Published July 2018 | Version v1
Journal article

Nitrous oxide emissions from near-zero water exchange brackish recirculating aquaculture systems

  • 1. Department of Environmental Hydrology and Microbiology, Zuckerberg Institute for Water Research, Blaustein Institutes for Desert Research, Ben-Gurion University of the Negev, Midreshet Ben-Gurion, 8499000 (Israel)

Description

Highlights: • Nitrification and denitrification in RAS water may cause significant N2O emissions. • Direct and potential N2O emissions from RAS compartments were quantified. • Overall N2O emissions of 885 mg/kg feed or 1.36 g/kg fish production were recorded. • Aquaculture N2O emittance account for 0.5% of global anthropogenic N2O emission The development of intensive recirculating aquaculture systems (RAS) with low water exchange has accelerated in recent years as a result of environmental, economic and other concerns. In these systems, fish are commonly grown at high density, 50 to 150 kg/m3, using high-protein (30%–60%) feeds. Typically, the RAS consists of a solid treatment and a nitrification unit; in more advanced RAS, there is an additional denitrification step. Nitrous oxide (N2O), a byproduct during nitrification and denitrification processes, is a potent greenhouse gas that destroys the ozone layer. The aim of this study was to measure and assess N2O emissions from a near-zero discharge land-based saline RAS. N2O flux was monitored from the RAS's fish tank, and moving-bed nitrification and activated-sludge (with intrinsic C source) denitrification reactors. N2O emission potential was also analyzed in the laboratory. N2O flux from the denitrification reactors ranged between 6.5 and 48 mg/day, equivalent to 1.27 ± 1.01% of the removed nitrate-N. Direct analysis from the fish tank and nitrification reactors could not be performed due to high aeration, which diluted the N2O concentration to below detection limits. Thus, its potential emission was estimated in the laboratory: from the fishponds, it was negligible; from the nitrification reactor, it ranged between 0.4 and 2.8% of the total ammonia-N oxidized. The potential N2O emission from the denitrification reactor was 3.72 ± 2.75% of the reduced nitrate-N, within the range found in the direct measurement. Overall, N2O emission during N transformation in a RAS was evaluated to be 885 mg/kg feed or 1.36 g/kg fish production, accounting for 1.23% of total N application. Consequently, it is estimated that N2O emission from aquaculture currently accounts for 2.4% of the total agricultural N2O emission, but will decrease to 1.7% by 2030.

Availability note (English)

Available from http://dx.doi.org/10.1016/j.scitotenv.2018.02.089

Additional details

Identifiers

DOI
10.1016/j.scitotenv.2018.02.089;
PII
S0048969718304790;

Publishing Information

Journal Title
Science of the Total Environment
Journal Volume
628
Journal Page Range
p. 603-610
ISSN
0048-9697
CODEN
STENDL

Optional Information

Copyright
Copyright (c) 2018 Elsevier B.V. All rights reserved.