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. 2014 Jul 24;225(8):2040. doi: 10.1007/s11270-014-2040-8

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