Abstract:Biosorption of manganese from its aqueous solution using yeast biomass Saccharomyces cerevisiae and fungal biomass Aspergillus niger was carried out. Manganese biosorption equilibration time for A. niger and S. cerevisiae were found to be 60 and 20 min, with uptakes of 19.34 and 18.95 mg/g, respectively. Biosorption increased with rise in pH, biomass, and manganese concentration. The biosorption equilibrium data fitted with the Freundlich isotherm model revealed that A. niger was a better biosorbent of mangane… Show more
“…In all the runs, the difference between the three replicates showed the errors were below than 5%. This modified method was adapted from previous studies investigating manganese biosorption by yeast and fungi (Parvathi et al, 2007). Mn 2þ stock solution was prepared using MnCl 2 .4H 2 O (Systerm: ChemAR Ò , Poland).…”
Section: Mn 2þ Biosorption Studymentioning
confidence: 99%
“…In addition, Mn 2þ also causes a bad taste and brownish water. Mn 2þ is released into the environment by industries such as those involved in the production of fertilizer, petrochemicals, electroplating, tanneries, metal processing, and mining industries (Hasan et al, 2011a;Parvathi et al, 2007). Regulations set by the Ministry of Health Malaysia require that the concentrations of manganese in raw water and treated water must be below 0.2 mg/L and 0.1 mg/L, respectively.…”
“…In all the runs, the difference between the three replicates showed the errors were below than 5%. This modified method was adapted from previous studies investigating manganese biosorption by yeast and fungi (Parvathi et al, 2007). Mn 2þ stock solution was prepared using MnCl 2 .4H 2 O (Systerm: ChemAR Ò , Poland).…”
Section: Mn 2þ Biosorption Studymentioning
confidence: 99%
“…In addition, Mn 2þ also causes a bad taste and brownish water. Mn 2þ is released into the environment by industries such as those involved in the production of fertilizer, petrochemicals, electroplating, tanneries, metal processing, and mining industries (Hasan et al, 2011a;Parvathi et al, 2007). Regulations set by the Ministry of Health Malaysia require that the concentrations of manganese in raw water and treated water must be below 0.2 mg/L and 0.1 mg/L, respectively.…”
“…Some industrial processes such as smelting, mining, metal forging, manufacturing of alkaline storage batteries, combustion of fossil fuel, electroplating, metal finishing, textile, ceramic, printing, pigments, fuels, photographic materials and explosive manufacturing result in the release of heavy metals in the environment (Salehizadeh and Shojaosadati 2003;Han et al 2006;Zaidi et al 2006;Parvathi et al 2006). Contamination of soils, groundwater, sediments, surface water and air with hazardous and toxic chemicals including heavy metals are serious problems, which have been faced by our world today (Ansari and Malik 2007).…”
Bioaccumulation and heavy metal resistance of Cd(2+), Cu(2+), Ni(2+), Zn(2+) and Mn(2+) ions by thermophilic Geobacillus toebii subsp. decanicus and Geobacillus thermoleovorans subsp. stromboliensis were investigated. The metal resistance from the most resistant to the most sensitive was found as Mn > Ni > Cu > Zn > Cd for both Geobacillus thermoleovorans subsp. stromboliensis and Geobacillus toebii subsp. decanicus. It was determined that the highest metal bioaccumulation was performed by Geobacillus toebii subsp. decanicus for Zn (36,496 μg/g dry weight cell), and the lowest metal bioaccumulation was performed by Geobacillus toebii subsp. decanicus for Ni (660.3 μg/g dry weight cell). Moreover, the dead cells were found to biosorbe more metal in their membranes compared to the live cells. In the presence of 7.32 mg/l Cd concentration, the levels of Cd absorbed in live and dead cell membranes were found as 17.44 and 46.2 mg/g membrane, respectively.
“…Beyond 50 min, the % biosorption is constant indicating the attainment of equilibrium conditions. The maximum biosorption of 79.45% (1.589 mg/g ) is attained for 50 min of agitation time with 10 g/L of 53 μm size biosorbent mixed in 50 mL of aqueous solution (C 0 =20 mg/L) [10,11].…”
Water pollution is one of the signs that humans have exceeded the limits and causing health problems for living beings on earth. The present paper comprises the optimization and biosorption of lead from aqueous solution using Albizia saman leaf powder as biosorbent. Single Step Optimization was considered for preliminary runs with the variables agitation time, biosorbent size, pH of the solution, initial concentration of the aqueous solution, dosage of biosorbent and temperature. The Central Composite Design (CCD) was used for final runs optimization using Response Surface Methodology (RSM). Results indicated that the optimum agitation time for biosorption of lead is 50 min. The increase in mass of biosorbent lead to increase in lead (pb) ion biosorption due to the increase in the number of active biosorption sites. Maximum percentage biosorption is observed at a pH of 6 and with particle size of 53 µm. Experimental data were better described by pseudosecond-order model. The adsorption isotherm could be well fitted by the Langmuir equation followed by Freundlich and Temkin. Over and all, Albizia Saman leaf powder can be used as an effective natural biosorbent for the economic treatment of aqueous solutions containing lead.
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