Table 2.
Characterisation of 4-nonylphenol and 4-tert-octylphenol concentration in sediment samples collected in river estuaries (A), at shallow coastal stations (B) and at deeper open water stations (C)
Sampling station/variable | 4-nonylphenol [ng∙g−1 dw] | 4-tert-octylphenol [ng g−1 dw] | |
---|---|---|---|
A. Rivers | |||
Min–max | Min–max | ||
ST6 | Gizdepka River | <LOQ—4.93 | 0.55–47.12 |
ST2 | Kacza River | <LOQ—2.21 | <LOQ—8.51 |
ST1 | Vistula Swibno | <LOQ—4.44 | <LOQ—23.43 |
n | 18 | 18 | |
x ± SD | 2.26 ± 1.63 | 7.58 ± 13.43 | |
Median | 0.63 | 2.71 | |
B. Coastal station | |||
ST7 | Swarzewo | <LOQ—3.13 | 0.5–48.88 |
ST5 | Mechelinki | <LOQ—2.32 | 0.14–38.72 |
ST4 | Gdynia Seaside Boulevard | <LOQ—13.56 | <LOQ—18.74 |
ST3 | Orlowo | <LOQ—2.21 | 0.16–14.90 |
n | 24 | 24 | |
x ± SD | 2.35 ± 3.38 | 9.57 ± 13.45 | |
Median | 1.34 | 3.24 | |
C. Open water stations (depths over 4 m) | |||
ME | <LOQ—0.23 | 0.15–2.45 | |
SP | <LOQ—2.66 | 1.02–11.75 | |
GDY | <LOQ—4.24 | 0.34–20.47 | |
GN | 0.08–3.95 | 1.77–17.89 | |
UW | <LOQ—249.08 | 2.61–18.44 | |
n | 30 | 30 | |
x ± SD | 12.58 ± 52.83 | 5.30 ± 5.51 | |
Median | 1.06 | 2.61 |
n sampling number, x mean value, SD standard deviation, LOQ limit of quantification, LOQ = 0.08 ng g−1 dw