DISTRIBUTION OF ARSENITE AND TOTAL DISSOLVED ARSENIC IN MAJOR FRENCH ESTUARIES - DEPENDENCE ON BIOGEOCHEMICAL PROCESSES AND ANTHROPOGENIC INPUTS

被引:70
作者
SEYLER, P
MARTIN, JM
机构
[1] Institut de Biogéochimie Marine, U.A. 386 CNRS, Ecole Normale Superiéure, F-92120 Montrouge, 1, rue Maurice Arnoux
关键词
D O I
10.1016/0304-4203(90)90018-8
中图分类号
O6 [化学];
学科分类号
0703 ;
摘要
The distribution of arsenite (As (III)), total dissolved arsenic and particulate arsenic was studied in major French rivers/estuaries: the Rhône, Gironde and Loire, which are representative of polluted, unpolluted, macrotidal and stratified systems. In these rivers, arsenite (1.3-2.1 nM) and total dissolved arsenic concentrations (8.8-20.5 nM) are comparable with mean concentrations in European and North American rivers. In the Rhône estuary (with flushing time of the order of 1 day) the maximum of dissolved arsenic (25-50 nM) occurring in the low-salinity zone is related to the variability of the river input. In the Gironde estuary (flushing time 20-86 days) arsenite and total dissolved As concentrations vs. chlorinity plots show a maximum (45 nm for dissolved arsenic) located in the low-salinity zone within the turbidity maximum. This maximum is interpreted as the result of remobilization processes which involve 'regeneration' of arsenic compounds from the degradation of organic matter, and perhaps of redox processes which occur in the anoxic 'fluid-mud layer' and/or sediments. In the Loire fluvio-estuarine system the maxima of arsenite (15 nM) and total dissolved arsenic (25 nM) are attributed to the anthropogenic inputs from land-based industries, and especially from the coal-power plant. The dissolved arsenic discharge has been estimated at 40 tons yr-1. © 1990.
引用
收藏
页码:277 / 294
页数:18
相关论文
共 40 条
[1]   EFFECTS OF TIDES ON MIXING AND SUSPENDED SEDIMENT TRANSPORT IN MACRO-TIDAL ESTUARIES [J].
ALLEN, GP ;
SALOMON, JC ;
BASSOULLET, P ;
DUPENHOAT, Y ;
DEGRANDPRE, C .
SEDIMENTARY GEOLOGY, 1980, 26 (1-3) :69-90
[2]  
ALOISI JC, 1982, OCEANOL ACTA, V5, P481
[3]   DETERMINATION OF ARSENIC SPECIES IN NATURAL-WATERS [J].
ANDREAE, MO .
ANALYTICAL CHEMISTRY, 1977, 49 (06) :820-823
[4]   ARSENIC, ANTIMONY, GERMANIUM, AND TIN IN THE TEJO ESTUARY, PORTUGAL - MODELING A POLLUTED ESTUARY [J].
ANDREAE, MO ;
BYRD, JT ;
FROELICH, PN .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1983, 17 (12) :731-737
[5]   BIOSYNTHESIS AND RELEASE OF ORGANOARSENIC COMPOUNDS BY MARINE-ALGAE [J].
ANDREAE, MO ;
KLUMPP, D .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1979, 13 (06) :738-741
[6]  
ANDREAE MO, 1984, TELLUS B, V36, P101, DOI 10.1111/j.1600-0889.1984.tb00232.x
[7]   AUTOMATED PROCEDURE FOR THE DETERMINATION OF SOLUBLE ARSENIC USING HYDRIDE GENERATION ATOMIC-ABSORPTION SPECTROSCOPY [J].
ARBABZAVAR, MH ;
HOWARD, AG .
ANALYST, 1980, 105 (1253) :744-750
[8]   CHEMICAL MASS-BALANCE IN ESTUARIES [J].
BOYLE, E ;
COLLIER, R ;
DENGLER, AT ;
EDMOND, JM ;
NG, AC ;
STALLARD, RF .
GEOCHIMICA ET COSMOCHIMICA ACTA, 1974, 38 (11) :1719-1728
[9]   DIRECT VOLATILIZATION SPECTRAL EMISSION TYPE DETECTION SYSTEM FOR NANOGRAM AMOUNTS OF ARSENIC AND ANTIMONY [J].
BRAMAN, RS ;
FOREBACK, CC ;
JUSTEN, LL .
ANALYTICAL CHEMISTRY, 1972, 44 (13) :2195-&
[10]   THE BEHAVIOR OF FLY-ASH DERIVED ARSENIC IN SEAWATER [J].
BRESLIN, VT ;
DUEDALL, IW .
MARINE CHEMISTRY, 1983, 13 (04) :341-356