Printer Friendly

Biosorption of [Cd.sup.2+] from aqueous solutions by tolerant fungus Humicola sp.

INTRODUCTION

Cadmium (Cd) is extensively used in different industrial products such as various alloys, protective plating, stabilizer for plastic and other. Furthermore, the problem of Cd contamination occurs when aqueous effluents from many industrial processes that containing dissolved heavy metals without treatment are disposed. High concentration of cadmium may have an adverse impact on the environment and can be accumulated and transferred into the sequence of food chains. The bioremoval treatment process of metals has received increasing attention in term of "Biosorption" because of its many advantages such as the ability to treat large volumes of wastewater, rapid kinetics and high selectivity in the removal and recovery of specific heavy metals. Several biomass types have been studied as potential adsorbents for heavy metals, including fungi [1], bacteria [2], algae [3] and yeast [4]. Some literatures report that many kinds of filamentous fungi are capable of removing Cd during sewage treatment, such as Aspergillus fumigatus [5], Penicillium chrysogenum [6], Eupenicillium sp. [7], Rhizopus cohnii [8].

The Mae Tao creek is known as the most worrisome site of Cadmium contamination in Thailand. Cadmium has contaminated the area because it is extracted during the production of zinc. There are many mining activities that may influence the Cd contamination throughout the environment, for instance, drilling, material transfer and removal of mine tailings and drainage. Krissanakriangkrai et al. [9] found that the high levels of Cd in the sediment from the Mae Tao creek was 31.67 [+ or -] 0.61 mg [kg.sup.-1] soil. Cadmium contaminations lead to changing of microbial community which can be used as an indicator for Cadmium contamination in sediment. In previews study on cadmium tolerance fungi isolated from polluted sites in the Mae Tao creek showed that there were 5 aquatic fungal resistant including Humicola sp., Penicillium sp., Aspergillus sp. 1, Aspergillus sp. 2 and Alternaria sp. Altogether, Humicola sp. could grow in the presence of high concentration [Cd.sup.2+] and considered as high Cd resistance fungi [10].

There is no information on the use Humicola sp. for the biosorption of heavy metals. In this study was to investigate the removal of [Cd.sup.2+] from aqueous solution by mycelium biomass of Humicola sp. from Mae Tao creek in Mae Sot District, Tak Province, Thailand.

MATERIALS AND METHODS

Microorganism:

Humicola sp. was isolated from Mae Tao creek in Mae Sot District, Tak Province, Thailand. Fungal spores were obtained from a 5 days old culture grown on Potato Dextrose Agar (PDA) at 30 [+ or -] 2[degrees]C. The spores were collected in 0.01 % tween-80 solution.

Biomass Preparation:

Humicola sp. biomass were cultivated in Potato Dextrose Broth (PDB), using the shake flask method. Spore suspension (1 x [10.sup.8] spores) were cultivated in 250 ml erlenmeyer flask with 50 ml PDB at 30 [+ or -] 1 C with shaker at a speed of 150 rpm for 3 days. The culture grew as discrete pellicles. Harvesting of the biomass was done by filtering and washed biomass is hereafter called viable biomass, while the non-viable biomass was autoclaved at 121[degrees]C for 20 minutes and then harvested by filtering through a membrane filter and dried at 80 [degrees]C in an oven for 12 hours. This was then ground, using a blender and sieved to pass through a 100 mesh sieve to obtain uniform particle size. Pellet viable biomass and non-viable biomass were used in the [Cd.sup.2+] uptake studies.

Batch Isotherm Experiments:

Biomass were put in contact with cadmium nitrate solution in concentrations that varies from 0 to 150 mg [1.sup.-] 1. Cd adsorption in aqueous solution before and after contact with the biomass was calculated using the following equation:

_ (C - Cf) V q W

Where: q is the metal uptake (mg Cd [g.sup.-1] dry wt.), Ci and Cf are the initial and final [Cd.sup.2+] concentrations in the supernatant, respectively (mg [l.sup.-1]), V is the volume of the Cd concentration (ml), and M is the dry weight of the biomass added (g). This definition of the uptake permits the direct calculation of the amount of metal taken up from the solution after contacting with the sorbent. The resulting values of Cf / q were plotted against Ci to obtain a Langmuir plot typical of the sorption behavior [11].

