&EPA United States Environmental Protection Agency Office of Transportation EPA420-B-04-011 and Air Quality July 2004 Acceleration Simulation Mode Test Procedures, Emission Standards, Quality Control Requirements, and Equipment Specifications Final Technical Guidance ------- EPA420-B-04-011 July 2004 Acceleration Simulation Mode Test Procedures, Emission Standards, Quality Control Requirements, and Equipment Specifications Final Technical Guidance Certification and Compliance Division Office of Transportation and Air Quality U.S. Environmental Protection Agency NOTICE This Technical Report does not necessarily represent final EPA decisions or positions. It is intended to present technical analysis of issues using data that are currently available. The purpose in the release of such reports is to facilitate an exchange of technical information and to inform the public of technical developments. ------- §85.1 §85.1 §85.1 TEST STANDARDS AND CALCULATIONS 3 (a) Emissions Standards 3 (b) Test Score Calculation 11 §85.2 TEST PROCEDURES 14 (a) General Requirements 14 (b) Vehicle Pre-Inspection and Preparation 14 (c) Equipment Preparation and Settings 16 (d) Test Procedures 18 (e) Second Chance Tests 24 §85.3 TEST EQUIPMENT SPECIFICATIONS 25 (a) Dynamometer Specifications 25 (b) Emission Sampling System 32 (c) Analytical Instruments 34 (d) Automated Test Process Software and Displays 38 §85.4 QUALITY CONTROL REQUIREMENTS 40 (a) General Requirements 40 (b) Dynamometer 40 (c) Emission Sampling System 45 (d) Analytic Instruments 46 §85.5 TEST RECORD INFORMATION 54 (a) General Information 54 (b) Ambient Test Conditions 54 (c) ASM Mode or Modes 54 (d) Diagnostic/Quality Assurance Information 54 APPENDIX A: CALCULATING AUDIT TOLERANCES 56 Page 2 Test Standards and Calculations ------- §85.1 §85.1 §85.1 Test Standards and Calculations (a) Emissions Standards (1) Start-up ASM Standards Start-up standards should be used during the first cycle of the program. The exhaust emissions standards for the following model years and vehicle types are cross- referenced by the number in the column in §85.1(a)(4), as noted in the column headings: (i) Light Duty Vehicles. Model Years Hydrocarbons Carbon Monoxide Oxides of Nitrogen 1996+ 1991-1995 1983-1990 1981-1982 1980 1977-1979 1975-1976 1973-1974 1968-1972 Table §85.1 (a)(4)(i) 1 2 4 4 4 11 11 13 13 (10 Hi gh- Altitude Li ght Duty Model Years 1983-1984 1982 (iii) Light Model Years 1996+ <3750 LVW 1996+ >3750 LVW 1991-1995 1988-1990 1984-1987 1979-1983 1975-1978 Hydrocarbons Table §85. 1 (a)(4)(i) 4 4 Duty Trucks 1 (less Hydrocarbons Table §85.1 (a)(4)(i) 1 2 5 7 7 11 12 Table §85. 1 (a)(4)(ii) 21 22 23 26 26 30 30 34 34 Vehicles. Carbon Monoxide Table §85. 1 (a)(4)(ii) 26 29 Table §85. 1 (a)(4)(iii) 41 42 43 43 48 48 50 50 51 Oxides of Nitrogen Table §85. 1 (a)(4)(iii) 43 43 than 6000 pounds GVWR). Carbon Monoxide Table §85. 1 (a)(4)(ii) 21 22 26 29 29 31 32 Oxides of Nitrogen Table §85. 1 (a)(4)(iii) 41 42 43 44 49 49 50 Page 3 Test Standards and Calculations ------- §85.1 §85.1 1973-1974 13 34 50 1968-1972 13 34 51 (iv) High-Altitude Light Duty Trucks 1 (less than 6000 pounds GVWR). Model Years Hydrocarbons Carbon Monoxide Oxides of Nitrogen Table §85.1 (a)(4)(i) Table §85.1 (a)(3)(ii) Table §85.1 (a)(4)(iii) 1991+ 6 28 43 1988-1990 9 30 44 1984-1987 9 30 49 1982-1983 12 33 49 (v) Light Duty Trucks 2 (greater than 6000 pounds GVWR). Model Years Hydrocarbons Carbon Monoxide Oxides of Nitrogen Table §85.1 (a)(4)(i) Table §85.1 (a)(4)(ii) Table §85.1 (a)(4)(iii) 1996+ <5750LVW 2 22 42 1996+ >5750LVW 5 26 45 1991-1995 5 26 46 1988-1990 7 29 47 1984-1987 7 29 49 1979-1983 11 31 49 1975-1978 12 32 50 1973-1974 13 34 50 1968-1972 13 34 51 (vi) High-Altitude Light Duty Trucks 2 (greater than 6000 pounds GVWR). Model Years Hydrocarbons Carbon Monoxide Oxides of Nitrogen Table §85.1 (a)(4)(i) Table §85.1 (a)(4)(ii) Table §85.1 (a)(4)(iii) 1991+ 6 28 46 1988-1990 9 30 47 1984-1987 9 30 49 1982-1983 12 33 49 (2) Original Final ASM Standards The following exhaust emissions standards are designed to achieve the emission reduction credits issued by EPA. They should only be used after at least one cycle of operation using the start-up standards in §85.1(a)(l). The exhaust emissions standards for the following model years and vehicle types are cross-referenced by the number in the column in §85.1(a)(4), as noted in the column headings. Revised Final Standards are provided in §85.1(a)(3) below. Use of these Revised Final Standards will provide the same emission reduction credits available as use of the Original Final ASM Standards. It is permissible to use combinations of the Original Page 4 Test Standards and Calculations ------- §85.1 §85.1 Final and Revised Final Standards, e.g. a state may implement the Original Final Standards for LDTs and the Revised Final Standards for LDVs. (i) Light Duty Vehicles. Model Years 1996+ 1983-1995 1981-1982 1980 1977-1979 1975-1976 1973-1974 1968-1972 Hydrocarbons Table §85.1 (a)(4)(i) 1 1 1 1 6 6 10 10 Carbon Monoxide Table §85.1 (a)(4)(ii) 21 21 23 23 27 27 32 32 (ii) High-Altitude Light Duty Vehicles. Model Years 1983-1984 1982 Hydrocarbons Table §85.1 (a)(4)(i) 2 2 Carbon Monoxide Table §85.1 (a)(4)(ii) 23 23 Oxides of Nitrogen Table §85.1 (a)(4)(iii) 41 41 41 45 45 48 48 49 Oxides of Nitrogen Table §85.1 (a)(4)(iii) 41 41 (iii) Light Duty Trucks 1 (less than 6000 pounds GVWR). Model Years 1996+ 1988-1995 1984-1987 1979-1983 1975-1978 1973-1974 1968-1972 Hydrocarbons Table §85.1 (a)(4)(i) 1 3 3 8 9 10 10 Carbon Monoxide Table §85.1 (a)(4)(ii) 21 24 24 28 29 32 32 Oxides of Nitrogen Table §85.1 (a)(4)(iii) 41 42 46 46 48 48 49 (iv) High-Altitude Light Duty Trucks 1 (less than 6000 pounds GVWR). Model Years 1988+ 1984-1987 1982-1983 Hydrocarbons Table §85.1 (a)(4)(i) 4 4 9 Carbon Monoxide Table §85.1 (a)(4)(ii) 26 26 30 Oxides of Nitrogen Table §85.1 (a)(4)(iii) 42 46 46 Page 5 (v) Light Duty Trucks 2 (greater than 6000 pounds GVWR). Model Years Hydrocarbons Carbon Monoxide Oxides of Nitrogen Test Standards and Calculations ------- §85.1 §85.1 Table §85.1 (a)(4)(i) Table §85.1 (a)(4)(ii) Table §85.1 (a)(4)(iii) 1996+ 1 21 41 1988-1995 3 24 44 1984-1987 3 24 46 1979-1983 8 28 46 1975-1978 9 29 48 1973-1974 10 32 48 1968-1972 10 32 49 (vi) High-Altitude Light Duty Trucks 2 (greater than 6000 pounds GVWR). Model Years Hydrocarbons Carbon Monoxide Oxides of Nitrogen Table §85.1 (a)(4)(i) Table §85.1 (a)(4)(ii) Table §85.1 (a)(4)(iii) 1988+ 4 26 44 1984-1987 4 26 46 1982-1983 9 30 46 (3) Revised Final ASM Standards The following exhaust emissions standards are designed to achieve the emission reduction credits issued by EPA. They should only be used after at least one cycle of operation using the start-up standards in §85.1(a)(l). The Revised Final Standards are of the form depicted below. Vehicle Engine Displacement (1) * Avg Emission <= Revised Standard The Avg Emission is defined in §85.1(b)(l)(iv) and the vehicle shall pass the appropriate ASM test if the product of Engine Displacement and the respective Avg Emission is less than or equal to the Revised Standard for all three pollutants (HC, CO &NO). NOTE: The only exception to the form described above is for the ASM2525 LDT1 HC standards. In this one case, the standards listed for HC in 85. l(3)(iv) below, are to be compared directly to the Avg HC reading as defined in §85. l(b)(l)(iv). If the Avg HC measurement is less than the Revised Standard, the vehicle's HC emissions are to receive a passing grade. This deviation from the procedure described above is only to be used for the HC ASM2525 LDT1 Revised Standards. It is permissible to use combinations of the Original Final and Revised Final Standards, e.g. a state may implement the Original Final Standards for LDTs and the Revised Final Standards for LDVs. The units of the Revised Standard are (ppm * liter) for HC and NO and (%* liter) for CO. Page 6 Test Standards and Calculations ------- §85.1 §85.1 There are no High Altitude or Light Duty Truck 2 Revised Final Standards available at this time. (i) ASM5015 Light Duty Vehicles Pollutant MY Revised Standard HC 1980+ 275 CO 1980-1982 1.3 1983+ 1.1 NO 1980 8,500 1981+ 3,600 (ii) ASM2525 Light Duty Vehicles Pollutant MY Revised Standard (iii) (iv) HC 1980-1989 1990+ CO 1980-1982 1983+ NO 1980 1981+ 500 300 2.3 1.6 4,750 3,500 ASM5015 Light Duty Trucks 1 (less than 6000 pounds GVWR) Pollutant MY HC 1980-1983 1984-1995 1996+ CO 1980-1983 1984-1995 1996+ NO 1980-1987 1988-1995 1996+ Revised Standard 1140 537 275 9.7 5.4 1.1 14,145 7,380 6,150 ASM2525 Light Duty Trucks 1 (less than 6000 pounds GVWR) Pollutant MY HC* 1980-1983 1984-1995 1996+ CO 1980-1983 1984-1995 1996+ NO 1980-1987 1988-1995 1996+ Revised Standard 340 160 82 23.28 12.96 4.4 32,200 16,800 14,000 See NOTE above in §85.1(3) regarding the application of the HC ASM2525 LDT1 Revised Standards. Page 7 Test Standards and Calculations ------- §85.1 §85.1 (4) ASM 2525 and 5015 Concentration Tables for Phase-In & Original Final Standards (i) ASM2525 and ASM5015 Hydrocarbon (ppm C6) Table Column # ETW 1750 1875 2000 2125 2250 2375 2500 2625 2750 2875 3000 3125 3250 3375 3500 3625 3750 3875 4000 4125 4250 4375 4500 4625 4750 4875 5000 5125 5250 5375 5500 5625 5750 5875 6000 6125 6250 6375 6500 6625 6750 6875 7000 7125 7250 7375 7500 1 5015 142 134 197 191 1 15 10Q 105 100 Q6 Q9 8q 86 83 81 78 76 74 79 71 6Q 67 66 65 63 69 61 60 58 57 56 S5 54 53 59 51 50 50 4Q 48 48 47 47 47 47 47 47 A7 1 2525 136 129 193 1 16 1 1 1 106 101 Q7 Q3 8Q 86 83 80 78 76 74 79 70 68 67 65 64 63 61 60 5Q 58 57 56 S5 54 53 59 51 50 4Q 48 48 47 46 46 46 46 46 46 46 Af. 2 5015 224 212 901 1Q1 189 173 166 15Q 159 146 141 136 139 198 194 190 117 114 119 10Q 107 104 109 100 Q8 Q6 Q4 Q3 Q1 8Q 87 86 84 83 81 80 7Q 77 76 76 75 75 74 74 74 74 7A 2 2525 216 205 1Q4 184 175 167 160 153 147 141 136 139 197 193 190 117 114 111 108 106 103 101 qq q7 q5 q3 q9 qo 88 86 85 83 89 80 7q 78 76 75 74 74 73 73 79 79 79 79 79 3 5015 257 243 930 9iq 908 iqs isq 181 173 167 160 155 14q 145 140 136 133 19Q 196 193 190 1 18 1 15 113 110 108 106 104 109 100 qs q6 q4 q9 qo sq 87 86 85 84 83 83 83 89 89 89 S9 ^ 2525 249 236 993 919 901 iq9 183 175 168 161 155 150 145 140 136 139 19Q 195 199 i iq 1 17 1 14 1 19 ioq 107 105 103 101 qq q7 q5 q3 qi qo 88 86 85 84 83 89 81 81 80 80 80 80 Sfl 4 5015 291 275 960 946 934 993 919 903 194 187 180 173 167 169 157 159 148 144 140 137 134 131 198 195 199 190 117 1 15 1 19 1 10 108 106 104 109 100 98 96 95 93 99 91 91 91 90 90 90 qn 4 2525 282 266 959 93q 997 916 906 1Q7 isq 181 174 168 169 157 159 148 144 140 137 133 130 197 194 199 iiq 117 114 1 19 1 10 107 105 103 101 qq q7 q5 q4 q9 qi qo sq sq 88 88 88 88 SS 5 5015 324 306 98q 974 960 947 936 995 916 907 iqq iqi 185 i7q 173 168 163 15q 155 151 147 144 141 137 134 139 19Q 196 193 191 1 18 116 113 111 ioq 107 105 103 109 101 100 qq qq qs qs qs qs 5 2525 315 2q? 981 967 953 941 930 91Q 910 901 1Q4 186 180 174 i6q 164 ISQ 155 151 147 143 140 137 134 131 198 196 193 190 1 18 1 15 113 111 108 106 104 109 101 qq qs q7 q7 q6 q6 q6 q6 qfi 6 5015 374 353 333 316 9qq 984 971 95q 947 937 998 91Q 91 1 904 iqs 1Q9 186 181 176 179 167 164 160 156 153 14Q 146 143 140 137 134 131 198 195 193 190 1 18 1 16 1 14 113 119 111 111 1 1 1 1 1 1 1 1 1 1 1 1 6 2525 364 344 395 308 9q9 977 964 959 941 931 999 914 906 iqq iq3 187 189 177 179 168 164 160 156 159 14Q 146 143 13q 136 133 130 198 195 199 190 1 18 1 15 1 13 1 19 110 ioq ioq 108 108 108 108 ins 7 5015 390 368 348 399 319 997 983 970 958 947 937 998 990 913 906 900 194 188 183 179 174 170 166 169 159 155 159 148 145 149 139 136 133 130 197 195 193 190 1 19 117 116 115 115 1 15 1 15 1 15 1 1 S 7 2525 381 359 339 391 305 990 976 963 959 941 939 993 915 908 901 195 189 184 179 175 170 166 169 159 155 159 148 145 149 139 136 133 130 197 194 199 190 1 18 1 16 114 113 113 119 1 19 1 19 1 19 1 19 8 5015 407 384 363 343 395 309 994 981 969 957 947 938 999 991 914 907 901 196 191 186 181 177 179 169 165 161 157 154 150 147 144 141 138 135 139 199 197 195 193 191 190 119 119 1 19 1 19 1 19 1 iq 8 2525 397 375 354 335 318 309 988 974 969 951 941 939 994 916 909 903 197 191 186 181 177 173 169 165 161 157 154 150 147 144 141 138 135 139 199 196 194 199 190 119 117 117 116 1 16 1 16 1 16 1 Ifi 9 5015 457 431 407 385 365 346 399 314 300 987 976 965 956 947 939 931 994 918 919 906 901 196 199 187 183 179 175 171 167 163 159 156 159 149 146 143 140 138 136 134 139 139 131 131 131 131 ni 9 2525 447 421 398 376 357 339 399 307 994 981 970 960 950 941 934 996 990 913 908 909 197 199 188 183 179 175 171 167 163 159 156 159 149 146 143 140 137 135 133 131 199 199 198 198 198 198 19S 10 5015 706 665 697 599 560 531 505 481 459 439 490 404 388 374 369 350 339 399 390 31 1 303 995 987 980 973 967 960 954 948 949 936 931 995 990 915 910 906 909 199 196 194 193 199 199 199 199 iq9 10 2525 694 653 616 589 551 599 496 479 451 431 413 397 389 368 355 344 333 393 314 305 997 990 989 975 969 969 956 950 944 938 939 996 991 916 911 906 909 198 195 199 190 189 188 188 188 188 1SS 11 5015 774 729 688 650 615 583 554 598 503 481 461 443 496 41 1 397 384 379 361 351 341 339 393 315 308 300 993 986 979 979 966 959 953 947 941 936 931 996 999 918 915 913 911 911 91 1 91 1 91 1 91 1 11 2525 761 717 676 638 604 573 544 518 495 473 453 435 419 404 390 377 365 355 345 335 396 318 310 309 995 988 981 974 967 961 955 948 943 937 939 997 999 918 914 911 909 907 907 906 906 906 9flfi 12 5015 843 794 749 707 669 635 603 574 548 594 509 489 464 447 439 418 405 393 389 371 361 359 343 335 397 319 311 304 996 989 989 976 969 963 957 951 946 949 938 934 939 930 999 999 999 999 99q 12 2525 828 780 736 6q5 658 694 5q3 564 53q 515 4q3 474 456 440 494 411 3qs 386 375 365 355 346 337 39q 391 313 305 9qs 9Q1 984 977 971 964 958 959 947 949 937 933 930 997 995 995 995 995 995 99S 13 5015 111 105 qq9 q38 887 841 800 761 796 6q5 666 63q 615 5q3 573 554 537 591 506 4q9 47q 467 455 444 433 493 419 409 3q3 383 374 365 357 348 341 333 396 390 315 310 307 305 304 304 304 304 1f\A 13 T595 109 103 975 991 879 897 786 748 714 683 654 698 604 583 563 544 597 519 497 484 471 459 447 436 495 415 405 395 386 376 367 359 350 349 334 397 390 314 309 304 301 999 998 998 998 998 9q» PageS Test Standards and Calculations ------- §85.1 §85.1 (ii) ASM2525 and ASM5015 Carbon Monoxide (%CO) Table Column # ETW 1750 1875 2000 2125 2250 2375 2500 2625 2750 2875 3000 3125 3250 3375 3500 3625 3750 3875 4000 4125 4250 4375 4500 4625 4750 4875 5000 5125 5250 5375 5500 5625 5750 5875 6000 6125 6250 6375 6500 6625 6750 6875 7000 7125 7250 7375 7500 21 5015 080 075 071 068 064 061 0 59 0 56 0 54 0 52 0 50 048 046 0 45 044 042 041 04Q 0 39 038 03? 036 036 035 0 34 0 34 033 0 32 032 031 030 030 0 99 0 99 098 098 09? 09? 096 096 096 096 095 095 095 095 n 9S 21 •>s->s 077 073 0 69 066 062 0 59 05? 0 54 0 52 0 50 048 046 045 043 042 041 04Q 0 39 038 0 3? 036 035 035 034 033 033 032 031 031 030 030 099 0 99 098 098 09? 09? 096 096 096 096 095 095 095 095 095 n 9S 22 5015 1 96 1 19 1 13 1 0? 1 02 097 093 0 89 0 85 0 82 0 79 076 073 071 069 06? 065 063 0 62 06Q 0 59 0 58 0 5? 055 0 54 0 53 0 52 0 51 0 50 049 048 04? 046 045 0 44 0 44 043 042 042 0 41 041 04Q 04Q 04Q 040 040 n An 22 2525 1 92 1 16 1 09 1 04 099 094 090 086 0 82 0 79 076 073 071 069 06? 065 063 061 06Q 0 58 05? 0 56 055 0 54 0 53 0 52 0 51 0 50 049 048 04? 046 045 0 44 0 44 043 042 042 041 041 0 41 04Q 04Q 04Q 040 040 n An 23 5015 1 64 1 55 1 4? 1 39 1 32 1 96 1 90 1 15 1 10 1 05 1 01 098 094 091 088 086 0 83 0 81 0 79 07? 075 074 072 070 0 69 0 6? 066 065 063 062 061 0 59 0 58 0 5? 0 56 0 55 0 54 053 0 52 0 52 0 51 0 51 0 51 0 51 0 50 0 50 n sn 23 2525 1 83 1 72 1 63 1 54 1 47 1 39 1 33 1 97 1 91 1 16 1 12 1 08 1 04 1 00 09? 094 0 92 0 89 0 8? 0 85 0 83 0 81 079 07? 076 074 073 071 070 068 06? 065 064 063 062 061 060 0 59 0 58 05? 0 5? 