Additions and Corrections 2007, Volume 41, Pages 1962–1969
Sarah G. Riddle, Michael A. Robert, Chris A. Jakober, Michael P. Hannigan and Michael J. Kleeman*: Size Distribution of Trace Organic Species Emitted From Heavy-Duty Diesel Vehicles Ratios of analyte mass to total organic carbon (OC) mass (µg/ g) for the PM1.8 and the PM0.1 size fractions are shown in Tables 1 and 2, respectively. Ratios of analyte mass to total elemental carbon (EC) mass (µg/g) for the PM1.8 and PM0.1 size fractions are shown in Tables 3 and 4, respectively. The PM0.1 values published in the original manuscript did not incorporate the pyrolysis correction in the OC and EC values used to normalize the mass of each analyte. The PM1.8 values published in the original manuscript did not incorporate correction for adsorption artifacts measured with a downstream filter. The authors apologize for these errors. The revised values shown in Tables 1–4 confirm all of the conclusions made in the original manuscript with a single exception. The abundance of PAHs relative to OC in the ultrafine size fraction and the PM1.8 size fraction are approximately equal. There is not an enhancement of the relative PAH concentration in the ultrafine size fraction as was stated in the original manuscript.
TABLE 1. Ratio of Analyte Mass (µg) to Organic Carbon Mass (g) for the RAAS Filter Measurements for Organic Compounds Emitted from HDDVs in the PM1.8 Size Fractiona 1999 Freightliner idle/Creep
1999 Freightliner 56k
1998 Kenworth 56K
1998 Kenworth 66K
1992 Volvo 56K
1985 Freightliner 56K
compound
ratio
error
ratio
error
ratio
error
ratio
error
ratio
error
ratio
error
hopanes 17R(H)-21β(H)-29-norhpane 17R(H)-21β(H)-hopane
348.4 186.2
34.4 18.4
171.5 122.3
17.0 12.2
285.0 278.5
32.7 31.9
163.1 196.6
19.7 24.7
144.9 234.3
18.5 29.7
177.0 197.7
16.0 18.2
steranes Rββ-20R-stigmastane Rββ-20S-stigmastane
101.7 83.3
10.1 8.2
78.5 61.5
7.8 6.1
133.3 112.9
15.3 13.0
81.7 25.3
11.3 6.7
65.2 101.1
8.3 12.8
171.8 118.4
15.7 11.1
9.2 ND 9.7 12.1 ND ND 22.3 48.1 13.1 5.0 11.9 4.3 10.4 8.4 8.5 36.7 16.2
2.9
96.6 ND 60.0 141.0 51.6 41.8 115.6 250.8 15.5 ND ND ND ND ND ND ND ND
12.5
125.1 ND 70.5 142.8 68.2 57.5 91.5 282.1 56.2 24.2 25.1 4.4 18.4 18.7 ND 20.7 ND
18.0
31.4 ND 165.8 205.4 114.5 82.8 71.6 156.9 41.8 30.9 51.9 4.3 15.4 2.1 ND 12.6 ND
9.3
73.8 ND 40.6 103.2 66.9 56.3 305.9 684.8 79.5 20.5 23.5 ND 31.6 ND ND ND ND
12.4
422.7 24.5 375.6 493.8 275.5 201.9 458.9 781.5 106.0 37.3 62.3 6.0 41.8 13.4 ND ND ND
47.8 6.0 50.8 61.9 42.4 37.2 51.8 88.0 12.3 7.3 29.6 14.6 6.5 5.2
b
PAHs phenanthrene anthracene A-methylphenanthrene B-methylphenanthrene C-methylphenanthrene D-methylphenanthrene fluoranthene pyrene benzo[ghi]fluoranthene chrysene benzo[b]fluoranthene benzo[k]fluoranthene benzo[e]pyrene benzo[a]pyrene indeno[1,2,3-cd]pyrene benzo[ghi]perylene coronene
14.9 14.9 3.7 7.2 2.7 2.9 8.0 1.7 3.4 4.0 7.4 5.8 3.0
25.7 29.7 25.5 25.2 14.5 30.8 4.1
29.1 33.5 29.0 28.6 13.4 39.5 8.8 6.3 15.0 3.1 6.5 7.6 8.3
a Uncertainty values represent analytical uncertainty. ND ) not detected. of relative retention times to those in the literature.
