Comparison of Emissions
Comparison of PAH and Nitro-PAH Emissions Among Standard Diesel Fuel, B100 Fuel, and Their Blend on Diesel Engines.
Joseph Pan*, Shraddha Quarderer, Tina Smeal, and Christopher Sharp
Southwest Research Institute, San Antonio, Texas 78238
Tests were carried out to examine PAH and nitro-PAH (n-PAH) emissions in a neat standard low sulphur diesel (2D), a neat B100 fuel, and a standard B100 blend (80% 2D/20% B100, B20) from three diesel engines.
The test engines were a 1997 Cummins N14, a 1997 Detroit Diesel Corporation (DDC) Series 50, and a 1995 Cummins B5.9. The emission tests were carried out in ways that the data generated could be submitted to the U.S. EPA in order to comply with Tier 1 requirements under Section 211(b) of the Clean Air Act.
The emissions were measured over the heavy-duty transient Federal Test Procedure (FTP). One-seventh of the cold start and six-sevenths of hot start emissions were collected on the same sampling media. The particulate samples were collected on filters and Soxhlet extracted with ethanol/toluene (30/70, v/v). The gas phase samples were collected on PUF/XAD-2 traps and Soxhlet extracted separately using hexane/ether (94/6 for PUF) and DCM (for XAD-2). The two extracts were combined prior to analysis. The sample extracts were cleaned up* and analyzed by GC/MS/SIM in positive ion electron impact (PIEI) mode for the PAHs. Separate GC/MS/SIM runs in negative ion chemical ionization (NICI) mode were performed for n-PAH analysis. Results are summarized as follows:
|
Summary of Transient Composite PAH and n-PAH Data for the CUMMINS B5.9 Engine |
PAH and n-PAH Compounds |
B100 |
80/20 Blend |
Standard Diesel |
No Catalyst Run 1 |
No Catalyst Run 2 |
Catalyst |
No Catalyst |
Catalyst |
No Catalyst |
Catalyst |
| Benzo(a)anthracene |
551 |
358 |
154 |
812 |
423 |
905 |
378 |
| Chrysene |
821 |
568 |
300 |
1272 |
744 |
1707 |
714 |
| Benzo(b)fluoranthene |
569 |
495 |
318 |
710 |
538 |
1164 |
374 |
| Benzo(k)fluoranthene |
715 |
450 |
292 |
783 |
466 |
1072 |
373 |
| Benzo(a)pyrene |
464 |
251 |
155 |
341 |
344 |
723 |
241 |
| Indeno(1,2,3-cd)pyrene |
1172 |
384 |
674 |
689 |
1144 |
1294 |
714 |
| Dibenz(a,h)anthracene |
124 |
149 |
84 |
217 |
181 |
304 |
141 |
| Benzo(g,h,i)perylene |
1278 |
549 |
940 |
755 |
1100 |
1354 |
773 |
Total PAHs |
5694 |
3204 |
2917 |
5579 |
4940 |
8523 |
3708 |
| 2-Nitrofluorene |
142 |
122 |
73 |
* |
365 |
257 |
478 |
| 1-Nitropyrene |
34 |
20 |
325 |
265 |
1644 |
210 |
2171 |
| 7-Nitrobenz(a)anthracene |
0.6 |
Trace |
4.5 |
9.8 |
44 |
34 |
60 |
| 6-Nitrochrysene |
Trace |
Trace |
6.2 |
1.9 |
58 |
11 |
56 |
| 6-Nitrobenz(a)pyrene |
1.9 |
0.7 |
2.2 |
8.6 |
11 |
6.1 |
6.8 |
| Total n-PAHs |
179 |
143 |
411 |
285 |
2122 |
518 |
2772 |
| *Data not included due to problem with very high cold-start filter value. All values are background corrected.
