SORPTION OF Pb(II), Cu(II) AND Cd(II) BY BIOMASS OF THE DIFFERENT ACTIVATED SLUDGE

AbstractBiomass of digested sludge and resting sludge can be easily applied as a cheap bio-adsorbent for heavy metal ions such as Pb2+, Cu2+ and Cd2+. Langmuir model was found to fit the experimental adsorption and desorption data of the heavy metal on to the biomass of sludge. That has the competit...

Mô tả đầy đủ

Đã lưu trong:

Chi tiết về thư mục
Những tác giả chính:	Nguyễn, Đình Trung, Trương, Đông Phương, Ning, Ping
Định dạng:	Journal article
Ngôn ngữ:	English
Được phát hành:	2022
Những chủ đề:	Activated sludge; Bio-sorption; Cd2+; Cu2+; Pb2+
Truy cập trực tuyến:	http://scholar.dlu.edu.vn/handle/123456789/1205 https://doi.org/10.22144/ctu.jen.2016.039
Các nhãn:	Thêm thẻ Không có thẻ, Là người đầu tiên thẻ bản ghi này!

Thư viện lưu trữ:	Thư viện Trường Đại học Đà Lạt

id	oai:scholar.dlu.edu.vn:123456789-1205
record_format	dspace
institution	Thư viện Trường Đại học Đà Lạt
collection	Thư viện số
language	English
topic	Activated sludge; Bio-sorption; Cd2+; Cu2+; Pb2+
spellingShingle	Activated sludge; Bio-sorption; Cd2+; Cu2+; Pb2+ Nguyễn, Đình Trung Trương, Đông Phương Ning, Ping SORPTION OF Pb(II), Cu(II) AND Cd(II) BY BIOMASS OF THE DIFFERENT ACTIVATED SLUDGE
description	AbstractBiomass of digested sludge and resting sludge can be easily applied as a cheap bio-adsorbent for heavy metal ions such as Pb2+, Cu2+ and Cd2+. Langmuir model was found to fit the experimental adsorption and desorption data of the heavy metal on to the biomass of sludge. That has the competition uptake between the difference metal with another when the adsorption system has the di-metal, and tri-metal combination. The maximal adsorption capacity of resting sludge was 0.517 mM Pb2+/g; 0.552 mM Cu2+/g; 0.389 mM Cd2+/g, and the maximal adsorption capacity of the digested sludge was 0.478 mM Pb2+/g, 0.43 mM Cu2+/g and 0.549 mM Cd2+/g. In the absorption system, it was found that, di-metal combine such as (Cu2+ - Cd2+), (Pb2+ Cd2+), and (Cu2+ - Pb2+), the metal uptake Cu2+ ≈ 3Cd2+, Pb2+ > 3Cd2+, and Cu2+ ≈ Pb2+ respectively. When tri-metal Cu2+ - Cd2+ - Pb2+ combines the number of complex formation varies in the following order: Pb2+ > Cu2+ > Cd2+. Extracellular polymeric substances (EPS) were extracted by sonication method. Humic substances were greater than protein and polysaccharide for digested sludge, for resting sludge the protein is greater than humic. The ratio protein/polysaccharide varies from 1.25 to 2.7, this ratio is highest for resting sludge. Affinity absorption of Cu2+ and Pb2+ was higher than Cd2+, that have the competition metal uptake with functional groups such as hydroxyl, carbonyl, amide on the biomass surface of the sludge.
format	Journal article
author	Nguyễn, Đình Trung Trương, Đông Phương Ning, Ping
author_facet	Nguyễn, Đình Trung Trương, Đông Phương Ning, Ping
author_sort	Nguyễn, Đình Trung
title	SORPTION OF Pb(II), Cu(II) AND Cd(II) BY BIOMASS OF THE DIFFERENT ACTIVATED SLUDGE
title_short	SORPTION OF Pb(II), Cu(II) AND Cd(II) BY BIOMASS OF THE DIFFERENT ACTIVATED SLUDGE