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b
62.5 64.5 60.6 59.8 13.1 24.3 7.3 12.1 56.1 28.0 8.6 9.5 23.6
34.7 37.1 35.4 35.1 44.3 98.6 12.6 7.2 18.5 8.7
Analyte identification based on comparisons
10.1021/es7022169 CCC: $40.75
2008 American Chemical Society
Published on Web 12/19/2007
TABLE 2. Ratio of Analyte Mass (µg) to Organic Carbon Mass (g) for the MOUDI Measurements for Organic Compounds Emitted from HDDVs in the PM0.1 Size Fractiona 1999 Freightliner idle/creep
1999 Freightliner 56k
1998 Kenworth 56K
1998 Kenworth 66K
1992 Volvo 56K
1985 Freightliner 56K
compound
ratio
error
ratio
error
ratio
error
ratio
error
ratio
error
ratio
error
hopanes 17R(H)-21β(H)-29-norhopane 17R(H)-21β(H)-hopane
149.6 127.0
9.0 7.7
138.9 125.2
9.0 8.2
104.6 111.1
6.7 7.1
560.4 649.8
48.7 57.2
189.6 184.6
14.1 13.8
93.1 124.9
6.6 9.5
steranes Rββ-20R-stigmastane Rββ-20S-stigmastaneb
42.0 37.9
2.5 2.3
66.6 47.8
4.3 3.1
41.5 29.5
2.7 2.0
195.0 155.3
18.6 15.6
0.0 0.0
PAHs phenanthrene anthracene A-methylphenanthrene B-methylphenanthrene C-methylphenanthrene D-methylphenanthrene fluoranthene pyrene benzo[ghi]fluoranthene chrysene benzo[b]fluoranthene benzo[k]fluoranthene benzo[e]pyrene benzo[a]pyrene indeno[1,2,3-cd]pyrene benzo[ghi]perylene coronene
19.9 ND ND ND ND ND 6.2 10.1 2.8 2.3 5.5 1.7 5.6 4.3 2.4 12.4 ND
2.8
105.2 ND 110.1 155.2 65.9 60.2 163.5 361.1 16.2 ND ND ND ND ND ND ND ND
10.7
27.8 ND 20.4 29.5 11.7 9.3 29.4 74.5 34.4 18.3 17.7 ND 6.4 5.8 ND ND ND
5.0
61.5 ND ND ND ND ND 62.5 200.8 49.4 27.3 36.9 ND 26.6 ND ND ND ND
12.6
125.4 ND 90.6 191.0 115.0 90.5 379.2 950.8 80.5 19.4 ND ND ND ND ND ND ND
1.9 3.0 1.7 2.2 6.1 1.3 2.5 3.0 5.7 3.4
24.4 26.4 23.1 23.0 15.7 34.2 3.6
23.2 23.2 23.1 23.1 4.6 9.1 4.7 4.8 12.4 5.0 5.9
a Uncertainty values represent analytical uncertainty. ND ) not detected. of relative retention times to those in the literature.
b
12.8 26.1 7.8 14.8 72.0 11.2
0.0 0.0 13.9 31.5 35.4 32.2 31.5 38.4 95.5 9.3 6.1
235.6 79.2 288.7 364.9 205.7 148.4 355.4 559.2 94.9 33.0 51.9 ND ND ND ND ND ND
22.4 9.8 42.6 46.9 38.8 36.8 33.2 52.0 9.3 7.4 33.2
Analyte identification based on comparisons
TABLE 3. Ratio of Analyte Mass (µg) to Elemental Carbon Mass (g) for the RAAS Filter Measurements from HDDVs in the PM1.8 Size Fractiona 1999 Freightliner idle/creep
1999 Freightliner 56k
1998 Kenworth 56K
1998 Kenworth 66K
1992 Volvo 56K
1985 Freightliner 56K
compound
ratio
error
ratio
error
ratio
error
ratio
error
ratio
error
ratio
error
hopanes 17R(H)-21β(H)-29-norhpane 17R(H)-21β(H)-hopane
723.9 386.8
72.2 38.6
104.2 74.3
8.5 6.1
218.6 213.5
19.6 19.2
114.8 138.4
10.9 14.0
28.4 45.9
2.1 3.4
45.8 51.2
3.2 3.7
steranes Rββ-20R-stigmastane Rββ-20S-stigmastaneb
211.3 173.0
21.1 17.3
47.7 37.4
3.9 3.1
102.2 86.6
9.2 7.8
57.5 17.8
6.7 4.5
12.8 19.8
1.0 1.4
44.5 30.7
3.2 2.3
PAHs phenanthrene anthracene A-methylphenanthrene B-methylphenanthrene C-methylphenanthrene D-methylphenanthrene fluoranthene pyrene benzo[ghi]fluoranthene chrysene benzo[b]fluoranthene benzo[k]fluoranthene benzo[e]pyrene benzo[a]pyrene indeno[1,2,3-cd]pyrene benzo[ghi]perylene coronene
19.2 ND 20.2 25.1 ND ND 46.3 99.9 27.1 10.4 24.7 9.0 21.5 17.5 17.7 76.2 33.7
6.1
58.7 ND 36.5 85.7 31.4 25.4 70.2 152.3 9.4 ND ND ND ND ND ND ND ND
6.9
95.9 ND 54.0 109.5 52.3 44.1 70.2 216.3 43.1 18.6 19.2 3.3 14.1 14.3 ND 15.9 ND
12.0
22.1 ND 116.8 144.6 80.6 58.3 50.4 110.5 29.4 21.8 36.6 3.0 10.9 1.5 ND 8.9 ND
6.3
14.5 ND 8.0 20.2 13.1 11.0 59.9 134.2 15.6 4.0 4.6 ND 6.2 ND ND ND ND
1.9
109.5 6.3 97.3 127.9 71.3 52.3 118.8 202.4 27.5 9.7 16.1 1.6 10.8 3.5 ND ND ND
10.7 1.5 12.0 14.3 10.2 9.2 11.6 19.7 2.8 1.8 7.6 3.8 1.6 1.3
30.9 30.9 7.7 14.9 5.7 6.0 16.6 3.6 7.2 8.2 15.3 12.1 6.2
15.5 17.4 15.4 15.3 7.9 16.6 2.4
22.0 24.5 21.9 21.7 9.0 26.0 6.0 4.6 11.5 2.4 4.9 5.7 6.2
a Uncertainty values represent analytical uncertainty. ND ) not detected. of relative retention times to those in the literature.
