Variability of herbicides (triazines, phenylureas) and tentative mass balance as a function of stream order, in the river Marne basin (France) - Triazine and phenylurea flux and stream order
M. Chevreuil et al., Variability of herbicides (triazines, phenylureas) and tentative mass balance as a function of stream order, in the river Marne basin (France) - Triazine and phenylurea flux and stream order, HYDROBIOL, 410, 1999, pp. 349-355
The magnitude of the contamination of the river Marne by various herbicides
of agricultural origin (triazines and phenylureas), led the CGE (Compagnie
Generale des Eaux) and the IHC/LGA (Institut d'Hydrologie et de Climatolog
ie/Laboratoire de Geologie Appliquee) to investigate the spatial and tempor
al distribution of these contaminants. The field work was carried out from
1991 through 1994 on the river Marne, particularly in the sub-basin of the
Grand Morin and its tributaries, direct (Orgeval) or secondary (Melarchez).
The chronic contamination of the streams by atrazine and simazine with a b
ackground concentration around 100 ng l(-1), results from contamination of
groundwaters in the Calcaire de Champigny and Calcaire de Brie layers (CGE,
1993). The maximum atrazine and simazine concentrations (> 500 ng l(-1)) w
ere usually found from April to June. During this period the atrazine conce
ntration peaks might reach 2000 ng l(-1) in the agricultural brooks as well
as in the river Marne. Isoproturon was also detected throughout the year,
except during the summer low water period. The maximum concentrations of is
oproturon were found between February and April: ranging from 500 ng l(-1)
to 1200 ng l(-1), depending on the rainfalls. The annual balances for 1991
and 1992, estimated from the exportation fluxes at the elementary catchment
s basin outlets, showed that the exportation levels of atrazine, simazine a
nd isoproturon did not exceed 0.3% of the mass applied agriculturally in th
e Melarchez basin and 1.5% of the mass of atrazine applied in the Grand Mor
in river basin. The evolution of herbicide concentrations, from the element
ary brook in a rural area to the river Marne outlet in an urban area, showe
d that there was no longitudinal decrease of contamination. In fact, the wa
ters of the river Marne lower course, and of its minor tributaries in the u
rban area, might display herbicide concentrations similar or even higher th
an those of rivers in the agricultural area.