title_full	SORPTION OF Pb(II), Cu(II) AND Cd(II) BY BIOMASS OF THE DIFFERENT ACTIVATED SLUDGE
title_fullStr	SORPTION OF Pb(II), Cu(II) AND Cd(II) BY BIOMASS OF THE DIFFERENT ACTIVATED SLUDGE
title_full_unstemmed	SORPTION OF Pb(II), Cu(II) AND Cd(II) BY BIOMASS OF THE DIFFERENT ACTIVATED SLUDGE
title_sort	sorption of pb(ii), cu(ii) and cd(ii) by biomass of the different activated sludge
publishDate	2022
url	http://scholar.dlu.edu.vn/handle/123456789/1205 https://doi.org/10.22144/ctu.jen.2016.039
_version_	1768305966782087168
spelling	oai:scholar.dlu.edu.vn:123456789-12052022-10-07T09:34:36Z SORPTION OF Pb(II), Cu(II) AND Cd(II) BY BIOMASS OF THE DIFFERENT ACTIVATED SLUDGE Nguyễn, Đình Trung Trương, Đông Phương Ning, Ping Activated sludge; Bio-sorption; Cd2+; Cu2+; Pb2+ AbstractBiomass of digested sludge and resting sludge can be easily applied as a cheap bio-adsorbent for heavy metal ions such as Pb2+, Cu2+ and Cd2+. Langmuir model was found to fit the experimental adsorption and desorption data of the heavy metal on to the biomass of sludge. That has the competition uptake between the difference metal with another when the adsorption system has the di-metal, and tri-metal combination. The maximal adsorption capacity of resting sludge was 0.517 mM Pb2+/g; 0.552 mM Cu2+/g; 0.389 mM Cd2+/g, and the maximal adsorption capacity of the digested sludge was 0.478 mM Pb2+/g, 0.43 mM Cu2+/g and 0.549 mM Cd2+/g. In the absorption system, it was found that, di-metal combine such as (Cu2+ - Cd2+), (Pb2+ Cd2+), and (Cu2+ - Pb2+), the metal uptake Cu2+ ≈ 3Cd2+, Pb2+ > 3Cd2+, and Cu2+ ≈ Pb2+ respectively. When tri-metal Cu2+ - Cd2+ - Pb2+ combines the number of complex formation varies in the following order: Pb2+ > Cu2+ > Cd2+. Extracellular polymeric substances (EPS) were extracted by sonication method. Humic substances were greater than protein and polysaccharide for digested sludge, for resting sludge the protein is greater than humic. The ratio protein/polysaccharide varies from 1.25 to 2.7, this ratio is highest for resting sludge. Affinity absorption of Cu2+ and Pb2+ was higher than Cd2+, that have the competition metal uptake with functional groups such as hydroxyl, carbonyl, amide on the biomass surface of the sludge. 4 20-27 2022-10-07T09:34:32Z 2022-10-07T09:34:32Z 2016-11-30 Journal article Bài báo đăng trên tạp chí trong nước (có ISSN), bao gồm book chapter http://scholar.dlu.edu.vn/handle/123456789/1205 https://doi.org/10.22144/ctu.jen.2016.039 en Can Tho University Journal of Science 2615-9422 APHA. 1992. Standard methods for the examination of water and wastewater, 18th edn. American Public Health Association, Baltimore, Md. Bagby, M.M., Sherrard, J.H., 1981. Combined eﬀects of Cd and Ni on the activated sludge process. J. Wat. Pollut. Control. Fed. 53: 1609–1619. Box, J.D., 1983. Investigation on the Folin - Ciocalteau phenol reagent for determination of polyphenolic substances in natural waters. Water Res. 17: 511– 525. Brown, M.J., Lester, J.N., 1982. Role of bacterial extra-cellular polymers in metal uptake in pure bacterial culture and activated sludge: eﬀect of metal concen-tration. Water Res. 16: 1539–1548. Chua, H., Yu, P.H.F., Sin, S.N., Cheung, M.W.L., 1999. Sub-lethal eﬀects of heavy metals on activated sludge microorganisms. Chemosphere. 