Effect of temperature, pH and contact time on Cd removal by fungus:

In order to evaluate the effect of temperature, pH and contact time on the [Cd.sup.2+] uptake, the experiment was conducted in the same manner, except the temperature of Cadmium solution was changed to 30, 40, 50, 60 and 70[degrees]C. The pH of the solution was prepared to be in the range between 3.0 and 9.0 before mixing biomass. The pH was adjusted to the required value with 0.1M NaOH or 0.1M HNO3. The period of contact time was studied up to 180 minutes by using procedure described earlier, samples were collected every 30 minutes (30, 60, 90, 120, and 180 minutes, respectively)

Cd desorption experiments:

The 0.1M HNO3 solution was used to elute [Cd.sup.2+] from both biomass. Following the [Cd.sup.2+] sorption experiments, the Cd-loaded biomass was prepared by centrifugation, washed and returned to 25 ml of the effluent 0.1 M HNO3 for 30 minutes on a rotary shaker (125 rpm). Metal concentrations were determined after separating the biomass from eluting agent by filtration.

Atomic absorption analysis:

The samples of [Cd.sup.2+] was measured by atomic absorption spectrophotometer (Variance spectra model AA- 220 FS) by using the Flameless method of graphite system.

Statistical analysis:

All the experiments were triplicated. Mean values were used in the analysis of data by using the analysis of variance (one--way ANOVA) and Post Hoc. Duncan test (p < 0.05).

RESULTS AND DISCUSSIONS

Uptake Mechanism of Cd by Viable and Non-viable biomass:

The removal ability of Cd in Humicola sp. was found to be in the same pattern for both biomass as increasing Cd concentration, however viable biomass reduced [Cd.sup.2+] removal more than non-viable biomass. At Cd concentration of 100 mg[l.sup.-1], viable and non-viable biomass removed Cd of 61.77 [+ or -] 3.25 mg Cd [g.sup.-1] dry wt. and 47.61 [+ or -] 2.24 mg Cd [g.sup.-1] dry wt., respectively (Table 1). This value is better than many of fungal biomasses such as, Rhizopus cohnii [8], Rhizopus nigricans[12], Aspergillus fumigatus [5] and Aspergillus niger [13] but lower than Penicillium chrysogenum as observed by Xu and et al. [6].

For a Cd uptake, mean concentrations followed by the same letter are not significantly different (p < 0.05)

The equilibrium isotherm of Cd adsorption by the Humicola sp. biomass can be described by Langmuir isotherm. Figure 1 shows the isothermal adsorption equilibrium of Cd at 30 [+ or -] 1[degrees]C and pH 7 on Humicola sp. mycelial. These isotherms follow the typical Langmuir adsorption pattern as shown by the linear transformation. The linearized form of Langmuir equation is represented by the following expression:

Ceq/q = Ceq/qmax + 1/qmaxb

Where Ceq is the equilibrium solution concentration (mg [l.sup.-1]), q max is the amount adsorbed at equilibrium (mg [g.sup.-1]), the Langmuir constants qmax and b are related to adsorption capacity and energy of adsorption, respectively [14]. The linear plot between Ceq/q with Ceq shows that investigated metal ions were adsorped by Humicola sp.. As compared in Table 2, the viable biomass has a greater capacity (qmax) and binding constant (.b) than non-viable biomass for Cd adsorption.

Effect of contact time on Cd removal:

Viable biomass of Humicola sp. could also remove Cd in solution and reached the equilibrium (p < 0.05) within 150 minutes, while the rate of biosorption by non-viable biomass was faster and contributed significantly (p < 0.05) to equilibrium uptake 97.91 % recovery being achieved within 120 minutes (figure 2a). Many researchers reported that the rate of absorption was observed in 2 phases, an initial phase of faster absorption then followed by the phase of slower adsorption. Initial faster uptake might be due to the availability of abundant metal species and empty metal binding sites of microbes. Slower phase might be due to saturation of metal binding site [15].

Effect of pH on Cd removal:

The pH level is one of the most important parameters on fungal biosorption of [Cd.sup.2+] ions from aqueous solutions by Humicola sp.. The result shows that Cd adsorption was also very low at pH 3 and increased to pH 6 in viable biomass and pH 5 in non-viable biomass then reached the equilibrium after that (p < 0.05) (Figure 2b). The low Cd biosorption at pH less than 4 has been suggested to the competition among metal ions from hydronium ions for the available biosorption sites. However, it is known that many heavy metals including Cadmium can undergo hydrolysis at different pH values, and the predominant form of the hydroxyl species depends on the pH value [16]. The predominant form of cadmium is [Cd.sup.2+] ion between pH 4 and 6 whereas CdO[H.sup.+] is predominant between pH 7 and 9. It is likely that viable biomass preferentially adsorb monovalent CdO[H.sup.+] as same as divalent [Cd.sup.2+].

