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Frontiers of Environmental Science & Engineering

ISSN 2095-2201

ISSN 2095-221X(Online)

CN 10-1013/X

Postal Subscription Code 80-973

2018 Impact Factor: 3.883

Front Envir Sci Eng    2013, Vol. 7 Issue (6) : 906-912    https://doi.org/10.1007/s11783-013-0579-z
RESEARCH ARTICLE
Decontamination efficiency and root structure change in the plant-intercropping model in vertical-flow constructed wetlands
Yonghua CHEN, Xiaofu WU(), Mingli CHEN, Kelin LI, Jing PENG, Peng ZHAN
Research Center of Environment Science and Engineering, Central South University of Forestry and Technology, Changsha 410004, China
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Abstract

Subtropical climatic conditions can contribute to the death of the aerial parts of constructed wetland plants in winter. This presents a barrier to the widespread application of constructed wetland and is an issue that urgently needs to be solved. Three contrasting experiments, the plant-intercropping model (A), the warm-seasonal plant model (B), and the non-plant model (C), were studied in terms of their efficiency in removing pollutants, and the change in root structure of plants in the plant-intercropping model within the vertical-flow constructed wetlands. The results indicate that model A was able to solve the aforementioned problem. Overall, average removal rates of three pollutants (CODCr, total nitrogen (TN) and total phosphorous (TP)) using model A were significantly higher than those obtained using models B and C (P<0.01). Moreover, no significant differences in removal rates of the three pollutants were detected between A and B during the higher temperature part of the year (P>0.05). Conversely, removal rates of the three pollutants were found to be significantly higher using model A than those observed using model B during the lower temperature part of the year (P<0.01). Furthermore, the morphologies and internal structures of plant roots further demonstrate that numerous white roots, whose distribution in soil was generally shallow, extend further under model A. The roots of these aquatic plants have an aerenchyma structure composed of parenchyma cells, therefore, roots of the cold-seasonal plants with major growth advantages used in A were capable of creating a more favorable vertical-flow constructed wetlands media-microenvironment. In conclusion, the plant-intercropping model (A) is more suitable for use in the cold environment experienced by constructed wetland during winter.

Keywords vertical-flow constructed wetlands      plant intercropping model      warm seasonal plant model     
Corresponding Author(s): WU Xiaofu,Email:wuxiaofu530911@vip.163.com   
Issue Date: 01 December 2013
 Cite this article:   
Yonghua CHEN,Xiaofu WU,Mingli CHEN, et al. Decontamination efficiency and root structure change in the plant-intercropping model in vertical-flow constructed wetlands[J]. Front Envir Sci Eng, 2013, 7(6): 906-912.
 URL:  
https://academic.hep.com.cn/fese/EN/10.1007/s11783-013-0579-z
https://academic.hep.com.cn/fese/EN/Y2013/V7/I6/906
Fig.1  Structure of a constructed wetland wastewater system
datetemperature /°Cinfluent /(mg·L-1)intercropped pattern (A)warm-seasonal plant pattern (B)non-plant pattern (C)
rate of removal/%rate of removal /%rate of removal /%
Sep-0823.5185.4230.6730.0629.55
Oct-0819.5190.1051.32 (A-C**)55.06 (B-C**)33.15
Nov-0812.4168.7754.05 (A-C**)55.11 (B-C**)32.14
Dec-088.4179.6939.59 (A-C**)39.52 (B-C**)31.83
Jan-094.3164.5837.28(A-B*, A-C**)32.3030.35
Feb-096.2170.3541.05(A-B*, A-C**)35.37 (B-C**)29.25
Mar-0912.7179.3144.96 (A-B**,A-C**)35.69 (B-C**)31.32
Apr-0917.4168.8046.03(A-B*,A-C**)41.80 (B-C*)36.65
average13.05175.8843.10(A-B*,A-C**)40.68 (B-C**)31.77
Tab.1  Removal efficiencies of CODin three modes
Fig.2  Change in COD concentration in the three models (A, B, C) with time
datetemperature /°Cinfluent /(mg·L-1)intercropped pattern (A)warm-seasonal plant pattern (B)non-plant pattern (C)
rate of removal/%rate of removal /%rate of removal /%
Sep-0823.555.6431.4933.6830.19
Oct-0819.551.3246.51 (A-C**)45.13 (B-C**)26.70
Nov-0812.446.9340.36 (A-C**)38.27 (B-C**)27.87
Dec-088.452.6836.20 (A-C**)30.1428.55
Jan-094.350.9834.88(A-B*, A-C**)29.64 (B-C**)26.66
Feb-096.248.0237.44(A-B*, A–C**)31.32(B-C**)25.07
Mar-0912.749.642.86(A-B*, A-C**)38.79 (B-C**)28.10
Apr-0917.448.6645.15(A-B*, A-C**)41.16 (B-C**)30.19
average13.0550.4839.36(A-B*, A-C**)36.14 (B-C**)27.92
Tab.2  Comparison between the treatment efficiencies of TN in three modes
Fig.3  Change in TN concentration in the three models (A, B, C) with time
datetemperature /°Cinfluent /(mg·L-1)intercropped pattern (A)warm-seasonal plant pattern (B)non-plant pattern (C)
rate of removal/%rate of removal /%rate of removal /%
Sep-0823.52.9635.0633.1532.13
Oct-0819.53.0645.16 (A-C**)45.05 (B-C**)38.85
Nov-0812.43.1146.57 (A-C**)45.18 (B-C**)38.97
Dec-088.42.9540.23 (A-C**)40.68 (B-C**)33.22
Jan-094.32.9430.61(A-B*, A-C**)26.42 (B-C**)24.83
Feb-096.23.0431.81(A-B*, A-C**)26.8927.52
Mar-0912.73.0132.08 (A-C**)28.9826.00
Apr-0917.42.9231.16 (A-C**)30.82(B-C**)26.94
average13.053.0036.84(A-B*, A-C**)34.82 (B-C**)31.43
Tab.3  Comparison of the removal of TP in three modes
Fig.4  Change of TP concentration in three modes
Fig.5  Root morphologies of cold-seasonal plants used in model A: (a) ; (b) ; (c) ; (d)
Fig.6  Internal structures of roots of cold-seasonal plants used in model A: (a); (b) ; (c) ; (d)
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