Analysis of Bio-Obtainable Endocrine Disrupting Metals in River Water and Sediment, Sewage Influent/Effluent, Sludge, Leachate, and Concentrated Leachate, in the Irish Midlands Shannon Catchment
Table 10
Concentrations of metals found in sludge (mg/kg) for each treatment type.
Metal
Site type
Sediment concentration (mg/kg)
(MPC mg/kg)
Nov
Dec
Jan
Feb
Mar
Apr
Kruskal-Wallis value for versus versus †
Mean % RSD
Ni 300–400
2905
2310
2210
2278
2180
375
.220
1.5
3625
4700
4055
3408
910
325
4.1
2633
2925
3208
3010
2480
175
2.1
Mn
243
358
185
658
698
410
.109
3.5
320
220
150
740
240
1642
1.9
178
180
123
90
241
615
2.4
Cd 20–40
15
16
12
15
20
100
.059
11.3
7
8
13
9
6
20
14.6
15
14
15
13
17
30
15.2
Zn 2500–4000
1187
1048
952
925
981
2001
.484
0.4
3400
1625
1002
1845
643
1745
0.3
846
844
888
1162
1081
2826
0.4
Co
8
10
8
9
10
7
.044
2.3
23
13
20
15
10
10
7.5
16
19
24
37
9
5
5.6
Pb 750–1200
150
300
325
250
375
750
.109
1.3
150
100
250
275
150
700
0.5
300
350
325
375
375
675
2.0
Cr n/a
253
296
410
372
473
372
.003
8.2
213
35
134
212
68
137
7.8
253
334
403
486
455
289
9.1
Cu 1000–1750
212
200
155
145
155
703
.164
3.4
625
373
373
478
33
1003
1.7
275
240
265
435
398
531
2.0
*Hg 16–25
—
0.16
—
0.34
—
0.42
.054*
—
—
0.42
—
0.36
—
0.40
—
—
0.88
—
1.14
—
0.88
—
Maximum permitted concentration as per EU directive 278/86. †Using Minitab15. This test, applied following evidence of nonnormality of the observed levels, tests for equality of medians of the treatment types (, , and ), that is, if we conclude that the medians are not the same. Adjustments made for ties as required.
*Only 3 samples from each site were chosen for mercury analysis