『Abstract
Chemical erosion rates have been determined on two upland granitic
catchments under agricultural pressure in Brittany, France. Intensive
agriculture has been carried out for at least 30 years in this
region. The influence of geochemical processes related to agriculture
on the chemistry of streamwaters is determined through a geochemical
mass balance. The elemental export fluxes from these two agricultural
catchments are then compared with other catchments around the
world.
The volume and concentrations of the precipitation are taken
into account, as well as the inputs of organic and chemical fertilizers,
groundwaters and streamwaters, to estimate the relative influence
on export fluxes, and then evaluate the elemental fluxes released
by weathering. The relatively high Si flux of about 1.8± 0.9 kmol
ha-1 yr-1 is directly attributed to the
chemical weathering of soil and rock in the catchment system.
However, the Si flux remains comparable to values found in both
small and large-sized catchments under temperate and tropical
conditions. On the other hand, extremely high fluxes of major
cations (Ca, Na and Mg) are observed, ranging from 4.2±2.6 to
8.0±4.9 kmol ha-1 yr-1, which can be attributed
to chemical weathering. These fluxes remain dramatically higher
than those found in granitic catchments worldwide.
Despite an integrated agriculture, the soil acidification induced
by fertilizer application leads mainly to a release of major cations
from the system, by processes of soil ion-exchange leaching as
well as weathering of soil and rock.
Keywords: Chemical erosion; Granitic catchment; Agricultural inputs;
Cation release; Soil acidification
1. Introduction
2. Study site description
3. Material and methods
3.1. Water sampling
3.2. Chemical analyses
4. Chemical budget computation
4.1. Water mass balance
4.2. Chemical budget computation
4.2.1. Precipitation budgets
4.2.2. Agricultural inputs
4.2.3. Biomass and water storage
4.2.4. Solute outputs
4.2.5. Chemical budgets
4.3. Uncertainties
4.3.1. Dry deposition
4.3.2. Biomass uptake and mineralization
4.3.3. Storm events
5. Results
5.1. Water chemistry
5.1.1. Precipitation (F(i)p)
5.1.2. Stream- and ground-waters
5.2. Agricultural inputs (F(i)ARG)
5.3. Stream solute fluxes and chemical erosion (F(i)SO
and N(i))
6. Discussion
6.1. Cation release and acidification processes
6.2. Comparison of H\Kerrien and Kerbernez catchments
6.3. Source of exported cations
6.4. Chemical fluxes and chemical erosion rates
7. Summary and conclusions
Acknowledgments
Appendix A
Appendix B
Appendix C
References