Comparison between sequential and single extraction procedures for metal speciation in fresh and dried Sedum Plumbizincicola

Zu-wei Song , Zhao-ping Zhong , Dao-xu Zhong , Long-hua Wu , Yong-ming Luo

Journal of Central South University ›› 2015, Vol. 22 ›› Issue (2) : 487 -494.

PDF
Journal of Central South University ›› 2015, Vol. 22 ›› Issue (2) : 487 -494. DOI: 10.1007/s11771-015-2547-1
Article

Comparison between sequential and single extraction procedures for metal speciation in fresh and dried Sedum Plumbizincicola

Author information +
History +
PDF

Abstract

Sequential and single extraction procedures were applied to both fresh and dried Sedum Plumbizincicola leaves and stems. The extractants, different from those of soil, sediment or sewage sludge metal fractions, were water, 80% (v/v) ethanol, 1 mol/L NaCl, 2% HAc and 0.6 mol/L HCl. Zn, Cd and Cu in the extracts and samples were measured by flame atomic adsorption spectrometry. In sequential extraction procedures, water soluble form and ethanol soluble form are the main fractions for Zn, while water soluble form and NaCl soluble form for Cd, and comparatively uniform distribution for Cu with the residue form most and HCl soluble form second. Single extraction procedures are used to compare the extraction efficiencies of the five reagents to screen appropriate extractants and operating conditions for liquid extraction to deal with large amount of harvested metal-contained biomass, which will pose a threat to the environment if treated improperly. The sequences of extraction efficiencies are HCl>NaCl≈HAc>Water≈Ethanol for Zn and HCl≈NaCl≈HAc>Water>Ethanol for Cd. As for Cu, all the five extractants cannot effectively extract Cu, but HCl achieves a higher efficiency (>70% in fresh samples, and 45%–60% in dried samples). Besides, extraction efficiencies for most extractants in fresh samples are higher than those in dried samples, and extraction efficiencies of stems and leaves for the five extractants are close. The two extraction procedures can obtain high degree of accuracy with the relative standard deviation (RSD) lower than 10%, and metal recoveries are controlled between 80%–120% with most of 90%–110%.

Keywords

Sedum Plumbizincicola / liquid extraction / biomass disposal / heavy metals

Cite this article

Download citation ▾
Zu-wei Song, Zhao-ping Zhong, Dao-xu Zhong, Long-hua Wu, Yong-ming Luo. Comparison between sequential and single extraction procedures for metal speciation in fresh and dried Sedum Plumbizincicola. Journal of Central South University, 2015, 22(2): 487-494 DOI:10.1007/s11771-015-2547-1

登录浏览全文

4963

注册一个新账户 忘记密码

References

[1]

JadiaC D, FulekarM H. Phytoremediation of heavy metals: Recent techniques [J]. African Journal of Biotechnology, 2009, 8(6): 921-928

[2]

PadmavathiammaP K, LiL Y. Phytoremediation technology: Hyper-accumulation metals in plants [J]. Water, Air, and Soil Pollution, 2007, 184(1/2/3/4): 105-126

[3]

GhoshM, SinghS P. A review on phytoremediation of heavy metals and utilization of its by products [J]. As J Energy Env, 2005, 6(4): 214-231

[4]

HetlandM D, GallagherJ R, DalyD J, HassettD J, HeebinkL VProcessing of plants used to phytoremediate lead-contaminated sites [M], 2001, San Diego, California, Battelle Press: 129-136

[5]

BlaylockM J, HuangJ WPhytoextraction of metals [M], 2000, New York, John Wiley and Sons: 53-70

[6]

BridgwaterA V, MeierD, RadleinD. An overview of fast pyrolysis of biomass [J]. Org Geochem, 1999, 30: 1479-1493

[7]

KoppoluaL, AgbloverF A, ClementsL D. Pyrolysis as a technique for separating heavy metals from hyperaccumulators. Part II: Lab-scale pyrolysis of synthetic hyperaccumulator biomass [J]. Biomass and Bioenergy, 2003, 25: 651-663

[8]

AkkajitP, DesutterT, TongcumpouC. Fractionation of Cd and Zn in Cd-contaminated soils amended by sugarcane waste products from an ethanol production plant [J]. Journal of Soils and Sediments, 2013, 13(6): 1057-1068

[9]

RodríguezL, RuizE, Alonso-AzcárateJ, RincónJ. Heavy metal distribution and chemical speciation in tailings and soils around a Pb-Zn mine in Spain [J]. Journal of Environmental Management, 2009, 90(2): 1106-1116

