环境科学
環境科學
배경과학
CHINESE JOURNAL OF ENVIRONMENTAL SCIENCE
2015年
3期
847-854
,共8页
王凯%李侃竹%周亦圆%刘振鸿%薛罡%高品
王凱%李侃竹%週亦圓%劉振鴻%薛罡%高品
왕개%리간죽%주역원%류진홍%설강%고품
沉积物%PPCPs%吸附特性%影响因素%吸附等温线
沉積物%PPCPs%吸附特性%影響因素%吸附等溫線
침적물%PPCPs%흡부특성%영향인소%흡부등온선
sediment%PPCPs%adsorption characteristic%influencing factor%adsorption isotherm
采用批平衡实验方法,研究了黄浦江沉积物对环丙沙星( CIP)、四环素( TC)、磺胺甲唑( SMX)和三氯生( TCS)的吸附特性,探讨了吸附时间、初始浓度、溶液pH值和温度等因素对吸附过程的影响.结果表明,CIP、TC、SMX和TCS在沉积物中的吸附过程均呈现先快速后缓慢的变化趋势,等温吸附平衡时间约为4 h.溶液pH值对CIP、TC和TCS的吸附过程具有显著影响,但对SMX的吸附影响较小.目标PPCPs吸附过程符合准二级反应动力学方程,吸附常数为4.89×10-3~1.96×10-2 kg·( min·mg)-1.吸附等温线能较好地符合Freundlich方程和线性方程,高温不利于CIP和TCS吸附,而利于TC和SMX吸附.沉积物对CIP、 TC和TCS的吸附能力较强,但对SMX吸附效果较差,当初始浓度为10 mg·L-1时,沉积物对CIP、 TC、SMX和TCS的平衡吸附量分别可达702.8、733.1、54.7和695.0 mg·kg-1.
採用批平衡實驗方法,研究瞭黃浦江沉積物對環丙沙星( CIP)、四環素( TC)、磺胺甲唑( SMX)和三氯生( TCS)的吸附特性,探討瞭吸附時間、初始濃度、溶液pH值和溫度等因素對吸附過程的影響.結果錶明,CIP、TC、SMX和TCS在沉積物中的吸附過程均呈現先快速後緩慢的變化趨勢,等溫吸附平衡時間約為4 h.溶液pH值對CIP、TC和TCS的吸附過程具有顯著影響,但對SMX的吸附影響較小.目標PPCPs吸附過程符閤準二級反應動力學方程,吸附常數為4.89×10-3~1.96×10-2 kg·( min·mg)-1.吸附等溫線能較好地符閤Freundlich方程和線性方程,高溫不利于CIP和TCS吸附,而利于TC和SMX吸附.沉積物對CIP、 TC和TCS的吸附能力較彊,但對SMX吸附效果較差,噹初始濃度為10 mg·L-1時,沉積物對CIP、 TC、SMX和TCS的平衡吸附量分彆可達702.8、733.1、54.7和695.0 mg·kg-1.
채용비평형실험방법,연구료황포강침적물대배병사성( CIP)、사배소( TC)、광알갑서( SMX)화삼록생( TCS)적흡부특성,탐토료흡부시간、초시농도、용액pH치화온도등인소대흡부과정적영향.결과표명,CIP、TC、SMX화TCS재침적물중적흡부과정균정현선쾌속후완만적변화추세,등온흡부평형시간약위4 h.용액pH치대CIP、TC화TCS적흡부과정구유현저영향,단대SMX적흡부영향교소.목표PPCPs흡부과정부합준이급반응동역학방정,흡부상수위4.89×10-3~1.96×10-2 kg·( min·mg)-1.흡부등온선능교호지부합Freundlich방정화선성방정,고온불리우CIP화TCS흡부,이리우TC화SMX흡부.침적물대CIP、 TC화TCS적흡부능력교강,단대SMX흡부효과교차,당초시농도위10 mg·L-1시,침적물대CIP、 TC、SMX화TCS적평형흡부량분별가체702.8、733.1、54.7화695.0 mg·kg-1.
A batch equilibrium method was used to investigate the adsorption characteristics of ciprofloxacin ( CIP ) , tetracycline ( TC) , sulfamethoxazole ( SMX) and triclosan ( TCS) onto Huangpu River sediments. Effects of adsorption time, initial concentration, solution pH and temperature on the adsorption process were studied. The results showed that the adsorption process of these PPCPs onto sediments was a two-step process:a rapid adsorption followed by a slow balance. The equilibrium time was about 4 h. The pH value had a significant effect on the adsorption of CIP, TC and TCS, whereas the effect on SMX adsorption was negligible. The kinetic results indicated that the adsorption processes followed the pseudo-second-order model, with adsorption rate in the range of 4. 89 × 10 -3-1. 96 × 10 -2 kg·( min·mg) -1 . Adsorption isotherms were well described by the Freundlich and linear equations. As temperature increased, the amount of SMX and TC adsorbed increased, whereas CIP and TCS decreased. CIP, TC and TCS had a strong tendency to adsorb onto sediments, while the adsorption of SMX was unfavorable. When the initial concentration of PPCPs was 10 mg·L-1 , the equilibrium adsorption capacities of CIP, TC, SMX and TCS reached 702. 8, 733. 1, 54. 7 and 695. 0 mg·kg-1 , respectively.