| Literature DB >> 29204472 |
Salar Hosseinipour Dizgah1, Kamran Taghavi2, Jalil Jaafari2,3, Esmaeil Roohbakhsh2, Seyed Davoud Ashrafi2,4.
Abstract
Data on this paper show the concentrations of COD, BOD5, TSS, K+, Ca2+, Na+, Cl-, [Formula: see text], [Formula: see text], Mn2+, Fe2+, Mg2+, Zn2+, Ni, Pb, Cu and Cd in the influent and effluent of wastewater, and also the nematode eggs, total and fecal coliform in effluents from wastewater treatment plant of Rasht, Guilan Province, in Iran. Measurements of pollutants in influent and effluent was measured according to standard methods (W.E. Federation and Association, A. P. H., 2005) [1]. Statistical analysis of the data was carried out using Special Package for Social Sciences (SPSS 16).Entities:
Keywords: Effluent; Influent; Rasht; Treatment; Wastewater
Year: 2017 PMID: 29204472 PMCID: PMC5709296 DOI: 10.1016/j.dib.2017.11.042
Source DB: PubMed Journal: Data Brief ISSN: 2352-3409
Mean and standard deviation of values of COD, BOD5, TSS, K+, Ca2+, Na+, Cl−, , , Mn2+, Fe2+, Mg2+, Zn2+, Ni, Pb, Cu, Cd, nematode eggs, total and fecal coliform in influent and effluent.
| Influent | Effluent | Influent | Effluent | ||||
|---|---|---|---|---|---|---|---|
| COD | mg/L | 239.7±47.1 | 46.1±7.3 | 287.8±24.7 | 52.6±4.1 | 60 | 200 |
| BOD5 | mg/L | 95.5±16.6 | 20.5±2.4 | 108.8±38.7 | 25±6.3 | 30 | 100 |
| pH | – | 7.6±0.3 | 7.8±0.3 | 7.8±0.3 | 8±0.2 | 6.5–8.5 | 6.5–8.4 |
| DO | mg/L | 1±0.2 | 2.6±0.5 | 1.3±0.3 | 2.9±0.7 | 2 | 2 |
| TSS | mg/L | 67.7±10.1 | 35.3±4.9 | 97.5±15.5 | 36.1±3 | 40 | 100 |
| EC | ds/m | 0.0799±0.008 | 0.0721±0.008 | 0.1150±0.01 | 0.1054±0.009 | – | 2.97 |
| K+ | mg/L | 34±2 | 26±2 | 32±4.5 | 24±3.6 | – | – |
| Ca2+ | mg/L | 210±15 | 130±6.2 | 174±4.5 | 120±2.6 | 75 | – |
| Na+ | mg/L | 90±6 | 75±2 | 102±4.5 | 83±4.3 | – | – |
| Cl− | mg /l | 124.2±2.1 | 53.2±0.9 | 266.2±18.5 | 230.7±7 | 600 | 600 |
| mg/L | 30±7.7 | 18.2±4.3 | 27.4±6 | 19±4.8 | 50 | – | |
| mg/L | 3.5±0.5 | 2.3±0.3 | 3.4±0.6 | 2.2±0.6 | 6 | – | |
| Mn2+ | mg/L | 0.32±0.01 | 0.29±0.01 | 0.48±0.05 | 0.31±0.04 | 1 | 1 |
| Fe2+ | mg/L | 0.63±0.02 | 0.46±0.01 | 0.71±0.07 | 0.58±0.05 | 2 | 2 |
| Mg2+ | mg/L | 6.8±0.1 | 6.7±0.1 | 9.3±0.8 | 9.2±0.8 | 100 | 100 |
| Zn2+ | mg/L | 0.4±0.01 | 0.12±0.1 | 0.39±0.04 | 0.18±0.03 | 2 | 2 |
| Ni | µg/L | 29±1 | 22±1 | 31±9 | 21±2 | 2000 | 2000 |
| Pb | µg/L | 9.48±0.001 | 8.24±0.001 | 12.22±0.2 | 10.44±0.1 | 1000 | 1000 |
| Cu | µg/L | 190±10 | 120±10 | 300±45 | 118±20 | 1000 | 200 |
| Cd | µg/L | 0.21±0.01 | 0.11±0.01 | 2.86±0.06 | 1.17±0.03 | 100 | 50 |
| Total | MPN/100 mL | – | 289±105 | – | 257±88 | 1000 | 1000 |
| Fecal | MPN/100 mL | – | 105±24 | – | 120±57 | 400 | 400 |
| Nematode eggs | Number / L | – | 0 | – | 0 | – | 1> |
Removal efficiency of COD, BOD5, TSS, K+, Ca2+, Na+, Cl−, , , Mn2+, Fe2+, Mg2+, Zn2+, Ni, Pb, Cu, Cd from wastewater treatment plant.
| COD | 80.7 | 81.7 |
| BOD5 | 78.5 | 77 |
| TSS | 47.8 | 62.9 |
| EC | 9.7 | 8.3 |
| K+ | 23.5 | 25 |
| Ca2+ | 38.1 | 31 |
| Na+ | 16.6 | 18.6 |
| Cl− | 57.1 | 13.3 |
| 39.3 | 30.6 | |
| 34.2 | 35.3 | |
| Mn2+ | 9.3 | 35.4 |
| Fe2+ | 26.9 | 18.3 |
| Mg2+ | 1.4 | 1 |
| Zn2+ | 70 | 53.3 |
| Ni | 24.1 | 32.2 |
| Pb | 13 | 14.5 |
| Cu | 36.8 | 60.6 |
| Cd | 47.6 | 59.1 |
Fig. 1Location of wastewater treatment plant.
| Environmental Engineering | |
| Pollutants in effluents | |
| Figure and table | |
| BOD measurement was carried out with a manometer instrument | |
| COD, | |
| TSS were measured by drying oven. | |
| Digital pH meter (Metrohm) was applied for pH analyzing. | |
| Electrochemical probes was used for DO measuring | |
| Metals and nonmetals measured with ICP and Flame Photometer | |
| Total and fecal coliform was measured with membrane filtration technique | |
| Raw, analyzed | |
| The data were obtained in two season, summer and winter, and the pH and DO measured in the place other samples from influent and effluent in polyethylene bottles were stored in a dark place at 4 °C temperature until the analysis. | |
| COD, BOD5, TSS, K+, Ca2+, Na+, Cl-, | |
| Rasht, Guilan Province, Iran | |
| The data are available within this paper. |