b
43.1 44.1 42.2 41.8 8.4 15.0 4.7 8.3 39.4 19.7 6.0 6.7 16.6
6.7 7.0 6.8 6.8 6.1 13.4 1.9 1.3 3.6 1.6
Analyte identification based on comparisons
VOL. 42, NO. 3, 2008 / ENVIRONMENTAL SCIENCE & TECHNOLOGY
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TABLE 4. Ratio of Analyte Mass (µg) to Elemental Carbon Mass (g) for the MOUDI Measurements from HDDVs in the PM0.1 Size Fractiona 1999 Freightliner idle/creep
1999 Freightliner 56k
1998 Kenworth 56K
1998 Kenworth 66K
1992 Volvo 56K
1985 Freightliner 56K
compound
ratio
error
ratio
error
ratio
error
ratio
error
ratio
error
ratio
error
hopanes 17R(H)-21β(H)-29-norhpane 17R(H)-21β(H)-hopane
443.4 376.4
36.0 30.6
134.6 121.3
11.3 10.2
141.2 150.0
14.6 15.5
398.1 461.6
35.9 42.1
37.3 36.3
2.3 2.2
26.4 35.5
1.8 2.6
steranes Rββ-20R-stigmastane Rββ-20S-stigmastaneb
124.4 112.4
10.1 9.2
64.5 46.3
5.4 3.9
56.0 39.9
5.8 4.2
138.5 110.3
13.6 11.4
ND ND
PAHs phenanthrene anthracene A-methylphenanthrene B-methylphenanthrene C-methylphenanthrene D-methylphenanthrene fluoranthene pyrene benzo[ghi]fluoranthene chrysene benzo[b]fluoranthene benzo[k]fluoranthene benzo[e]pyrene benzo[a]pyrene indeno[1,2,3-cd]pyrene benzo[ghi]perylene coronene
59.0 ND ND ND ND ND 18.5 29.9 8.2 6.8 16.4 5.1 16.6 12.9 7.2 36.9 ND
8.9
102.0 ND 106.7 150.4 63.9 58.3 158.4 349.9 15.7 ND ND ND ND ND ND ND ND
11.8
37.5 ND 27.6 39.8 15.8 12.6 39.7 100.6 46.4 24.7 24.0 ND 8.7 7.8 ND ND ND
7.4
43.7 ND ND ND ND ND 44.4 142.6 35.1 19.4 26.2 ND 18.9 ND ND ND ND
9.0
5.7 9.2 4.9 6.5 18.1 3.8 7.5 8.8 16.8 10.3
24.4 26.8 22.7 22.5 17.4 38.0 3.6
31.3 31.5 31.2 31.2 7.0 14.8 7.4 6.7 16.8 6.8 8.1
a Uncertainty values represent analytical uncertainty. ND ) not detected. of relative retention times to those in the literature.
b
9.2 18.8 5.6 10.5 51.2 8.0
24.7 ND 17.8 37.6 22.7 17.8 74.7 187.2 15.8 3.8 ND ND ND ND ND ND ND
2007, Volume 41, Pages 2387–2394
E. Matthew Fiss, Krista L. Rule, and Peter J. Vikesland*: Formation of Chloroform and other Chlorinated Byproducts by Chlorination of Triclosan-Containing Products The value for a parameter in the Potential Health Significance section was reported incorrectly. The triclosan mass concentration (TC) used in the model was 3.3 mg triclosan/g soap, which represents the upper end of the range of triclosan concentrations measured in the tested soaps. If the reported value of 2.0 mg triclosan/g soap were applied, the resulting inhalational exposure would range from 3.5 to 14.5 mg/yr.
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2.5 6.1 6.8 6.3 6.1 6.9 17.1 1.7 1.2
66.9 22.5 82.0 103.6 58.4 42.2 100.9 158.8 27.0 9.4 14.7 ND ND ND ND ND ND
6.3 2.7 12.0 13.2 11.0 10.4 9.3 14.5 2.6 2.1 9.4
Analyte identification based on comparisons
ES7022169 10.1021/es7022169 Published on Web 12/19/2007
ES702530R 10.1021/es702530r Published on Web 12/20/2007
ND ND
