吉林大学学报(理学版)
吉林大學學報(理學版)
길림대학학보(이학판)
JOURNAL OF JILIN UNIVERSITY(SCIENCE EDITION)
2014年
2期
376-382
,共7页
周楠楠%李一楠%郭志勇%李义%花修艺%李耀睿%董德明
週楠楠%李一楠%郭誌勇%李義%花脩藝%李耀睿%董德明
주남남%리일남%곽지용%리의%화수예%리요예%동덕명
生物扰动%平面光极%DO 传感器%沉积物%生物地球化学
生物擾動%平麵光極%DO 傳感器%沉積物%生物地毬化學
생물우동%평면광겁%DO 전감기%침적물%생물지구화학
bioturbation%planar optode%DO sensor%sediment%biogeochemistry
采用改进的平面传感膜制备方法,建立应用于淡水/沉积物模拟体系的溶解氧(DO)二维分布监测系统。结果表明:采用物理包埋法将荧光指示剂三(4,7-联苯-1,10-邻菲啰啉)二氯化钌固定于乙基纤维素膜上,制备的DO 平面传感膜荧光强度随DO 质量浓度的增加而减小,符合荧光淬灭的 Stern-Volmer 方程,具有 DO 响应范围宽(0~20 mg/L)、响应速度快(<60 s)、准确性高、可逆性和稳定性好等优点;在生物扰动存在下,沉积物 DO 变化较小,对上覆水DO 影响较大,这是由于物理混合和氧化还原等多种机制综合作用所致,生物扰动将直接或间接影响这些作用。
採用改進的平麵傳感膜製備方法,建立應用于淡水/沉積物模擬體繫的溶解氧(DO)二維分佈鑑測繫統。結果錶明:採用物理包埋法將熒光指示劑三(4,7-聯苯-1,10-鄰菲啰啉)二氯化釕固定于乙基纖維素膜上,製備的DO 平麵傳感膜熒光彊度隨DO 質量濃度的增加而減小,符閤熒光淬滅的 Stern-Volmer 方程,具有 DO 響應範圍寬(0~20 mg/L)、響應速度快(<60 s)、準確性高、可逆性和穩定性好等優點;在生物擾動存在下,沉積物 DO 變化較小,對上覆水DO 影響較大,這是由于物理混閤和氧化還原等多種機製綜閤作用所緻,生物擾動將直接或間接影響這些作用。
채용개진적평면전감막제비방법,건립응용우담수/침적물모의체계적용해양(DO)이유분포감측계통。결과표명:채용물리포매법장형광지시제삼(4,7-련분-1,10-린비라람)이록화조고정우을기섬유소막상,제비적DO 평면전감막형광강도수DO 질량농도적증가이감소,부합형광쉬멸적 Stern-Volmer 방정,구유 DO 향응범위관(0~20 mg/L)、향응속도쾌(<60 s)、준학성고、가역성화은정성호등우점;재생물우동존재하,침적물 DO 변화교소,대상복수DO 영향교대,저시유우물리혼합화양화환원등다충궤제종합작용소치,생물우동장직접혹간접영향저사작용。
A new plane sensing membrane was developed in the study,and then a system was established to monitor the spatial and temporal distribution of dissolved oxygen (DO)in a simulated freshwater/sediment microcosm.Sensing foils were fabricated by physical entrapping fluorescent indicator tris(4,7-diphenyl-1,10-phenanthroline)ruthenium dichloride in ethyl cellulose film,and the emission fluorescence intensity was decreased with the increase of the concentration of dissolved oxygen,which conforms to the Stern-Volmer equation of the fluorescence quenching mechanism.The sensor is precise,stable,with fast response time (<60 s)and good reversibility,and has a wide DO-sensitive range (0-20 mg/L).According to the monitoring results by the system,although the temporal and spatial variation in the sediment was minor under bioturbation,the sediment has significant effects on the DO of overlying water.Complex changes of DO in the system were the result of combined effects of a variety of mechanisms such as physical mixing and redox.And these effects were all affected by bioturbation.