Previous Page  5 / 9 Next Page
Information
Show Menu
Previous Page 5 / 9 Next Page
Page Background

Volume 6, Issue 6 (Suppl)

J Geol Geophys, an open access journal

ISSN: 2381-8719

Soil Science 2017

December 04-05 2017

Page 32

conference

series

.com

December 04-05, 2017 | Madrid, Spain

Annual Congress on

SOIL SCIENCES

Bodoque J M, J Geol Geophys 2017, 6:6(Suppl)

DOI: 10.4172/2381-8719-C1-013

Restoring hydromorphological functionality to improve natural purification capacity of a heavily

modified water body

W

e determined the natural purification ability of a floodplain where irrigated agriculture is a dominant and hydraulic

connectionwith theassociatedriver is limited.Denitrificationactivitywas characterizedbyusingdifferentmethodological

approaches based on i) End-Members Mixing Analysis; ii) characterization of macroinvertebrates of the hyporheic zone;

iii) analysis of the denitrification potential; iv) analysis of the bacterial community structure; and v) hydrologic modeling.

All the approaches, except EMMA analysis, lead to the same conclusion. Denitrification is almost non-existent because the

study site does not have the hydric soil and oxygen-limited conditions needed to enable denitrification. Invertebrates did not

show statistically significant differences (P-value higher than 0.05) between the diversity indices corresponding to each of the

sampling campaigns. However, significant differences (P-value less than 0.01) were found between the piezometers closest to

the river banks and the rest; this may be interpreted because of low hydraulic connectivity. Denitrification potential did not

show significant statistical differences (P-value less than 0.01) between the sampling campaigns conducted. This shows that

besides the absence of connectivity, irrigation is not able to significantly activate denitrification. Additionally, results from the

characterization of the bacterial community structure are consistent with floodplains where denitrification is not effective since

most bacterial communities are not linked with NO3. Hydrologic modeling showed that decay change is very low, on the order

of 0.01 mgN/L.day, although it would improve around 10% if ordinary floods occur. During the summer months theoretical

concentrations of nitrates were lower than expected (e.g. ΔNO3 = - 41 in August 2013), according to the EMMA analysis,

which might be due to the intensity of irrigation is spatiotemporally variable in the study site. Our results show that floodplain

denitrification has been drastically reduced due to the suppression of flood-pulses. In this context, the creation of riverine

wetlands where the hydrological regime is restored would lead to a decay of nitrates whose dynamic evolution increases with

flooding, as scenarios tested by hydrological modeling have demonstrated.

Bodoque J M

University of Castilla-La Mancha, Spain