The ionic strength effect on microcystin and natural organic matter surrogate adsorption onto PAC

被引:85
作者
Campinas, Margarida [1 ]
Rosa, Maria Joao [1 ]
机构
[1] Univ Algarve, Fac Marine & Environm Sci, Ctr Marine & Environm Res, P-8005139 Faro, Portugal
关键词
microcystins; PAC; adsorption; NOM surrogates; surface concentration; ionic strength;
D O I
10.1016/j.jcis.2006.02.042
中图分类号
O64 [物理化学(理论化学)、化学物理学];
学科分类号
070304 ; 081704 ;
摘要
This work aims to contribute to a better understanding of the ionic strength effect on microcystin and natural organic matter (NOM) surrogate adsorption by analyzing the importance of adsorbate molecular size, and surface concentration. Adsorption kinetics and/or isotherms were performed on PAC Norit SA-UF for four microcystin variants (MC-LR, MC-LY, MC-LW, MC-LF), and three NOM surrogates (salicylic acid (SA), tannic acid (TA), Aldrich humic acid (AHA)) at different solution ionic strengths. Results showed that the ionic strength effect depends upon the adsorbate surface concentration, cation charge (mono or divalent), and adsorbate molecular size. Potassium seemed not to affect the MC-LR adsorption, while calcium enhanced MC-LR kinetics and adsorption capacity. K+ and, particularly, Ca2+ improved the adsorption kinetics of the other microcystin variants. For identical surface concentration and ionic strength, the impact of K+ and Ca2+ on NOM surrogates depended on the adsorbate molecular size: K+ effect was only observed for AHA, whereas Ca2+ caused no effect on SA adsorption, slightly enhanced TA adsorption, and greatly enhanced AHA adsorption. MC-LR isotherms with two salt concentrations (KCl or CaCl2) indicated that, for the studied range of equilibrium surface concentration (5.3-18.7 mg/g), an enhanced adsorption regime prevails, and no transition regime was observed. (c) 2006 Elsevier Inc. All rights reserved.
引用
收藏
页码:520 / 529
页数:10
相关论文
共 38 条
[1]  
Andelkovic T., 2004, FACTA U SER PHYS CHE, V3, P79
[2]   Adsorption of NOM onto activated carbon: Effect of surface charge, ionic strength, and pore volume distribution [J].
Bjelopavlic, M ;
Newcombe, G ;
Hayes, R .
JOURNAL OF COLLOID AND INTERFACE SCIENCE, 1999, 210 (02) :271-280
[3]  
Campos C, 2000, J AM WATER WORKS ASS, V92, P69
[4]   Effects of polyelectrolytes on reduction of model compounds via coagulation [J].
Chang, EE ;
Chiang, PC ;
Tang, WY ;
Chao, SH ;
Hsing, HJ .
CHEMOSPHERE, 2005, 58 (08) :1141-1150
[5]   MOLECULAR-WEIGHT, POLYDISPERSITY, AND SPECTROSCOPIC PROPERTIES OF AQUATIC HUMIC SUBSTANCES [J].
CHIN, YP ;
AIKEN, G ;
OLOUGHLIN, E .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1994, 28 (11) :1853-1858
[6]   The impact of conventional water treatment processes on cells of the cyanobacterium Microcystis aeruginosa [J].
Chow, CWK ;
Drikas, M ;
House, J ;
Burch, MD ;
Velzeboer, RMA .
WATER RESEARCH, 1999, 33 (15) :3253-3262
[7]   Cyanobacterial toxins, the perception of water quality, and the prioritisation of eutrophication control [J].
Codd, GA .
ECOLOGICAL ENGINEERING, 2000, 16 (01) :51-60
[8]   EFFECT OF ADSORPTION OF ORGANIC-MATTER ON FOULING OF ULTRAFILTRATION MEMBRANES [J].
CROZES, G ;
ANSELME, C ;
MALLEVIALLE, J .
JOURNAL OF MEMBRANE SCIENCE, 1993, 84 (1-2) :61-77
[9]   A study of the factors affecting the removal of humic acid by activated carbon prepared from biomass material [J].
Daifullah, AAM ;
Girgis, BS ;
Gad, HMH .
COLLOIDS AND SURFACES A-PHYSICOCHEMICAL AND ENGINEERING ASPECTS, 2004, 235 (1-3) :1-10
[10]   Sorption and cosorption of 1,2,4-trichlorobenzene and tannic acid by organo-clays [J].
Dentel, SK ;
Jamrah, AI ;
Sparks, DL .
WATER RESEARCH, 1998, 32 (12) :3689-3697