Effects of Vegetation, Season and Temperature on the Removal of Pollutants in Experimental Floating Treatment Wetlands

The research and interest towards the use of constructed floating wetlands for (waste)water treatment is emerging as more treatment opportunities are marked out, and the technique is applied more often. To evaluate the effect of a floating macrophyte mat and the influence of temperature and season on physico-chemical changes and removal, two constructed floating wetlands (CFWs), including a floating macrophyte mat, and a control, without emergent vegetation, were built. Raw domestic wastewater from a wastewater treatment plant was added on day 0. Removal of total nitrogen, NH4–N, NO3–N, P, chemical oxygen demand (COD), total organic carbon and heavy metals (Cu, Fe, Mn, Ni, Pb and Zn) was studied during 17 batch-fed testing periods with a retention time of 11 days (February–March 2007 and August 2007–September 2008). In general, the CFWs performed better than the control. Average removal efficiencies for NH4–N, total nitrogen, P and COD were respectively 35%, 42%, 22% and 53% for the CFWs, and 3%, 15%, 6% and 33% for the control. The pH was significantly lower in the CFWs (7.08 ± 0.21) than in the control (7.48 ± 0.26) after 11 days. The removal efficiencies of NH4–N, total nitrogen and COD were significantly higher in the CFWs as the presence of the floating macrophyte mat influenced positively their removal. Total nitrogen, NH4–N and P removal was significantly influenced by temperature with the highest removal between 5°C and 15°C. At lower and higher temperatures, removal relapsed. In general, temperature seemed to be the steering factor rather than season. The presence of the floating macrophyte mat restrained the increase of the water temperature when air temperature was >15°C. Although the mat hampered oxygen diffusion from the air towards the water column, the redox potential measured in the rootmat was higher than the value obtained in the control at the same depth, indicating that the release of oxygen from the roots could stimulate oxygen consuming reactions within the root mat, and root oxygen release was higher than oxygen diffusion from the air.

[1]  G. J. Gascho,et al.  USE OF FLOATING VEGETATION TO REMOVE NUTRIENTS FROM SWINE LAGOON WASTEWATER , 2004 .

[2]  A. Werker,et al.  Treatment variability for wetland wastewater treatment design in cold climates , 2002 .

[3]  D. T. Hill,et al.  Effect of plant fill ratio on water temperature in constructed wetlands 1 This work was supported by , 2000 .

[4]  D. Revitt,et al.  Experimental reedbed systems for the treatment of airport runoff , 1997 .

[5]  J. Skousen,et al.  Treatment of Domestic Wastewater by Three Plant Species in Constructed Wetlands , 2001 .

[6]  J. Vymazal Removal of nutrients in various types of constructed wetlands. , 2007, The Science of the total environment.

[7]  A. E. Greenberg,et al.  Standard methods for the examination of water and wastewater. 19th ed. 1995. , 1995 .

[8]  R. Wein,et al.  The Contribution of Typha Components to Floating Mat Buoyancy , 1988 .

[9]  Janjit Iamchaturapatr,et al.  Nutrient removals by 21 aquatic plants for vertical free surface-flow (VFS) constructed wetland , 2007 .

[10]  R. Wein,et al.  Seasonal Change in Gas Content and Buoyancy of Floating Typha Mats , 1988 .

[11]  Vassilios A. Tsihrintzis,et al.  Effect of temperature, HRT, vegetation and porous media on removal efficiency of pilot-scale horizontal subsurface flow constructed wetlands , 2007 .

[12]  P. F. Cooper,et al.  Constructed wetlands in water pollution control. , 1990 .

[13]  Hans Bertil Wittgren,et al.  Wastewater treatment wetlands in cold climates , 1997 .

[14]  O. Stein,et al.  Temperature and wetland plant species effects on wastewater treatment and root zone oxidation. , 2002, Journal of environmental quality.

[15]  A. E. Greenberg,et al.  Standard methods for the examination of water and wastewater : supplement to the sixteenth edition , 1988 .

