Environmental Engineering Reference
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although the adsorption capacities reported were low (TableĀ  10.6).
Netpradit et al. [146-148] studied the capacity and mechanisms of metal
hydroxide sludge in removing azo reactive dyes. The sludge is a dried
waste from the electroplating industry, which is produced by precipi-
tation of metal ions in wastewater with calcium hydroxide. It contains
insoluble metal hydroxides and other salts. The authors demonstrated
that metal hydroxide sludge was an effective positively charged adsorbent
with maximum adsorption capacities for azo reactive dyes. The charge of
the dyes is an important factor for the adsorption due to the ion exchange
mechanism. Similar interesting results were reported by Santos et al. [83],
Table 10.6 Reported adsorption capacities q max (mg g -1 ) for industrial
byproducts (selected papers).
Adsorbent
Dye
q max
Reference
Activated red mud
Reactive Blue 19
454.54
[160]
Activated red mud
Acid Blue 113
83.33
[161]
Activated red mud
Reactive Black 5
35.58
[161]
Boron waste
Astrazon Red
74.73
[162]
Chrome sludge
Basic Blue 9
0.51
[163]
Fe (III)/Cr (III) hydroxide
Basic Blue 9
22.8
[164]
Fly ash
Alizarin Sulfonic
11.21
[98]
Fly ash
Rhodamine B
10
[165]
Fly ash
Basic Blue 9
5.57
[166]
Fly ash
Basic Blue 9
5.52
[149]
Fly ash
Basic Blue 9
4.6
[167]
Leather waste
Reactive Red
163
[158]
Leather waste
Basic Blue 9
80
[158]
Metal hydroxide sludge
Reactive Blue 19
91
[168]
Metal hydroxide sludge
Reactive Red 2
62.5
[148]
Metal hydroxide sludge
Reactive Red 141
56.18
[148]
Metal hydroxide sludge
Reactive Red 120
48.31
[148]
Palm oil mill sludge
Basic Blue 9
50.7
[169]
Red mud
Basic Blue 9
2.49
[155]
Red mud
Direct Red 28
4.05
[156]
Sewage sludge
Basic Blue 9
114.9
[47]
Sludge waste
Bomaplex Red CR-L
192.31
[170]
 
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