131
Once the sophisticated water force resistance of the two-chamber bioreactor has
been constructed, the bioreactor is to be connected into biowaste chamber in order
to collect the biowaste into the shut separation chamber into the basement. The
other chamber is to be connected with the separated wastewater for the process of
treatment of primary, secondary, and tertiary mechanism and then implemented into
UV application to disinfect wastewater. The UV application and filtration constitute
the simplest way of treating wastewater involving disinfection (DIS) system in
which one fills a detention chamber with water and exposes it to full UV light for a
few hours (Fig. 7.1). Once the wastewater temperature hits 50 °C due to the subject
of UV light of approximately 320 nm, it functions immediately to kill all bacteria,
viruses, and molds and disinfects water completely through bacteriological disinfection process.
This treatment mechanism removes nearly 100% microorganisms and other contaminants from the wastewater effluent which could be used for local gardening.
Then, the other product sludge (human feces including domestic waste) in another
chamber of the bioreactor is being conducted for disinfection process in situ into an
anaerobic chamber (Fig. 7.2). This is the conversion mechanism performed by electrochemical filters of activated carbon nanotubes (CNT), which has the capability to
electrolyze and oxidize pollutants in the anode actively from the sludge [6, 16, 17]. It
is an advanced mechanism of biowaste disinfection mechanism that combines both
electrolysis and oxidation process into the anode of carbon nanotubes and catalyzes
the process of oxidation by H 2 O 2 into the cathode of carbon nanotubes. The function
here is to accelerate the rate of sludge treatment, and its active oxidation process into
the tank is being calculated and demonstrated a pathway that H 2 O 2 flow is very much
effective to disinfect the biowaste by the electrode and the cathode potential in order
to achieve the content of biowaste pH, flow rate, and oxygen dissolved into a normal
clean biomaterial form [18–20]. Hence, the maximum flow of H 2 O 2 is being accounted
for 1.38 mol/L/m
2
C by achieving CNT/L/m
2
with the implementation of cathode
Fig. 7.1 The application of photo-physics radiation in purifying water that illustrates that once
one applies UV light of 320 nm into wastewater, it begins to kill the microorganisms once the
temperature momentum hits 50 °C
Materials and Methods
Once the sophisticated water force resistance of the two-chamber bioreactor has
been constructed, the bioreactor is to be connected into biowaste chamber in order
to collect the biowaste into the shut separation chamber into the basement. The
other chamber is to be connected with the separated wastewater for the process of
treatment of primary, secondary, and tertiary mechanism and then implemented into
UV application to disinfect wastewater. The UV application and filtration constitute
the simplest way of treating wastewater involving disinfection (DIS) system in
which one fills a detention chamber with water and exposes it to full UV light for a
few hours (Fig. 7.1). Once the wastewater temperature hits 50 °C due to the subject
of UV light of approximately 320 nm, it functions immediately to kill all bacteria,
viruses, and molds and disinfects water completely through bacteriological disinfection process.
This treatment mechanism removes nearly 100% microorganisms and other contaminants from the wastewater effluent which could be used for local gardening.
Then, the other product sludge (human feces including domestic waste) in another
chamber of the bioreactor is being conducted for disinfection process in situ into an
anaerobic chamber (Fig. 7.2). This is the conversion mechanism performed by electrochemical filters of activated carbon nanotubes (CNT), which has the capability to
electrolyze and oxidize pollutants in the anode actively from the sludge [6, 16, 17]. It
is an advanced mechanism of biowaste disinfection mechanism that combines both
electrolysis and oxidation process into the anode of carbon nanotubes and catalyzes
the process of oxidation by H 2 O 2 into the cathode of carbon nanotubes. The function
here is to accelerate the rate of sludge treatment, and its active oxidation process into
the tank is being calculated and demonstrated a pathway that H 2 O 2 flow is very much
effective to disinfect the biowaste by the electrode and the cathode potential in order
to achieve the content of biowaste pH, flow rate, and oxygen dissolved into a normal
clean biomaterial form [18–20]. Hence, the maximum flow of H 2 O 2 is being accounted
for 1.38 mol/L/m
2
C by achieving CNT/L/m
2
with the implementation of cathode
Fig. 7.1 The application of photo-physics radiation in purifying water that illustrates that once
one applies UV light of 320 nm into wastewater, it begins to kill the microorganisms once the
temperature momentum hits 50 °C
Materials and Methods