (9/2002) Summary of Land Uses: Unit Type Trip Rate Size Total Trips Apartments high rise 5.91 trips / dwelling units 9,500.00 56,173.50 Retail 45.64 trips / 1000 sq. ft. 2,254.00 102,879.33 General office building 15.12 trips / 1000 sq. ft. 3,265.00 49,366.80 Vehicle Assumptions: Fleet Mix: Vehicle Type Percent Type Non-Catalyst Catalyst Diesel Light Auto 53.50 0.00 100.00 0.00 Light Truck < 3,750 lbs 15.70 0.00 99.40 0.60 Light Truck 3,751- 5,750 16.50 0.00 100.00 0.00 Med Truck 5,751- 8,500 7.50 0.00 98.70 1.30 Lite-Heavy 8,501-10,000 1.00 0.00 80.00 20.00 Lite-Heavy 10,001-14,000 0.30 0.00 66.70 33.30 Med-Heavy 14,001-33,000 0.90 0.00 22.20 77.80 Heavy-Heavy 33,001-60,000 0.80 0.00 0.00 100.00 Line Haul > 60,000 lbs 0.00 0.00 0.00 100.00 Urban Bus 0.20 0.00 50.00 50.00 1.50 40.00 60.00 0.00 School Bus 0.10 0.00 0.00 100.00 Motor Home 2.00 0.00 90.00 10.00 Travel Conditions Residential Commercial Home- Home- Home- Work Shop Other Commute Non-Work Customer Urban Trip Length (miles) 11.5 4.9 6.0 10.3 5.5 5.5 Rural Trip Length (miles) 11.5 4.9 6.0 10.3 5.5 5.5 Trip Speeds (mph) 35.0 40.0 40.0 40.0 40.0 40.0 % of Trips - Residential 20.0 37.0 43.0 % of Trips - Commercial (by land use) Retail 2.0 1.0 97.0 General office building 35.0 17.5 47.5 Page: 5 Changes made to the default values for Land Use Trip Percentages Changes made to the default values for Area The wood stove option switch changed from on to off. ---PAGE BREAK--- The fireplcase option switch changed from on to off. The landscape year changed from 2004 to 2020. Changes made to the default values for Operations The operational emission year changed from 2004 to 2025. The double counting internal work trip limit changed from to 11234.7. The double counting shopping trip limit changed from to 9667.98322. The double counting other trip limit changed from to 24154.605. Page: 6 URBEMIS 2002 For Windows 7.5.0 File Name: C:\Program Files\URBEMIS 2002 For Windows\Projects2k2\Platinum Triangle.urb Project Name: Platinum Triangle Project Location: South Coast Air Basin (Los Angeles area) On-Road Motor Vehicle Emissions Based on EMFAC2002 version 2.2 DETAIL REPORT (Pounds/Day - Summer) AREA SOURCE EMISSION ESTIMATES (Summer Pounds per Day, Unmitigated) Source ROG NOx CO SO2 PM10 Natural Gas 8.70 115.20 47.91 - 0.22 Wood Stoves - No summer emissions Fireplaces - No summer emissions Landscaping 0.09 0.02 0.83 0.00 0.00 Consumer 464.77 - - - - TOTALS(lbs/day,unmitigated) 473.56 115.22 