0 56 0 56 0 56 0 56 0 56 n =,f. 24 5015 902 1 91 1 81 1 71 1 62 1 54 1 4? 1 41 1 34 1 99 1 94 1 19 1 15 1 U 1 08 1 05 1 02 0 99 096 0 94 092 0 89 0 8? 0 85 0 84 0 82 0 80 078 07? 075 073 072 07Q 0 69 0 6? 066 065 064 063 062 0 61 0 61 0 61 0 61 061 061 n f.\ 24 2525 943 999 9 1? 905 1 94 1 85 1 76 1 68 1 60 1 54 1 48 1 42 1 37 1 32 1 98 1 94 1 90 1 17 1 14 1 U 1 08 1 06 1 03 1 01 0 99 0 9? 095 0 92 090 0 89 0 8? 0 85 0 83 0 81 0 80 078 07? 076 074 073 073 072 072 072 072 072 n 79 25 5015 991 9 09 1 9? 1 8? 1 7? 1 69 1 61 1 53 1 4? 1 41 1 35 1 30 1 96 1 91 1 17 1 14 1 U 1 08 1 05 1 02 1 00 09? 095 093 0 91 0 89 0 8? 0 85 083 0 81 080 078 076 075 073 072 071 069 068 06? 0 6? 066 066 066 066 066 n f.f. 25 2525 973 9 58 943 930 9 18 9 0? 1 9? 1 88 1 80 1 72 1 66 1 59 1 53 1 48 1 43 1 39 1 35 1 31 1 98 1 94 1 91 1 18 1 16 1 13 1 10 1 08 1 05 1 03 1 01 099 09? 094 0 92 0 91 0 89 0 8? 0 85 0 84 0 83 0 82 0 81 0 80 0 80 0 80 080 080 n sn 26 5015 978 963 948 935 993 9 12 9 02 1 92 1 84 1 76 1 69 1 63 1 57 1 52 1 47 1 42 1 38 1 34 1 31 1 97 1 94 1 91 1 18 1 15 1 13 1 10 1 08 1 05 1 03 1 01 099 09? 0 94 0 92 0 91 0 89 0 8? 086 0 84 083 0 82 0 82 0 82 0 81 0 81 0 81 n si 26 2525 364 343 394 3 06 990 976 9 62 9 50 939 999 9 19 9 U 9 03 1 96 1 89 1 84 1 78 1 73 1 68 1 64 1 60 1 56 1 52 1 48 1 45 1 42 1 38 1 35 1 32 1 99 1 96 1 94 1 91 1 18 1 16 1 13 1 U 1 09 1 08 1 06 1 05 1 04 1 04 1 04 1 04 1 04 i ru 27 5015 997 9 81 965 9 51 938 996 9 15 905 1 96 1 88 1 80 1 74 1 6? 1 62 1 56 1 52 1 47 1 43 1 39 1 36 1 32 1 99 1 96 1 93 1 90 1 17 1 15 1 12 1 10 1 07 1 05 1 03 1 01 098 096 0 94 093 091 090 088 0 88 0 8? 0 8? 0 8? 086 086 n Kf. 27 2525 394 371 3 51 332 3 14 998 9 84 970 9 58 94? 93? 998 990 9 12 9 05 1 98 1 92 1 8? 1 82 1 77 1 72 1 68 1 64 1 60 1 57 1 53 1 49 1 46 1 43 1 39 1 36 1 33 1 30 1 97 1 95 1 92 1 90 1 18 1 16 1 14 1 13 1 12 1 12 1 12 1 12 1 12 1 19 28 5015 3 16 9 98 9 82 96? 9 53 940 9 99 9 18 9 09 9 00 1 92 1 84 1 78 1 72 1 66 1 61 1 56 1 52 1 48 1 44 1 40 1 37 1 34 1 30 1 98 1 95 1 92 1 19 1 16 1 14 1 U 1 09 1 0? 1 04 1 02 1 00 098 096 095 094 093 0 92 0 92 0 92 092 092 n Q9 28 2525 494 400 37? 3 5? 338 391 305 9 91 978 966 9 55 945 936 998 990 9 13 90? 901 1 95 1 90 1 85 1 81 1 76 1 72 1 68 1 64 1 60 1 5? 1 53 1 50 1 46 1 43 1 40 1 3? 1 34 1 31 1 98 1 96 1 94 1 93 1 91 1 90 1 90 1 90 1 90 1 90 1 9fl 29 5015 3 54 334 3 16 9 99 9 83 9 69 9 56 9 44 933 993 9 14 9 06 1 99 1 92 1 86 1 80 1 74 1 69 1 65 1 61 1 56 1 53 1 49 1 46 1 42 1 39 1 36 1 33 1 30 1 97 1 94 1 91 1 19 1 16 1 14 1 U 1 09 1 0? 1 06 1 04 1 03 1 02 1 02 1 02 1 02 1 02 1 f!9 29 2525 485 45? 431 408 3 86 366 348 332 3 1? 303 991 979 9 69 960 9 51 943 936 999 992 9 16 9 U 906 9 01 1 96 1 91 1 8? 1 82 1 78 1 74 1 70 1 66 1 62 1 59 1 55 1 52 1 49 1 46 1 43 1 41 1 39 1 37 1 36 1 36 1 36 1 36 1 36 1 If. 30 5015 3 92 3 70 349 331 3 13 998 9 83 970 9 58 94? 93? 998 990 9 12 905 1 99 1 93 1 87 1 82 1 77 1 73 1 68 1 64 1 61 1 57 1 53 1 50 1 46 1 43 1 40 1 37 1 34 1 31 1 98 1 95 1 93 1 90 1 18 1 16 1 15 1 14 1 13 1 12 1 12 1 12 1 12 1 19 30 2525 545 5 14 485 458 434 412 391 373 3 56 341 39? 3 14 3 02 9 91 9 82 973 964 9 5? 9 49 943 936 931 9 95 9 19 9 14 9 09 904 9 00 1 95 1 90 1 86 1 82 1 78 1 74 1 70 1 66 1 63 1 60 1 57 1 55 1 54 1 52 1 52 1 52 1 52 1 52 1 S9 31 5015 431 406 3 83 363 3 44 396 3 10 996 9 83 971 9 60 9 50 940 9 32 9 94 9 1? 9 U 905 1 99 1 94 1 89 1 84 1 80 1 76 1 72 1 68 1 64 1 60 1 56 1 53 1 49 1 46 1 43 1 40 1 37 1 34 1 31 1 99 1 97 1 95 1 94 1 93 1 93 1 92 1 92 1 92 1 99 31 2525 606 570 538 5 09 482 45? 435 4 14 395 3 78 362 348 335 393 3 12 3 02 993 9 85 97? 969 9 62 9 55 9 49 943 93? 932 996 991 9 16 9 U 906 9 01 1 96 1 92 1 88 1 84 1 80 1 77 1 74 1 72 1 70 1 68 1 68 1 68 1 68 1 68 1 fiS 32 5015 507 478 451 496 404 383 365 348 332 3 18 305 9 93 9 82 9 72 963 9 55 94? 940 933 99? 9 91 9 16 9 U 906 901 1 96 1 92 1 8? 1 83 1 79 1 75 1 71 1 6? 1 63 1 60 1 5? 1 54 1 51 1 48 1 46 1 45 1 44 1 43 1 43 1 43 1 43 i /n 32 2525 796 6 84 645 6 10 578 548 591 496 473 453 434 4 1? 401 38? 374 362 3 51 3 40 331 392 3 13 305 998 990 9 83 97? 970 964 9 58 9 51 946 940 934 999 994 9 19 9 15 9 U 9 0? 9 04 902 9 00 9 00 9 00 900 900 9 nn 33 5015 596 496 468 443 490 398 379 361 345 330 3 1? 3 04 993 9 83 973 965 9 5? 949 943 936 930 9 94 9 19 9 14 9 09 9 04 1 99 1 95 1 90 1 86 1 82 1 77 1 74 1 70 1 66 1 63 1 60 1 57 1 54 1 52 1 50 1 49 1 49 1 49 1 49 1 49 1 AQ 33 2525 744 705 668 634 600 569 541 5 15 492 470 451 433 41? 402 3 88 376 364 3 54 344 334 395 3 1? 3 09 3 02 995 9 8? 9 81 974 968 961 9 55 9 49 943 938 933 998 9 93 9 19 9 15 9 12 9 10 9 08 9 08 9 08 908 908 9 ftS 34 5015 802 756 7 14 675 640 60? 578 5 51 596 503 483 464 44? 431 4 1? 404 391 3 80 3 70 3 60 3 51 3 42 334 396 3 18 3 U 303 99? 990 9 83 97? 970 9 64 9 59 9 53 948 943 9 39 935 9 32 999 998 99? 99? 9 9? 9 9? 9 97 34 T^5 990 99Q 99Q 966 9 14 86? 895 785 750 7 1? 6 8? 66Q 635 6 13 5 92 573 5 55 539 594 5 09 496 483 471 460 449 438 498 4 18 408 398 3 89 3 80 371 362 3 54 34? 340 334 398 393 3 90 3 1? 3 1? 3 1? 3 1? 3 1? •3 17 Page 9 Test Standards and Calculations ------- §85.1 §85.1 (iii) ASM2525 and ASM5015 Nitric Oxide (ppm NO) Table Column # ETW 1750 1875 2000 2125 2250 2375 2500 2625 2750 2875 3000 3125 3250 3375 3500 3625 3750 3875 4000 4125 4250 4375 4500 4625 4750 4875 5000 5125 5250 5375 5500 5625 5750 5875 6000 6125 6250 6375 6500 6625 6750 6875 7000 7125 7250 7375 7500 41 5015 1212 1 149 1077 1018 Q64 915 86Q 898 7Q1 756 795 6Q6 670 647 695 605 586 56Q 553 538 594 510 4Q8 486 474 463 459 441 431 490 410 401 3Q1 383 374 366 35Q 359 346 341 338 335 335 335 335 335 T3S 41 2525 1095 1031 Q73 Q90 871 897 786 74Q 715 684 656 630 607 585 566 547 531 515 501 487 475 463 451 440 430 490 410 400 3Q1 389 373 364 356 348 340 333 396 390 315 311 307 305 305 305 305 305 ™s 42 5015 1819 1713 1616 1597 1446 1379 1304 1949 1186 1 134 1088 1045 1006 970 937 907 879 853 899 807 786 766 747 798 711 694 677 661 646 631 616 601 587 574 561 549 538 598 519 519 507 503 509 509 509 509 Sfl9 42 2525 1642 1547 1460 1380 1307 1940 1179 1193 1079 1096 984 945 910 878 848 891 796 773 751 731 719 694 677 661 645 630 615 600 586 573 559 546 534 599 510 499 489 480 473 466 461 458 457 457 457 457 /LS7 43 5015 2272 9181 9058 1944 1839 1744 1657 1577 1504 1438 1378 1393 1973 1997 1184 1146 1110 1077 1046 1017 990 964 939 916 893 879 850 830 810 790 771 759 734 717 701 685 671 658 647 638 631 696 694 695 695 695 fi9S 43 2525 2114 1991 1877 1774 1678 1599 1519 1440 1374 1313 1958 1908 1 163 1191 1089 1047 1014 984 956 930 905 889 859 838 818 798 778 760 741 793 706 689 673 657 649 698 615 604 593 585 578 574 573 573 573 573 S7T 44 5015 2725 9649 9499 9360 9939 9115 9009 1919 1893 1749 1668 1601 1539 1483 1439 1384 1340 1300 1969 1997 1 194 1169 1139 1104 1076 1049 1093 998 974 950 996 904 889 860 840 899 804 788 775 763 755 749 747 747 747 747 747 44 2525 2587 9435 9995 9167 9050 1943 1845 1756 1675 1601 1533 1471 1415 1363 1316 1973 1933 1 195 1 161 1 198 1098 1069 1049 1015 990 966 949 919 896 874 853 839 819 793 774 757 741 797 714 704 696 691 689 689 689 689 fiSQ 45 5015 3178 31 17 9941 9776 9695 9487 9361 9946 9149 9046 1959 1879 1806 1740 1679 1693 1571 1593 1479 1437 1398 1360 1395 1991 1959 1997 1 196 1 167 1 138 1109 1089 1055 1099 1004 980 958 937 919 909 889 879 879 870 870 870 870 S7fl 45 2525 3060 9879 9713 9561 9499 9995 9179 9073 1976 1888 1808 1734 1667 1606 1550 1498 1451 1407 1365 1397 1991 1957 1994 1193 1163 1 134 1 106 1078 1051 1095 1000 975 951 998 906 886 867 850 835 893 813 807 805 805 805 805 sns 46 5015 3631 3586 3383 3199 3018 9859 9714 9581 9460 9350 9949 9157 9073 1997 1996 1869 1809 1747 1695 1647 1609 1559 1518 1479 1441 1405 1369 1335 1301 1969 1937 1906 1176 1 147 1 190 1094 1070 1049 1030 1014 1003 995 999 999 999 999 QQ9 46 2525 3532 3393 3131 9955 9794 9646 9519 9389 9977 9175 9089 1997 1990 1849 1784 1794 1669 1618 1570 1596 1484 1444 1406 1370 1336 1309 1969 1937 1906 1176 1147 1118 1090 1064 1039 1015 993 973 956 941 931 994 991 991 991 991 Q91 47 5015 4084 4054 3894 3609 3411 3931 3066 9916 9779 9654 9539 9435 9340 9953 9174 9100 9033 1970 1919 1857 1806 1757 1711 1666 1694 1583 1549 1503 1465 1498 1399 1357 1393 1990 1959 1930 1903 1179 1158 1140 1197 1 1 18 1115 1115 1115 1115 111S 47 2525 4005 3767 3548 3348 3165 9998 9845 9706 9579 9463 9357 9960 9179 9099 9018 1950 1887 1899 1775 1794 1677 1639 1589 1548 1508 1470 1433 1397 1369 1397 1994 1961 1930 1 199 1 171 1 144 1 119 1096 1077 1060 1048 1040 1037 1037 1037 1037 im7 48 5015 4990 4990 4707 4441 4197 3974 3771 3585 3416 3961 3190 9999 9874 9767 9668 9578 9494 9417 9345 9977 9914 9154 9096 9049 1989 1938 1889 1840 1793 1747 1703 1659 1617 1577 1539 1503 1469 1439 1413 1391 1374 1364 1360 1360 1360 1360 nfifl 48 2525 4950 4655 4384 4136 3909 3701 3519 3339 3181 3037 9906 9787 9677 9577 9486 9401 9393 9951 9184 9199 9063 9007 1953 1903 1854 1806 1760 1715 1679 1699 1587 1547 1508 1471 1435 1401 1371 1343 1318 1998 1983 1973 1969 1969 1969 1969 19fiQ 49 5015 4990 4990 4778 4578 4395 4998 4076 3936 3809 3669 3510 3366 3934 3113 3009 9900 9806 9719 9638 9569 9490 9493 9359 9997 9938 9180 9195 9070 9017 1966 1916 1867 1890 1774 1731 1690 1653 1619 1590 1565 1546 1534 1530 1531 1531 1531 1ST1 49 2525 4960 4738 4535 4349 4179 4094 3881 3759 3579 3417 3970 3135 3019 9899 9796 9701 9614 9533 9457 9387 9390 9958 9198 9140 9085 9039 1980 1930 1881 1833 1786 1740 1697 1654 1614 1577 1549 1510 1483 1460 1443 1439 1498 1498 1498 1498 149S 50 5015 4990 4990 4919 4853 4799 4736 4685 4639 4596 4484 4990 41 14 3959 3804 3669 3544 3499 3393 3994 3131 3044 9961 9883 9807 9735 9665 9597 9530 9466 9403 9341 9989 9994 9168 91 16 9066 9090 1979 1943 1913 1890 1875 1870 1874 1874 1874 1S7/L 50 2525 4980 4906 4838 4776 4790 4668 4690 4577 4374 4176 3996 3839 3681 3544 3418 3309 3195 3096 3003 9917 9836 9759 9686 9616 9549 9483 9490 9359 9998 9940 9183 9197 9074 9099 1973 1997 1884 1846 1813 1785 1764 1750 1745 1745 1745 1745 174S 51 5015 4990 4990 4990 4990 4990 4990 4990 4990 4990 4899 4680 4488 431 1 4150 4009 3867 3741 3695 3517 3416 3391 3930 3145 3063 9983 9907 9833 9760 9690 9691 9554 9489 9496 9366 9308 9954 9904 9159 9119 9087 9069 9046 9040 9045 9045 9045 9fUS 51 2525 4990 4990 4990 4990 4990 4990 4990 4990 4779 4556 4359 4180 4016 3866 3798 3609 3485 3377 3976 3189 3094 3010 9930 9854 9780 9709 9640 9573 9507 9443 9381 9391 9969 9906 9159 9109 9056 9014 1977 1947 1994 1909 1904 1904 1904 1904 IQfU Page 10 Test Standards and Calculations ------- §85.1 §85.1 (b) Test Score Calculation (1) Exhaust Gas Measurement Calculation. (i) Measurement Start. The analysis and recording of exhaust gas concentrations shall begin 15 seconds after the applicable test mode begins, or sooner if the system response time (to 95% of full scale) is less than 15 seconds. The analysis and recording of exhaust gas concentrations shall not begin sooner than the time period equivalent to the response time of the slowest transducer. (ii) Sample Rate. Exhaust gas concentrations shall be analyzed at a minimum rate of once per second. (iii) Negative Values. Negative concentration readings shall be integrated as zero and recorded as such. (iv) Emission Measurement Calculations. Partial stream (concentration) emissions shall be calculated based on a running 10 second average. The values used for HCG), COG), and NOG) are the raw (uncorrected) tailpipe concentrations. ]THCG)*DCFG) (A) AvgHC = -^ 10 £COG)*DCF(J) (B) 10 10 (C) 10 (v) Dilution Correction Factor. The analyzer software shall multiply the raw emissions values by the Dilution Correction Factor (DCF) during any valid ASM emissions test. The DCF accounts for exhaust sample dilution (either intentional or unintentional) during an emissions test. The analyzer software shall calculate the DCF using the following procedure, and shall select the appropriate vehicle fuel formula. If the calculated DCF exceeds 3.0 then a default value of 3.0 shall be used. (A) X = 2 J measured 2 J 2 measured measured Page 11 Test Standards and Calculations ------- §85.1 §85.1 Where [CO2]measured and [CO]measured are the instantaneous ASM emissions test readings. (B) Calculate [CO2]adjUsted using the following formulas. (1) For Gasoline: V rrn 1 = _ — _ *100 L Jadjusted 4.644 + 1.88X (2) For Methanol or Ethanol: V rrn 1 = _ — _ *100 L Jadjusted 4.73 + 1.88X (3) For Compressed Natural Gas (CNG): (4) For Liquid Propane Gas (LPG): (C) Calculate the DCF using the following formula: L ^ " 2 J adjusted DCF = [LxU2 Jmeasur ed (vi) NO Humidity Correction Factor. The NO measurement shall be adjusted based on relative humidity using a correction factor Kh, calculated as follows: (A) Standard Method 1 1.0-0.0047(H-75) Where: H = Absolute humidity in grains of water per pound of dry air. = (43.478)Ra*Pd PB-(Pd*Ra/100) Ra = Relative humidity of the ambient air, percent. Page 12 Test Standards and Calculations ------- §85.1 §85.1 Pd = Saturated vapor pressure, mm Hg at the ambient dry bulb temperature*. = (.4.14438* 10'3) + (5.76645* 10'3 * Td) - (6.32788* 10'5 * Td2) + (2.12294*10'6 * Td3) - (7.85415*10'9 * Td4) + (6.55263*10'u *Td5) Where :Td = Dry bulb temperature, °F PB= Barometric pressure, mm Hg. (B) Revised method* v _ [0.004977(H-75)-0.004447(1-75)] j^h - e Where: H =Absolute humidity in grains of water per pound of dry air. T =Temperature in °F. NOTE: If the calculated KH using either method of calculation is greater than 2.19, the value of KH shall be set at 2.19. (2) Pass/Fail Determination. A pass or fail determination shall be made for each applicable test mode based on a comparison of the applicable test standards and the measured value for HC, CO, and NO as described in §85. l(b)(l)(iv). A vehicle shall pass the test mode if the emission values for HC, CO, and NO are simultaneously below or equal to the applicable short test standards for all three pollutants. A vehicle shall fail the test mode if the values for HC, CO, or NO, or any combination of the three, are above the applicable standards at the expiration of the test time. * SAEJ1094, §6.1.1.3, p.38, June 1992. This equation is a least squares fit to the Keenan and Keyes "steam table." It reproduces steam table values within 0.0001 in Hg for temperatures from 20° to 110°F. * This revised method for calculating Kh as a function of both T and H is based on work performed by Sierra Research under contract 68-C4-0056, Work Assignment 2-04. If the calculated value of Kh exceeds 2.19, the value of Kh shall be set to 2.19. This analysis used the same MY69, 5-vehicle sample employed for the original Kh factor study that resulted in the current CFR standard Kh calculation method (listed in (vi)(F) above). However, in many cases IM testing occurs outside the temperature limits set by the CFR for the standard method; therefore, at this time EPA recommends using the revised method when testing above 86°F. The new method makes the calculation of Kh more accurate over a wider range of temperatures. Page 13 Test Standards and Calculations ------- §85.2 §85.2 §85.2 Test Procedures (a) General Requirements. (1) Vehicle Characterization. The following information shall be determined for the vehicle being tested and used to automatically select the dynamometer power absorption settings: (i) Vehicle type: LDGV, LDGT1, LDGT2, HDGT, and others as needed (ii) Chassis model year (iii) Make (iv) Model (v) Number of cylinders (vi) Cubic inch or liters displacement of the engine (vii) Transmission type (viii) Equivalent Test Weight. (2) Ambient Conditions. The ambient temperature, absolute humidity, and barometric pressure shall be recorded continuously during the test cycle or as a single set of readings up to 4 minutes before the start of the driving cycle. (3) Restart. If shut off, the vehicle shall be restarted as soon as possible before the test and shall be running for at least 30 seconds prior to the start of