Unit in ng/hp-hr. Trace-less than 0.5 ng/hp-hr |
*Joseph C. Pan, et al. Analysis of PAH in Fish by HRGC/HRMS. Proceedings of the 46th ASMS Conference on Mass Spectrometry and Allied Topics, June 4-8, 1998, Orlando, FL, pp. 370.
|
Summary of Transient Composite of PAH and n-PAH Data for the Cummins N14 Engine |
PAH and n-PAH Compound |
B100 [Avg 3 Runs] |
80/20 Blend (B20) [1 Run] |
Standard Diesel (2D) [Avg 3 Runs] |
|
Benzo(a)anthracene |
1555 |
3158 |
3309 |
|
Chrysene |
585 |
1928 |
3987 |
|
Benzo(b)fluoranthene |
443 |
1945 |
1629 |
|
Benzo(k)fluoranthene |
383 |
1738 |
1806 |
|
Benzo(a)pyrene |
231 |
1456 |
1435 |
|
Indeno(1,2,3-cd)pyrene |
205 |
832 |
916 |
|
Dibenz(a,h)anthracene |
62 |
295 |
315 |
|
Benzo(g,h,i)perylene |
236 |
1478 |
1252 |
|
Total PAHs |
3700 |
12830 |
14649 |
|
2-Nitrofluorene |
9.4 |
144 |
123 |
|
1-Nitropyrene |
5.8 |
37 |
82 |
|
7-Nitrobenz(a)anthracene |
Trace |
0.7 |
1.9 |
|
6-Nitrochrysene |
Trace |
Trace |
0.8 |
|
6-Nitrobenz(a)pyrene |
Trace |
0.9 |
2.5 |
|
Total n-PAHs |
15.2 |
182 |
210 |
|
Unit in ng/hp-hr. Trace-less than 0.5 ng/hp-hr |
| Summary of Transient Composite PAH and n-PAH Data for the DDC Series 50 Engine |
PAH and n-PAH Compound |
B100 |
80/20 Blend |
Standard Diesel |
| No Catalyst |
Catalyst |
No Catalyst |
Catalyst |
No Catalyst |
Catalyst |
|
Benzo(a)anthracene |
410 |
84 |
522 |
233 |
1152 |
495 |
|
Chrysene |
469 |
259 |
736 |
345 |
1755 |
691 |
|
Benzo(b)fluoranthene |
209 |
175 |
229 |
99 |
437 |
214 |
|
Benzo(k)fluoranthene |
219 |
111 |
228 |
107 |
527 |
274 |
|
Benzo(a)pyrene |
183 |
29 |
268 |
152 |
1614 |
226 |
|
Indeno(1,2,3-cd)pyrene |
129 |
99 |
142 |
49 |
234 |
86 |
|
Dibenz(a,h)anthracene |
23 |
24 |
47 |
20 |
87 |
38 |
|
Benzo(g,h,i)perylene |
424 |
301 |
381 |
149 |
558 |
184 |
|
Total PAHs |
2066 |
1082 |
2553 |
1154 |
6364 |
2208 |
|
2-Nitrofluorene |
40 |
14 |
70 |
67 |
88 |
90 |
|
1-Nitropyrene |
5.2 |
37 |
19 |
249 |
83 |
76 |
|
7-Nitrobenz(a)anthracene |
ND |
Trace |
0.9 |
0.7 |
1.4 |
1.4 |
|
6-Nitrochrysene |
ND |
1.8 |
0.8 |
4.0 |
0.8 |
5.8 |
|
6-Nitrobenz(a)pyrene |
Trace |
Trace |
2.4 |
1.8 |
11.1 |
4.2 |
| Total n-PAHs |
45.2 |
52.8 |
93.1 |
323 |
184 |
177 |
|
Unit in ng/hp-hr. Trace-less than 0.5 ng/hp-hr |
Conclusions:
- The pure B100 fuel produced much less PAH and n-PAH than the standard diesel fuel.
- The 20% B100/80% diesel blend produced substantially less PAH and n-PAH than the standard low sulphur diesel fuel in most cases.
- The catalyst reduced PAH emissions of all fuels on two test engines. The catalyst increased n-PAH emissions of most fuels on two test engines.
|