48.74 0.00 0.22 Page: 7 UNMITIGATED OPERATIONAL EMISSIONS ROG NOx CO SO2 PM10 Apartments high rise 180.46 127.53 1,536.71 3.44 568.05 Retail 191.83 199.92 2,248.90 4.97 869.63 General office building 124.01 119.12 1,398.59 3.08 535.48 TOTAL EMISSIONS (lbs/day) 496.30 446.56 5,184.20 11.49 1,973.16 Does not include correction for passby trips. Does not include double counting adjustment for internal trips. OPERATIONAL (Vehicle) EMISSION ESTIMATES Analysis Year: 2025 Temperature 90 Season: Summer EMFAC Version: EMFAC2002 (9/2002) Summary of Land Uses: Unit Type Trip Rate Size Total Trips Apartments high rise 5.91 trips / dwelling units 9,500.00 56,173.50 Retail 45.64 trips / 1000 sq. ft. 2,254.00 102,879.33 General office building 15.12 trips / 1000 sq. ft. 3,265.00 49,366.80 Vehicle Assumptions: Fleet Mix: Vehicle Type Percent Type Non-Catalyst Catalyst Diesel Light Auto 53.50 0.00 100.00 0.00 Light Truck < 3,750 lbs 15.70 0.00 99.40 0.60 Light Truck 3,751- 5,750 16.50 0.00 100.00 0.00 Med Truck 5,751- 8,500 7.50 0.00 98.70 1.30 Lite-Heavy 8,501-10,000 1.00 0.00 80.00 20.00 Lite-Heavy 10,001-14,000 0.30 0.00 66.70 33.30 Med-Heavy 14,001-33,000 0.90 0.00 22.20 77.80 Heavy-Heavy 33,001-60,000 0.80 0.00 0.00 100.00 ---PAGE BREAK--- Line Haul > 60,000 lbs 0.00 0.00 0.00 100.00 Urban Bus 0.20 0.00 50.00 50.00 1.50 40.00 60.00 0.00 School Bus 0.10 0.00 0.00 100.00 Motor Home 2.00 0.00 90.00 10.00 Travel Conditions Residential Commercial Home- Home- Home- Work Shop Other Commute Non-Work Customer Urban Trip Length (miles) 11.5 4.9 6.0 10.3 5.5 5.5 Rural Trip Length (miles) 11.5 4.9 6.0 10.3 5.5 5.5 Trip Speeds (mph) 35.0 40.0 40.0 40.0 40.0 40.0 % of Trips - Residential 20.0 37.0 43.0 % of Trips - Commercial (by land use) Retail 2.0 1.0 97.0 General office building 35.0 17.5 47.5 Page: 8 Changes made to the default values for Land Use Trip Percentages Changes made to the default values for Area The wood stove option switch changed from on to off. The fireplcase option switch changed from on to off. The landscape year changed from 2004 to 2020. Changes made to the default values for Operations The operational emission year changed from 2004 to 2025. The double counting internal work trip limit changed from to 11234.7. The double counting shopping trip limit changed from to 9667.98322. The double counting other trip limit changed from to 24154.605. ---PAGE BREAK--- CALINE4: CALIFORNIA LINE SOURCE DISPERSION MODEL JUNE 1989 VERSION PAGE 