Research Article
Evaluation of the Presence of Endocrine-Disrupting Compounds in Dissolved and Solid Wastewater Treatment Plant Samples of Gran Canaria Island (Spain)
Table 5
Sludge and particulate matter (solid fractions) concentrations (ng·g−1) for each target compound in both WWTPS under study.
| Sludge samples | Jul '10 | Sep '10 | Nov '10 | Jan '11 | March '11 | May '11 | Jul '11 | Frequency (%) | Average |
| WWTP 1 | | | | | | | | | | NPa | 216.1 ± 9.1 | 479.1 ± 22.7 | 52.7 ± 2.1 | 211.3 ± 5.2 | 324.5 ± 6.7 | 175.9 ± 12.3 | 22.1 ± 0.2 | 100 | 211.7 | OPa | 49.3 ± 1.4 | 22.2 ± 1.2 | 39.1 ± 3.0 | 20.7 ± 2.0 | 8.7 ± 0.6 | 14.0 ± 2.3 | 22.3 ± 1.0 | 100 | 25.2 | NPEOsa | 461.1 ± 15.7 | 890.1 ± 35.1 | 125.4 ± 11.1 | 471.5 ± 8.1 | 92.1 ± 6.7 | 92.4 ± 3.3 | 451.4 ± 10.1 | 100 | 369.1 | OPEOsa | 74.5 ± 6.0 | 55.9 ± 1.7 | 21.9 ± 1.2 | 190.1 ± 9.5 | 25.1 ± 1.5 | 129.3 ± 9.1 | 44.0 ± 1.3 | 100 | 77.3 | BPAa | 0.9 ± 0.1 | BQLc | 7.7 ± 0.7 | BQLc | BQLc | 2.5 ± 0.2 | 7.9 ± 0.5 | 57.1 | 4.8 | E2a | 10.1 ± 1.0 | 5.1 ± 0.3 | 14.1 ± 0.9 | BQLc | 17.9 ± 1.4 | 20.6 ± 1.6 | 39.1 ± 1.1 | 85.7 | 17.8 | E1a | BQLc | BQLc | 7.5 ± 0.3 | BQLc | 1.7 ± 0.1 | BQLc | 3.2 ± 0.3 | 42.9 | 4.1 | E3a | BQLc | BQLc | BQLc | BQLc | BQLc | BQLc | 0.3 ± 0.0 | 14.3 | 0.3 | EEa | 27.1 ± 2.1 | 21.1 ± 2.0 | 22.0 ± 1.7 | 5.9 ± 0.4 | 38.9 ± 2.1 | 9.3 ± 0.5 | 42.0 ± 2.7 | 100 | 23.8 | DESa | BQLc | BQLc | 3.0 ± 0.4 | BQLc | 0.9 ± 0.1 | 11.5 ± 0.7 | BQLc | 42.9 | 5.1 |
| WWTP 2 | | | | | | | | | | NPa | 91.0 ± 5.0 | 101.2 ± 7.9 | 370.2 ± 26.3 | 250.1 ± 9.3 | 27.7 ± 2.1 | 63.0 ± 1.1 | 32.0 ± 1.8 | 100 | 133.6 | OPa | 60.1 ± 2.5 | 38.1 ± 3.1 | 35.1 ± 2.2 | 50.9 ± 1.7 | 12.5 ± 0.2 | 16.7 ± 1.3 | 71.2 ± 0.9 | 100 | 40.7 | NPEOsa | 240.9 ± 19.6 | 500.4 ± 32.3 | 612.1 ± 19.1 | 96.1 ± 1.1 | 218.3 ± 15.5 | 683.4 ± 4.5 | 403.9 ± 27.1 | 100 | 393.6 | OPEOsa | 311.8 ± 6.3 | 43.2 ± 2.1 | 104.0 ± 7.1 | 44.8 ± 2.3 | 47.5 ± 2.5 | 191.0 ± 7.0 | 161.6 ± 3.3 | 100 | 129.1 | BPAa | BQLc | BQLc | 15.9 ± 0.9 | 2.7 ± 0.2 | 1.9 ± 0.1 | BQLc |
7.6 ± 0.7 | 71.4 | 6.8 | E2a | 1.7 ± 0.2 | 7.2 ± 0.3 | 33.9 ± 1.0 | 21.1 ± 1.1 | 7.7 ± 0.1 | 73.7 ± 3.2 | 1.5 ± 0.1 | 100 | 21.0 | E1a | 4.3 ± 0.2 | BQLc | 5.0 ± 0.3 | BQLc | 4.5 ± 0.1 | 1.5 ± 0.1 | BQLc | 57.1 | 3.8 | E3a | BQLc | BQLc | BQLc | BQLc | BQLc | BQLc | BQLc | 0 | 0.0 | EEa | 111.1 ± 9.3 | 56.1 ± 2.1 | 121.7 ± 1.3 | 13.1 ± 0.4 | 25.8 ± 2.1 | 83.1 ± 3.9 | 55.9 ± 3.3 | 100 | 66.7 | DESa | BQLc | BQLc | 17.5 ± 0.4 | BQLc | BQLc | BQLc | 3.8 ± 0.3 | 28.6 | 10.7 |
