Name:
ASTM D7363-13 PDF
Published Date:
03/15/2013
Status:
Active
Publisher:
ASTM International
1.2 Lower molecular weight PAHs are more water soluble than higher molecular weight PAHs. Therefore, USEPA-regulated PAH concentrations in pore water samples vary widely due to differing saturation water solubilities that range from 0.2 µg/L for indeno[1,2,3-cd]pyrene to 31 000 µg/L for naphthalene. This method can accommodate the measurement of microgram per litre concentrations for low molecular weight PAHs and nanogram per litre concentrations for high molecular weight PAHs.
1.3 The USEPA narcosis model predicts toxicity to benthic organisms if the sum of the toxic units (ΣTUc) calculated for all “34 PAHs” measured in a pore water sample is greater than or equal to 1. For this reason, the performance limit required for the individual PAH measurements was defined as the concentration of an individual PAH that would yield 1/34 of a toxic unit (TU). However, the focus of this method is the 10 parent PAHs and 14 groups of alkylated PAHs (Table 1) that contribute 95 % of the toxic units based on the analysis of 120 background and impacted sediment pore water samples.3 The primary reasons for eliminating the rest of the 5-6 ring parent PAHs are: (1) these PAHs contribute insignificantly to the pore water TU, and (2) these PAHs exhibit extremely low saturation solubilities that will make the detection of these compounds difficult in pore water. This method can achieve the required detection limits, which range from approximately 0.01 µg/L, for high molecular weight PAHs, to approximately 3 µg/L for low molecular weight PAHs.
| Analyte | Added d-PAH | d-PAH Internal | Conc. for One | Performance Limit | Basis for |
| Naphthalene | A | A | 193.47 | 5.69 | B |
| 2-Methylnaphthalene |
| B | 81.69 | 2.40 | B |
| 1-Methylnaphthalene | B | B | 81.69 | 2.40 | B |
| C2-Naphthalenes |
| A | 30.24 | 0.89 | B |
| C3-Naphthalenes |
| A | 11.10 | 0.33 | B |
| C4-Naphthalenes |
| A | 4.05 | 0.12 | C |
| Acenaphthylene |
| C | 308.85 | 9.03 | B |
| Acenaphthene | C | C | 55.85 | 1.64 | B |
| Fluorene | D | D | 39.30 | 1.16 | B |
| C1-Fluorenes |
| D | 13.99 | 0.41 | B |
| C2-Fluorenes |
| D | 5.30 | 0.16 | B |
| C3-Fluorenes |
| D | 1.92 | 0.06 | S |
| Phenanthrene | E | E | 19.13 | 0.56 | B |
| Anthracene |
| E | 20.72 | 0.61 | B |
| C1-Phenanthrenes/Anthracenes |
| E | 7.44 | 0.22 | B |
| C2-Phenanthrenes/Anthracenes |
| E | 3.20 | 0.09 | B |
| C3-Phenanthrenes/Anthracenes |
| E | 1.26 | 0.04 | B |
| C4-Phenanthrenes/Anthracenes |
| E | 0.56 | 0.02 | S |
| Fluoranthene |
| F | 7.11 | 0.21 | B |
| Pyrene | F | F | 10.11 | 0.30 | B |
| C1-Fluoranthenes/Pyrenes |
| F | 4.89 | 0.14 | C |
| Benz[a]anthracene |
| G | 2.23 | 0.066 | B |
| Chrysene | G | G | 2.04 | 0.060 | B |
| C1-Chrysenes/Benz[a]anthracenes |
| G | 0.86 | 0.025 | C |
1.4 The test method may also be applied to the determination of additional PAH compounds (for example, 5- and 6-ring PAHs as described in Hawthorne et al.).4 However, it is the responsibility of the user of this standard to establish the validity of the test method for the determination of PAHs other than those referenced in 1.1 and Table 1.
1.5 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety and health practices and determine the applicability of regulatory limitations prior to use. For specific hazard statements, refer to Section 9.
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| Number of Pages : | 24 |
| Published : | 03/15/2013 |
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