the ASM driving cycle. (4) Void Test Conditions. The test shall immediately end and any exhaust gas measurements shall be voided if the instantaneous measured concentration of CO plus CO2 falls below six percent or the vehicle's engine stalls at any time during the test sequence. (5) Vehicle Brakes. The vehicle's brakes shall not be applied during the test modes. If the vehicle's brakes are applied during testing the mode timer shall be reset to zero (tt = 0). Some dynamometers do not have the ability to automatically sense if a vehicle's brakes become engaged. In these instances, it shall be the responsibility of the Program to implement technician training and test procedures so that a test shall be manually restarted if the vehicle's brakes are applied. (6) Test Termination. The test shall be aborted or terminated upon reaching the overall maximum test time. (b) Vehicle Pre-Inspection and Preparation. (1) Accessories. All accessories (air conditioning, heat, defogger, radio, automatic traction control if switchable, etc.) shall be turned off (if necessary, by the inspector). (2) Traction Control and Four-Wheel Drive (AWD). Most vehicles with traction control can be tested on AWD dynamometers; however, this is not true for all vehicles and dynamometer models. Page 14 7/28/04 Test Procedures ------- §85.2 §85.2 Vehicles with traction control systems that cannot be turned off shall not be tested on two wheel drive dynamometers. Vehicles with AWD that cannot be turned off shall only be tested on AWD dynamometers. If the AWD function can be disabled, then AWD vehicles may be tested on two wheel drive dynamometers. It is the responsibility of all vehicle OEMs to notify the Certification and Compliance Division of EPA in writing of any vehicles that can't be tested on AWD dynamometers so that EPA may share this information with state IM programs. (c) Exhaust Leaks. The vehicle shall be inspected for exhaust leaks. Audio assessment while blocking exhaust flow, or gas measurement of carbon dioxide or other gases shall be acceptable. Vehicles with leaking exhaust systems shall be rejected from testing. (4) Fluid Leaks. The vehicle shall be inspected for fluid leaks. Vehicles with leaking engine oil, transmission fluid, or coolant shall be rejected from testing. (5) Mechanical Condition. Vehicles with obvious mechanical problems (engine, transmission, brakes, or exhaust) that either create a safety hazard or could bias test results shall be rejected from testing. (6) Operating Temperature. The vehicle shall be at normal operating temperature prior to the start of the test. The vehicle temperature gauge, if equipped and operating, shall be checked to assess temperature. Vehicles in overheated condition shall be rejected from testing. (7) Tire Condition. Vehicles shall be rejected from testing if tread indicators, tire cords, bubbles, cuts, or other damage are visible. Vehicles shall be rejected from testing if they have space-saver spare tires or if they do not have reasonably sized tires on the drive axle or axles. Vehicles may be rejected if they have different sized tires on the drive axle or axles. In test-and-repair facilities, drive wheel tires shall be checked with a gauge for adequate tire pressure. In test-only facilities, drive wheel tires shall be visually checked for adequate pressure level. Drive wheel tires that appear low shall be inflated to approximately 30 psi, or to tire sidewall pressure, or vehicle manufacturer's recommendation. Alternatively, vehicles with apparent low tire pressure may be rejected from testing. (8) Gear Selection. The vehicle shall be operated during each mode of the test with the gear selector in drive for automatic transmissions and in second (or third if more appropriate) for manual transmissions for the loaded modes. (9) Roll Rotation. The vehicle shall be maneuvered onto the dynamometer with the drive wheels positioned on the dynamometer rolls. Prior to test initiation, the rolls shall be rotated until the vehicle laterally stabilizes on the dynamometer. Vehicles that cannot be stabilized on the dynamometer shall be rejected from testing. Drive wheel tires shall be dried if necessary to prevent slippage. (10) Vehicle Restraint. Testing shall not begin until the vehicle is restrained. Any restraint system shall meet the requirements of §85.3(a)(5)(ii). In addition, the parking brake shall be set for front wheel drive vehicles prior to the start of the test, unless parking brake functions on front axle or if is automatically disengaged when in gear. Page 15 Test Procedures ------- §85.2 §85.2 (11) Vehicle Conditioning. (i) Queuing Time. When a vehicle waits in a queue more than 20 minutes or when a vehicle is shut-off for more than 5 minutes prior to the test, vehicle conditioning shall be performed for 60 seconds, as specified in §85.2(b)(12)(ii)(C) below. This 60 second period is in addition to the test times described in §85.2(d). Emissions may be monitored during this cycle and if passing readings are obtained, as specified for the ASM cycle in §85.2(d), then the cycle may be terminated and the respective ASM mode skipped. (ii) Discretionary Preconditioning. At the program's discretion, any vehicle may be preconditioned using any of the following methods: (A) Non-loaded Preconditioning. Increase engine speed to approximately 2500 RPM, for up to 4 minutes, with or without a tachometer. (B) Loaded Preconditioning. Drive the vehicle on the dynamometer at 30 miles per hour for up to 240 seconds at road-load. (C) ASM Preconditioning. Drive the vehicle on the dynamometer using either mode of the ASM test as specified in §85.2(d). (D) Transient Preconditioning. After maneuvering the vehicle onto the dynamometer, drive a transient cycle consisting of speed, time, acceleration, and load relationships such as the IM240. (c) Equipment Preparation and Settings. (1) Analyzer Warm-Up. Emission testing shall be locked out until the analyzer is warmed- up and stable. The analyzer shall reach stability within 30 minutes from startup. If an analyzer does not achieve stability within the allotted time frame, it shall remain locked out from testing. The instrument shall be considered "warmed-up" when the zero and span readings for HC, CO, NO, and CO2 have stabilized within the accuracy values specified in §85.3(c)(3)(vi) for five minutes without adjustment. (2) Emission Sample System Purge. While the equipment is in operation, the sample system shall be continuously purged after each test for at least 15 minutes if not taking measurements. If the equipment has been shut down, the system shall be purged for 5 minutes or until the HC reading is less than 15 ppm C6 prior to the start of a test. (3) Probe Insertion. The sample probe shall be inserted into the vehicle's tailpipe to a minimum depth of 10 inches. If the vehicle's exhaust system prevents insertion to this depth, a tailpipe extension shall be used. Page 16 Test Procedures ------- §85.2 §85.2 (4) Multiple exhaust pipes. Exhaust gas concentrations from vehicle engines equipped with functionally independent multiple exhaust pipes shall be sampled simultaneously. The collection system shall be designed such that the flow through both probes is within ± 10%. (5) Analyzer Preparation. The analyzer shall perform an automatic zero, an ambient air reading, and an HC hang-up check prior to each test. This process shall occur within two minutes of the start of the test. (i) Automatic Gas Zero. The analyzer shall conduct automatic zero adjustments using the zero gas specified in §85.4(d)(2)(iii). The zero adjustment shall include the HC, CO, CC>2, and NO channels. Bottled or generated zero air may be used. (ii) Ambient Air Reading. Filtered ambient air shall be introduced to the analyzer before the sample pump, but after the sample probe, hose, and filter/water trap. The analyzer shall record the concentrations of the four measured gases, but shall make no adjustments. (1) The sample through probe has less than 15 ppm HC, 0.02% CO, and 25ppmNO. (iii) HC Hang-up Determination. The analyzer shall sample ambient air through the probe to determine background pollution levels and HC hang-up. The analyzer shall be locked out from testing until: (1) The residual HC in the sampling system (probe sample - ambient air reading) is less than 7 ppm. (6) Cooling System. When ambient temperatures exceed 72°F, testing shall not begin until the cooling system blower is positioned and activated. The cooling system shall be positioned to direct air to the vehicle cooling system, but shall not be directed at the catalytic converter. The use of a cooling system is optional when testing at temperatures below 50°F. If a cooling system is in use, testing shall not begin until the cooling system is positioned and activated. Furthermore, the hood may be opened at the state's discretion. (7) Dynamometer Warm-Up. Dynamometers that do not have temperature compensation shall be automatically warmed-up prior to official testing and shall be locked out until warmed-up. Dynamometers resting (not operated for at least 30 seconds and at least 15 mph) for more than 30 minutes shall pass the coast-down check specified in §85.4(b)(l) prior to use in testing. As specified in §85.4(a)(2), control charts may be used to demonstrate allowing a longer duration of inactivity before a required warm-up. If the dynamometer is not warmed-up as outlined above, then the parasitic losses, typically bearing and windage friction expressed as a function of velocity, shall be characterized as a function of bearing temperature or some alternative parameter that the manufacturer ca demonstrate is correlated with parasitic losses. Based on this characterization, the dynamometer load shall be automatically adjusted to compensate Page 17 Test Procedures ------- §85.2 §85.2 for changes in parasitic losses as a function of dynamometer temperature in order to ensure dynamometer load accuracy without having to perform dynamometer warm-ups. All-wheel-drive dynamometers must characterize losses for the entire system, i.e. both roll sets. If an all-wheel-drive dynamometer can be operated in either two- or all- wheel-drive mode, parasitic losses must be characterized in both two- and all-wheel- drive modes. System software shall automatically change parasitic losses depending on how the vehicle is tested. (8) Dynamometer Settings. Dynamometer power absorption and inertia weight settings shall be automatically chosen from an EPA-supplied or EPA-approved electronic look- up table which will be referenced based upon the vehicle identification information obtained in §85.2(a)(l)*. Vehicles not listed shall be tested using default power absorption and inertia settings in the latest version of the EPA I/M Look-up Table, as posted on EPA's web site: www.epa.gov/orcdizux/im.htm. At a minimum the look-up table on the ASM host computer should be updated once per year. (9) Engine Speed. Engine speed measurement equipment shall be attached on all 1996 and newer light duty vehicles and trucks, and in test-and-repair programs, engine speed shall also be monitored on all pre-1996 vehicles. On vehicles equipped with OBD systems (1996 and newer), it is recommended that the SAE-standardized OBD-plug be used. Engine speed measurement equipment shall meet the requirements of §85.3(c)(5). (d) Test Procedures. The test sequence shall consist of either a single ASM mode or both ASM modes described in §85.2(d)(l) and (2), and may be performed in either order (with appropriate change in transition requirements in §85.2(d)(l)(iv)). Vehicles that fail the first-chance test described in §85.2(d) shall receive a second-chance test if the conditions in §85.2(e) apply. An Alternative ASM mode is described in §85.2(d)(3). This new procedure was designed to improve vehicle throughput by reducing the likelihood of failing a vehicle because it had locked into a non- representative high emitting mode of operation. Vehicles that fail the Alternative ASM Test Procedure may be granted a second-chance test at the state's discretion. The test timer shall start (tt=0) when the conditions specified in §85.2(b) and §85.2(c) are met and the mode timer initiates as specified in §85.2(d)(l), §85.2(d)(2), or §85.2(d)(3). Maximum test times for various test scenarios are described in §85.2 (e)(l) below. The test shall be immediately terminated or aborted upon reaching the overall maximum test time. EPA last updated the look-up table on September 10, 1998 (I/M LOOK-UP TABLE, RELEASE 1.6.1). Since that time the table has been updated by states, contractors and consulting firms. Page 18 Test Procedures ------- §85.2 §85.2 (1) ASM5015Mode. (i) The mode timer shall start (mt=0) when the dynamometer speed (and corresponding power) is maintained within 15±1.0 miles per hour for 5 continuous seconds. The dynamometer shall apply the constant torque over the duration of the ASM mode. Torque shall be set to the correct torque necessary to generate the required horsepower at 15.0 mph. If actual torque applied deviates by more than 2% from the target torque for more than two consecutive seconds, the test mode timer shall be set to mt=0. (ii) The dynamometer power shall be automatically selected from an EPA-supplied or EPA-approved look-up table, based upon the vehicle identification information described in §85.2(a)(l). If a vehicle is not specifically listed in the EPA-approved table, default values from the same table shall be used. If an appropriate default value is not available in the EPA-approved table, ASM loading should be taken from the following table: Default ASM5015 Actual Horsepower Settings For 8.6" Dynamometers HP50158 Vehicle Type Sedans Station Wagons Mini-vans Pickup Trucks Sport/Utility Full Vans Number of Cylinders 3 7.9 8.1 10.2 9.6 10.1 10.3 4 11.4 11.7 14.1 13.1 13.4 13.9 5&6 13.8 13.8 15.8 16.4 15.5 17.7 8 16.4 16.1 17.9 19.2 19.4 19.6 >8 16.0 16.1 18.2 21.1 21.1 20.5 Default ASM5015 Actual Horsepower Settings For 20" Dynamometers HP501520 Vehicle Type Sedans Station Wagons Mini-vans Pickup Trucks Sport/Utility Full Vans Number of Cylinders 3 8.1 8.3 10.4 9.8 10.5 10.8 4 11.8 12.1 14.5 13.4 13.8 14.4 5&6 14.3 14.2 16.3 16.8 15.9 18.2 8 16.9 16.6 18.5 19.8 19.9 20.2 >8 16.6 16.6 18.7 21.7 21.7 21.1 If the dynamometer speed or torque falls outside the speed or torque tolerance for more than 2 consecutive seconds, or for more than 5 seconds total, the mode Page 19 Test Procedures ------- §85.2 §85.2 timer shall reset to zero and resume timing. The minimum mode length shall be determined as described in §85.2(d)(iii). The maximum mode length shall be 90 seconds elapsed time (mt=90). During the 10 second period used for the pass decision, the dynamometer speed shall not fall more than 0.5 mph (absolute drop, not cumulative). If the speed at the end of the 10 second period is more than 0.5 mph less than the speed at the start of the 10 second period, testing shall continue until the speed stabilizes enough to meet this criterion. The ten second emissions window shall be matched to the corresponding vehicle speed trace time window. This shall be performed by subtracting the nominal response time for the analyzers from the mode time to determine the time for the corresponding vehicle speed. (iii) The pass/fail analysis shall begin after an elapsed time of 25 seconds (mt=25). A pass/fail determination shall be made for the vehicle and the mode shall be terminated as follows: (A) The vehicle shall pass the ASM5015 mode and the mode shall be immediately terminated if, at any point between an elapsed time of 25 seconds (mt=25) and 90 seconds (mt=90), the 10 second running average measured values for each pollutant are simultaneously less than or equal to the applicable test standards described in §85.1 (a). (B) Pass/Fail determinations may be made at mt=15 seconds if a 