alexa Nutrients Removal Efficiency Assessment of Constructed Wetland for the Rural Domestic Wastewater Growing Distinct Species of Vegetation

ISSN: 2161-0525

Journal of Environmental & Analytical Toxicology

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Nutrients Removal Efficiency Assessment of Constructed Wetland for the Rural Domestic Wastewater Growing Distinct Species of Vegetation

Ittehad Hussain1, Xiwu Lu1*, Javid Hussain2, Raana Fahim1 and Stanislaus Tombe Venusto Lako1
1School of Energy and Environment, Department of Environmental Science and Engineering, Southeast University, Nanjing 210096, P.R. China
2Department of Environmental Science, Balochinstan University of Information Technology and Management Science, Quetta, Pakistan
*Corresponding Author: Xiwu Lu, School of Energy and Environment, Department of Environmental Science and Engineering, Southeast University, Nanjing 210096, P.R. China, Tel: +862583793022, Email: [email protected]

Received Date: Oct 08, 2018 / Accepted Date: Oct 18, 2018 / Published Date: Oct 25, 2018

Abstract

In this study, the performance of horizontal subsurface flow constructed wetland for the nutrients removal in rural domestic wastewater using different vegetation plants has been assessed with hydraulic loading rate 0.2 m·d-1 and hydraulic retention time 1.25 d. The system was built and operated for twelve weeks as a tertiary treatment after biological processes to improve the quality of effluents of rural sewage. Three different vegetation species i.e., Mustard, Celery and Watercress were selected and grown in the wetlands. The system exhibited high pollutants removal efficiencies as Mustard achieving 76.53%, 90.18%, 79.89%, 93.14% and 70.77%for TN, NO3-N, TP, NH4-N and TSS, while Celery showed 71.73%, 90.18%, 71.95%, 77.15% and 75.39% and Watercress presented removal efficiency as 73.41%, 93.64%, 80.95%, 86.69% and 81.91%, respectively. The concentrations of pollutants in all effluents of three different plants were lower than the Class 1A regulated values recommended by Chinese National Standards GB18918-2002. Horizontal subsurface flow constructed wetlands planted with Mustard, Celery and Watercress is a reasonable alternative method for the treatment of rural domestic wastewater.

Keywords: Nutrients; Removal; Vegetation species; Wastewater

Highlights

• Three different vegetation species i.e., Mustard, Celery and Watercress were selected and grown in the wetlands.

• The influent and effluent concentrations of total nitrogen (TN), total nitrate (NO3-N), total phosphorous (TP), ammonium (NH4-N) and total suspended solids (TSS) were analyzed and measured.

• The system exhibited high pollutants removal efficiencies.

• The concentrations of pollutants in all effluents of three different plants were lower than the Class 1A regulated values recommended by Chinese National Standards GB18918-2002.

Introduction

Water is an essential environmental factor to maintain the food supply and productive environment for the survival of human beings and other living organisms. Rapidly growing human population and economies have soared the demands of freshwater [1], Wastewater in developing countries is released to water bodies and aquatic habitants improperly and untreated that has resulted in devastating impacts on environment and human health [2], Many regions of the world are already facing water crisis, with about one billion people without having inadequate fresh and drinking water. In addition, more than 90% of infectious diseases in developing countries are caused and transmitted to human beings through polluted water [1]. The main sources of polluting water can be residential, commercial, industrial and agricultural activities. Wastewater must be treated to overcome its adverse effect on public health and ecosystem [3]. In developing countries, conventional treatment of wastewater may not be applicable for its costly expenses and installation. Therefore, reasonable and environment-friendly methods are needed for the treatment of wastewater [4]. Constructed wetlands have been significantly used since last years as an alternative method and considered as an appropriate technology for the treatment of waste water in small communities [5]. CWs are artificially designed systems consisting of medium like soil, sand and gravels and planted by plants tolerant to saturated environmental conditions [6], which offer efficient and attractive pollutants removal efficiency through physical, chemical, and biological mechanisms. Many of contaminants such as pathogens, organic materials, nutrients, and toxic heavy metals can be removed and minimized with the help of Constructed wetlands through filtration, sedimentation, coagulation, adsorption, plant uptakes and microbial transformation.

In Horizontal subsurface flow constructed wetlands (HFCWs), nutrients and organic matter are removed by aerobic bacteria attached to plant roots and porous media. Therefore, wetland plants have vital and effective role in the purification of wastewater [7]. The main objective of this study was aimed to improve constructed wetland system to overcome the pollution indicators (total nitrogen, total phosphorous, nitrate, ammonium nitrogen and total suspended solids and to experience the improvement of productive environment and economic growth of vegetations.