[10]

JamaliM K, KaziT G, ArainM B, AfridiH I, JalbaniN, KandhroG A, BaigJ A. Speciation of heavy metals in untreated sewage sludge by using microwave assisted sequential extraction procedure [J]. Journal of hazardous materials, 2009, 163(2): 1157-1164

[11]

NematiK, BakarN K A, AbasM R, SobhanzadehE. Speciation of heavy metals by modified BCR sequential extraction procedure in different depths of sediments from Sungai Buloh, Selangor, Malaysia [J]. Journal of Hazardous Materials, 2011, 192(1): 402-410

[12]

ReidM K, SpencerK L, ShotboltL. An appraisal of microwave-assisted Tessier and BCR sequential extraction methods for the analysis of metals in sediments and soils [J]. Journal of Soils and Sediments, 2011, 11(3): 518-528

[13]

AlborésA F, CidB P, GómezE F, LópezE F. Comparison between sequential extraction procedures and single extractions for metal partitioning in sewage sludge samples [J]. Analyst, 2000, 125(7): 1353-1357

[14]

WuL H, ZhouS B, BiD, GuoX H, QinW H, WangH, WangC J, LuoY M. Sedum plumbizincicola, a new species of the crassulaceae from Zhejiang, China [J]. Soils, 2006, 38(5): 632-633

[15]

WuL H, ZhongD X, DuY Z, LuS Y, FuD Q, LiZ, LiX D, ChiY, LuoY M, YanJ H. Emission and control characteristics for incineration of Sedum plumbizincicola biomass in a laboratory-scale entrained flow tube furnace [J]. International Journal of Phytoremediation, 2013, 15(3): 219-231

[16]

XuJ L, BaoZ P, YangJ R, LiuH, SongW C. Chemical forms of Pb, Cd and Cu in crops [J]. Chin J Appl Ecol, 1991, 2(3): 244-248

[17]

LiS L, LiN, XuL S, TanW N, ZhouS B, WuL H, LuoY M. Characters of Zn and Cd Accumulation and distribution in leaves of sedum plumbiziucicola at different ages [J]. Soils, 2010, 42(3): 446-452

[18]

WuH M, LiF L, MouH Q, ZhangH. Analysis of heavy metal fractions in plants by two steps sequential extraction procedure [J]. Environmental Science & Technology, 2012, 35(7): 133-137

[19]

TianS-keMechanisms behind detoxification of heavy metals (Zn/Cd/Pb) in the hyperaccumulator Sedum alfredii Hance [D], 2010, Hangzhou, Zhejiang University

[20]

MaJ F, UenoD, ZhaoF J, McgrathS P. Subcellular localisation of Cd and Zn in the leaves of a Cd-hyperaccumulating ecotype of Thlaspi caerulescens [J]. Planta, 2005, 220: 731-736

[21]

BraudeG L, NashA M, WolfW J, CarrR L, ChaneyR L. Cadmium and lead content of soybean products [J]. Journal of Food Science, 1980, 45(5): 1187-1189

[22]

YuH, YangZ Y, YangZ J, XiangZ X. Chemical forms and subcellular and molecular distribution of Cd in two Cd-accumulation rice genotypes [J]. Chin J Appl Ecol, 2008, 19(10): 2221-2226

[23]

LiuQ, LiW Q, WangX Y, RenX E, ChuZ H. The absorption of copper in spinach and rape and its chemical bound forms [J]. Acta Agriculture Universitatis Jiangxiensis, 2005, 27(1): 150-153

[24]

HallJ L. Cellular mechanisms for heavy metal detoxification and tolerance [J]. Journal of Experimental Botany, 2002, 53(366): 1-11

[25]

YangX, FengY, HeZ L, StoffellaP J. Molecular mechanisms of heavy metal hyperaccumulation and phytoremediation [J]. Journal of Trace Elements in Medicine and Biology, 2005, 18: 339-353

[26]

VerbruggenN, HermansC, SchatH. Molecular mechanisms of metal hyperaccumulation in plants [J]. New Phytologist, 2009, 181: 759-776

[27]

WangJ-f, ZhuQ-q, LiuZheng. A primary study on chemical bound forms of copper and zinc in wheat and rape [J]. Chin J Appl Ecol, 2000, 11(4): 629-630

AI Summary AI Mindmap
PDF

108

Accesses

0

Citation

Detail

Sections
Recommended

AI思维导图

/