39: 2681–2692. Dubois, M., Giles, K.A., Hamilton, J.K, Rebers, P.A., Smith, F., 1956. Anal. Chem. 28: 350-356. Erikson, L., Steen, I., Tendaj, M., 1992. Evaluation of sludge properties at an activated sludge plant. Water Sci. Technol. 25: 251–265. Frelund, B., Palmgren, R., Keiding, K., Nielsen, P.H., 1995. Extraction of activated sludge exopolymers by a cation exchange resin. Water Res (in press). Frolund, B., Gribe, T., Nielsen, PH., 1995. Enzymatic activity in the activated sludge floc matrix. Appl Microbiol Biotechnol (in press). Fukushi, K., Kato, S., Antsuki, T., Omura, T., 2001. Isolation of copper binding proteins from activated sludge culture. Water Sci. Technol. 44: 453–459. Gökçay, C.F., Yetiş, Ü., 1991. Eﬀect of chromium (VI) on activated sludge. Wat. Res. 25: 65–73. Goodwin, J.A.S., Forster, C.F., 1989. A further examination into the composition of activated sludge surfaces in relation to their settlement characteristics. Water Res. 20: 1427–1528. Guibaud, G., Tixier, N., Bouju, A., Baudu, M., 2003. Relation between extracellular polymers composition and its ability to complex Cd, Cu and Pb. Chemosphere. 52: 1701–1710. Guibaud, G., Baudu, M., Dollet, P., Condat, M.L., Dagot, C., 1999. Rôle des polymèeres extracellulaires dans l’adsorption du cadmium par les boues active’es. Environ. Technol. 20: 1045–1054. Lee, M.Y., Shin, H.J., Lee, S.H., Park, J.M., Yang, J.W., 1998. Removal of lead in a ﬁxed-bed column packed with activated carbon and crab shell. Separation Science and Technology. 33: 1043–1056. Li, J.Y., Shukla, S.S., Dorris, K.L., Shukla, A., Margrave, J.L., 2003. Adsorption of chromium from aqueous solutions by maple sawdust. Journal of Hazardous Materials. 100 (1–3): 53–56. Lowry, O.H., Rosebrough, N.J., Farr, A.L., Randall, R.J., 1951. Protein measurement with the Folin phenol reagent. J Biol Chem. 193:265-275. Patterson, J.W., 1975. Wastewater Treatment Technology. Ann Arbor Science, New York. Qodah, Al.Z., 2006. Biosorption of heavy metal ions from aqueous solutions by activated sludge. Desalination. 196: 164–176. Sobeck, D.C., Higgins, M.J., 2002. Examination of three theories for mechanisms of cation-induced bioﬂocculation. Water Res. 36: 527–538. Tsai, W.T., Lai, C.W., Hsien, K.J., 2004. Adsorption kinetics of herbicide paraquat from aqueous solution onto activated bleaching earth. Chemosphere. 55: 829–837. Urbain, V., Manem, J., Block, J.C., 1993. Bioﬂocculation in activated sludge: an analytical approach. Water Res. 27: 829–838. Varrault, G., Bermond, A., 2002. Trace metal sorption ability of insolubilized humic acids. Environ. Technol. 22: 421–428. Xuejiang, W., Ling, C., Siqing, X., Jianfu, Z., Chovelon, J-M., Renault, N.J., 2006. Biosorption of Cu(II) and Pb(II) from aqueous solutions by dried activated sludge, Minerals Engineering. 19: 968–971. Yetiş, Ü., Gökçay, C.F., 1989. Eﬀect of nickel(II) on activated sludge. Wat. Res. 23: 1003–1007.

SORPTION OF Pb(II), Cu(II) AND Cd(II) BY BIOMASS OF THE DIFFERENT ACTIVATED SLUDGE

Những quyển sách tương tự