50% safety margin in cutpoints is applied from mt=15 to mt=25 seconds, i.e. emissions for all pollutants are simultaneously 50% below the appropriate ASM standards. (C) The vehicle shall fail the ASM5015 mode and the mode shall be terminated if the requirements of §85.2(d)(l)(iii)(A) are not satisfied by an elapsed time of 90 seconds (mt=90). (iv) Upon termination of the ASM5015 mode, the vehicle shall immediately begin accelerating to the speed required for the ASM2525 mode. The dynamometer torque shall smoothly transition during the acceleration period and shall automatically reset to the load required for the ASM2525 mode as specified in §85.2(d)(2)(i) once the roll speed specified in §85.2(d)(2)(i) is achieved. (2) ASM2525 Mode. (i) The mode timer shall start (mt=0) when the dynamometer speed (and corresponding power) are maintained within 25±1.0 miles per hour for 5 continuous seconds. The dynamometer shall apply the constant torque over the duration of the ASM mode. Torque shall be set to the correct torque necessary to generate the required horsepower at 25.0 mph. If actual torque applied deviates by more than 2% from the target torque for more than two consecutive seconds, the test mode timer shall be set to mt=0. Page 20 Test Procedures ------- §85.2 §85.2 (ii) The dynamometer power shall be automatically selected from an EPA-supplied or EPA-approved look-up table, based upon the vehicle identification information described in §85.2(a)(l). If a vehicle is not specifically listed in the EPA-approved table, default values from the same table shall be used. If an appropriate default value is not available in the EPA-approved table, ASM loading should be taken from the following table: Default ASM2525 Actual Horsepower Settings For 8.6" Dynamometers HP25258 Vehicle Type Sedans Station Wagons Mini-vans Pickup Trucks Sport/Utility Full Vans Number of Cylinders 3 6.7 6.8 8.8 8.0 8.8 9.0 4 9.5 9.7 11.7 10.9 11.2 11.6 5&6 11.5 11.5 13.2 13.6 12.9 14.7 8 13.7 13.4 14.9 16.0 16.1 16.3 >8 13.3 13.3 15.3 17.8 17.8 17.2 Default ASM2525 Actual Horsepower Settings For 20" Dynamometers HP252520 Vehicle Type Sedans Station Wagons Mini-vans Pickup Trucks Sport/Utility Full Vans Number of Cylinders 3 6.9 7.0 8.9 8.1 8.9 9.1 4 10.1 10.4 12.5 11.4 11.8 12.5 5&6 12.3 12.2 14.0 14.4 13.6 15.5 8 14.5 14.2 15.9 16.9 17.1 17.3 >8 14.3 14.4 16.3 18.8 18.8 18.3 If the dynamometer speed or torque falls outside the speed or torque tolerance for more than two consecutive seconds, or for more than 5 seconds total, the mode timer shall reset to zero and resume timing. The minimum mode length shall be determined as described in §85.2(d)(2)(iii). The maximum mode length shall be 90 seconds elapsed time (mt=90). During the 10 second period used for the pass decision, the dynamometer speed shall not fall more than 0.5 mph (absolute drop, not cumulative). If the speed at the end of the 10 second period is more than 0.5 mph less than the speed at the start of the 10 second period, testing shall continue until the speed stabilizes enough to meet this criterion. Page 21 Test Procedures ------- §85.2 §85.2 (iii) The pass/fail analysis shall begin after an elapsed time of 25 seconds (mt=25). A pass or fail determination shall be made for the vehicle and the mode shall be terminated as follows: (A) The vehicle shall pass the ASM2525 mode if, at any point between an elapsed time of 25 seconds (mt=25) and 90 seconds (mt=90), the 10- second running average measured values for each pollutant are simultaneously less than or equal to the applicable test standards described in §85.1 (a). If the vehicle passed the ASM5015 mode, as described in §85.2(d)(l)(iii), the ASM2525 mode shall be terminated upon obtaining passing scores for all three pollutants. If the vehicle failed the ASM5015 mode, the ASM2525 mode shall continue for an elapsed time of 90 seconds (mt=90). (B) Pass/Fail determinations may be made at mt=15 seconds if a 50% safety margin in cutpoints is applied from mt=15 to mt=25 seconds, i.e. emissions for all pollutants are 50% below the appropriate ASM standards. (C) The vehicle shall fail the ASM2525 mode and the mode shall be terminated if the requirements of §85.2(d)(2)(iii)(A) are not satisfied by an elapsed time of 90 seconds (mt=90). (3) Alternative ASM2525 (ASM5015) Test Procedure (i) The Alternative ASM2525 (ASM5015) test cycle consists of three modes as depicted qualitatively below. (The same figure may be applied to the Alternative ASM5015 test if one simply recognizes that the y-axis speed value in this case should be 15 mph rather than 25 mph.) Mode 1 is 30 seconds in duration at 25 mph (15 mph), Mode 2 is a short duration speed variation, and Mode 3 is 135 seconds at 25 mph (15 mph). (ii) The timers for Mode 1 and Mode 3 shall start when the vehicle speed, dynamometer loading and dilution are within the test limits specified above in §85.2(d) (specifically §85.2(d) (l)(i) and §85.2(d)(l)(ii) for the ASM5015 or §85.2(d) (2)(i) and §85.2(d)(2)(ii) for the ASM2525) for 2 continuous seconds and no low flow error is recorded. (iii) In Mode 1, the vehicle shall pass the test and the test shall be terminated immediately if at any point between 15 and 30 seconds the 10 second running average measured values for each pollutant are simultaneously less than or equal to 50% of the applicable standards. (iv) If the 10 second running average measured values for each pollutant are not simultaneously less than or equal to 50% of the applicable standards, a speed variation up to 30 mph in 2 seconds, down to 20 mph in 4 seconds and back to 25 mph in 2 seconds shall be performed. During the speed variation there are no acceleration or speed limits; however, the target speeds must be reached. Page 22 Test Procedures ------- §85.2 §85.2 (v) For the ASM5015 test, the speed variation is from 15 mph to 20 mph, down to 10 mph and back to 15 mph in the same time increments outlined above for the ASM2525. (vi) When the vehicle has returned to 25 mph (15 mph) for 2 seconds, Mode 3 shall begin. (vii) The vehicle shall pass the test and the test shall be terminated immediately if at any point between 15 and 30 seconds the 10 second running average measured values for each pollutant are simultaneously less than or equal to 50% of the applicable standards. (viii) Starting at Second 31 in Mode 3, the vehicle shall pass the test and the test shall be terminated immediately if the 10 second running average measured values for each pollutant are simultaneously less than or equal to the applicable standards. Q. E 20 0) 5 - Qualitative Illustration of Alternative ASM Test Procedure Model 30 sec. Mode 2 ModeS 135 sec. I I Time (s) (e) Second Chance Tests. (1) If the vehicle fails the first-chance test, the test timer shall reset to zero and a second- chance test shall be performed, except as noted below. If the vehicle is not tested within 20 minutes of failing the test it shall be preconditioned by driving the vehicle at the designated test speed and appropriate inertia weight settings for an additional 60 seconds prior to the start of the retest. The second-chance test shall be of the same maximum duration as the first chance test. As each test mode is roughly 90 seconds long, the total maximum test time can vary accordingly depending on whether a one or two mode ASM test is implemented. A retest on only one mode would increase the Page 23 Test Procedures ------- §85.2 §85.2 total test time to roughly 180 seconds, while performing a retest for each mode on a vehicle that failed both modes would extend the total test time to approximately 360 seconds. Depending on the length of time it takes to perform the speed wiggle in the Alternative ASM Test Procedure, the maximum time for a single mode should be roughly 170-180 seconds. Retesting a failed vehicle could double this time to 340-360 seconds. Therefore, although the Alternative ASM Test Procedure is designed to improve a vehicle's chances of passing, performing retests using this procedure could double the overall test time versus the Original ASM Test Procedure. (2) For vehicles that fail one mode of a two mode ASM test, the failed mode may be repeated or extended as described below. An exception to this would be in the case of vehicles already subjected to preconditioning as specified in §85.2(b)(12)(i) or if at least 90 seconds of loaded preconditioning were performed, as specified in §85.2(b)(12)(ii), then the second-chance test may be omitted. (i) If the vehicle failed only the first mode (ASM5015) of the first chance test, then that mode shall be repeated upon completion of the second mode (ASM2525). The repeated mode shall be performed as described in §85.2(d)(l) except that the provisions of §85.2(d)(l)(iv) shall be omitted. The test will terminate when the mode ends or when the vehicle passes, whichever occurs first. (ii) If the vehicle is failing only the second mode (ASM2525) of the first chance test, then the second mode shall not end at 90 seconds but shall continue for up to 180 seconds. Mode and test timers shall not reset but rather continue up to 180 seconds. The provisions of §85.2(d)(2) shall continue to apply throughout the 180 second test period. (iii) If the vehicle failed both modes (ASM5015 and ASM2525) of the first chance test, then the vehicle shall receive a second-chance test for the ASM5015. If the vehicle fails the second-chance ASM5015, then the vehicle shall fail the test. Otherwise, the vehicle shall also receive a second-chance ASM2525. Page 24 Test Procedures ------- §85.3 §85.3 §85.3 Test Equipment Specifications (a) Dynamometer Specifications*. (1) General Requirements (i) While dynamometer roll diameters may range from 8.5" to 21", it is preferable that only one diameter of dynamometer roll be used throughout each program whenever possible. (ii) The dynamometer structure (e.g., bearings, rollers, pit plates, etc.) shall accommodate all light-duty vehicles and light-duty trucks up to 8500 pounds GVWR and axle weights up to 6,000 Ibs. (iii) Dynamometer ASM load horsepower (HP5015 or HP2525) shall be automatically selected based on the vehicle parameters in the test record. (iv) All dynamometers shall have an identification plate permanently affixed showing at a minimum, the dynamometer manufacturers name, the system provider's name, production date, model number, serial number, dynamometer type, maximum axle weight, maximum HP absorbed, roll diameter, roll width, base inertia weight, and electrical requirements. (v) The dynamometer shall be designed to meet specifications at an ambient temperature range of 35° to 110°F, and at absolute humidity values representative of the testing location. A wider range of operating temperatures shall be used to reflect local operating conditions if applicable. (vi) Dynamometers shall be equipped with both torque and speed test points to be used during audits. Test points shall be easily accessed with test clips. The torque signal shall be a DC voltage free of electrical noise. Maximum absorbed torque shall produce between +5 and +10 volts of signal. Maximum motored torque shall produce between -5.0 and -10.0 volts. The speed signal shall consist of a 5 volt pulse signal that can be counted by an external pulse counter. Alternative designs will be considered on a case-by-case basis. (vii) Alternative dynamometer specifications, designs or error checking may be allowed if proposed by a state and upon a determination by the Administrator that, for the purpose of properly conducting an approved short test, the evidence supporting such deviations show that proper vehicle loading will be applied. NOTE: Throughout the specification, whenever dynamometer inertia weight is used in an equation, the units should be referenced as "Ibs" and coast-down times should be referenced in "seconds". Page 25 7/28/04 Test Equipment Specifications ------- §85.3 §85.3 (2) Power Absorption. (i) Vehicle Loading. The vehicle loading used during the ASM driving cycles shall follow the equation in §85.3(a)(2)(ii) at 15 and 25 mph. Unless otherwise noted, any horsepower displayed during testing shall be expressed as HP . (ii) Indicated Horsepower. At constant velocity, the power absorber shall load the vehicle according the following equations: fflP = TRLHP - PLHP - GTRL Where: IHP is the dynamometer indicated, or set, horsepower. TRLHP is the track, or total, horsepower for a particular vehicle. PLHP is Parasitic Losses Horsepower due to internal dynamometer friction. Parasitic losses are specific to each dynamometer and are a function of speed. GTRL is Generic Tire/Roll Interface Losses at the specified speed. For two-wheel-drive dynamometers, values may either be taken directly from the EPA-approved Look-up Table, or be calculated according to the procedures outlined in the EPA's EVI240 Equipment Specification. TRLHP, PLHP, GTRL, and therefore IHP, are all expressed as three term polynomials of the type: HP = A*Obmph + B*Obmph2 + C*Obmph3 Where: HP represents individual expressions relating IHP, TRLHP, PLHP, or GTRL as a function of velocity. A, B, or C represent horsepower coefficients for the individual expressions relating IHP, TRLHP, PLHP, or GTRL as a function of velocity. Obmph is the velocity in miles per hour. Expressions for TRLHP, and GTRL are found in Appendices H and I of the EVI240 Guidance (iii) Range of Power Absorber. The range of the power absorber shall be sufficient to simulate the load required to perform an ASM5015 and an ASM2525 on all light-duty vehicles and light-duty trucks with ETW values up to 7,500 Ibs. And This is the actual Horsepower value contained in the look-up table for a vehicle being tested (using the ASM5015 or 2525) on a dynamometer with the specified diameter rollers. It is the sum of the Indicated Horsepower and the Parasitic Losses. Page 26 Test Equipment Specifications ------- §85.3 §85.3 5015 tire losses of 3.3 HP. To this end, the power absorber shall be sufficient to absorb a peak load of 33.3 hp at 14 mph for five minutes straight. In addition, the power absorber shall be sufficient to absorb and dissipate energy from continuous cycles consisting of five minutes of 25 horsepower at 14 mph followed by three minutes at rest. (iv) Power Absorber. Only electric power absorbers shall be used unless alternatives are proposed by the state and approved by the Administrator. The power absorber shall be adjustable in 0.1 hp increments at both 15 MPH and 25 MPH. The accuracy of the power absorber (PAU + parasitic losses) shall be ±0.25 horsepower or ±2% of required power, whichever is greater, in either direction of rotation. For field auditing the accuracy shall be ±0.5 horsepower. (v) Accuracy Over the Operating Range. The dynamometer's accuracy when warm shall not deviate more than ±0.5 horsepower over the full ambient operating range of 35°F to 110°F. This may be accomplished by intrinsic design or by software correction techniques. At any constant temperature, the dynamometer shall have an accuracy of ±0.5 horsepower within 15 seconds from the time the rolls start turning, and shall have an accuracy of ±0.25 horsepower within 30 seconds from the time the rolls start turning. For temperatures outside the specified range, the dynamometer shall provide correction or proceed with a manufacturer warm-up sequence until full warm condition has been reached. (3) Inertia. (i) Test Inertia. The dynamometer shall be equipped with mechanical flywheel(s) or with full inertia simulation providing an inertia weight of 2000 pounds ±40 pounds. Any deviation from the 2000 pound base inertia shall be quantified and the coast-down time shall be corrected accordingly. For all-wheel-drive dynamometers that may be operated in either two- or four- wheel-drive modes, the inertia in two-wheel-drive mode must comply with the above requirements. The inertia in four-wheel-drive mode may be different, however it shall be quantified to within 10 Ibs. The actual test inertia weight shall be marked on the ID plate required in §85.3(a)(l)(iv). In the case of all-wheel-drive dynamometers, the test inertia must be displayed for both two- and all-wheel-drive operation. (ii) Inertia/Inertia Simulation. The dynamometer shall be capable of conducting, at a minimum, diagnostic level transient inertia simulations with an acceleration rate between 0 and 3.3 miles per hour per second with a minimum load (power) of 25 horsepower at 14 mph over the inertia weight range of 2000 pounds to 6000 pounds. For the diagnostic level inertia simulation, the 25 horsepower criterion is a requirement on acceleration only, while for the full inertia simulation option, the requirement is for both acceleration and deceleration. Mechanical inertia simulation shall be provided in 500 pound increments; electric inertia simulation shall be provided in 1 pound increments. Any Page 2 7 Test Equipment Specifications ------- §85.3 §85.3 deviation from the stated inertia shall be quantified and the inertia simulation shall be corrected accordingly. Mechanical or electrical inertia simulation, or a combination of both, may be used, subject to review and approval by the state. (A) Diagnostic Level Simulation. 