Organochlorines, mercury, and selenium in great blue heron eggs from Indiana Dunes National Lakeshore, Indiana

被引:12
作者
Custer, TW
Hines, RK
Stewart, PM
Melancon, MJ
Henshel, DS
Sparks, DW
机构
[1] US Geol Survey, Biol Resources Div, Upper Mississipi Sci Ctr, La Crosse, WI 54602 USA
[2] US Geol Survey, Biol Resources Div, Lake Michigan Ecol Res Stn, Porter, IN 46304 USA
[3] US Geol Survey, Biol Resources Div, Patuxent Wildlife Res Ctr, Laurel, MD 20708 USA
[4] Indiana Univ, Sch Publ & Environm Affairs, Bloomington, IN 47405 USA
[5] US Fish & Wildlife Serv, Bloomington Ecol Field Off, Bloomington, IN 47403 USA
关键词
organochlorines; great blue herons; PCB congeners; mercury; selenium; Indiana Dunes National Lakeshore;
D O I
10.1016/S0380-1330(98)70795-6
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
In 1993, 20 great blue heron (Ardea herodias; GBH) eggs (one per nest) were collected from a colony at the Indiana Dunes National Lakeshore, Indiana (INDU). The eggs were artificially incubated until pipping and were then analyzed for organochlorines, mercury, and selenium. Livers of embryos were analyzed for hepatic microsomal ethoxyresorufin-O-dealkylase (EROD) activity. Brains were measured for asymmetry. Egg-laying began in early April and the mean clutch size was 4.2 eggs per clutch. Organochlorine concentrations were generally low (geometric mean p,p'-DDE = 1.6 mu g/g wet weight; polychlorinated biphenyl [PCB] = 4.9 mu g/g); however, one egg had elevated concentrations of p,p'-DDE (13 mu g/g) and PCBs (56 mu g/g). EROD activity in the embryos analyzed from INDU was not elevated. The frequency (11%) of brain asymmetry was low. Eggshells averaged 3.4% thinner than eggshells collected prior to the use of DDT. Mercury (geometric mean = 0.9 mu g/g dry weight) concentration in GBH eggs were within background levels. Selenium (4.0 mu g/g dry weight) concentrations in eggs were above background levels, but below a concentration threshold associated with reproductive impairment.
引用
收藏
页码:3 / 11
页数:9
相关论文
共 51 条
[1]  
Anderson DW., 1972, Proceedings of the International Ornithology Congress, V15, P514
[2]   COMPARISON OF POLYCHLORINATED DIBENZODIOXIN LEVELS WITH HEPATIC MIXED-FUNCTION OXIDASE INDUCTION IN GREAT BLUE HERONS [J].
BELLWARD, GD ;
NORSTROM, RJ ;
WHITEHEAD, PE ;
ELLIOTT, JE ;
BANDIERA, SM ;
DWORSCHAK, C ;
CHANG, T ;
FORBES, S ;
CADARIO, B ;
HART, LE ;
CHENG, KM .
JOURNAL OF TOXICOLOGY AND ENVIRONMENTAL HEALTH, 1990, 30 (01) :33-52
[3]  
Blus L.J., 1980, Murrelet, V61, P63, DOI 10.2307/3535035
[4]  
BROCK K. J., 1986, BIRDS INDIANA DUNES
[5]  
CONNORS P G, 1975, Canadian Field-Naturalist, V89, P157
[6]   Nest initiation and clutch size of Great Blue Herons on the Mississippi River in relation to the 1993 flood [J].
Custer, TW ;
Hines, RK ;
Custer, CM .
CONDOR, 1996, 98 (02) :181-188
[7]   TRANSFER AND ACCUMULATION OF ORGANOCHLORINES FROM BLACK-CROWNED NIGHT-HERON EGGS TO CHICKS [J].
CUSTER, TW ;
CUSTER, CM .
ENVIRONMENTAL TOXICOLOGY AND CHEMISTRY, 1995, 14 (03) :533-536
[8]  
Custer TW, 1997, ENVIRON TOXICOL CHEM, V16, P260, DOI [10.1002/etc.5620160223, 10.1897/1551-5028(1997)016&lt
[9]  
0260:CCABRI&gt
[10]  
2.3.CO