Modelling for the Efficient Effluent Dye Removal to Reuse Water and Salt
Abstract
:1. Introduction
2. Materials and Methods
3. Results and Discussion
3.1. Decolouration Kinetics
3.2. Influence of NaCl Concentration
3.3. Kinetic Adjustments
3.4. Models of Kinetic Parameters
3.5. Optimisation of the Industrial Working Conditions
4. Conclusions
Supplementary Materials
Author Contributions
Funding
Data Availability Statement
Conflicts of Interest
References
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Trial | pH | CNaCl (mS/cm) | Ctotal (mS/cm) | di (g/L) | Reference |
---|---|---|---|---|---|
1 | 5 | 30.0 | 30.0 | 1.0 | 5-30-30-1 |
2 | 7 | 30.0 | 30.0 | 1.0 | 7-30-30-1 |
3 | 9 | 30.0 | 30.0 | 1.0 | 9-30-30-1 |
4 | 7 | 50.0 | 50.0 | 1.0 | 7-50-50-1 |
5 | 7 | 10.0 | 10.0 | 1.0 | 7-10-10-1 |
6 | 7 | 30.0 | 30.0 | 2.0 | 7-30-30-2 |
7 | 7 | 10.0 | 10.0 | 0.1 | 7-10-10-0.1 |
8 | 9 | 50.0 | 50.0 | 0.1 | 9-50-50-0.1 |
9 | 5 | 50.0 | 50.0 | 0.1 | 5-50-50-0.1 |
10 | 9 | 10.0 | 10.0 | 0.1 | 9-10-10-0.1 |
11 | 5 | 10.0 | 10.0 | 0.1 | 5-10-10-0.1 |
12 | 5 | 50.0 | 50.0 | 2.0 | 5-50-50-2 |
13 | 9 | 50.0 | 50.0 | 2.0 | 9-50-50-2 |
14 | 9 | 10.0 | 10.0 | 2.0 | 9-10-10-2 |
15 | 5 | 10.0 | 10.0 | 2.0 | 5-10-10-2 |
16 | 7 | 50.0 | 50.0 | 2.0 | 7-50-50-2 |
17 | 11 | 50.0 | 50.0 | 2.0 | 11-50-50-2 |
18 | 11 | 10.0 | 10.0 | 2.0 | 11-10-10-2 |
19 | 5 | 0.0 | 50.0 | 2.0 | 5-0-50-2 |
20 | 5 | 1.7 | 50.0 | 2.0 | 5-1.7-50-2 |
21 | 5 | 5.7 | 50.0 | 2.0 | 5-5.7-50-2 |
22 | 5 | 9.9 | 50.0 | 2.0 | 5-9.9-50-2 |
23 | 5 | 14.0 | 50.0 | 2.0 | 5-14-50-2 |
24 | 5 | 25.4 | 50.0 | 2.0 | 5-25.4-50-2 |
25 | 5 | 50.0 | 50.0 | 2.0 | 5-50-50-2 |
26 | 5 | 0.0 | 10.0 | 0.1 | 5-0-10-0.1 |
27 | 9 | 0.0 | 10.0 | 2.0 | 9-0-10-2 |
28 | 5 | 0.0 | 50.0 | 2.0 | 5-0-50-2 |
29 | 9 | 0.0 | 50.0 | 0.1 | 9-0-50-0.1 |
30 | 5 | 0.0 | 10.0 | 2.0 | 5-0-10-2 |
31 | 9 | 0.0 | 10.0 | 0.1 | 9-0-10-0.1 |
32 | 5 | 0.0 | 50.0 | 0.1 | 5-0-50-0.1 |
33 | 9 | 0.0 | 50.0 | 2.0 | 9-0-50-2 |
34 | 7 | 0.0 | 30.0 | 1.0 | 7-0-30-1 |
References | k | y0 | R2 |
---|---|---|---|
5-30-30-1 | 3.3767 | −0.5401 | 0.9991 |
7-30-30-1 | 2.8270 | −0.5790 | 0.9922 |
9-30-30-1 | 2.4928 | −0.2927 | 0.9982 |
7-50-50-1 | 3.2751 | −0.3448 | 0.9776 |
7-10-10-1 | 1.6757 | −0.6081 | 0.9809 |
7-30-30-2 | 1.5874 | −0.6329 | 0.9927 |
7-10-10-0.1 | 3.7328 | −0.0958 | 0.9931 |
9-50-50-0.1 | 3.8001 | 0.1352 | 0.9977 |
5-50-50-0.1 | 6.0583 | 0.1574 | 0.9949 |
9-10-10-0.1 | 3.1596 | −0.2100 | 0.9964 |
5-10-10-0.1 | 4.2216 | −0.1662 | 0.9910 |
5-50-50-2 | 2.1372 | −1.2010 | 0.9799 |
9-50-50-2 | 1.9905 | −0.6159 | 0.9917 |
9-10-10-2 | 0.8535 | −0.4519 | 0.9910 |
5-10-10-2 | 0.8937 | −0.4385 | 0.9922 |
7-50-50-2 | 2.4245 | −0.8043 | 0.9871 |
11-50-50-2 | 2.0558 | −0.5636 | 0.9887 |
11-10-10-2 | 0.9568 | −0.4864 | 0.9861 |
5-0-50-2 | 0.2031 | 0.0376 | 0.9979 |
5-1.7-50-2 | 0.1825 | 0.0153 | 0.9985 |
5-5.7-50-2 | 0.2660 | −0.1215 | 0.9921 |
5-9.9-50-2 | 0.7408 | −0.3557 | 0.9994 |
5-14-50-2 | 0.9115 | −0.4370 | 0.9836 |
5-25.4-50-2 | 1.4326 | −0.6496 | 0.9931 |
5-50-50-2 | 2.1176 | −0.5234 | 0.9923 |
5-0-10-0.1 | 0.2753 | 0.0057 | 0.9978 |
9-0-10-2 | 0.1658 | −0.0176 | 0.9925 |
5-0-50-2 | 0.3706 | 0.0223 | 0.9940 |
9-0-50-0.1 | 0,8183 | −0.0120 | 0.9990 |
5-0-10-2 | 0.1516 | −0.0089 | 0.9968 |
9-0-10-0.1 | 0.2210 | 0.0130 | 0.9965 |
5-0-50-0.1 | 0.5439 | 0.0218 | 0.9946 |
9-0-50-2 | 0.3782 | −0.0208 | 0.9980 |
7-0-30-1 | 0.2525 | −0.0033 | 0.9943 |
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Buscio, V.; López-Grimau, V.; Vallés, B.; Pepió, M.; Gutiérrez-Bouzán, C. Modelling for the Efficient Effluent Dye Removal to Reuse Water and Salt. Processes 2022, 10, 2024. https://doi.org/10.3390/pr10102024
Buscio V, López-Grimau V, Vallés B, Pepió M, Gutiérrez-Bouzán C. Modelling for the Efficient Effluent Dye Removal to Reuse Water and Salt. Processes. 2022; 10(10):2024. https://doi.org/10.3390/pr10102024
Chicago/Turabian StyleBuscio, Valentina, Víctor López-Grimau, Bettina Vallés, Montserrat Pepió, and Carmen Gutiérrez-Bouzán. 2022. "Modelling for the Efficient Effluent Dye Removal to Reuse Water and Salt" Processes 10, no. 10: 2024. https://doi.org/10.3390/pr10102024