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Table 3 Trace element loadings in aquatic sediments

From: Use of enzymatic tools for biomonitoring inorganic pollution in aquatic sediments: a case study (Bor, Serbia)

 

LCu

LPB

LZn

LNi

LCr

LAs

LFe

1.1.

497.012 ± 261.23

45.323 ± 10.241

87.828 ± 42.581

4.629 ± 0.923

34.215 ± 12.903

96.217 ±23.088

23.002 ±16.603

1.2.

1491.629 ± 190.238

125.619 ± 23.298

137.504 ± 54.261

4.695 ± 0.231

13.593 ± 12.094

182.707 ± 76.142

2190.084 ± 51.371

1.3.

1097.572 ± 319.027

160.991 ± 39.903

140.428 ± 72.945

3.272 ± 1.274

10.722 ± 5.894

259.295 ± 172.074

3361.688 ± 193.092

1.4.

1747.989 ± 424.722

64.905 ± 17.072

106.701 ± 43.706

5.424 ± 0.254

15.985 ± 7.439

24.127 ± 12.994

8.584 ± 4.026

1.5.

324.123 ± 281.556

43.123 ± 9.342

222.123 ± 83.293

7.291 ± 1.712

13.907 ± 12.093

13.723 ± 5.096

8.514 ± 3.339

2.1.

363.687 ± 120.502

47.384 ± 12.723

231.192 ± 31.528

7.529 ± 0.925

13.563 ± 2.055

17.693 ± 12.856

9.165 ± 5.015

2.2.

3770.809 ± 501.235

262.922 ± 42.311

2294.104 ± 305.812

11.227 ± 2.157

77.882 ± 54.737

333.726 ± 154.432

3299.040 ± 1266.065

2.3.

4433.846 ± 320.026

400.128 ± 59.637

3241.251 ± 577.243

12.871 ± 2.815

120.305 ± 48.862

523.103 ± 187.963

3519.447 ± 823.497

2.4.

3982.523 ± 448.204

360.164 ± 41.723

2923.382 ± 219.939

11.129 ± 1.997

121.019 ± 51.993

450.725 ± 152.209

4377.842 ± 265.936

2.5.

6283.177 ± 1218.743

480.102 ± 39.271

7150.596 ± 1023.724

17.528 ± 3.063

211.177 ± 79.451

858.593 ± 302.665

7150.245 ± 1088.278

3.1.

515.600 ± 257.692

66.223 ± 13.026

221.754 ± 51.038

4.229 ± 0.416

20.652 ± 13.634

92.754 ± 43.025

2127.441 ± 319.037

3.2.

2851.629 ± 403.271

211.698 ± 51.249

1170.629 ± 286.566

5.203 ± 0.684

40.944 ± 28.784

309.941 ± 152.227

3164.483 ± 1259.025

3.3.

1537.691 ± 284.361

120.872 ± 27.313

1735.728 ± 359.244

14.850 ± 1.274

15.229 ± 8.502

257.579 ± 104.429

34.661 ± 26.904

3.4.

2142.184 ± 430.009

81.553 ± 9.099

1470.534 ± 477.209

4.772 ± 0.619

113.380 ± 73.959

223.329 ± 138.862

34.220 ± 9.266

3.5.

4348.423 ± 385.206

115.426 ± 17.272

7190.323 ±1301.358

16.819 ± 3.219

125.506 ± 174.097

721.801 ± 302.940

42.688 ± 27.055

4.1.

501.724 ± 131.049

56.177 ± 16.055

152.718 ± 72.905

5.447 ± 1.441

23.619 ± 13.056

32.743 ± 21.623

7.170 ± 1.426

4.2.

2585.617 ±494.654

151.628 ± 25.014

2170.356 ± 567.023

7.202 ± 1.723

54.928 ± 24.174

219.506 ± 132.038

2749.279 ± 173.032

4.3.

3237.605 ± 1020.392

220.827 ± 6.251

1873.529 ± 510.698

8.896 ± 1.529

103.205 ± 75.022

335.858 ± 152.445

33.037 ± 17.994

4.4.

2945.256 ± 306.004

218.501 ± 26.569

1773.583 ± 490.115

6.711 ±1.204

117.325 ± 37.947

237.891 ± 87.707

26.615 ± 7.777

4.5.

4847.427 ± 881.220

215.933 ± 30.091

6371.991 ± 1756.093

13.803 ± 3.719

178.533 ± 16.093

681.203 ± 172.902

56.608 ± 12.201

DTV

36

85

140

35

100

-

-

GTV

60

100

200

50

100

20

-

  1. Abbreviations. LCu, copper levels in aquatic sediments; LPb, lead levels in aquatic sediments; LZn, zinc levels in aquatic sediments; LNi, nickel levels in aquatic sediments; LCr, chromium levels in aquatic sediments; LAs, arsenic levels in aquatic sediments; LFe, iron levels in aquatic sediments; 1.1., site S1 (July 2011); 1.2., site S2 (July 2011); 1.3., site S3 (July 2011); 1.4., site S4 (July 2011); 1.5., site S5 (July 2011); 2.1., site S1 (November 2011); 2.2., site S2 (November 2011); 2.3., site S3 (November 2011); 2.4., site S4 (November 2011); 2.5., site S5 (November 2011); 3.1., site S1 (March 2012); 3.2., site S2 (March 2012); 3.3., site S3 (March 2012); 3.4., site S4 (March 2012); 3.5., site S5 (March 2012); 4.1., site S1 (July 2012); 4.2., site S2 (July 2012); 4.3., site S3 (July 2012); 4.4., site S4 (July 2012); 4.5., site S5 (July 2012); DTV, Dutch targer values for TE concentrations in aquatic sediments; GTV, German target values for TE concentrations in aquatic sediments.
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BMC Chemistry

ISSN: 2661-801X

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