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Table 1 Properties of the lake waters used in this study: lake pH and DOC concentrations were determined in the test water used for the bioassays

From: Predictions of Cu toxicity in three aquatic species using bioavailability tools in four Swedish soft freshwaters

Lake

Abiskojaure (n = 32)

Fiolen (n = 58)

St. Envättern (n = 56)

Älgsjön (n = 58)

RT90 X–Y

758,208–161,749

633,025–142,267

655,587–158,869

655,275–153,234

Latitude

68.3067°N

57.0917°N

59.0948°N

59.0948°N

Longitude

18.6550°E

14.5317°E

16.3693°E

16.3693°E

Catchment

Above treeline, tundra vegetation

Coniferous forest, some agriculture

Coniferous forest

Coniferous forest, some wetlands

Lake area (km2)

2.8

1.6

3.7

0.35

Max depth (m)

35

10

11

7.7

pHa

7.6

6.5

6.5

6.5

DOC (mg/L)a

0.88

7.0

10

17

Ca (mg/L)

4.5 ± 1.46

2.9 ± 0.22

3.4 ± 0.19

5.6 ± 0.93

Mg (mg/L)

0.70 ± 0.21

1.0 ± 0.1

0.85 ± 0.06

1.9 ± 0.30

Na (mg/L)

1.0 ± 0.53

3.9 ± 0.27

2.2 ± 0.09

3.2 ± 0.54

K (mg/L)

0.59 ± 0.13

1.5 ± 0.15

0.29 ± 0.02

0.85 ± 0.15

SO4 (mg/L)

4.3 ± 1.35

6.2 ± 0.68

5.9 ± 0.56

5.6 ± 1.31

Cl (mg/L)

1.1 ± 0.87

6.0 ± 0.51

2.8 ± 0.17

2.8 ± 0.42

Alk (mg CaCO3/L)

10 ± 4.43

3.0 ± 0.76

3.0 ± 0.62

13 ± 3.31

Hardness (mg CaCO3/L)

13

9.8

10

18

Cu (µg/L)*

0.91

0.74

0.38

0.78

Fe (µg/L)a

2.01

33

31

393

Cd (µg/L)a

0.012

0.034

0.006

0.006

Zn (µg/L)a

0.5

5

1.6

0.8

Pb (µg/L)a

0.005

0.1

0.06

0.08

Al (µg/L)a

1.5

49.7

33.7

56.9

  1. Major ion concentrations represent multi-annual means of all data 2000–2009 from the Swedish national monitoring program. Trace metal concentrations (0.22 µm filtered) were determined in the Daphnia test waters at test 0 and 48 h, the numbers presented is at test 48 h
  2. * Original concentration without any addition, detection (± 0.08)
  3. aAnalysed from bioassays at the end of 48 h