1. System Response. The torque response to a step change shall be at least 90% of the requested change within 300 milliseconds. 2. Simulation Error. An inertia simulation error (ISE) shall be continuously calculated any time the actual dynamometer speed is between 10 MPH and 60 MPH. The ISE shall be calculated by the equation in §85.3(a)(3)(ii)(C), and shall not exceed 3% of the inertia weight selected (IWS) for the vehicle under test. (B) Full Inertia Simulation. (Recommended Option) 1. System Response. The torque response to a step change shall be at least 90% of the requested change within 300 milliseconds. Torque response shall settle to within 2% of the requested change within 600 milliseconds. 2. Simulation Error. Horsepower simulation error (HPSE) shall be continuously calculated any time the dynamometer speed is greater than 5 mph. The HPSE is defined as the average difference between the desired power (DP) and the achieved power (AP) in 10 measurements taken at 0.5-second sequential intervals over the previous 5 seconds, divided by the total power (TP = inertia plus road load). However, if augmented braking is applied or the desired PAU power is less than or equal to zero* during any 0.5-second measurement, then the difference between the desired and achieved power for that 0.5-second measurement shall be set to 0. Values set to be 0 shall be used in the 5-second moving averages. If TP is less than 5HP over the 5-second period, set TP to 5HP. (C) Horsepower Simulation Error Calculation. ^(DP-AP) HPSE= ' This shall only apply to eddy current dynamometers, not full electric dynamometers. Page 28 Test Equipment Specifications ------- §85.3 §85.3 Where: i - current 0.5-second interval, starting at second 5 DP -desired power (inertia plus road load minus GTRL and PLHP) AP - achieved power (measured at the load cell) TP - total power (inertia plus road load) A violation occurs if HPSE is greater than ±0.25%. (4) Parasitic Losses. (i) The parasitic losses (PLHP) in each dynamometer system (including but not limited to windage, bearing friction, and system drive friction) shall be characterized at 15 and 25 mph upon initial acceptance, and during each dynamometer calibration. The parasitic power losses shall be determined as indicated in §85.4(b)(2). 00 For all-wheel-drive dynamometers that can be operated in either two or four- wheel-drive modes, parasitic losses must be characterized in both modes. Software controlling the dynamometer must automatically adjust programmed parasitic losses depending upon the mode in which the dynamometer is operating. (5) Rolls. (i) Size and Type. The dynamometer shall be equipped with twin rolls. The rolls shall be coupled side to side. In addition, the front and rear rolls shall be coupled. The dynamometer roll diameter shall be between 8.5 and 21.0 inches. The spacing between the roll centers shall comply with the equation in §85.3(a)(5)(iii). The dynamometer rolls shall accommodate an inside track width of 30 inches and an outside track width of at least 100 inches. (ii) Roll Installation. Rolls shall be installed in the floor such that vehicles will be be reasonably level when tested. The system shall be designed and installed such that ±8 degrees of level is achieved for vehicles having an 86" wheelbase and 27" outer diameter tires; an 89" wheelbase and 18" outer diameter tires; and a 170" wheelbase with 33" outer diameter tires. Either in-floor or above- ground installations are acceptable providing they meet these criteria. (iii) Roll Spacing. The spacing between the roll centers shall comply with the following equation to within +0.5 inches and -0.25 inches. Roll Spacing = (24.375 + D) * Sin 31.5 Where: Roll Spacing is the distance between the roll centerlines in inches. D= Roll diameter in inches Page 29 Test Equipment Specifications ------- §85.3 §85.3 (iv) Roll Surface. The surface finish and hardness shall be such that tire slippage is minimized when testing vehicles using the inertia weight and horsepower settings found in the EPA I/M Look-up Table while following the driving schedule, and that tire wear and noise are minimized. Knurled roll surfaces are acceptable . (v) Vehicle Lift. A vehicle lift system located between the dynamometer rolls shall be provided to facilitate drive axle positioning and vehicle egress from the dynamometer. (vi) Vehicle Restraint System. The system shall include a system of safely restraining the forward and side-to-side motion of front wheel drive vehicles, and the forward motion of rear wheel drive vehicles during the driving schedule, while allowing unobstructed ingress and egress from the dynamometer. (6) Load Measuring Device (i) Torque Measurement. The dynamometer shall have a torque measurement system accurate to within ±2% of full scale. (ii) Dead Weights. Dead weights used to calibrate a torque meter or load measuring device shall be traceable to NIST and be accurate to within ±0.5%. Dead weights traceable to standards other than NIST may be used upon approval of the Administrator. (iii) Dynamic Calibrations. Designs using an F = MA method for calibrating the load cell are also acceptable; however, systems using such dynamic calibrations must provide an external means of accurately determining base inertia or performing load cell calibrations. (7) All-Wheel-Drive-Dynamometers. (i) Design. The dynamometer shall meet the requirements for two-wheel-drive vehicles and be capable of testing traction control and all-wheel-drive vehicles in a safe manner without damaging the vehicle. (ii) Wheelbase. The all-wheel-drive dynamometer shall be capable of testing vehicles having wheelbases ranging from 84 to 125 inches. The separation between the front and rear dynamometer rolls shall be automatically adjustable in increments of 1.00" or less and shall be accurate to ±0.25" of the selected vehicle wheelbase. Once a vehicle is positioned on the dynamometer, the It should be noted that knurlling or altering the surface of the dynamometer will effect the CTRL coefficients. However, at this time it is believed that the impact such alterations may have will be minimal and not affect emissions measurements. Page 30 Test Equipment Specifications ------- §85.3 §85.3 dynamometer must allow the vehicle to be centered on the dynamometer, including fine tuning the roll separation as necessary to meet the actual wheelbase of the vehicle within 0.1". After the roll separation matches the vehicle, the dynamometer must automatically lock the roll separation prior to the beginning of loaded testing. The roll separation lock must be sufficient to maintain the roll separation to within 0.25" of the vehicle wheelbase when 1000 Ibs offeree is applied to either compress or extend the dynamometer roll separation. (iii) Speed Synchronization. Front and rear rolls shall maintain speed synchronization within ±0.1 mph during steady-state operation. During transient speed operation, secondary roll speed must be maintained within ±0.1 mph or 1% of the primary roll speed, whichever is greater. Since many traction control vehicles will not be equipped with all-wheel drive, the secondary rolls must have sufficient power to drive and maintain speed for the non-drive wheels without assistance from the vehicle. (iv) Bi-directionality. Dynamometers in which one set of rolls is considered primary (i.e., drive wheels for non-all-wheel-drive vehicles must be place on one set) must be bi-directional. This will allow both front- and rear-wheel-drive vehicles to be tested in all-wheel-drive mode. (v) Disengageable Secondary Rolls. Dynamometers may be configured so that secondary rolls may be automatically disengaged when all-wheel-drive testing is not required. If the secondary rolls are disengaged, the system shall automatically compensate for the change in parasitic losses and base inertia as well and the change in generic tire roll losses. (vi) Base inertia. All-wheel-drive dynamometers that can be operated in either two- or all-wheel-drive modes must account for changes in base inertia resulting from the two different configurations. (8) Other Requirements. (i) Vehicle Speed. The measurement of roll speed shall be accurate within 0.1 mph over the full operating range. The dynamometer shall accommodate vehicle speeds of up to 60 mph. (ii) Vehicle Restraint. In §85.2(b)(10). (iii) Vehicle Cooling. In §85.2(c)(6). (iv) Four-Wheel Drive. If used, four-wheel drive dynamometers shall insure the application of correct vehicle loading as defined in §85.3(a)(2), shall not damage the four wheel drive system of the vehicle, and shall accommodate vehicles equipped with anti-lock brakes and/or traction control. Front and rear wheel rolls shall maintain speed synchronization within 0.2 mph. (v) Installation. In §85.3(a)(5)(ii). Page 31 Test Equipment Specifications ------- §85.3 §85.3 (vi) Augmented Braking. Dynamometers shall apply augmented braking on major decelerations during transient drive cycles, if such cycles are used in the program. The dynamometer software shall provide a signal output to inform the operator when augmented braking is activated. Augmented braking shall be actuated only when the negative force applied by the vehicle at the roll surface is greater than 110 Ibs. Augmented braking shall be applied so that at least 50% of the braking force beyond 110 Ibs required to meet the deceleration requirements of the drive trace is absorbed by the dynamometer. (b) Emission Sampling System. (1) The sampling system shall be designed to insure durable, leak free operation and be easily maintained. Materials that are in contact with the gases sampled shall not contaminate or change the character of the gases to be analyzed, including gases from vehicles not fueled by gasoline (except diesels). The system shall be designed to be corrosion-resistant and be able to withstand typical vehicle exhaust temperatures when the vehicle is driven through the ASM test cycle for the maximum test length described in §85.2(e). (2) The sampling system shall draw exhaust gas from the vehicle, shall remove particulate matter and aerosols from the sampled gas, shall drain condensed water from the sample if necessary, and shall deliver the resultant gas sample to the analyzers/sensors for analysis and then deliver the analyzed sample directly outside the building. The sampling system shall, at a minimum, consist of a tailpipe probe, flexible sample line, water removal system, a particulate trap, sample pump, and flow control components. (3) Sample Probe. (i) Insertion. The sample probe shall allow at least a 16 inch insertion depth of the sample probe into the vehicle's exhaust. In addition, the probe shall be inserted at least 10 inches into the vehicle's exhaust. Use of a tailpipe extension is permitted as long as the extension does not change the exhaust back pressure by more than ±1.0 inch of water pressure. (ii) Retention. The probe shall incorporate a positive means of retention to prevent it from slipping out of the tailpipe during use. High through-put test systems may use alternative means to insure probe retention. (iii) Flexibility. The probe shall be designed so that the tip extends 16 inches into the tailpipe. The probe tip shall be shielded so that debris is not scooped up by the probe when it is inserted into the tailpipe. High through-put test systems may use alternative means to insure adequate probe insertion. (iv) Probe Tip. Probe tips shall be designed and constructed to prevent sample dilution. (v) Materials. All materials in contact with exhaust gas prior to and throughout the measurement portion of the system shall be unaffected by and shall not affect Page 32 Test Equipment Specifications ------- §85.3 §85.3 the sample (i.e., the materials shall not react with the sample, and they shall not taint the sample). Acceptable materials include stainless steel, Teflon, silicon rubber, and Tedlar. Dissimilar metals with thermal expansion factors of more than 5% shall not be used in either the construction of probes or connectors. The sample probe shall be constructed of stainless steel or other non-corrosive, non-reactive material which can withstand exhaust gas temperatures at the probe tip of up to 1,100°F for 10 minutes. (vi) System Hoses and Connections. Hoses and all other sample handling components must be constructed of, or plated with a non-reactive, non- corrosive, high temperature material which will not affect, or be affected by, the exhaust constituents and tracer gases. (vii) Dual Exhaust. The sample system shall provide for the testing of dual exhaust equipped vehicles. When testing a vehicle with functional dual exhaust pipes, a dual sample probe of a design certified by the analyzer manufacturer to provide equal flow in each leg shall be used. The equal flow requirement is considered to be met if the flow rate in each leg of the probe has been measured under two sample pump flow rates (the normal rate and a rate equal to the onset of low flow), and if the flow rates in each of the legs are found to be equal to each other (within 15% of the flow rate in the leg having lower flow). (4) Particulate Filter. The particulate filter shall be capable of trapping 97% of all particulate and aerosols 5 microns or larger. The filter element shall not absorb or adsorb hydrocarbons. The filter housing shall be transparent or translucent to allow the operator to observe the filter element's condition without removing the housing. The filter element shall be easily replaceable and shall provide for reliable sealing after filter element changes. (5) Water Trap. The water trap shall be sized to remove exhaust sample water from vehicles fueled with gasoline, propane, compressed natural gas, reformulated gasoline, alcohol blends or neat, and oxygenated fuels. The filter element, bowl and housing shall be inert to these fuels as well as to the exhaust gases from vehicles burning these fuels. The condensed water shall be drained from the water trap's bowl either continuously or automatically on a periodic basis such that the following performance requirement is maintained. Sufficient water shall be trapped, regardless of fuel, to prevent condensation in the sample system or in the optical bench's sample cell. (6) Low Flow Indication. The analyzer shall lock out official testing when the sample flow is below the acceptable level. The sampling system shall be equipped with a flow meter (or equivalent) that shall indicate sample flow degradation when measurement error exceeds 3% of the gas