Effect of temperature on Cd removal:

The maximum value of Cd removal occurred at room temperature (30[degrees]C) in viable and non-viable biomass was 62.18 [+ or -] 1.49 mg [l.sup.-1] dry wt. and 48.05 [+ or -] 0.78 mg [l.sup.-1] dry wt., respectively. The Cd removal in both biomass were decreased after 40[degrees]C (figure 2c). The temperature higher than 40[degrees]C caused a change in the texture of the viable biomass and thus reduced its sorption capacity. Biomass contains more than one type of sites for metal binding, thus the effect of temperature on each site is different and contributes to overall metal uptake. The effect of temperature on biosorption also depends on the heat of sorption [17].

Cadmium desorption:

Desorption experiments indicate that the desorption efficiency with 0.1 M HNO3 solution reaches 78.95% and 86.77% in viable and non-viable biomass, respectively. The decrease in lead uptake by acid desorbent might be due to the increase of the concentrations of competing hydronium ions. It is also possible that the physical structure of the biomass becomes damaged by this acid [18].

Summary:

The results of this research show that visible biomass of Humicola sp. biomass from Mae Tao creek sediment is great quantities for the removal of [Cd.sup.2+] from aqueous solution. The adsorption process can be described by Langmuir equation. Adsorption of [Cd.sup.2+] is fairly rapid in first 30 minutes and increased slowly to reach equilibrium in 150 minutes for viable biomass and 120 minutes for non-viable biomass. The temperature and pH are affected this process. For the desorption, 0.1 M HN[O.sub.3] showed in the highest efficiency to elute [Cd.sup.2+] from the biomass.

ARTICLE INFO

Article history:

Received 4 September 2014

Received in revised form 24 November 2014

Accepted 8 December 2014

Available online 16 December 2014

ACKNOWLEDGEMENTS

Financial support from Nakhon Sawan Rajabhat University, Thailand are gratefully acknowledged.

REFERENCES

[1] Alluri, H.K., S.R. Ronda, V.S. Settalluri, J. Singh, B. Suryanarayana and P. Venkateshwar, 2007. Review Biosorption: An eco-friendly alternative for heavy metal removal, African Journal Biotechnology, 6(25): 2924-2931.

[2] Matis, K.S. and A.l. Zouboulis, 1994. Waste microbial biomass for cadmium ion removal: application of flotation for downstream separation. Bioresoure Technology, 49(3): 253-259.

[3] Kuyucak, N. and B. Volosky, 1989. Dosorption of cobalt--laden algal biosorbent. Biotechnology and Bioengineering, 33(7): 815-822.

[4] Anaemene, I.A., 2012. The use of Candida sp. in the biosorption of heavy metals from industrial effluent. European Journal of Experimental Biology, 2(3).488-484 :

[5] Al-Garni, S.M., K.M. Ghanem and A.S. Bahobail, 2009. Biosorption characteristics of Aspergillus fumigatus in removal of cadmium from an aqueous solution. African Journal of Biotechnology, 8(17): 4163-4172.

[6] Xu, X., L. Xia, Q. Huang, J. Gu and W. Chen, 2012. Biosorption of cadmium by a metal-resistant filamentous fungus isolated from chicken manure compost. Environmental Technology, 33(13-15): 1661-1670.

[7] Levinskaite, L., A. Smirnov, B. Luksiene, R. Druteikiene, V. Remeikis and D. Baltrunas, 2009. Pu(IV) and Fe(III) accumulation ability of heavy metal-tolerant soil fungi, Nukleonika, 54(4): 285-290.

[8] Jin-ming, L., X. Xiao and L. Sheng-lian, 2010. Biosorption of cadmium(II) from aqueous solutions by industrial fungus Rhizopus cohnii. Transactions of Nonferrous Metals Society of China, 20: 1104-1111.

[9] Krissanakriangkrai, O., W. Supanpaiboon, S. Juwa, S. Chaiwong, W. Swaddiwudhipong and K.A. Anderson, 2009. Bioavailable Cadmium in Water, Sediment, and Fish, in a Highly Contaminated Area on the Thai-Myanmay Border. Thammasat International Journal of Science and Technology, 14(4): 60-68.

[10] Netpae, T., 2014. Cadmium biofilter by fungus from Maetaw brook sediment in Maesord distric, Tak province.Rajabhat Nakhon Sawan University, Nakhon Sawan Province, Thailand. (in Thai).

[11] Langmuir, I., 1916. The constitution and fundamental properties of solids and liquids, Part. I: Solids. Journal of the American Chemical Society, 38: 2221-2295.

[12] Holan, Z.R. and B. Volesky, 1995. Accumulation of cadmium, lead and nickel by fungal and wood biosorbents. Applied Bioch Biotech, 53: 133-146.

