Abstract

Treatment wetlands can reduce nitrogen (N) pollution in waterways. However, the shortage of information on their cost-effectiveness has resulted in their relatively slow uptake in tropical and subtropical Australia, including the catchments of the Great Barrier Reef and Moreton Bay. We assessed the performance of constructed treatment wetlands (CW) and vegetated drains (VD) that treat agricultural runoff, and of sewage treatment plant wetlands (STPW), which polish treated effluent. Treatment performance was estimated as changes in concentration (dissolved inorganic nitrogen, DIN, and total nitrogen, TN; mg L−1) and annual load reductions (kg N ha−1 yr−1). We calculated their cost-effectiveness by comparing their N removal against the costs incurred in their design, construction, and maintenance. Overall, CWs and VDs reduced DIN concentrations by 44% (0.52 to 0.29 mg L−1), and STPW reduced them by 91% (2.3 to 0.2 mg L−1); STPWs also reduced TN concentrations by 72%. The efficiency varied among sites, with the best performing CWs and VDs being those with relatively high inflow concentrations (>0.2 mg L−1 of DIN, >0.7 mg L−1 of TN), low suspended solids, high vegetation cover and high length: width ratio. These high performing CWs and VDs removed N for less than USD 37 kg−1 DIN (AUD 50 kg−1 DIN), less than the end-of-catchment benchmark for the Great Barrier Reef of USD 110 kg−1 DIN (AUD 150 kg−1 DIN). When adequately located, designed, and managed, treatment wetlands can be cost-effective and should be adopted for reducing N in tropical and subtropical Australia.

Highlights

  • We evaluated cost-effectiveness at the site scale (e.g., [19,20]), with no adjustments for dissolved inorganic nitrogen (DIN)

  • constructed treatment wetlands (CW) and vegetated drains (VD) reduced DIN concentrations by 44%, from 0.52 to 0.29 mg L−1, and sewage treatment plant wetlands (STPW) reduced them by 91% from 2.3 to 0.2 mg L−1 (Figures 2 and 3)

  • Treatment wetlands in tropical and subtropical Australia analysed in this metaanalysis removed DIN and TN from the water column when they complied with certain characteristics

Read more

Summary

Introduction

Nitrogen (N) pollution in waterways is one of the most significant environmental challenges of our times, threatening the wellbeing of humanity [1]. More than a century ago, the discovery of artificial N fixation (the Haber–Bosch process) paved the way to industrial fertiliser manufacture, allowing for large-scale food production [2]. Fossil fuel combustion has contributed to elevated levels of reactive N in the atmosphere [3,4]. The increase in N in waterways due to agricultural and urban runoff, atmospheric deposition, and sewage discharge has caused large scale degradation of aquatic ecosystems [4]

Objectives
Methods
Discussion
Conclusion

Talk to us

Join us for a 30 min session where you can share your feedback and ask us any queries you have

Schedule a call

Disclaimer: All third-party content on this website/platform is and will remain the property of their respective owners and is provided on "as is" basis without any warranties, express or implied. Use of third-party content does not indicate any affiliation, sponsorship with or endorsement by them. Any references to third-party content is to identify the corresponding services and shall be considered fair use under The CopyrightLaw.