value used for checking, or causes the system response time to exceed 13 seconds to 90 percent of a step change in input (excluding NO), whichever is less. Alternatively, the sample vacuum may be continuously monitored to detect a low flow condition. (7) Exhaust Ventilation System. The high quantities of vehicle emissions generated during loaded mode testing shall be properly vented to prevent buildup of hazardous concentrations of HC, CO, CO2 and NOx. Sufficient ventilation shall be provided in Page 33 Test Equipment Specifications ------- §85.3 §85.3 the station to maintain HC, CO, CC>2 and NO levels below recommended Occupational Safety and Health Association (OSHA) standards*. (i) The ventilation system shall discharge the vehicle exhaust outside the building. (ii) The flow of the exhaust collection system shall not cause dilution of the exhaust at the sample point in the probe. (iii) The flow of the exhaust collection system shall not cause a change of more than ±1.0 inches of water pressure in the vehicle's exhaust system at the exhaust system outlet. (c) Analytical Instruments. (1) General Requirements. (i) Measured Gases. The analyzer system shall consist of analyzers for HC, CO, NO, and CO2, (C>2 optional). It is recommended that the system provide digital displays for exhaust concentrations of HC, CO, NO, and CO2, as well as for vehicle speed; however, it is recognized that some BAR97 systems do not provide these features. (ii) Emission Accuracy. The system shall ensure that the analytical system provides an accurate accounting of the actual exhaust emissions produced during the test, taking into consideration the individual channel accuracy, repeatability, interference effects, sample transport times, and analyzer response times. (iii) Sample Rate. The analyzer shall be capable of measuring exhaust concentrations of the gases specified in §85.3(c)(l)(i) at a minimum rate of once per second. (iv) Alternative Equipment. Alternative analytic equipment specification, materials, designs, or detection methods may be allowed if proposed by a state and upon a determination by the Administrator, that for the purpose of properly conducting a test, the evidence supporting such deviations will not significantly affect the proper measurement of emissions. (2) Performance Requirements. (i) Temperature Operating Range. The analyzer system and all associated hardware shall operate within the performance specifications described in §85.3(c)(3) at ambient air temperatures ranging from 35°F to HOT. Analyzers shall be designed so that adequate air flow is provided around critical components to prevent overheating (and automatic shutdown) and to prevent the condensation of water vapor which could reduce the reliability and durability of The following limits may be found in 29 CFR 1910.1000 Table Z-l. CO 50 ppm; CO2 5000 ppm; NO2 5 ppm; n-Hexane 500 ppm; Propane 1000 ppm. Page 34 Test Equipment Specifications ------- §85.3 §85.3 the analyzer. The analyzer system shall otherwise include necessary features to keep the sampling system within the specified range. (ii) Humidity Operating Range. The analyzer system and all associated hardware shall operate within the performance specifications described in §85.3(c)(3) at a minimum of 85% relative humidity throughout the required temperature range. (iii) Interference Effects. The interference effects for non-interest gases shall not exceed ±4 ppm for hydrocarbons, ±0.02% for carbon monoxide, ±0.20% for carbon dioxide, and ±20 ppm for nitric oxide when using the procedure specified in §85.4(d)(5)(iv). Corrections for collision-broadening effects of combined high CO and CC>2 concentrations shall be taken into account in developing the factory calibration curves, and are included in the accuracy specifications. (iv) Barometric Pressure Compensation. Barometric pressure compensation shall be provided. Compensation shall be made for elevations up to 6000 feet (above mean sea level). At any given altitude and ambient conditions specified in §85.3(c)(2)(i) and (ii), errors due to barometric pressure changes of ±2 inches of mercury shall not exceed the accuracy limits specified in §85.3(c)(3). (iv) System Lockout During Warm-up. Functional operation of the gas sampling unit shall remain disabled through a system lockout until the instrument meets stability and warm-up requirements. The instrument shall be considered "warm" when the zero and span readings for HC, CO, NO, and CO2 have stabilized, within the accuracy values specified in §85.3(c)(3) for five minutes without adjustment. (v) Zero Drift Lockout. If zero or span drift cause the optical bench signal levels to move beyond the adjustment range of the analyzer, the system shall be locked out from testing. (vi) Electromagnetic Isolation and Interference. Electromagnetic signals found in an automotive service environment shall not cause malfunctions or changes in the accuracy in the electronics of the analyzer system. The instrument design shall ensure that readings do not vary as a result of electromagnetic radiation and induction devices normally found in the automotive service environment, including high energy vehicle ignition systems, radio frequency transmission radiation sources, and building electrical systems. (vii) Vibration and Shock Protection. System operation shall be unaffected by the vibration and shock encountered under the normal operating conditions encountered in an automotive service environment. (viii) Propane Equivalency Factor. The nominal PEF range shall be between 0.490 and 0.540. For each audit/calibration point, the nominal PEF shall be conveniently displayed for the quality assurance inspector and other authorized personnel. Ideally, the PEF shall appear on the monitor in conjunction with the HC reading during any audit or at the operator's request. Page 35 Test Equipment Specifications ------- §85.3 §85.3 If an optical bench must be replaced in the field, any external labels shall be changed to correspond to the nominal PEF of the new bench. The analyzer shall incorporate an algorithm relating PEF to HC concentration. Corrections shall be made automatically. The corrected PEF value may cover the range of 0.470 to 0.560 (ix) System Response Requirements. The response time from the probe to the display for HC, CO, and CO2 analyzers shall not exceed 8 seconds for 90% of a step change in input, nor shall it exceed 12 seconds to 95% of a step change in input. The response time for a step change in O2 from 20.9% O2 to 0.1% O2 shall be no longer than 40 seconds. For NO analyzers, the response time shall not exceed 12 seconds for 90% of a step change in input. The response time for a step change in NO from a stabilized reading to 10% of that reading shall be no longer than 12 seconds. (3) Detection Methods, Instrument Ranges, Accuracy, and Repeatability. (i) Hydrocarbon Analysis. Hydrocarbon analysis shall be determined by non- dispersive infrared (NDIR) analyzer. The analyzer shall cover at least the range of 0 ppm HC to 9999 ppm HC, where ppm HC is parts per million of hydrocarbon volume as hexane. The accuracy of the instrument from 0-2000 ppm HC shall be ±3% of point or 4 ppm C6, whichever is greater. The accuracy of the instrument between 2001 ppm HC and 5000 ppm HC shall be at least ±5% of point and the accuracy of the instrument between 5001 ppm HC and 9999 ppm HC shall be at least ±10% of point. The instrument shall comply with the quality control specifications in §85.4(d). (ii) Carbon Monoxide Analysis. Carbon monoxide analysis shall be determined by non-dispersive infrared (NDIR) analyzer. The analyzer shall cover at least the range of 0.00 % CO to 14.00% CO, where % CO is % volume CO. The accuracy of the instrument between 0.01% and 10.00% CO shall be ±3% of point or 0.02% CO, whichever is greater. The accuracy of the instrument between 10.01% and 14.00% shall be at least ±5% of point. The instrument shall comply with the quality control specifications in §85.4(d). (iii) Carbon Dioxide Analysis. Carbon dioxide analysis shall be determined by non- dispersive infrared (NDIR) analyzer. The analyzer shall cover at least the range of 0.0 % CO2 to 18.0% CO2. The accuracy of the instrument between 0.01% and 16.00% CO2 shall be ±3% of point or 0.3% CO2, whichever is greater. The accuracy of the instrument between 16.01% and 18.00% shall be at least ±5% of point. The instrument shall comply with the quality control specifications in §85.4(d). (iv) Nitric Oxide Analysis. The analyzer shall cover at least the range of 0 ppm NO to 5000 ppm NO, where ppm NO is parts per million nitric oxide. The accuracy of the instrument between 0 and 4000 ppm shall be at least ±4% of point or 25 ppm NO, whichever is greater. The accuracy of the instrument between 4001 and 5000 ppm shall be at least ±8% of point. The instrument shall comply with the quality control specifications in §85.4(d). Page 36 Test Equipment Specifications ------- §85.3 §85.3 (v) Oxygen Analysis, (optional) If an oxygen analyzer is included, the analyzer shall cover at least the range of 0.0% O2 to 25.0% O2. The accuracy of the instrument over this range shall be at least 5% of point or ±0.1% O2, whichever is greater. The instrument shall comply with the quality control specifications in §85.4(d). (vi) Repeatability. The repeatability for the HC analyzer in the range of 0-1400 ppm HC shall be 2% of point or 3 ppm HC absolute, whichever is greater. In the range of 1400-2000 ppm HC, the repeatability shall be 3% of point. The repeatability for the CO analyzer in the range of 0-7.00% CO shall be 2% of point or 0.02% CO absolute, whichever is greater. In the range of 7.00% to 10.00% CO, the repeatability shall be 3% of point. The repeatability for the CO2 analyzer in the range of 0-10.0% CO2 shall be 2% of point or 0.1% CO2 absolute, whichever is greater. In the range of 10.0% to 16.0% CO2, the repeatability shall be 3% of point. The repeatability of the NO analyzer shall be 3% of point or 20 ppm NO, whichever is greater. The repeatability of the O2 analyzer shall be 3% of point or 0.1% O2, whichever is greater. (vii) Rounding Rule. Rounding beyond the decimal places shown in §85.3(c)(3) shall follow the standard mathematical practice of going to the next higher number for any numerical value of five or more. This shall also hold true for pass/fail decisions. For example, if 2.00% CO passes and 2.01% CO fails, and the reading is 2.0049%, the value shall be rounded down and the decision shall be a pass. If the reading is 2.0050, the value shall be rounded up and the decision shall be a fail. The value displayed and printed on the test report shall be consistent with the value used for the pass/fail decision. (4) Ambient Conditions. The current relative humidity, dry-bulb temperature, and barometric pressure shall be measured and recorded prior to the start of every inspection in order to calculate Kh (nitric oxide correction factor §85. l(b)(l)(vi)). (i) Relative Humidity. The relative humidity measurement device shall cover the range from 5% to 95% RH, between 35°F - 110°F, with a minimum accuracy of ±3% RH. Wet bulb thermometers shall not be used. (ii) Dry-bulb Temperature. The dry-bulb temperature device shall cover the range from OT - 140T with a minimum accuracy of 3°F. (iii) Barometric Pressure. The barometric pressure measurement device shall cover the range from 610 mm Hg - 810 mm Hg absolute (24-32 inches), and 35T - HOT, with a minimum accuracy of ±3% of point or better. (5) Engine Speed Detection. The analyzer shall utilize a tachometer capable of detecting engine speed in revolutions per minute (RPM) with a 0.5 second response time and an accuracy of ±3% of the true RPM. On vehicles equipped with onboard diagnostic (OBD) systems, it is recommended that the engine speed be taken by connecting to the SAE standardized OBD link on 1996 and newer vehicles. RPM readings shall be recorded on a second-by-second basis for the 10 second period upon which the pass/fail decision is based. Page 37 Test Equipment Specifications ------- §85.3 §85.3 (6) OBD Fault Code Retrieval. Starting in 2001 the system shall include the hardware and software necessary to access the onboard computer systems on 1996 and newer vehicles, determine OBD readiness, and recover stored fault codes using the SAE standardized link. (d) Automated Test Process Software and Displays. (1) Software. The testing process, data collection, and quality control features of the analyzer system shall be automated to the greatest degree possible. The software shall automatically select the emission standards and set the vehicle load based on an EPA- provided or approved look-up table. Vehicle identification information shall be derived from a database accessed over a real-time data system to a host computer system. Entry of license plate and all or part of the VIN shall be sufficient to access the vehicle record. Provision shall be made for manual entry of data for vehicles not in the host computer system. Alternative methods for matching test records to the appropriate vehicle and ensuring that the vehicle is tested using the proper parameters may be used if approved by the Administrator. (2) Test and mode timers. The analyzer shall be capable of simultaneously determining the amount of time elapsed in a test (overall test time), and in a mode within that test (mode time). (3) Clocks and Timers. The clock used to check the coast-down time shall be accurate to within 0.1% of reading between 0.5 and 100 seconds, with a resolution of 0.001 seconds. The test mode timers used shall be accurate to within 0.1% of reading between 10 and 1000 seconds with a resolution of 0.1 seconds. (4) Driver's Aid. The system shall be equipped with a driver's aid that shall be clearly visible to the driver as the test is performed. The aid shall continuously display the required speed, the number of seconds into the test mode, the driver's actual speed/time performance (a display showing the deviation between set-point and actual driving trace), engine RPM, the use of augmented braking, and necessary prompts and alerts. It is recommended that an analog speed display be used as this has been demonstrated to improve a driver's ability to maintain the ±1.0 mph tolerance. The driver's aid shall also be capable of displaying test and equipment status and other messages as required. Dynamic information being displayed shall be refreshed at a minimum rate of twice per second. Emissions values shall not be displayed during official testing. (5) Minimum Analyzer Display Resolution. The analyzer electronics shall have sufficient resolution to achieve the following: HC 1 ppm HC as hexane NO 1 ppm NO CO 0.01 % CO CO2 0.1 %CO2 O2 0.1 % O2 (optional) RPM 10 RPM Speed 0.1 mph Page 38 Test Equipment Specifications ------- §85.3 §85.3 Load 0.1 hp Relative Humidity 1 % RH Dry Bulb Temperature 1 °F Barometric Pressure 1 mm Hg Page 39 Test Equipment Specifications ------- §85.4 §85.4 §85.4 Quality Control Requirements (a) General Requirements (1) Minimums. The frequency and standards for quality control specified here are minimum requirements, unless modified as specified in §85.4(a)(2). Greater frequency or tighter standards may be used as needed. (2) Statistical Process Control. Reducing the frequency of the quality control checks, modifying the procedure or specification, or eliminating the quality control checks altogether may be allowed if the state demonstrates and the Administrator determines, for the purpose of properly conducting an approved short test, that sufficient Statistical Process Control (SPC) data exist to make a determination, that the SPC data support such action, and that taking such action will not significantly reduce the quality of the emissions measurements. Should emission measurement performance or quality deteriorate