Loading…
Redox potential dynamics in a horizontal subsurface flow constructed wetland for wastewater treatment: Diel, seasonal and spatial fluctuations
Redox potential was measured in a treatment bed of a constructed wetland (CW) with subsurface horizontal flow used for municipal wastewater treatment. CW was situated in the Czech Republic, designed for 150 person equivalents; it was planted with Phragmites australis and put into operation in 2001....
Saved in:
Published in: | Ecological engineering 2008-10, Vol.34 (3), p.223-232 |
---|---|
Main Authors: | , , |
Format: | Article |
Language: | English |
Subjects: | |
Citations: | Items that this one cites Items that cite this one |
Online Access: | Get full text |
Tags: |
Add Tag
No Tags, Be the first to tag this record!
|
Summary: | Redox potential was measured in a treatment bed of a constructed wetland (CW) with subsurface horizontal flow used for municipal wastewater treatment. CW was situated in the Czech Republic, designed for 150 person equivalents; it was planted with
Phragmites
australis and put into operation in 2001. The system was very efficient in removing organic pollution (BOD
5 82% and COD 74.0%), nitrogen (62.6%), phosphorus (75.4%) and suspended solids (52%). Redox potential (
E
H) was measured in two depths (0.2 and 0.5
m) of the treatment bed at regular distances from inflow using platinum electrodes, continuously, every 15
min during a more-than-2-year period (27 months) from 2002 to 2004.
E
H ranged from −400 to +800
mV. The fluctuations were the most intense in the upper layer (0.2
m) at the furthest distance from inflow (13
m) and
E
H changed within very short time periods (hours) by several hundred millivolts. Among the factors affecting
E
H concentrations of pollutants, pore water temperature and water flow rate were determined.
Vegetated treatment beds of subsurface horizontal flow constructed wetlands filled with mineral substrate can be extremely dynamic systems, in which oxidation–reduction status changes within short time from anaerobic to aerobic and vice versa. Anaerobic conditions do not prevail necessarily in the upper layer of treatment bed, in which plant roots are present. |
---|---|
ISSN: | 0925-8574 1872-6992 |
DOI: | 10.1016/j.ecoleng.2008.08.008 |