[16]  Ü. Mander,et al.  Experimentally constructed wetlands for wastewater treatment in Estonia , 2000 .

[17]  Jos T. A. Verhoeven,et al.  Wetlands for wastewater treatment: Opportunities and limitations , 1999 .

[18]  W. Mitsch,et al.  Wetlands. 2nd ed. , 1993 .

[19]  H. Čížková,et al.  Redox potential dynamics in a horizontal subsurface flow constructed wetland for wastewater treatment: Diel, seasonal and spatial fluctuations , 2008 .

[20]  Takao Suzuki,et al.  Removal of nitrogen, phosphorus and COD from waste water using sand filtration system with Phragmites Australis , 1987 .

[21]  O. Stein,et al.  Temperature, Plants, and Oxygen: How Does Season Affect Constructed Wetland Performance? , 2005, Journal of environmental science and health. Part A, Toxic/hazardous substances & environmental engineering.

[22]  Chris C. Tanner,et al.  Effect of loading rate and planting on treatment of dairy farm wastewaters in constructed wetlands—II. Removal of nitrogen and phosphorus , 1995 .

[23]  Lena Gumaelius,et al.  A comparative study of Cyperus papyrus and Miscanthidium violaceum-based constructed wetlands for wastewater treatment in a tropical climate. , 2004, Water research.

[24]  David Steer,et al.  The interacting effects of temperature and plant community type on nutrient removal in wetland microcosms. , 2005, Bioresource technology.

[25]  Per Stålnacke,et al.  Removal Efficiency of Three Cold-Climate Constructed Wetlands Treating Domestic Wastewater: Effects of Temperature, Seasons, Loading Rates and Input Concentrations , 1999 .

[26]  William J. Mitsch,et al.  The effects of season and hydrologic and chemical loading on nitrate retention in constructed wetlands: a comparison of low- and high-nutrient riverine systems , 1999 .

[27]  John Todd,et al.  Ecological design applied , 2003 .

[28]  Laura Ortiz,et al.  Effect of design parameters in horizontal flow constructed wetland on the behaviour of volatile fatty acids and volatile alkylsulfides. , 2005, Chemosphere.

[29]  P Kuschk,et al.  Annual cycle of nitrogen removal by a pilot-scale subsurface horizontal flow in a constructed wetland under moderate climate. , 2003, Water research.

[30]  R. Kadlec,et al.  Temperature Effects in Treatment Wetlands , 2001, Water environment research : a research publication of the Water Environment Federation.

[31]  J. Maestre,et al.  Long-term ammonia removal in a coconut fiber-packed biofilter: analysis of N fractionation and reactor performance under steady-state and transient conditions. , 2009, Water research.

[32]  P. Garbett,et al.  AN INVESTIGATION INTO THE APPLICATION OF FLOATING REED BED AND BARLEY STRAW TECHNIQUES FOR THE REMEDIATION OF EUTROPHIC WATERS , 2007 .

[33]  Robert H. Kadlec,et al.  Chemical, physical and biological cycles in treatment wetlands , 1999 .

[34]  W. Armstrong,et al.  MEASUREMENT AND MODELLING OF OXYGEN RELEASE FROM ROOTS OF PHRAGMITES AUSTRALIS , 1990 .

[35]  O. Stein,et al.  Ammonium Removal in Constructed Wetland Microcosms as Influenced by Season and Organic Carbon Load , 2005, Journal of environmental science and health. Part A, Toxic/hazardous substances & environmental engineering.

[36]  H. Brix Do macrophytes play a role in constructed treatment wetlands , 1997 .

[37]  Jan Vymazal,et al.  The use of sub-surface constructed wetlands for wastewater treatment in the Czech Republic: 10 years experience , 2002 .

[38]  Saravanamuthu Vigneswaran,et al.  Constructed Wetlands for Wastewater Treatment , 2001 .

[39]  Grietje Zeeman,et al.  The effects of operational and environmental variations on anaerobic wastewater treatment systems: a review. , 2006, Bioresource technology.