Materials and Methods

Experimental setup and design of HSF CW

The horizontal subsurface flow constructed wetland system was designed and operated at the Campus of Southeast University, New District, Wuxi city, Jiangsu province, P.R China, consisting total area 100 m2. The region has four distinct seasons having humid monsoon climate with ample rainfall and sunshine. The average annual temperature over last three decades (since 1982) is 16°C with 123 rainy days and average precipitation is 1121.7 mm [8]. Horizontal subsurface flow constructed wetland was established for the experimental work and the size of each bed was 2.5 m × 0.3 m × 0.5 m (length × width × height), made of concrete and lined with epoxy coatings. Each bed was packed with a supporting layer of 10 cm course Gravels, 5-10 cm clay, 10 cm small gravels and 5-10 cm cermasite stones (Figure 1). The wastewater was entered from distribution channel connected to wastewater tank with controlled flow. Three different species of vegetation plants were selected (Table 1). and grown in constructed wetland and selection was made on their easy availability in market and ability to climatic adaption. All beds were inspected on daily basis to avoid any obstruction in flow especially in inlet and outlet pipes that may be caused by suspended solids presented in wastewater. Panoramic view and plants’ growth conditions in HSF CWs during study duration are shown in Figure 1.

environmental-analytical-toxicology-schematic

Figure 1: Schematic diagram of HSF CWs and conditions of plants during experimental duration.

S #. Plant Name Scientific Name Used Name
1 Mustard  Brassica Brassica
2 Celery Apium Graveolens Apium
3 Watercress Nasturtium Officinale Nasturtium

Table 1: Selected vegetation plants for experimental work.

Setup operation and sampling

Wastewater from the residential area, restaurants and student’s dormitories in premises of Southeast University, Wuxi Campus was allowed to enter into wetland system after primary treatment. Three different beds were constructed, and each bed was planted with random vegetation plants as Brassica , Apium and Nasturtium (Table 1). Water samples were collected from inlet and outlet of the wetland beds in plastic bottles on weekly basis for evaluation performance and experimental work. Characteristics of wastewater are presented in Table 2.

Operational time (weeks) TN (mg/l) TP (mg/l) NO3-N (mg/l) NH4-N (mg/l) TSS (mg/l)
1 31.06 1.73 16.37 16.78 18
2 25.24 1.39 13.26 17.34 12
3 41.56 1.68 24.19 15.17 16
4 46.22 1.65 26.43 21.17 18
5 43.37 1.72 24.65 19.84 13
6 44.78 2.06 26.43 18.51 16
7 45 1.83 26.45 19.95 14
8 47.45 2.29 25.12 22.51 15
9 49.65 2.17 26.76 23.18 9
10 43.11 1.94 25.81 18.75 45
11 47.05 2.19 28.28 19.01 64
12 49.15 2.04 27.08 20.51 20
Average 45.29 2.03 25.84 21 23

Here, TN=total nitrogen, TP= total phosphorus, TSS=total suspended solids.

Table 2: Raw sewage characteristics during experimental duration at temperature 7.1 to 21.4°C.

Determination methods

Standard methods recommended by US Environmental Protection Agency (US EPA) were used for the determination of Nitrate (NO3-N), Total Nitrogen (TN), Total Phosphorous (TP), Ammonium (NH-N) and Total Suspended Solids (TSS) [9]. The following equation was used to calculate the TSS in water sample (mg/l).

TSS (mg/l)=((A-B) × 1000)/V

Where, A represent dried weight of residue and filter paper,

B=Weight of filter paper,

V=Wastewater sample used.

Whereas, Dissolved Oxygen and pH were measured by using DO Meter (DO200) and pH Meter (pH100) YSI, respectively.

Statistical analysis

Microsoft Excel (MS Office package-10) and Origin 9 (Origin Lab Corporation) were used for data analysis and nutrients removal variances.

Results and Discussion

Average experimental data for this study is shown in (Tables 2 and 3) for both inlets and outlets of three species of vegetations i.e., Mustard, Celery and Watercress. Almost all three species of plants offered significant increase in removal efficiencies for TN. Concentrations of TN were 76.53%, 71.73% 73.41% (Figures 2-4), whereas 79.89%, 71.95, 80.95% for TP (Figure 3). The efficiency for NO3-N and NH4-N achieved by Mustard, Celery and Watercress was 79.89%, 71.95%, 80.95% and 93.14%, 77.15%, 86.69%, respectively (Figures 5 and 6), while the removal efficiency for TSS by all these three species of plants i.e., Mustard, Celery and Watercress was 70.77%, 75.39% and 81.94%, respectively (Figure 6).

environmental-analytical-toxicology-durations

Figure 2: TN concentrations during twelve weeks of experimental durations.

environmental-analytical-toxicology-twelve

Figure 3: TP concentrations during twelve weeks of experimental durations.

environmental-analytical-toxicology-during

Figure 4: NO-N concentration during 12 weeks of experimental durations.

environmental-analytical-toxicology-experimental

Figure 5: NH4-N concentration during 12 weeks of experimental durations.

environmental-analytical-toxicology-concentration

Figure 6: TSS concentration during 12 weeks of experimental durations.