[13] Barros Junior, L.M., G.R. Macedo, M.M.L. Duarte, E.P. Silva and A.K.C.L. Lobato, 2003. Biosorption of cadmium using the fungus Aspergillus niger. Brazilian Journal of Chemical Engineering, 20(3): 229-39.

[14] Ahalya Ahalya, N., R.D. Kanamadi and T.V. Ramachandra, 2006. Biosorption of Iron (III) from aqueous solution using the husk of Cicer arientinum. Indian Journal of Chemical Technology, 13: 122-127.

[15] Mathivanan, K. and R. Rajaram, 2014. Tolerance and biosorption of cadmium (II) ions by highly cadmium resistant bacteria isolate from industrially polluted estuatine environment. Indian Journal of Geo-Marine Sciences, 43(4): 580-588.

[16] Netpae, T., 2012. Removal of lead from aqueous solutions by Aspergillus niger from artificial vinegar factory. Electronic Journal of Biology, 8(1): 7-10.

[17] Qaiser, S. and A.R. Saleemi, 2007. Heavy metal uptake by agro based waste materials. Electronic Journal of Biotechnology, 10(3): 409-416.

[18] Pimpa, W. and T. Netpae, 2004. Use of pelletted biomass of Aspergillus oryzae for lead removal. Thai Environmental Engineering Journal, 18(1): 21-28.

(1) Tinnapan Netpae, (2) Sawitree Suckley, (3) Chitchol Phalaraksh

(1) Environmental Science Program, Faculty of Science and Technology, Nakhon Sawan Rajabhat University, Thailand.

(2) Chemistry Program, Faculty of Science and Technology, Nakhon Sawan Rajabhat University, Thailand.

(3) Department of Biology, Faculty of Science, Chiang Mai University, Thailand.

Corresponding Author: Tinnapan Netpae, Environmental Science Program, Faculty of Science and Technology, Nakhon Sawan Rajabhat University, Thailand.

E-mail: tinnapan_net@yahoo.com

Table 1: Cadmium uptake on viable and non viable biomass of Humicola sp.

Cd concentration         Cadmium uptake (mg Cd [g.sup.-1] dry wt.)
(mg [l.sup.-1])
                       Viable biomass          Non-viable biomass

0                  0.00 [+ or -] 0.00 (a)    0.00 [+ or -] 0.00 (a)
1                  0.88 [+ or -] 0.07 (a)    0.86 [+ or -] 0.03 (a)
5                  4.67 [+ or -] 0.29 (b)    5.08 [+ or -] 0.63 (b)
10                 8.79 [+ or -] 0.64 (c)    10.31 [+ or -] 0.64 (c)
25                 20.89 [+ or -] 1.98 (d)   26.02 [+ or -] 2.07 (d)
50                 33.36 [+ or -] 1.95 (e)   39.04 [+ or -] 2.54 (e)
100                61.77 [+ or -] 3.25 (f)   47.61 [+ or -] 2.24 (f)
150                60.84 [+ or -] 1.25 (f)   47.17 [+ or -] 2.40 (f)

Table 2: Comparison of the Langmuir constants for Cd adsorption by
Humicola sp. biomass.

                        qmax (mg Cd          b (mg
                     [g.sup.-1] dry wt.)   [l.sup.-1])

Viable biomass              67.61             9.78
Non-viable biomass          48.71             2.77

Table 2: Desorption of [Cd.sup.2+] on biomass of Humicola sp. used
with 0.1 M HN[O.sub.3].

Biomass                   Cadmium uptake             Removal
                     (mg Cd [g.sup.-1] dry wt.)   efficiency (%)

Viable biomass          48.77 [+ or -] 8.35           78.95
Non-viable biomass      41.31 [+ or -] 4.94           86.77
COPYRIGHT 2014 American-Eurasian Network for Scientific Information
No portion of this article can be reproduced without the express written permission from the copyright holder.
Copyright 2014 Gale, Cengage Learning. All rights reserved.

Article Details
Printer friendly Cite/link Email Feedback
Author:Netpae, Tinnapan; Suckley, Sawitree; Phalaraksh, Chitchol
Publication:Advances in Environmental Biology
Article Type:Report
Date:Oct 1, 2014
Words:2696
Previous Article:The study of bioaccumulation of heavy metals (Zn, Cu, Cd, Pb) in (Metapenaeus affinis) and (Litopenaeus vannamei) in khouzestan province, the north...
Next Article:Acid effect on ion changes from haemolymph of Orthetrum sabina nymph.
Topics:

Terms of use | Privacy policy | Copyright © 2019 Farlex, Inc. | Feedback | For webmasters