as a result of allowing such actions, the approval shall be suspended and the frequencies, procedures specifications, or checks specified here or otherwise approved shall be reinstated, pending further determination by the Administrator. (b) Dynamometer (1) Coast Down Check. (i) The calibration of each dynamometer shall be automatically checked every 72 hours in low volume stations (less than 4000 tests per year) and daily in high volume stations by a dynamometer coast-down procedure equivalent to 40 CFR §86.118-78 (for reference see National Vehicle and Fuel Emission Laboratory's Testing Services Division test procedure TP-302A and TP-202) between the speeds of 30-20 mph if the ASM2525 is used and 20-10 mph if the ASM5015 is used. All rotating dynamometer components shall be included in the coast- down check. Speed windows smaller than ± 5 mph may be used provided that they show the same calibration capabilities. (ii) The dynamometer calibration shall be checked at two random horsepower settings for each speed range using the 2000 Ib. test inertia. The two random horsepower settings shall be between 8.0 and 18.0 horsepower. The random selection shall be evenly distributed throughout the 8 to 18 FTP range. A shunt resistor for a load cell performance check shall not be used. (iii) The coast-down procedure shall use a vehicle-off-dynamometer type method or equivalent. Using a vehicle to bring the dynamometer up to speed and removing the vehicle before the coast-down shall not be permitted. If either the measured 30-20 mph coast-down time or 20-10 mph coast-down time is outside the window bounded by the Calculated Coast-Down Time (CCDT) (seconds) ± 6% then it shall be locked out for official testing purposes until recalibration allows a passing value. Page 40 7/28/04 Quality Control Requirements ------- §85.4 §85.4 If the dynamometer fails a coast-down check, a parasitic loss determination shall be required and performed automatically. (A) Randomly select an IHP2525 value that is between 8.0 hp and 18.0 hp and set dynamometer PAU to this value. Coast-down dynamometer from 30-20 mph. 0.5* DIW 32.2 :(v320-v220) 550*(IHP2525+PLHP25) Where: DIW ¥20 IHP2525 PLHP2s = Dynamometer Inertia Weight. Total "inertia" weight of all rotating components in dynamometer. = Velocity in feet/sec at 30 mph. = Velocity in feet/sec at 20 mph. = Randomly selected ASM2525 indicated horsepower. = Parasitic Horsepower for specific dynamometer at 25 mph. (B) Randomly select an IHP50i5 value that is between 8.0 hp and 18.0 hp and set dynamometer PAU to this value. Coast-down dynamometer from 20-10 mph. 0.5* DIW CCDT 32.2 72 - V2" '20 MO- @15mph 550*(IHP5015+PLHP15) Where: DIW V20 Vio IHP50i5 PLHPis Dynamometer Inertia Weight. Total "inertia" weight of all rotating components in dynamometer. Velocity in feet/sec at 20 mph. Velocity in feet/sec at 10 mph. Randomly selected ASM5015 indicated horsepower. Parasitic Horsepower for specific dynamometer at 15 mph. Page 41 Quality Control Requirements ------- §85.4 §85.4 (2) Parasitic Value Calculations. Parasitic losses should be measured any time service is performed on a dynamometer, as the first step in diagnosing a dynamometer's inability to pass a coast-down, or if the load measuring device is re-calibrated. (i) Parasitic losses shall be calculated using the following equations at 25 and 15 mph whenever a coast-down check is performed, except the indicated horsepower (IHP) shall be set to zero for these tests. -Parasitic losses shall be determined using the equations listed below. After new parasitic values are calculated, the coast-down check procedure contained in §85.4(b)(l) must be passed before the dynamometer can be returned to service. (ii) Parasitic losses at 25 mph for a dynamometer with specified diameter rollers. 0.5*DIW PLHP25 = 32.2 :(v320-v220) 550*(ACDT) Where: DIW = Dynamometer Inertia Weight. Total "inertia" weight of all rotating components in dynamometer. (iii) = Velocity in feet/sec at 30 mph. = Velocity in feet/sec at 20 mph. ACDT = Actual coast-down time required for dynamometer to coast from 30 to 20 mph. Parasitic losses at 15 mph for a dynamometer with specified diameter rollers. 0.5* DIW PLHP15 = 32.2 2 - v 20 M O 550* (ACDT) Where: DIW V20 Vio ACDT Dynamometer Inertia Weight. Total "inertia" weight of all rotating components in dynamometer. Velocity in feet/sec at 20 mph. Velocity in feet/sec at 10 mph. Actual coast-down time required for dynamometer to coast from 20 to 10 mph. Page 42 Quality Control Requirements ------- §85.4 §85.4 (3) Roll Speed. There is no need to perform roll speed checks on a regular basis, providing the coast-down procedures are being performed and adhered to. This is because dynamometers will not be able to pass the coast-down test with erroneous speed readings, especially when the load is changed from coast-down to coast-down. (4) Load Measuring Device. If the dynamometer fails a coast-down check immediately after performing a parasitic loss determination, then the dynamometer load measuring device may be malfunctioning or out of calibration. In this case, or in the case of the load measuring system being serviced, the load-measuring device shall be checked using a dead-weight method or an equivalent procedure proposed by the state and approved by the Administrator. The check shall cover at least three points over the range of loads used for vehicle testing. Dead weights shall be traceable to the National Institute of Standards (NIST) and shall be accurate to within ±0.1%. Dead weights traceable to standards other than NIST may be used upon approval of the Administrator. The dynamometer shall provide an automatic load measuring device calibration and verification feature. (5) Certification Testing. (i) Load Cell Verification (if equipped). This test confirms the proper operation of the dynamometer load cell and associated systems. Weights in the proper range shall be supplied by the system supplier. Weights shall be NIST traceable to 0.1% of point. Dead weights traceable to standards other than NIST may be used upon approval of the Administrator. (A) Calibrate the load cell according to the manufacturer's direction. (B) Using a dead weight method, load the test cell to 20%, 40%, 60%, and 80% (in ascending order) of the range used for ASM testing. Record the readings for each weight. Remove the weights in the same steps (descending order) and record the results. (C) Perform steps A through B two more times (total of three). Calculate the average value for each weight. Multiply each average weight from E by the length of the torque arm. (D) Acceptance Criteria: The difference for each reading from the weight shall not exceed 1% of full scale. (ii) Speedometer Verification. This test confirms the accuracy of the dynamometer's speedometer. (A) Measure the dynamometer roll diameter to within ±0.01 inch. This may be accomplished using a PI tape. If the dynamometer is able to motor to a constant speed, set the dynamometer speed to 15 mph. If the dynamometer does not have the ability to motor at constant speeds, place a vehicle on the dynamometer and drive the vehicle at a constant speed as close to 15 mph as possible. Independently measure and record dynamometer roll rotational frequency using a frequency counting device such as a strobe tachometer. Mathematically convert the roll diameter to circumference Page 43 Quality Control Requirements ------- §85.4 §85.4 and multiply by the rotational frequency to obtain linear speed. Compare this speed to the speed measured by the test system. Repeat at 25 mph. (B) Acceptance Criteria: The difference for each reading from set dynamometer speed shall not exceed 0.1 mph. (iii) Parasitics Verification. Parasitic losses shall be verified at 25 and 15 mph using the procedure in §85.4(b)(2), using time data from a system independent source (e.g. stopwatch) and speed data from the system. The indicated horsepower (IHP) shall be set to zero for these tests. (A) Acceptance Criteria: The difference between the externally calculated value and the machine calculated value shall not exceed 10% of the independently measured value. (iv) Verify Coast-Down. The coast-down procedure shall use a vehicle off- dynamometer type method or equivalent. Using a vehicle to bring the dynamometer up to speed and removing the vehicle before the coast-down shall not be permitted. (A) To verify the coast-downs at 25 mph, use the procedure and equations described in §85.4(b)(2)(ii). (B) To verify the coast-downs at 15 mph, use the procedure and equations described in §85.4(b)(2)(iii). (C) Acceptance Criteria: The measured 30-20 mph coast-down time and the 20-10 mph coast-down time must be inside the window bounded by CCDT (seconds) ± 6% at both speeds. (6) Field Auditing. (i) Frequency. Field audits should be performed on each dynamometer at least once per year (A) Calibrate the load cell according to the manufacturer's direction. (ii) Perform coast-down check to verify system does not self diagnose any problems. Correct any problems as necessary. (iii) Dynamometer load verification may be performed either with an existing dynamometer tester or by reading voltage directly from the dynamometer load cell. If an existing dynamometer tester is used, follow the directions provided by the tester manufacturer. If voltage measurement is used, follow the directions below: (A) Determine the ratio for converting load cell voltage into dynamometer load. (B) Test a known vehicle on the ASM test while measuring voltage at the load cell. Page 44 Quality Control Requirements ------- §85.4 §85.4 (C) Determine vehicle load by plugging known values into the loading equation found in §85.3.a.2.ii. Determine vehicle load by plugging known values into the loading equation found in §85.3.a.2.ii. (D) Compare the applied load with the target load from the EPA-approved lookup table (or the applicable table for the particular emissions inspection program) (c) Emission Sampling System. (1) Leak Check. The entire sample system shall be checked for vacuum leaks on a daily basis and proper flow on a continuous basis. This may be accomplished using a vacuum decay method, reading a span gas, or other methods proposed by a state and approved by the Administrator. The analyzer shall not allow an error of more than 1% of reading using the high-range span gas described in §85.4(d)(2)(iii)(C). The analyzer shall be locked out from testing if the leak check is not performed when due or fails to pass the check. (2) Dilution. The flow rate on the analyzer shall not cause more than 10% dilution during sampling of exhaust of a 1.6 liter engine a normal idle. Ten percent dilution is defined as a sample of 90% exhaust and 10% ambient air. (3) Dilution Acceptance Test. (i) Set vehicle with 1.6 liter maximum engine displacement at factory - recommended idle speed, OEM configuration exhaust system, transmission in neutral, hood up (a fan to cool the engine may be used if needed). Set idle speed not to exceed 920 RPM. (Set for 900 RPM with a tolerance ± 20 RPM.) (ii) With a laboratory grade analyzer system, sample the exhaust at 40 centimeters depth with a flow sample rate below 320 liters per hour. Allow sufficient time for this test. Record all HC, CO, NO, CO2, and O2 readings. A chart recorder or electronically stored data may be used to detect the point of stable readings. (iii) While operating the candidate analyzer system in a mode which has the same flow rate as the official test mode, record the levels of HC, CO, NO, CO2, and O2. Ensure that the probe is installed correctly. (iv) Repeat step (ii). (iv) Acceptance Criteria: If the difference of the readings between (ii) and (iv) exceed five percent of the average of (ii) and (iv), repeat (ii), (iii), and (iv); otherwise average (ii) and (iv) and compare with (iii). If (iii) is within 10 percent of the average of (ii) and (iv), then the equipment meets the dilution specification. Page 45 Quality Control Requirements ------- §85.4 §85.4 (d) Analytic Instruments. (1) General Requirements. The analyzer shall, to the extent possible, maintain accuracy between gas calibrations taking into account all errors, including noise, repeatability, drift, linearity, temperature, and barometric pressure. (2) Two-Point Gas Calibration and Low-Range Audit. (i) Analyzers shall automatically require a zero gas calibration and a high-range gas calibration for HC, CO, NO, and CO2. The system shall also use a low- range gas to check the calibration in the range of vehicle emission standards. In high volume stations (4000 or more tests per year), analyzers shall be calibrated within four hours before each test. In low volume stations (below 4000 tests per year), analyzers shall be calibrated within 72 hours before each test. If the system does not calibrate or is not calibrated, the analyzer shall lock out from testing until corrective action is taken. This calibration check shall include measuring the NO cell response to ensure it is < 15 seconds with a warning displayed when the response exceeds 7 seconds. (ii) Gas Calibration and Check Procedure. Gas calibration shall be accomplished by introducing calibration gases that meet the requirements of §85.4(d)(2)(iii) into the calibration port. The pressure in the sample cell shall be the same with the calibration gas flowing as with the sample flowing during testing. The analyzer channels shall be adjusted to the center of the allowable tolerance range as a result of the calibration. The system shall record the gas reading data from before the adjustment and other data pertinent to control charting analyzer performance. (A) Zero the analyzer and perform a leak check. (B) Calibrate the analyzer using the low and high-range calibration gas as specified in §85.4(d)(2)(iii). (C) Purge the analyzers completely by flowing the low-range calibration gas specified in §85.4(d)(2)(iii) for 60 seconds. If the low-range calibration gas readings differ from the true cylinder value by more ±3% of point for HC, ±3% of point for CO, ±3% of point for CO2, or ±25 ppm NO the analyzer shall be locked out from testing. (iii) The following gases shall be used for the 2-point calibration and low-range audit. The Low- and High-Range Calibration Gases are the same concentrations and purity as the Low- and High-Range Audit Gases. Appendix A contains a table with sample calculations illustrating how the Low and High Audit Limits for the Calibration Gases are to be determined. The tolerances are based on a 2% blend tolerance, accurate to 1%. It is Page 46 Quality Control Requirements ------- §85.4 §85.4 recommended that NIST traceable standards accurate to 1% be used to verify all bottle names*. (A) Zero Gas O2 = 20.7% HC < 1 ppm THC CO < 1 ppm CO2 < 400 ppm NO < 1 ppm N2 = Balance 99.99 % pure (B) Low-Range Calibration Gas HC = 200 ppm propane CO = 0.5 % CO2 = 6.0 % NO =300 ppm N2 = Balance 99.99 % pure (C) High-Range Calibration Gas HC = 3200 ppm propane CO = 8.0 % CO2 = 12.0 % NO = 3000 ppm N2 = Balance 99.99 % pure (iv) Traceability. The audit and span gases used for the gas calibration shall be traceable to National Institute of Standards and Technology (NIST) standards ±1%. Gases shall have a 2% blend tolerance. (3) Five-Point Calibration Audit. (i) Analyzers shall automatically require and successfully pass a five point gas audit for HC, CO, NO, and CO2. For high volume stations, audits shall be checked monthly. In low volume stations, analyzers shall undergo the audit procedure every six months. (ii) Gas Audit Procedure. Calibration auditing shall be accomplished by introducing audit gas through the probe. The pressure in the sample cell shall be the same with the audit gas flowing as with the sample flowing during testing. (A) Zero the analyzer and perform a leak check. EPA has been informed that adherence to this minimum NIST