Environmental factors influencing microcystin distribution and concentration in the Midwestern United States

被引:137
作者
Graham, JL
Jones, JR
Jones, SB
Downing, JA
Clevenger, TE
机构
[1] Univ Missouri, Dept Fisheries & Wildlife Sci, Columbia, MO 65211 USA
[2] Columbia Environm Res Ctr, Columbia, MO 65201 USA
[3] Iowa State Univ, Dept Ecol Evolut & Organismal Biol, Ames, IA 50011 USA
[4] Univ Missouri, Dept Civil & Environm Engn, Columbia, MO 65211 USA
关键词
microcystin; cyanotoxin; cyanobacteria; midwest; ELISA; nonlinear;
D O I
10.1016/j.watres.2004.08.004
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
During May-September 2000-2001, physicochemical data were collected from 241 lakes in Missouri, Iowa, northeastern Kansas, and southern Minnesota U.S.A., to determine the environmental variables associated with high concentrations of the cyanobacterial hepatotoxin microcystin (MC). The study region represents a south-north latitudinal gradient in increasing trophic status, with total phosphorus (TP) and total nitrogen (TN) values ranging between 2-995 and 90-15870 mug/L, respectively. Particulate MC values, measured by ELISA, ranged from undetectable to 4500 ng/L and increased with increasing latitude. Despite latitudinal trends, environmental variables explained <50% of the variation in MC values. Inspection of MC-TN and MC-Secchi bivariate plots revealed distinctly nonlinear trends, suggesting optima for maximum MC values. Nonlinear interval maxima regression indicated that MC-TN maxima were characterized by a unimodal curve, with maximal (>2000 ng/L) MC values occurring between 1500 and 4000 mug/L TN. Above 8000 mug/L TN all MC values were <150 ng/L. MC-Secchi maxima were characterized by exponential decline, with maximal MC values occurring at Secchi depths <2.5 m. The development of empirical relationships between environmental variables and MC values is critical to effective lake management and minimization of human health risks associated with the toxin. This study indicates MC values are linked to the physicochemical environment; however, the relationships are not traditional linear models. (C) 2004 Elsevier Ltd. All rights reserved.
引用
收藏
页码:4395 / 4404
页数:10
相关论文
共 34 条
[1]  
[Anonymous], 1995, Standard methods for the examination of water and wastewater, V19th
[2]  
[Anonymous], 1983, Statistical methods
[3]  
[Anonymous], 2001, CYANOTOXINS OCCURREN, DOI DOI 10.1007/978-3-642-59514-1
[4]   A METHOD OF ESTIMATING THE SLOPE OF UPPER-BOUNDS OF PLOTS OF BODY SIZE AND ABUNDANCE IN NATURAL ANIMAL ASSEMBLAGES [J].
BLACKBURN, TM ;
LAWTON, JH ;
PERRY, JN .
OIKOS, 1992, 65 (01) :107-112
[5]  
BLOMQVIST P, 1994, ARCH HYDROBIOL, V132, P141
[6]  
Carmichael WW, 1997, ADV BOT RES, V27, P211
[7]  
CHU FS, 1994, LAKELINE, V14, P41
[8]   NITRATE AND ORGANIC N ANALYSES WITH 2ND-DERIVATIVE SPECTROSCOPY [J].
CRUMPTON, WG ;
ISENHART, TM ;
MITCHELL, PD .
LIMNOLOGY AND OCEANOGRAPHY, 1992, 37 (04) :907-913
[9]  
DOWNING JA, 2000, IOWA LAKES SURVEY SU
[10]  
Fenneman N.M., 1938, Physiography of the eastern United States