Abstract

Denitrifying woodchip bioreactors are a practical nitrogen (N) mitigation technology but evaluating the potential for bioreactor phosphorus (P) removal is highly relevant given that (1) agricultural runoff often contains N and P, (2) very low P concentrations cause eutrophication, and (3) there are few options for removing dissolved P once it is in runoff. A series of batch tests evaluated P removal by woodchips that naturally contained a range of metals known to sorb P and then three design and environmental factors (water matrix, particle size, initial dissolved reactive phosphorus (DRP) concentration). Woodchips with the highest aluminum and iron content provided the most dissolved P removal (13±2.5 mg DRP removed/kg woodchip). However, poplar woodchips, which had low metals content, provided the second highest removal (12±0.4 mg/kg) when they were tested with P-dosed river water which had a relatively complex water matrix. Chemical P sorption due to woodchip elements may be possible, but it is likely one of a variety of P removal mechanisms in real-world bioreactor settings. Scaling the results indicated bioreactors could remove 0.40 to 13 g DRP/ha. Woodchip bioreactor dissolved P removal will likely be small in magnitude, but any such contribution is an added-value benefit of this denitrifying technology.

Highlights

  • Denitrifying woodchip bioreactors, woodchip-filled trenches where maintenance of anoxic conditions enhance denitrification, are a simple on-farm technology promoted for nitratenitrogen (NO3-N) treatment in agricultural drainage waters and effluents worldwide (Schipper et al 2010)

  • The 84% dissolved reactive P (DRP) concentration reduction by the field bioreactor woodchips was significantly greater than the concentration changes caused by the white oak and cypress (p = 0.006 and 0.005, respectively, for pairwise multiple comparison Tukey tests) and was not significantly different from the four other treatments

  • The significant differences in DRP concentrations over the batch tests demonstrated the possibility for woodchips to influence P dynamics in a bioreactor, both positively and negatively

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Summary

Introduction

Denitrifying woodchip bioreactors, woodchip-filled trenches where maintenance of anoxic conditions enhance denitrification, are a simple on-farm technology promoted for nitratenitrogen (NO3-N) treatment in agricultural drainage waters and effluents worldwide (Schipper et al 2010). Woodchips can obviously act as a physical filter to trap sediment and particulate P (Choudhury et al 2016; Sharrer et al 2016), but beyond this, woodchip bioreactors have provided dissolved reactive P (DRP) removal ranging from 0.01 to 0.88 g DRP/m3-day (Dougherty 2018; Hua et al 2016; Sharrer et al 2016; von Ahnen et al 2018) with Weigelhofer and Hein (2015) reporting removal as high as 166 g phosphate-P/m3-day for straw-filled bioreactors. Dissolved P load and concentration reductions by woodchips across bioreactor literature have been as high as >50% (Dougherty 2018; Hua et al 2016; Husk et al 2018), though most reported reductions are more moderate (≈10%; Goodwin et al 2015; Warneke et al 2011; Zoski et al 2013). While DRP removal has been observed across a variety of studies, P removal in woodchip bioreactors has not been systematically tested

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