| Particulate matter | Jul '10 | Sep '10 | Nov '10 | Jan '11 | March '11 | May '11 | Jul '11 | Frequency (%) | Average |
| WWTP 1 | | | | | | | | | | NPa | 198.6 ± 5.3 | 754.3 ± 39.1 | 105.7 ± 4.7 | 390.4 ± 33.3 | 401.6 ± 30.7 | 200.0 ± 15.9 | 90.9 ± 3.4 | 100 | 305.9 | OPa | 22.7 ± 0.9 | 50.0 ± 2.9 | 19.9 ± 1.1 | 120.4 ± 8.0 | 68.1 ± 4.3 | 30.5 ± 0.9 | 11.6 ± 1.0 | 100 | 50.1 | NPEOsa | 618.3 ± 40.2 | 391.8 ± 19.5 | 93.6 ± 6.1 | 290.5 ± 17.4 | 214.2 ± 16.1 | 183.5 ± 12.0 | 207.9 ± 10.6 | 100 | 285.7 | OPEOsa | 99.2 ± 3.9 | 69.6 ± 3.1 | BQLc | 78.9 ± 7.0 | 33.9 ± 1.9 | 40.7 ± 2.1 | 60.8 ± 5.9 | 85.7 | 63.9 | BPAa | 3.7 ± 0.2 | 12.3 ± 0.8 | BQLc | BQLc | BQLc | BQLc | 12.7 ± 0.6 | 42.9 | 9.6 | E2a | 21.5 ± 2.7 | 9.0 ± 0.7 | 51.7 ± 0.6 | 29.5 ± 3.3 | 7.1 ± 2.0 | 31.8 ± 1.3 | 50.3 ± 3.0 | 100 | 28.7 | E1a | 22.5 ± 0.9 | 14.0 ± 0.9 | BQLc | 5.1 ± 0.4 | BQLc | 11.0 ± 0.8 | BQLc | 57.1 | 13.2 | E3a | BQLc | BQLc | BQLc | 3.1 ± 0.1 | BQLc | BQLc | BQLc | 14.3 | 3.1 | EEa | 14.0 ± 0.7 | BQLc | 7.7 ± 0.4 | BQLc | 105.1 ± 7.8 | 12.9 ± 1.0 | 19.1 ± 0.5 | 71.4 | 31.8 | DESa | 14.3 ± 1.0 | BQLc | 6.3 ± 0.3 | BQLc | 10.4 ± 0.4 | BQLc | BQLc | 42.9 | 10.3 |
| WWTP 2 | | | | | | | | | | NPa | 129.2 ± 7.9 | 212.4 ± 3.9 | 209 ± 9.6 | 301.8 ± 19.1 | 63.6 ± 2.9 | 331.9 ± 20.1 | 99.5 ± 1.8 | 100 | 192.5 | OPa | 34.8 ± 0.7 | 41.6 ± 2.9 | 49.0 ± 3.3 | 69.7 ± 3.8 | 5.0 ± 0.2 | 22.9 ± 1.4 | 17.7 ± 0.9 | 100 | 34.4 | NPEOsa | 89.5 ± 5.3 | 350.1 ± 3.1 | 189.6 ± 10.6 | 78.0 ± 2.0 | 189.2 ± 4.9 | 1003 ± 61.9 | 106.8 ± 14.7 | 100 | 286.6 | OPEOsa | 129.6 ± 11.8 | 51.0 ± 2.1 | 128.4 ± 5.1 | 77.1 ± 0.9 | 31.7 ± 0.9 | 59.7 ± 5.1 | 184.6 ± 3.9 | 100 | 100.4 | BPAa | 21.5 ± 1.5 | BQLc | BQLc | BQLc | 3.9 ± 0.6 | BQLc | BQLc | 28.6 | 12.7 | E2a | 33.0 ± 2.0 | BQLc | 33.7 ± 2.9 | 22.7 ± 0.7 | 14.6 ± 0.4 | 44.8 ± 0.7 | 25.1 ± 3.3 | 85.7 | 29.0 | E1a | 13.5 ± 0.3 | 5.9 ± 0.3 | 21.3 ± 2.0 | BQLc | BQLc | 32.7 ± 0.8 | 5.5 ± 0.2 | 57.1 | 15.8 | E3a | BQLc | BQLc | BQLc | BQLc | BQLc | BQLc | BQLc | 0 | 0.0 | EEa | 33.9 ± 0.9 | 12.0 ± 0.1 | 75.9 ± 2.7 | 29.0 ± 3.1 | 91.8 ± 2.9 | 29.4 ± 0.5 | BQLc | 85.7 | 45.3 | DESa | 4.1 ± 0.3 | BQLc | 23.7 ± 2.0 | BQLc | BQLc | 6.9 ± 0.1 | BQLc | 42.9 | 11.6 |
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Mean and standard deviation of three determinations; bconcentration below the limit of detection; cconcentration below the limit of quantification.
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