1 JOB: Chapman/Rampart RUN: Hour 1 (WORST CASE ANGLE) POLLUTANT: Carbon Monoxide I. SITE VARIABLES U= 1.0 M/S Z0= 175. CM ALT= 0. BRG= WORST CASE VD= .0 CM/S CLAS= 7 VS= .0 CM/S MIXH= 1000. M AMB= 5.8 PPM SIGTH= 5. DEGREES TEMP= 15.0 DEGREE II. LINK VARIABLES LINK * LINK COORDINATES * EF H W DESCRIPTION * X1 Y1 X2 Y2 * TYPE VPH (G/MI) A. NF * 5 -450 5 -150 * AG 739 1.1 .0 15.0 B. NA * 7 -150 7 0 * AG 715 1.9 .0 13.5 C. ND * 7 0 7 150 * AG 467 1.5 .0 9.9 D. NE * 5 150 5 450 * AG 467 1.1 .0 15.0 E. SF * -5 450 -5 150 * AG 279 1.1 .0 15.0 F. SA * -7 150 -7 0 * AG 210 1.9 .0 13.5 G. SD * -7 0 -7 -150 * AG 283 1.5 .0 9.9 H. SE * -5 -150 -5 -450 * AG 283 1.1 .0 15.0 I. WF * 450 9 150 9 * AG 2348 1.1 .0 19.5 J. WA * 150 11 0 11 * AG 2239 1.6 .0 18.0 K. WD * 0 11 -150 11 * AG 2167 1.3 .0 13.5 L. WE * -150 9 -450 9 * AG 2167 1.1 .0 19.5 M. EF * -450 -9 -150 -9 * AG 1445 1.1 .0 19.5 N. EA * -150 -11 0 -11 * AG 1392 1.5 .0 18.0 O. ED * 0 -11 150 -11 * AG 1894 1.3 .0 13.5 P. EE * 150 -9 450 -9 * AG 1894 1.1 .0 19.5 Q. NL * 0 -150 0 0 * AG 24 1.9 .0 9.9 R. SL * 0 150 0 0 * AG 69 1.9 .0 9.9 S. WL * 150 0 0 0 * AG 109 1.5 .0 9.9 T. EL * -150 0 0 0 * AG 53 1.5 .0 9.9 ---PAGE BREAK--- CALINE4: CALIFORNIA LINE SOURCE DISPERSION MODEL JUNE 1989 VERSION PAGE 2 JOB: Chapman/Rampart RUN: Hour 1 (WORST CASE ANGLE) POLLUTANT: Carbon Monoxide III. RECEPTOR LOCATIONS * COORDINATES RECEPTOR * X Y Z 1. NE * 16 21 1.8 2. SE * 16 -21 1.8 3. SW * -16 -21 1.8 4. NW * -16 21 1.8 IV. MODEL RESULTS (WORST CASE WIND ANGLE ) * * PRED * CONC/LINK * BRG * CONC * (PPM) RECEPTOR * (DEG) * (PPM) * A B C D E F G H 1. NE * 97. * 6.2 * .0 .0 .0 .0 .0 .0 .0 .0 2. SE * 276. * 6.1 * .0 .0 .0 .0 .0 .0 .0 .0 3. SW * 81. * 6.1 * .0 .0 .0 .0 .0 .0 .0 .0 4. NW * 96. * 6.2 * .0 .0 .0 .0 .0 .0 .0 .0 * CONC/LINK * (PPM) RECEPTOR * I J K L M N O P Q R S T 1. NE * .0 .3 .0 .0 .0 .0 .0 .0 .0 .0 .0 .0 2. SE * .0 .0 .0 .0 .0 .2 .0 .0 .0 .0 .0 .0 3. SW * .0 .0 .0 .0 .0 .0 .2 .0 .0 .0 .0 .0 4. NW * .0 .2 .0 .0 .0 .0 .0 .0 .0 .0 .0 .0 ---PAGE BREAK--- CALINE4: CALIFORNIA LINE SOURCE DISPERSION MODEL JUNE 1989 VERSION PAGE 1 JOB: Howell/Katella RUN: Hour 1 (WORST CASE ANGLE) POLLUTANT: Carbon Monoxide I. SITE VARIABLES U= 1.0 M/S Z0= 175. CM ALT= 0. BRG= WORST CASE VD= .0 CM/S CLAS= 7 VS= .0 CM/S MIXH= 1000. M AMB= 5.8 PPM SIGTH= 5. DEGREES TEMP= 15.0 DEGREE II. LINK VARIABLES LINK * LINK COORDINATES * EF H W DESCRIPTION * X1 Y1 X2 Y2 * TYPE VPH (G/MI) A. NF * 5 -450 5 -150 * AG 427 1.2 .0 