  Mustard Celery Watercress
Min Max Mean ± SD Min Max Mean ± SD Min Max Mean ± SD
TN 3.1 8.71 6.17 ± 0.2625 7.43 11.92 7.43 ± 0.1720 10.09 0.57 6.99 ± 0.1235
NO3-N 0.17 0.50 0.36 ± 0.123 0.31 6.24 2.58 ± 2.0483 0.09 2.68 1.20 ± 0.9244
NH4-N 1.52 6.64 4.34 ± 1.5283 0.69 3.50 7.20 ± 1.0107 0.22 5.06 2.12 ± 1.2986
TP 0.09 0.57 0.45 ± 0.1235 0.23 0.78 0.50 ± 0.1964 0.16 4.61 0.36 ± 1.5095
TSS 1.00 7.00 6.33 ± 2.0226 2.00 9.00 5.33 ± 2.7747 1.00 7.00 3.91 ± 1.7494

Table 3: Average values of effluents of the three different plants in HSFCW.

Nutrients have great and significant role in affecting plants growth in constructed wetland systems [10]. For the most favorable growth and uptake, each species of plant needs different amount of nutrients [11]. The efficiency assessment of horizontal subsurface flow constructed wetland was evaluated for twelve weeks under variable temperature ranging from 7.1 to 21.4°C. All three plants grew well when added with a mixture of NO3-N and NH4-N [12]. Brassica , A. graveolens and N. officinale were green, fresh, healthy and grew well in all beds under NO3-N/NH4-N ratio of 1:1, and increasing amounts of NO3-N subdued growth [13].

In constructed wetlands, nitrogen removal is occurred due the absorptions by the substrate, nitrification, volatilization and plant uptake [14]. Many researchers has observed, that mostly amount of NH4-N removal is occurred by microbial action sand little amount is removed through plant absorption in constructed wetlands [15], whereas most of the NH4-N is removed by volatilization on higher pH [16]. The processes of nitrification are affected by inorganic carbon source, alkalinity, dissolved oxygen, temperature, pH and NH4-N concentration [17]. NH-N uptake consumes high amount of oxygen than NO3-N. Ammonium breakdown takes place in the roots and sugar is delivered from leaves to roots after reaction, whereas NO3-N is conveyed to leaves and reduces to ammonium after it reacts with sugar [18]. Plants consumes more sugar at high respiration leaving less for NH4-N metabolism. Brassica , Apium greveleons and Nasturtium officinale in horizontal subsurface flow constructed wetland grew with well root system and strong oxygen transferring capabilities providing good aerobic environment around the root systems that prefer nitrifying bacteria and exceed NH4-N removal abilities. Roots and Rhizomes below the ground are critical for the nitrogen removal from wastewater. They provide nutrients and exudates to fuel the microorganisms [19]. Plant root system is a vital parameter to consider before choosing plants for constructed wetlands, because bigger root system can get up much amount of nutrients and thus increase the removal of nutrients.

Conclusion

The recent study presented the effect of three different species of plants in horizontal subsurface flow constructed wetland for the removal of pollutants in rural domestic wastewater. For different reasons, Brassica , Apium greveleons and Nasturtium officinale are efficient to get optimum nutrients (TN, TP, NO3-N, NH4-N and TSS) removal under variable temperature ranging from 7.1°C to 21.5°C using same media substrate. This study suggests its implementation to reduce the gap between food supplies and water needs and this will also boost the applications of constructed wetlands for the productive environment.

Acknowledgements

Our gratitude goes to Ministry of Environment, People Republic of China for its support, permitting this study and equipping laboratory facilities. This research was financially supported by National Science and Technology Major Project No. 2017ZX07202004.

References

Citation: Hussain I, Lu X, Hussain J, Fahim R, Lako STV (2018) Nutrients Removal Efficiency Assessment of Constructed Wetland for the Rural Domestic Wastewater Growing Distinct Species of Vegetation. J Environ Anal Toxicol 8: 588. DOI: 10.4172/2161-0525.1000588

Copyright: © 2018 Hussain I, et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.

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