standard may not be an ironclad guarantee of accuracy. Requiring gases to be analyzed using EPA-600/R-97-121 may be a more reliable method; however, it may also cause a significant increase in cost. Page 47 Quality Control Requirements ------- §85.4 §85.4 (B) Flow the low range audit gas specified in §85.4(d)(3)(iii) through the sample probe, ensuring that the tip is equal to ambient barometric pressure ±0.1 inches Hg (a balloon teed into the gas flow line is an acceptable pressure indicator; the balloon should stand slightly erect). (C) When the HC, CO, NO, and CO2 gases have been flowing for 60 seconds record the readings as well as the PEF value for HC at each audit blend. (D) Repeat steps B and C for each audit gas specified in §85.4(d)(3)(iii). (E) Compare the readings with the audit gas values using the equation listed below. Be sure to divide the HC reading by its PEF if this calculation is not performed automatically in the analyzer software. (Reading - True Cylinder Value) Tolerance % = 100*- True Cylinder Value (F) If the analyzer response when reading any of the Audit Gases exceeds ±4.0% for HC/PEF, CO, and CO2, or ±5.0% for NO, then the analyzer shall fail the gas audit and shall be locked out from testing until it passes. (iv) The following gases shall be used for the five-point calibration audit. (A) Zero Audit Gas O2 = 20.7% (if O2 span is desired) HC < O.lppmTHC CO < 0.5 ppm CO2 < 1 ppm NO < 0.1 ppm N2 = Balance 99.99 % pure (B) Low Range Audit Gas HC = 200 ppm propane CO = 0.5 % CO2 = 6.0 % NO =300 ppm N2 = Balance 99.99 % pure (C) Low-Middle Range Audit Gas HC = 960 ppm propane CO = 2.4 % CO2 = 3.6% NO = 900 ppm N2 = Balance 99.99 % pure (D) High-Middle Range Audit Gas HC = 1920 ppm propane CO = 4.8 % CO2 = 7.2 % NO = 1800 ppm Page 48 Quality Control Requirements ------- §85.4 §85.4 N2 = Balance 99.99 % pure (E) High Range Audit Gas HC = 3200 ppm propane CO = 8.0 % CO2 = 12.0 % NO = 3000 ppm N2 = Balance 99.99 % pure (iv) Traceability. These gases shall be traceable to National Institute of Standards and Technology (NIST) standards ±1%. Gases shall have a 2% blend tolerance. (4) Service, Repair and Modification. (i) Each time an analyzer's emissions measurement system, sensor, or other related electronic components are repaired or replaced, the five point calibration audit required in §85.4(d)(3) shall be performed, at a minimum, prior to returning the unit to service. (ii) Each time the sample line integrity is broken, a leak check shall be performed prior to testing. (5) Certification Testing. (i) Analyzer accuracy. This test confirms the ability of the candidate instruments to read various concentrations of gases within the tolerances required by this specification. The test compares the response of the candidate instrument with that of standard instruments, and also estimates the uncertainty of the readings. The analyzer shall be zeroed and gas calibrated using the high-range calibration gas. The instrument shall be tested using propane, carbon monoxide, carbon dioxide, and nitric oxide in nitrogen, with a certified accuracy of ±1%, in the following concentrations: 0%, 10%, 20%, 30%, 40%, 50%, 60%, 70%, 80%, 90%, and 100% of the high range audit gas (A) Introduce the gases in ascending order of concentrations beginning with the zero gas. Record the readings of the standard and candidate instruments to each concentration value. A gas divider may be used to divide the high range audit gas to the concentrations described in §85.4(d)(5)(i). (B) After the highest concentration has been introduced and recorded, introduce the same gases to the standard and candidate analyzers in descending order, including the zero gas. Record the reading of analyzers to each gas, including negatives (if any). (C) Repeat steps A and B for the candidate only, four more times (total of five times). (D) Calculation Procedure: Page 49 Quality Control Requirements ------- §85.4 §85.4 1. Calculate the average value of each concentration for the readings of the standard instruments. 2. Calculate the mean and standard deviation of each candidate's readings for each concentration. Include both upscale and downscale readings for the same gas concentration. (All calculations may not be possible for zero concentrations.) 3. For each concentration, calculate the difference between the candidate mean and the standard average. 4. For each concentration, compute the following: (i) Yi = x + Ksd (ii) Y2 = x - Ksd Where Ksd= std dev * 3.5 for zero and the highest concentration value Ksd= std dev * 2.5 for all other concentration values x = mean (arithmetic average) of the set of candidate readings. 5. Compute the uncertainty (U) of the calibration curve for each concentration as follows: (i) Ui = concentration value - YI (ii) U2 = concentration value - Y2 6. Acceptance Criteria: (a) For each concentration, the differences calculated in Step 3 shall be no greater than the accuracy tolerances specified in §85.3(c)(3) for each instrument. (b) For each concentration, the uncertainties, (Ui and U2) shall be no greater than the accuracy tolerances required in §85.3(c)(3). (E) Alternative Calculation Procedure: 1. Use a gas divider readings as the standard values and compare them to the measured values of a sample lot of instruments 2. Compute the absolute and percent of point deltas using the equation in Section §85.4(d)(3)(ii)(E). 3. For each point, the instruments shall pass the criteria provided in Section §85.4(d)(3)(ii)(F). (ii) Analyzer System Repeatability. This test characterizes the ability of the instrument to give consistent readings when repeatedly sampling the same gas concentration. Page 50 Quality Control Requirements ------- §85.4 §85.4 (A) Using the high range span gas, introduce the gas through the calibration port. Record the readings. (B) Purge with ambient air for at least 30 seconds but no more than 60 seconds. (C) Repeat steps A and B above four more times. (D) Repeat steps A, B, and C, introducing the gas through the sample probe. (E) Acceptance Criteria: The differences between the highest and lowest readings from both ports shall not exceed the values specified in §85.3(c)(3)(vi). (iii) Analyzer System Response Time. This test determines the speed of response of the candidate instrument when a sample is introduced at the sample probe. (A) Gas calibrate the candidate instrument per the manufacturer's instructions. (B) Using a solenoid valve or equivalent selector system, remotely introduce an high range span gas to the probe. The gas pressure at the entrance to the probe shall be equal to room ambient. (C) Measure the elapsed time required for the instrument display to read 90% and 95% of the final stabilized reading for HC, CO, CO2 and NO. (Optional: Also, measure the time required for the O2 analyzer to read 0.1% O2). Alternatively the bench outputs may be recorded against a time base to determine the response time. Record all times in seconds. (D) Switch the solenoid valve to purge with zero air for at least 40 seconds but no more than 60 seconds. (E) Measure the elapsed time required for the NO instrument display to read 10% of the stabilized reading in Step C. (F) Repeat steps A, B, and C, two more times (total three times). (G) Acceptance Criteria: The response (drop time for O2 and NO; rise time for HC, CO, CO2 and NO) times shall meet the requirement specified in §85.3(c)(2)(x). The response time shall also be within ±1 second of the nominal response time supplied by the equipment supplier for use in §85.5(b)(5). (iv) Analyzer Interference Effects. The following acceptance test procedure shall be performed at 45°F, 75°F, and 105°F conditions, except as noted. (A) Zero and span the instrument. (B) Sample the following gases for at least one minute. Record the response of each channel to the presence of these gases. Page 51 Quality Control Requirements ------- §85.4 §85.4 1. 16% Carbon Dioxide in Nitrogen. 2. 1600 ppm Hexane in Nitrogen. 3. 10% Carbon Monoxide in Nitrogen. 4. 3000 ppm Nitric Oxide in Nitrogen. 5. 75 ppm Sulfur Dioxide (SO2) in Nitrogen. 6. 75 ppm Hydrogen Sulfide (H2S) in Nitrogen. (C) Water-Saturated Hot Air. Water-saturated hot air shall be drawn through the probe from the top of a sealed vessel partially filled with water through which ambient air will be bubbled. The water shall be maintained at a temperature of!22°F±9°F. This test shall be performed at only the 75°F, and 105°F conditions. (D) Acceptance Criteria: The interference effects shall not exceed the limits specified in §85.3(c)(2)(iii). (v) Electromagnetic Isolation and Interference. This test shall measure the ability of the candidate instrument to withstand electromagnetic fields which could exist in vehicle testing and repair facilities. For all tests described below, sample "Low-Middle Range Audit Gas" specified in §85.4(d)(3)(iii)(C), at atmospheric pressure, through the sample probe. Record analyzer reading during test periods. (A) Radio Frequency Interference Test. 1. Use a test vehicle with an engine having a high energy ignition system (or equivalent), a solid core coil wire and a 3/8" air gap. Leave engine off. 2. Locate the candidate instrument within 5 feet of the ignition coil. Gas calibrate the candidate instrument. 3. Sample gas specified above. Wait 20 seconds, and record analyzer readings. 4. Start engine. With the hood open and gas flowing to the analyzer, cycle the engine from idle through 25 mph on the dynamometer at ASM loads and record the analyzer readings. 5. Relocate the instrument to within 6 inches of one side of the vehicle near the engine compartment. Follow procedure described in step 4 and record analyzer readings. 6. Relocate the instrument to within 6 inches of the other side of the vehicle near the engine compartment. Follow procedure described in step 4 and record analyzer readings. 7. Acceptance Criteria: The analyzer readings shall deviate no more than 0.5% full scale. Page 52 Quality Control Requirements ------- §85.4 §85.4 (B) Induction Field Test. Use a variable speed (commutator type) hand drill having a plastic housing and rated at 3 amps or more. While the analyzer is sampling the gas, vary the drill speed from zero to maximum while moving from the front to the sides of the instrument at various heights. Acceptance Criteria: The analyzer readings shall deviate no more than 0.5% full scale. (C) Line Interference Test. Plug the drill used in part B above into one outlet of a #16-3 wire extension cord approximately 20 feet long. Connect the instrument into the other outlet of the extension cord. Repeat part B above. Acceptance Criteria: The analyzer readings shall deviate no more than 0.5% full scale. (D) VHF Band Frequency Interference Test. Locate both a citizens ban radio (CB), with output equivalent to FCC legal maximum, and a highway patrol transmitter (or equivalent) within 50 feet of the instrument. While the analyzer is sampling the gas, press and release transmit button of the both radios several times. Acceptance Criteria: The analyzer readings shall deviate no more than 0.5% full scale. (E) Ambient Conditions Instruments. Upon installation and every six months thereafter, the performance of the ambient conditions instruments shall be cross-checked against a master weather station. Acceptance Criteria: The individual instruments shall be within the tolerance specified in §85.3(c)(4). (v) Ambient Conditions Instruments. Upon installation and every six months thereafter, the performance of the ambient conditions instruments shall be cross checked against a master weather station. Acceptance Criteria: The individual instruments shall be within the tolerance specified in §85.3(c)(4). Page 53 Quality Control Requirements ------- §85.5 §85.5 §85.5 Test Record Information The following information shall be collected for each test performed (both passing and failing tests), recorded in electronic form, and made available to EPA upon request. (a) General Information. (1) Test Record Number (2) Inspection station and inspector numbers (3) Test system number (4) Dynamometer site (5) Date of test (6) Emission test start time and the time final emission scores are determined. (7) Vehicle identification number (8) License plate number (9) Test certificate number (10) Vehicle model year, make, and type (11) Number of cylinders or engine displacement (12) Transmission type (13) Odometer reading (14) Type of test performed (i.e., initial test, first retest, or subsequent retest) (b) Ambient Test Conditions. (1) Relative humidity (%) (2) Dry-bulb temperature (°F). (3) Atmospheric pressure (mm Hg) (4) NO correction factor (5) Nominal response time for each instrument (Transport + T90) (c) ASM Mode or Modes. The following information shall be captured separately for each test mode (ASM5015 and/or ASM2525) performed. (1) Final HC running average (AvgHC) (ppm) (2) Final CO running average (AvgCO) (%) (3) Final NO running average (AvgNO) (ppm) (4) Total horsepower used to set the dynamometer (THP5015) (hp) (5) Engine RPM running average corresponding to the final test score (6) Dilution correction factor (DCF) (d) Diagnostic/Quality Assurance Information. (1) Test time (seconds) (2) Mode time (seconds) (3) Vehicle speed (mph) for each second of the test (4) Engine RPM for each second of the test (5) Dynamometer load (pounds) for each second of the test (6) HC concentration (ppm) for each second of the test, not corrected for dilution (7) CO concentration (%) for each second of the test, not corrected for dilution Page 54 7/28/04 Test Record Information ------- §85.5 §85.5 (8) NO concentration (ppm) corrected for humidity for each second of the test, not corrected for dilution (9) CO2 concentration (%) for each second of the test (10) O2 concentration (%) for each second of the test (optional) Page 55 Test Record Information ------- §85.5 §85.5 Appendix A: Calculating Audit Tolerances "Actual Cylinder" field is input by the auditor in ppm or %. Audit limits are calculated and filled in by the spreadsheet (or the auditor). The tolerances are based on a 2% blend tolerance, accurate to 1%. It is recommended that NIST traceable standards accurate to 1% be used to verify all bottle names. Spreadsheet for Calculating Range High Mid High Mid Low Low Zero Gas HC (ppm) CO (%) C02 (%) NO (ppm) HC (ppm) CO (%) CO2 (%) NO (ppm) HC (ppm) CO (%) C02 (%) NO (ppm) HC (ppm) CO (%) CO2 (%) NO (ppm) HC (ppm) CO (%) C02 (%) NO (ppm) Gas Concentration Recom- mended 3200 8.00 12.00 3000 1920 4.80 7.20 1800 960 2.40 3.60 900 200 0.50 6.00 300 0 0.00 0.00 0 Actual Cylinder 3191 8.11 11.90 2987 1918 4.83 7.15 1801 960 2.39 3.57 902 203 0.49 6.01 299 0 0.00 0.00 0 Accuracy %of Reading 3.0% 3.0% 3.0% 4.0% 3.0% 3.0% 3.0% 4.0% 3.0% 3.0% 3.0% 4.0% 3.0% 3.0% 3.0% 4.0% 3.0% 3.0% 3.0% 4.0% Point 8 0.02 0.30 25 8 0.02 0.30 25 8 0.02 0.30 25 8 0.02 0.30 25 8 0.02 0.30 25 Gas 1 .0% 1 .0% 1 .0% 1 .0% 1 .0% 1 .0% 1 .0% 1 .0% 1 .0% 1 .0% 1 .0% 1 .0% 1 .0% 1 .0% 1 .0% 1 .0% 1 .0% 1 .0% 1 .0% 1 .0% ASM Audit Tolerances Audit Tolerance %of Reading 4.0% 4.0% 4.0% 5.0% 4.0% 4.0% 4.0% 5.0% 4.0% 4.0% 4.0% 5.0% 4.0% 4.0% 4.0% 5.0% 4.0% 4.0% 4.0% 5.0% % (as point) 128 0.32 0.48 149 77 0.19 0.29 90 38 0.10 0.14 45 8 0.02 0.24 15 0 0.00 0.00 0 Point 40 0.10 0.42 55 27 0.07 0.37 43 18 0.04 0.34 34 10 0.02 0.36 28 9 0.02 0.30 26 Applied Tnlprflnrp (greater of % or point) 128 0.32 0.48 149 77 0.19 0.37 90 38 0.10 0.34 45 10 0.02 0.36 28 9 0.02 0.30 26 Audit Limits Low 3063 7.79 11.42 2838 1841 4.64 6.78 1711 922 2.29 3.23 857 193 0.47 5.65 271 -9 -0.02 -0.30 -26 High 3319 8.43 12.38 3136 1995 5.02 7.52 1891 998 2.49 3.91 947 213 0.51 6.37 327 9 0.02 0.30 26 In the "Actual Cylinder" column, enter the gas concentrations from the audit cylinders The audit low and high tolerances are calculated in the columns on the right Page 56 Test Record Information ------- |