Abstract

Herein, the progress of nitrate removal by a heterotrophic culture in a batch reactor and continuous-flow fixed-biofilm reactor was examined. Two batch experiments for nitrate reduction with acetate degradation using 250 mL batch reactors with acclimated denitrifying biomass were conducted. The experimental results indicated that the nitrate was completely reduced; however, the acetate remained at a concentration of 280 mg/L from initial nitrate concentration of 100 mg/L. However, the acetate was fully biodegraded by the denitrifying biomass at an initial nitrate concentration of 300 mg/L. To evaluate the biokinetic parameters, the concentration data of nitrate, nitrite, acetate, and denitrifying biomass from the batch kinetic experiments were compared with those of the batch kinetic model system. A continuous-flow fixed-biofilm reactor was used to verify the kinetic biofilm model. The removal efficiency of nitrate in the fixed-biofilm reactor at the steady state was 98.4% accompanied with 90.5% acetate consumption. The experimental results agreed satisfactorily with the model predictions. The modeling and experimental approaches used in this study could be applied in the design of a pilot-scale, or full-scale, fixed-biofilm reactor for nitrate removal in water and wastewater treatment plants.

Highlights

  • Nitrate-containing wastewater is often generated from manufacturing processes involving the production of fertilizers, explosives, pectin, cellophane and metals [1,2], which contains nitrate concentrations higher than 1000 mg NO3 −N/L [3]

  • The modeling and experimental approaches used in this study could be applied in the design of a pilot-scale, or full-scale, fixed-biofilm reactor for nitrate removal in water and wastewater treatment plants

  • Nitrate was first reduced to nitrite and the denitrifying biomass degraded nitrite as an electron acceptor and reduced it to other compounds (i.e., nitric oxide (NO), nitrous oxide (N2 O), and N2 )

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Summary

Introduction

Nitrate-containing wastewater is often generated from manufacturing processes involving the production of fertilizers, explosives, pectin, cellophane and metals [1,2], which contains nitrate concentrations higher than 1000 mg NO3 −N/L [3]. In addition to industrial activity, the nitrate contamination of ground and surface waters is associated with recirculating aquaculture systems (RAS). The nitrate concentration in RAS in the range of 100–500 mg/L was reported [4,5]. Ground and surface waters can be used as the water resource for the purposes of drinking, irrigation, and aquaculture. The removal of nitrate from ground and surface waters becomes a major concern because of human health risks related to methemoglobinemia; and the possibility of carcinogens in the stomach and intestines [8]. The World Health Organization (WHO) has set a nitrate concentration standard for drinking water of 11.3 mg NO3 –N/L in order to protect water resources and reduce hazards to human health

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