Published at : 16 Dec 2019
Volume : IJtech
Vol 10, No 8 (2019)
DOI : https://doi.org/10.14716/ijtech.v10i8.3477
Khansa Luqyana Hapsari | University of Indonesia |
Firyal Tharifa | University of Indonesia |
Setyo Sarwanto Moersidik | Universty of Indonesia |
Sandyanto Adityosulindro | Universitas Indonesia |
Cindy Rianti Priadi | Universitas Indonesia |
Process
instability often occurs in anaerobic digestion (AD) due to inhibitors,
such as the high sodium content in food waste. Recent studies have reported
that magnesium can reduce the sodium ion’s toxicity towards methanogens. This
study aimed to analyze the effect of magnesium addition to Volatile Solids
Destruction (VSD), Chemical Oxygen Demand (COD) reduction, and biogas
production in AD of food waste. The experiment consisted of two phases, the
control phase and the experimental phase, without and with MgSO4, respectively. The
control phase results were: average COD reduction, VSD, and methane yield up to
80.9%, 87.6%, 340 mL
CH4/gr VS/day, respectively. The experimental
phase results were: average COD reduction, VSD, and methane yield up to 78.5%,
83.9%, 125 mL CH4/gr
VS/day, respectively. Overall, the study’s results showed that
MgSO4 had a negative impact on VSD and methane yield. The addition
of MgSO4 seemed to cause instability in the AD system, which
resulted in a decrease in the VSD value and a decrease in the methane
concentration.
Biogas; COD; Inhibition; Methane; Solid waste; VSD
Waste management is a fundamental
process for finding solutions to the problems arising from waste produced by individuals
and industry (Pongrácz, 2002). Society’s awareness of environmental issues is
considered to drive the search for waste disposal methods that are alternatives
to landfills (Shukor et al., 2018). Anaerobic
digestion (AD) is a widely used domestic waste processing method that is able
to convert various biodegradable waste materials into energy (Wijayanti et al., 2018) through a biological
anaerobic process that converts organic matter into biogas and digestate (Lin et al., 2018). In comparison to other
aerobic technology, anaerobic processes, such as AD, offer several advantages,
including low energy use and low sludge production; moreover, the produced
biogas can function as an energy source. Furthermore, the anaerobic process
does not have a strong odor because the process is carried out in an enclosed
space (Abdel-Shafy &
Richardson, 1996).
However, operational problems, such as instability in the system and
fluctuating biogas productivity, are disadvantages of AD (Lin et al., 2018). Failure to maintain the balance between acid
bacteria and methanogen bacteria is known to be the main cause of instability
in the system (Demirel & Yenigün, 2002). Furthermore, various elements, such as sodium (Na), are believed
To counter Na
toxicity, a mechanism known as antagonism can be implemented (Kugelman & McCarty, 1965). Antagonism is achieved by the presence of
another cation that reduces the toxicity of other types of cations, which can reactivate enzymes that have been damaged due to an
excess amount of the toxic cation. This may induce a stimulatory effect from
one type of cation, which, in this case, is magnesium (Mg), which could act as
an antagonist cation against Na (Kugelman &
McCarty, 1965). The study
conducted by Bashir
and Matin (2004) found that
the handling of Na inhibition at a concentration of 9,000 mg/L can be done by
adding Mg, which can reduce the toxic effects of Na. Hence, in our study, we
further analyzed the effect of the addition of Mg on Na toxicity in anaerobic
waste treatment. Toward that end, we evaluated the following parameters:
Volatile Solids Destruction (VSD) and Chemical Oxygen Demand (COD)
reduction. Both VSD and COD reduction
represent the efficiency of the AD process in reducing organic matter,
depending on the methods and concentrations used in the process.
The increase in VSD is related to the increased production of
biogas (Anwar et al.,
2016). According
to Budiyono et al. (2013), in an
AD system, COD is consumed through microbial activity and is converted into
methane (CH4). Both of these parameters are important because they
represent the performance of the AD process.
The results of this experiment demonstrated that the addition of
MgSO4 did not improve the performance of the AD process. The
addition of a significant amount of MgSO4 caused
a significant decrease in VSD (p < 0.05), as seen in the VSD value of 83.9% ± 0.04% obtained in the experimental phase and
the VSD value of 87.6% ± 0.07% obtained in the control phase. Moreover, the
addition of MgSO4 caused a significant decrease in the CH4 yield (p < 0.05), as seen in the CH4 yield of 125±107.2 mL CH4/gr
VS/day obtained in the experimental phase and the CH4 yield of
339±156.5 mL CH4/gr VS/day
obtained in the control phase. However, in this experiment, the addition of MgSO4 did not significantly influence the efficiency of COD
reduction, as seen in the COD reduction of 78.5% ± 0.2% in the experimental
phase and the COD reduction of 80.9% ± 0.12% ??in the control phase. Further study on the synergistic effect
of MgSO4 must be analyzed in a complex food waste AD environment.
This research and its publication are supported by the Superior Applied Research Grant 2019 from the Higher Education and Research Ministry Indonesia (number NKB-1728/ UN2.R3.1/HKP.05.00/2019).
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