Table 1.
Compounds | Detection limit (μg/kg) | Biosolids concentration (μg/kg) Avg. (Min, Max) |
Detected Frequency (%) | Annual Load (kg/year)a (Min-Max) |
|||
---|---|---|---|---|---|---|---|
To biosolids | To land application | To incineration | To landfills | ||||
| |||||||
Polybrominated diphenylethers (PBDEs) | |||||||
| |||||||
BDE-7 | 0.025 | 1.1 (0.2, 1.7) | 100 | 5–7 | 3–4 | 1–1.3 | 1 |
BDE -8/11 | 0.029 | 0.2 (0.14, 0.4) | 100 | 1–2 | 0.6–0.9 | 0.2–0.3 | 0.2 |
BDE -12/13 | 0.052 | 0.17 (0.07, 0.24) | 60 | 0.9–1.1 | 0.4–0.6 | 0.1–0.2 | 0.1 |
BDE-15 | 0.010 | 2.6 (0.47, 7.7) | 100 | 13–17 | 7–10 | 2–3 | 2.5 |
BDE-17/25 | 0.023 | 23.7 (8.9, 42.2) | 100 | 121–152 | 60–91 | 24–30 | 20–26 |
BDE-28/33 | 0.027 | 13.4 (8.4, 18.6) | 100 | 68–85 | 34–51 | 14–17 | 12–15 |
BDE-32 | 0.016 | 0.08 (0.04, 0.16) | 100 | 0.4–1 | 0.2–0.3 | 0.1 | <0.1 |
BDE-37 | 0.011 | 0.24 (0.16, 0.37) | 100 | 1–2 | 0.6–0.9 | 0.2–0.3 | 0.2 |
BDE-47 | 0.055 | 789 (314, 1120) | 100 | 4026–5052 | 2012–3031 | 805–1010 | 684–859 |
BDE-49 | 0.015 | 38.4 (7.7, 62) | 100 | 196–246 | 98–148 | 39–49 | 33–42 |
BDE-51 | 0.015 | 2.9 (0.7, 5.1) | 100 | 15–18 | 7–11 | 3–4 | 2.5–3 |
BDE-66 | 0.020 | 16.6 (5.7, 26.1) | 100 | 85–106 | 42–63 | 17–21 | 14–18 |
BDE-71 | 0.016 | 9.3 (1.7, 17.8) | 100 | 48–60 | 24–36 | 10–12 | 8–10 |
BDE-75 | 0.033 | 1.2 (0.3, 1.7) | 100 | 6–7 | 3–4 | 1–1.5 | 1 |
BDE-77 | 0.016 | 0.06(0.05, 0.08) | 80 | 0.3–0.4 | 0.1–0.2 | <0.1 | <0.1 |
BDE-85 | 0.009 | 37 (16.8, 51.9) | 100 | 189–237 | 94–142 | 38–47 | 32–40 |
BDE-99 | 0.051 | 1004 (402, 1510) | 100 | 5123–6429 | 2561–3858 | 1025–1286 | 871–1093 |
BDE-100 | 0.018 | 179 (75.3, 229) | 100 | 913–1146 | 457–688 | 183–229 | 155–194 |
BDE-119/120 | 0.025 | 1.7 (1.2, 2.4) | 100 | 9–11 | 4–7 | 1.5–2 | 1.5 |
BDE-138/166 | 0.032 | 15 (7.4, 20) | 100 | 77–96 | 38–58 | 15–19 | 13–16 |
BDE-140 | 0.019 | 3.4 (1.7, 4.6) | 100 | 17–22 | 9–13 | 3–4 | 3–4 |
BDE-153 | 0.012 | 103 (43.9, 138) | 100 | 528–663 | 264–398 | 106–133 | 90–113 |
BDE-154 | 0.016 | 81.8 (34.3, 124) | 100 | 417–523 | 209–314 | 83–105 | 71–89 |
BDE-155 | 0.013 | 4.5 (1.8, 6.6) | 100 | 23–29 | 11–17 | 5–6 | 4–5 |
BDE-181 | 0.020 | 0.5 (0.1, 1) | 100 | 2–3 | 1–2 | 0.5 | 0.4 |
BDE-183 | 0.010 | 14 (8.4, 20.5) | 100 | 72–90 | 36–54 | 14–18 | 12–15 |
BDE-190 | 0.028 | 2 (0.9, 3.4) | 100 | 10–13 | 5–7 | 2–2.5 | 2 |
BDE-203 | 0.040 | 26.8 (9.3, 59.2) | 100 | 137–171 | 68–103 | 27–34 | 23–29 |
BDE-206 | 0.245 | 587 (149, 1420) | 100 | 2992–3754 | 1496–2253 | 598–751 | 509–638 |
BDE-207 | 0.219 | 663 (157, 1430) | 100 | 3381–4243 | 1690–2546 | 676–849 | 575–721 |
BDE-208 | 0.175 | 409 (112, 965) | 100 | 2088–2620 | 1044–1572 | 418–524 | 355–445 |
BDE-209 | 2.470 | 5360 (1420, 14200) | 100 | 27336–34304 | 13668–20582 | 5467–6861 | 4647–5832 |
| |||||||
Polybrominated biphenyls (PBBs) | |||||||
| |||||||
PBB-101b | 0.005 | 4.7 | - | 24–30 | 12–18 | 4.8–6 | 4.1–5.1 |
PBB-153b | 0.005 | 49.1 | - | 250–314 | 125–189 | 50.1–62.9 | 42.6–53.4 |
| |||||||
Other BFRs | |||||||
| |||||||
PBEB | 0.0002 | 1.6 (0.77, 2.5) | 100 | 8–10 | 4–6 | 1.6–2 | 1.5 |
HBB | 0.001 | 0.5 (0.16, 1.3) | 100 | 2–3 | 1–2 | 0.5 | 0.4 |
BTBPE | 0.6 | 1964 (37.3, 9060) | 100 | 10015–12568 | 5008–7541 | 2003–2514 | 1702–2137 |
DBDPE | 4 | 485 (6.43, 1440) | 60 | 2475–3105 | 1237–1863 | 495–621 | 421–528 |
alpha-HBCDb | 0.15 | 6.7 | - | 34–43 | 17–26 | 6.9–8.6 | 5.8–7.3 |
beta-HBCDb | 0.1 | 0.8 | - | 4–5 | 1.9–2.9 | 0.8–1 | 0.7–0.9 |
gamma-HBCDb | 0.14 | 12.3 | - | 63–79 | 31.4–47.2 | 12.6–15.8 | 10.7–13.4 |
Annual load values were calculated based on the estimated percentage of total sewage sludges use and disposal (50–60% to land application;17% to landfills; 20% to incineration). (NEBRA, 2007; Jones-Lepp and Stevens, 2007; National Research Council, 2002)
These compounds were analyzed in the mega-composite sample (mixture of composites 1 through 5) and hence minima and maxima values are not available.