15.0 B. NA * 5 -150 5 0 * AG 244 1.8 .0 9.9 C. ND * 5 0 5 150 * AG 525 1.5 .0 9.9 D. NE * 5 150 5 450 * AG 525 1.2 .0 15.0 E. SF * -7 450 -7 150 * AG 907 1.2 .0 15.0 F. SA * -5 150 -5 0 * AG 653 2.1 .0 9.9 G. SD * -5 0 -5 -150 * AG 112 1.4 .0 9.9 H. SE * -7 -150 -7 -450 * AG 112 1.2 .0 15.0 I. WF * 450 9 150 9 * AG 2074 1.1 .0 19.5 J. WA * 150 9 0 9 * AG 1987 1.6 .0 13.5 K. WD * 0 9 -150 9 * AG 2669 1.3 .0 13.5 L. WE * -150 9 -450 9 * AG 2669 1.1 .0 19.5 M. EF * -450 -7 -150 -7 * AG 1470 1.1 .0 19.5 N. EA * -150 -7 0 -7 * AG 1138 1.5 .0 13.5 O. ED * 0 -7 150 -7 * AG 1572 1.3 .0 13.5 P. EE * 150 -7 450 -7 * AG 1572 1.1 .0 19.5 Q. NL * 0 -150 0 0 * AG 183 1.8 .0 9.9 R. SL * 0 150 0 0 * AG 254 1.8 .0 9.9 S. WL * 150 0 0 0 * AG 87 1.5 .0 9.9 T. EL * -150 0 0 0 * AG 332 1.5 .0 9.9 ---PAGE BREAK--- CALINE4: CALIFORNIA LINE SOURCE DISPERSION MODEL JUNE 1989 VERSION PAGE 2 JOB: Howell/Katella RUN: Hour 1 (WORST CASE ANGLE) POLLUTANT: Carbon Monoxide III. RECEPTOR LOCATIONS * COORDINATES RECEPTOR * X Y Z 1. NE * 12 17 1.8 2. SE * 12 -16 1.8 3. SW * -10 -16 1.8 4. NW * -10 17 1.8 IV. MODEL RESULTS (WORST CASE WIND ANGLE ) * * PRED * CONC/LINK * BRG * CONC * (PPM) RECEPTOR * (DEG) * (PPM) * A B C D E F G H 1. NE * 263. * 6.2 * .0 .0 .0 .0 .0 .0 .0 .0 2. SE * 278. * 6.1 * .0 .0 .0 .0 .0 .0 .0 .0 3. SW * 83. * 6.1 * .0 .0 .0 .0 .0 .0 .0 .0 4. NW * 97. * 6.2 * .0 .0 .0 .0 .0 .0 .0 .0 * CONC/LINK * (PPM) RECEPTOR * I J K L M N O P Q R S T 1. NE * .0 .0 .3 .0 .0 .0 .0 .0 .0 .0 .0 .0 2. SE * .0 .0 .0 .0 .0 .1 .0 .0 .0 .0 .0 .0 3. SW * .0 .0 .0 .0 .0 .0 .2 .0 .0 .0 .0 .0 4. NW * .0 .3 .0 .0 .0 .0 .0 .0 .0 .0 .0 .0 ---PAGE BREAK--- CALINE4: CALIFORNIA LINE SOURCE DISPERSION MODEL JUNE 1989 VERSION PAGE 1 JOB: Manchester I-5/Katella RUN: Hour 1 (WORST CASE ANGLE) POLLUTANT: Carbon Monoxide I. SITE VARIABLES U= 1.0 M/S Z0= 175. CM ALT= 0. BRG= WORST CASE VD= .0 CM/S CLAS= 7 VS= .0 CM/S MIXH= 1000. M AMB= 5.8 PPM SIGTH= 5. DEGREES TEMP= 15.0 DEGREE II. LINK VARIABLES LINK * LINK COORDINATES * EF H W DESCRIPTION * X1 Y1 X2 Y2 * TYPE VPH (G/MI) A. NF * 5 -450 5 -150 * AG 349 1.1 .0 15.0 B. NA * 5 -150 5 0 * AG 281 2.1 .0 9.9 C. SF * -7 450 -7 150 * AG 352 1.1 .0 15.0 D. SA * -9 150 -9 0 * AG 93 2.1 .0 13.5 E. SD * -9 0 -9 -150 * AG 1121 2.1 .0 9.9 F. SE * -7 -150 -7 -450 * AG 1121 1.1 .0 15.0 G. WF * 450 11 150 11 * AG 3456 1.1 .0 24.0 H. WA * 150 9 0 9 * AG 3318 1.9 .0 13.5 I. WD * 0 9 -150 9 * AG 3393 1.4 .0 18.0 J. WE * -150 11 -450 11 * AG 3393 1.1 .0 24.0 K. EF * -450 -7 -150 -7 * AG 2665 1.1 .0 24.0 L. EA * -150 -9 0 -9 * AG 2665 1.6 .0 22.5 M. ED * 0 -9 150 -9 * AG 2308 1.3 .0 18.0 N. EE * 150 -7 450 -7 * AG 2308 1.1 .0 24.0 O. NL * 0 -150 0 0 * AG 68 2.1 .0 9.9 P. SL * 0 150 0 0 * AG 259 2.1 .0 9.9 Q. WL * 150 0 0 0 * AG 138 1.5 .0 9.9 III. RECEPTOR LOCATIONS * COORDINATES RECEPTOR * X Y Z 1. NE * 12 17 1.8 2. SE * 12 -21 1.8 3. SW * -17 -21 1.8 4. NW * -17 17 1.8 ---PAGE BREAK--- CALINE4: CALIFORNIA LINE SOURCE DISPERSION MODEL JUNE 1989 VERSION PAGE 2 JOB: Manchester I-5/Katella RUN: Hour 1 (WORST CASE ANGLE) POLLUTANT: Carbon Monoxide IV. MODEL RESULTS (WORST CASE WIND ANGLE ) * * PRED * CONC/LINK * BRG * CONC * (PPM) RECEPTOR * (DEG) * (PPM) * A B C D E F G H 1. NE * 98. * 6.4 * .0 .0 .0 .0 .0 .0 .0 .5 2. SE * 277. * 6.3 * .0 .0 .0 .0 .0 .0 .0 .0 3. SW * 79. * 6.3 * .0 .0 .0 .0 .0 .0 .0 .0 4. NW * 96. * 6.5 * .0 .0 .0 .0 .0 .0 .0 .4 * CONC/LINK * (PPM) RECEPTOR * I J K L M N O P Q 1. NE * .0 .0 .0 .0 .0 .0 .0 .0 .0 2. SE * .0 .0 .0 .3 .0 .0 .0 .0 .0 3. SW * .0 .0 .0 .0 .2 .0 .0 .0 .0 4. NW * .1 .0 .0 .0 .0 .0 .0 .0 .0 ---PAGE BREAK--- CALINE4: CALIFORNIA LINE SOURCE DISPERSION MODEL JUNE 1989 VERSION PAGE 1 JOB: Santiago/Meats RUN: Hour 1 (WORST CASE ANGLE) POLLUTANT: Carbon Monoxide I. SITE VARIABLES U= 1.0 M/S Z0= 175. CM ALT= 0. BRG= WORST CASE VD= .0 CM/S CLAS= 7 VS= .0 CM/S MIXH= 1000. M AMB= 5.8 PPM SIGTH= 5. DEGREES TEMP= 15.0 DEGREE II. LINK VARIABLES LINK * LINK COORDINATES * EF H W DESCRIPTION * X1 Y1 X2 Y2 * TYPE VPH (G/MI) A. NF * 5 -450 5 -150 * AG 1279 1.2 .0 15.0 B. NA * 5 -150 5 0 * AG 784 1.8 .0 9.9 C. ND * 5 0 5 150 * AG 504 1.3 .0 9.9 D. NE * 5 150 5 450 * AG 504 1.2 .0 15.0 E. SF * -5 450 -5 150 * AG 395 1.2 .0 15.0 F. SA * -5 150 -5 0 * AG 366 1.7 .0 9.9 G. SD * -5 0 -5 -150 * AG 1155 1.4 .0 9.9 H. SE * -5 -150 -5 -450 * AG 1155 1.2 .0 15.0 I. WF * 450 5 150 5 * AG 428 1.2 .0 15.0 J. WA * 150 5 0 5 * AG 287 1.6 .0 9.9 K. WD * 0 5 -150 5 * AG 864 1.3 .0 9.9 L. WE * -150 5 -450 5 * AG 864 1.2 .0 15.0 M. EF * -450 -5 -150 -5 * AG 1666 1.2 .0 15.0 N. EA * -150 -5 0 -5 * AG 1549 1.9 .0 9.9 O. ED * 0 -5 150 -5 * AG 1245 1.3 .0 9.9 P. EE * 150 -5 450 -5 * AG 1245 1.2 .0 15.0 Q. NL * 0 -150 0 0 * AG 495 1.8 .0 9.9 R. SL * 0 150 0 0 * AG 29 1.7 .0 9.9 S. WL * 150 0 0 0 * AG 141 1.6 .0 9.9 T. EL * -150 0 0 0 * AG 117 1.6 .0 9.9 ---PAGE BREAK--- CALINE4: CALIFORNIA LINE SOURCE DISPERSION MODEL JUNE 1989 VERSION PAGE 2 JOB: Santiago/Meats RUN: Hour 1 (WORST CASE ANGLE) POLLUTANT: Carbon Monoxide III. RECEPTOR LOCATIONS * COORDINATES RECEPTOR * X Y Z 1. NE * 12 12 1.8 2. SE * 12 -12 1.8 3. SW * -12 -12 1.8 4. NW * -12 12 1.8 IV. MODEL RESULTS (WORST CASE WIND ANGLE ) * * PRED * CONC/LINK * BRG * CONC * (PPM) RECEPTOR * (DEG) * (PPM) * A B C D E F G H 1. NE * 186. * 6.1 * .0 .1 .0 .0 .0 .0 .0 .0 2. SE * 276. * 6.2 * .0 .0 .0 .0 .0 .0 .0 .0 3. SW * 84. * 6.1 * .0 .0 .0 .0 .0 .0 .0 .0 4. NW * 174. * 6.2 * .0 .0 .0 .0 .0 .0 .1 .0 * CONC/LINK * (PPM) RECEPTOR * I J K L M N O P Q R S T 1. NE * .0 .0 .0 .0 .0 .0 .0 .0 .0 .0 .0 .0 2. SE * .0 .0 .0 .0 .0 .2 .0 .0 .0 .0 .0 .0 3. SW * .0 .0 .0 .0 .0 .0 .1 .0 .0 .0 .0 .0 4. NW * .0 .0 .0 .0 .0 .0 .0 .0 .0 .0 .0 .0 ---PAGE BREAK--- CALINE4: CALIFORNIA LINE SOURCE DISPERSION MODEL JUNE 1989 VERSION PAGE 1 JOB: Sportstown/Katella RUN: Hour 1 (WORST CASE ANGLE) POLLUTANT: Carbon Monoxide I. SITE VARIABLES U= 1.0 M/S Z0= 175. CM ALT= 0. BRG= WORST CASE VD= .0 CM/S CLAS= 7 VS= .0 CM/S MIXH= 1000. M AMB= 5.8 PPM SIGTH= 5. DEGREES TEMP= 15.0 DEGREE II. LINK VARIABLES LINK * LINK COORDINATES * EF H W DESCRIPTION * X1 Y1 X2 Y2 * TYPE VPH (G/MI) A. NF * 7 -450 7 -150 * AG 1115 1.3 .0 15.0 B. NA * 7 -150 7 0 * AG 213 1.9 .0 9.9 C. ND * 7 0 7 150 * AG 141 1.5 .0 9.9 D. NE * 7 150 7 450 * AG 141 1.3 .0 15.0 E. SF * -5 450 -5 150 * AG 208 1.3 .0 15.0 F. SA * -5 150 -5 0 * AG 77 1.9 .0 9.9 G. SD * -5 0 -5 -150 * AG 1138 2.1 .0 9.9 H. SE * -5 -150 -5 -450 * AG 1138 1.3 .0 15.0 I. WF * 450 9 150 9 * AG 2678 1.1 .0 19.5 J. WA * 150 11 0 11 * AG 2264 1.6 .0 18.0 K. WD * 0 11 -150 11 * AG 3166 1.4 .0 13.5 L. WE * -150 9 -450 9 * AG 3166 1.1 .0 19.5 M. EF * -450 -9 -150 -9 * AG 2379 1.1 .0 19.5 N. EA * -150 -11 0 -11 * AG 2320 1.6 .0 18.0 O. ED * 0 -11 150 -11 * AG 1935 1.3 .0 13.5 P. EE * 150 -9 450 -9 * AG 1935 1.1 .0 19.5 Q. NL * 0 -150 0 0 * AG 902 2.1 .0 9.9 R. SL * 0 150 0 0 * AG 131 1.9 .0 9.9 S. WL * 150 0 0 0 * AG 414 1.5 .0 9.9 T. EL * -150 0 0 0 * AG 59 1.5 .0 9.9 ---PAGE BREAK--- CALINE4: CALIFORNIA LINE SOURCE DISPERSION MODEL JUNE 1989 VERSION PAGE 2 JOB: Sportstown/Katella RUN: Hour 1 (WORST CASE ANGLE) POLLUTANT: Carbon Monoxide III. RECEPTOR LOCATIONS * COORDINATES RECEPTOR * X Y Z 1. NE * 14 21 1.8 2. SE * 14 -21 1.8 3. SW * -12 -21 1.8 4. NW * -12 21 1.8 IV. MODEL RESULTS (WORST CASE WIND ANGLE ) * * PRED * CONC/LINK * BRG * CONC * (PPM) RECEPTOR * (DEG) * (PPM) * A B C D E F G H 1. NE * 261. * 6.2 * .0 .0 .0 .0 .0 .0 .0 .0 2. SE * 276. * 6.3 * .0 .0 .0 .0 .0 .0 .0 .0 3. SW * 78. * 6.3 * .0 .0 .0 .0 .0 .0 .0 .0 4. NW * 174. * 6.4 * .0 .0 .0 .0 .0 .0 .2 .0 * CONC/LINK * (PPM) RECEPTOR * I J K L M N O P Q R S T 1. NE * .0 .0 .3 .0 .0 .0 .0 .0 .0 .0 .0 .0 2. SE * .0 .0 .0 .0 .0 .3 .0 .0 .0 .0 .0 .0 3. SW * .0 .0 .0 .0 .0 .0 .2 .0 .0 .0 .0 .0 4. NW * .0 .0 .1 .0 .0 .0 .0 .0 .0 .0 .0 .0 ---PAGE BREAK--- CALINE4: CALIFORNIA LINE SOURCE DISPERSION MODEL JUNE 1989 VERSION PAGE 1 JOB: State College/Orangewood RUN: Hour 1 (WORST CASE ANGLE) POLLUTANT: Carbon Monoxide I. SITE VARIABLES U= 1.0 M/S Z0= 175. CM ALT= 0. BRG= WORST CASE VD= .0 CM/S CLAS= 7 VS= .0 CM/S MIXH= 1000. M AMB= 5.8 PPM SIGTH= 5. DEGREES TEMP= 15.0 DEGREE II. LINK VARIABLES LINK * LINK COORDINATES * EF H W DESCRIPTION * X1 Y1 X2 Y2 * TYPE VPH (G/MI) A. NF * 9 -450 9 -150 * AG 1862 1.1 .0 19.5 B. NA * 11 -150 11 0 * AG 1625 1.8 .0 18.0 C. ND * 11 0 11 150 * AG 2443 1.8 .0 13.5 D. NE * 9 150 9 450 * AG 2443 1.1 .0 19.5 E. SF * -9 450 -9 150 * AG 1718 1.1 .0 19.5 F. SA * -11 150 -11 0 * AG 1508 1.8 .0 18.0 G. SD * -11 0 -11 -150 * AG 2064 1.6 .0 13.5 H. SE * -9 -150 -9 -450 * AG 2064 1.1 .0 19.5 I. WF * 450 7 150 7 * AG 2788 1.1 .0 15.0 J. WA * 150 9 0 9 * AG 2185 1.8 .0 13.5 K. WD * 0 9 -150 9 * AG 2045 1.8 .0 9.9 L. WE * -150 7 -450 7 * AG 2045 1.1 .0 15.0 M. EF * -450 -7 -150 -7 * AG 1521 1.1 .0 15.0 N. EA * -150 -9 0 -9 * AG 995 1.7 .0 13.5 O. ED * 0 -9 150 -9 * AG 1337 1.4 .0 9.9 P. EE * 150 -7 450 -7 * AG 1337 1.1 .0 15.0 Q. NL * 0 -150 0 0 * AG 237 1.7 .0 9.9 R. SL * 0 150 0 0 * AG 210 1.7 .0 9.9 S. WL * 150 0 0 0 * AG 603 1.7 .0 9.9 T. EL * -150 0 0 0 * AG 526 1.7 .0 9.9 ---PAGE BREAK--- CALINE4: CALIFORNIA LINE SOURCE DISPERSION MODEL JUNE 1989 VERSION PAGE 2 JOB: State College/Orangewood RUN: Hour 1 (WORST CASE ANGLE) POLLUTANT: Carbon Monoxide III. RECEPTOR LOCATIONS * COORDINATES RECEPTOR * X Y Z 1. NE * 21 17 1.8 2. SE * 21 -17 1.8 3. SW * -21 -17 1.8 4. NW * -21 17 1.8 IV. MODEL RESULTS (WORST CASE WIND ANGLE ) * * PRED * CONC/LINK * BRG * CONC * (PPM) RECEPTOR * (DEG) * (PPM) * A B C D E F G H 1. NE * 260. * 6.4 * .0 .0 .1 .0 .0 .0 .0 .0 2. SE * 351. * 6.4 * .0 .0 .3 .0 .0 .0 .0 .0 3. SW * 80. * 6.3 * .0 .0 .0 .0 .0 .0 .1 .0 4. NW * 171. * 6.3 * .0 .0 .0 .0 .0 .0 .2 .0 * CONC/LINK * (PPM) RECEPTOR * I J K L M N O P Q R S T 1. NE * .0 .0 .2 .0 .0 .0 .0 .0 .0 .0 .0 .0 2. SE * .0 .0 .0 .0 .0 .0 .0 .0 .0 .0 .0 .0 3. SW * .0 .0 .0 .0 .0 .0 .1 .0 .0 .0 .0 .0 4. NW * .0 .0 .1 .0 .0 .0 .0 .0 .0 .0 .0 .0