Assessment of the performance of an anoxic-aerobic
microalgal-bacterial system treating digestate
Andr
es F. Torres-Franco
a, b, c
, Maribel Zuluaga
a, b, d
, Diana Hern
andez-Rold
an
a, b, d
,
Deborah Leroy-Freitas
a, b, c
, Cristian A. Sepúlveda-Mu
~
noz
a, b
, Saúl Blanco
e, f
,
C
esar R. Mota
c
, Raúl Mu
~
noz
a, b, *
a
Department of Chemical Engineering and Environmental Technology, Valladolid University, Dr. Mergelina, s/n., 47011, Valladolid, Spain
b
Institute of Sustainable Processes, Dr. Mergelina, s/n, 47011, Valladolid, Spain
c
Department of Sanitary and Environmental Engineering, Federal University of Minas Gerais, Belo Horizonte, 31270-010, Brazil
d
Faculty of Environmental Engineering UPAEP University, Puebla, 21 Sur 1103, Barrio de Santiago, 72410, Puebla, Mexico
e
University of Le on, Campus de Vegazana, 24071, Le on, Spain
f
Laboratory of Diatomology, Institute of Environment, Natural Resources and Biodiversity, La Serna 58, 24007, Le on, Spain
highlights graphical abstract
4 and 2-fold diluted digestate was
efficiently treated in an anoxic-
aerobic system.
Undiluted digestate treatment
inhibited nitrification and favored
NH
3
stripping.
Chlorella vulgaris and Proteobacteria
dominated the microalgal-bacterial
community.
Nutrients recovery as microalgal-
bacterial biomass was quantified via
mass balances.
article info
Article history:
Received 17 August 2020
Received in revised form
15 December 2020
Accepted 21 December 2020
Available online 29 December 2020
Handling Editor: Derek Muir
Keywords:
Microalgal-bacterial symbiosis
Digestate
Nitrification-denitrification
Microalgae
Photobioreactor
abstract
The performance of an anoxic-aerobic microalgal-bacterial system treating synthetic food waste diges-
tate at 10 days of hydraulic retention time via nitrification-denitrification under increasing digestate
concentrations of 25%, 50%, and 100% (v/v) was assessed during Stages I, II and III, respectively. The
system supported adequate treatment without external CO
2
supplementation since sufficient inorganic
carbon in the digestate was available for autotrophic growth. High steady-state Total Organic Carbon
(TOC) and Total Nitrogen (TN) removal efficiencies of 85e96% and 73e84% were achieved in Stages I and
II. Similarly, PO
3
4
-P removals of 81 ± 15% and 58 ± 4% were recorded during these stages. During Stage
III, the average influent concentrations of 815 ± 35 mg TOC$L
1
, 610 ± 23 mg TN$L
1
, and 46 ± 11 mg
PO
3
4
-P$L
1
induced O
2
limiting conditions, resulting in TOC, TN and PO
3
4
-P removals of 85 ± 3%,
73 ± 3%, and 28 ± 16%, respectively. Digestate concentrations of 25% and 50% favored nitrification-
denitrification mechanisms, whereas the treatment of undiluted digestate resulted in higher ammonia
volatilization and hampered nitrification-denitrification. In Stages I and II, the microalgal community was
dominated by Chlorella vulgaris and Cryptomonas sp., whereas Pseudoanabaena sp. was more abundant
during Stage III. Illumina sequencing revealed the presence of carbon and nitrogen transforming bacteria,
with dominances of the genera Gemmata, Azospirillum, and Psychrobacter during Stage I, II, and III,
respectively. Finally, the high settleability of the biomass (98% of suspended solids removal in the settler)
* Corresponding author. Department of Chemical Engineering and Environmental
Technology, Valladolid University, Dr. Mergelina, s/n., 47011, Valladolid, Spain.
E-mail address: mutora@iq.uva.es (R. Mu~ noz).
Contents lists available at ScienceDirect
Chemosphere
journal homepage: www.elsevier.com/locate/chemosphere
https://doi.org/10.1016/j.chemosphere.2020.129437
0045-6535/© 2020 Elsevier Ltd. All rights reserved.
Chemosphere 270 (2021) 129437
Chemosphere
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