Polymer-water partition coefficients in polymeric passive samplers

被引:16
作者
Asgarpour Khansary, Milad [1 ]
Shirazian, Saeed [2 ]
Asadollahzadeh, Mehdi [1 ]
机构
[1] Islamic Azad Univ, South Tehran Branch, Young Researchers & Elite Club, Tehran, Iran
[2] Univ Limerick, Bernal Inst, Dept Chem & Environm Sci, Limerick, Ireland
关键词
Polymer; Water; Partition coefficients; Passive Samplers; Hansen solubility; ORGANIC-COMPOUNDS; GENERATION; MODEL; AIR;
D O I
10.1007/s11356-016-8029-7
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Passive samplers are of the most applied methods and tools for measuring concentration of hydrophobic organic compounds in water (c (1) (W)) in which the polymer-water partition coefficients (D) are of fundamental importance for reliability of measurements. Due to the cost and time associated with the experimental researches, development of a predictive method for estimation and evaluation of performance of polymeric passive samplers for various hydrophobic organic compounds is highly needed and valuable. For this purpose, in this work, following the fundamental chemical thermodynamic equations governing the concerned local equilibrium, successful attempts were made to establish a theoretical model of polymer-water partition coefficients. Flory-Huggins model based on the Hansen solubility parameters was used for calculation of activity coefficients. The method was examined for reliability of calculations using collected data of three polymeric passive samplers and ten compounds. A regression model of form ln(D) = 0.707ln(c (1) (p) ) - 2.7391 with an R (2) = 0.9744 was obtained to relate the polymer-water partition coefficients (D) and concentration of hydrophobic organic compounds in passive sampler (c (1) (p)). It was also found that polymer-water partition coefficients are related to the concentration of hydrophobic organic compounds in water (c (1) (W)) as ln(D) = 2.412ln(c (1) (p)) - 9.348. Based on the results, the tie lines of concentration for hydrophobic organic compounds in passive sampler (c (1) (p) ) and concentration of hydrophobic organic compounds in water (c (1) (W)) are in the form of ln(c (1) (W)) = 0.293ln(c (1) (p)) + 2.734. The composition of water sample and the interaction parameters of dissolved compound-water and dissolved compound-polymer, temperature, etc. actively influence the values of partition coefficient. The discrepancy observed over experimental data can be simply justified based on the local condition of sampling sites which alter these effective factors.
引用
收藏
页码:2627 / 2631
页数:5
相关论文
共 27 条
[21]  
Spiegel MR., 1999, MATH HDB FORMULAS TA
[22]   Modeling Uptake of Hydrophobic Organic Contaminants into Polyethylene Passive Samplers [J].
Thompson, Jay M. ;
Hsieh, Ching-Hong ;
Luthy, Richard G. .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2015, 49 (04) :2270-2277
[23]  
Tosun Ismail., 2007, Modeling in transport phenomena: a conceptual approach
[24]   On the general water harvesting capability of metal-organic frameworks under well-defined climatic conditions [J].
Trapani, F. ;
Polyzoidis, A. ;
Loebbecke, S. ;
Piscopo, C. G. .
MICROPOROUS AND MESOPOROUS MATERIALS, 2016, 230 :20-24
[25]   Atmospheric water vapour processor designs for potable water production: A review [J].
Wahlgren, RV .
WATER RESEARCH, 2001, 35 (01) :1-22
[26]   A research on application of water treatment technology for reclaimed water irrigation [J].
Xu, Meng ;
Bai, Xiao ;
Pei, Liang ;
Pan, Hulin .
INTERNATIONAL JOURNAL OF HYDROGEN ENERGY, 2016, 41 (35) :15930-15937
[27]   Field-analysis of potable water quality and ozone efficiency in ozone assisted biological filtration systems for surface water treatment [J].
Zanacic, Enisa ;
Stavrinides, John ;
McMartin, Dena W. .
WATER RESEARCH, 2016, 104 :397-407