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International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 05 Issue: 06 | June 2018 www.irjet.net p-ISSN: 2395-0072
© 2018, IRJET | Impact Factor value: 6.171 | ISO 9001:2008 Certified Journal | Page 209
Performance evolution of different MBBR media in wastewater treatment
Shriyesh Mane 1, Rohan Kotwal2, Sujit Mandave3, Nikita Landge4, Hema Kedari5,
Prof. Sachin Mane6
1,2,3,4,5,6 Savitribai Phule Pune University, D. Y. Patil College of Engineering, Akurdi, Pune, India
ABSTRACT: The moving bed biofilm reactor (MBBR) is a
biological wastewater treatment process in which
microorganisms grow as biofilm on suspended carriers.
Conventionally, MBBRs are mainly designed and optimized
based on the carrier surface area, neglecting the dynamic
relationship between carrier design, reactor operation and
biofilm characteristics, such as biofilm thickness and the
composition of the microbial community. This paper
evaluates performance of MBBR process for commercial
waste water. We have used three different types of MBBR
carriers viz. BI16, PP22, Mutag biochip 25TM. This study
also compares percentage of BOD removal for different types
of MBBR. The efficiency has been improved by improving the
surface area per unit volume of the carrier element. It is
suggested that the Moving Bed Biofilm Reactor technology
could be used an ideal and efficient option for the treatment
of domestic and industrial waste water, when the available
area is minimum.
Key Words: Wastewater treatment, moving bed biofilm
reactor (MBBR), biochemical oxygen demand (BOD),
Hydraulic retention time(HRT), Bio-film media, STP
INTRODUCTION
Water is one of the basic necessities of life. Wastewater has
to be treated efficiently. The capacity and effluent quality
of treatment plants must improve in order to meet the
increased wastewater load, caused by growing
populations. In addition to this, treatment plants often
need to be compact, odor-free and almost invisibly
incorporated into the city environment. In the recent year,
the treatment of waste water is considered to be very
essential before its discharge to the environment, as it
needs public health protection from water borne diseases,
environmental protection of our land and water. The
waste water contains about 99.7% to 99.9 % liquid waste
and 0.1 % to 0.3 %of solid waste and millions of micro-
organisms. The organic solid which can be undergo
decomposition by micro-organism will fix the
characteristics of the sewage and measured in term of BOD
(biochemical oxygen demand in mg/lit). Hence the organic
solids and inorganic solids are to be removed by suitable
treatment technologies.
The moving bed biofilm reactor (MBBR) is a biological
wastewater treatment process in which microorganisms
grow as biofilm on suspended carriers. This keeps check of
BOD, COD, pH and many other parameters that would
affect the quality of wastewater. MBBR process can be
used effectively to treat water from lower concentration to
higher concentration. This process promotes suspended
growth as well as attached growth. Carriers are used here
that helps bio-degradation of organic matter in
wastewater, with the help of microbial bio-film that grows
on its surface. Aeration system is used for continuous
suspension of carriers. This process uses carriers of
different size and shapes, covering different surface area,
having different potential to form bio-film. Over last few
years there has been a growing interest in biofilm process
of wastewater treatment. There are several reasons for the
fact that biofilm process more and more often are being
favored such as:
 The treatment plant requires less space.
 The final treatment result is less dependent on
biomass separation since the biomass concentration to
be separated is at least 10 times lower.
 The attached biomass become more specialized (high
concentration of relevant organism) at a given point in
the process train, because there is no sludge return.
The desired objective of this paper is to investigate the
reactor performance with respect to different size and
shape of the carrier and HRT, i.e. 4hrs and 12hrs.
I. OBJECTIVE
• To analyze the performance of different carriers of
MBBR in waste water treatment.
o By changing aeration period
o By changing the shape and size of carrier.
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 05 Issue: 06 | June 2018 www.irjet.net p-ISSN: 2395-0072
© 2018, IRJET | Impact Factor value: 6.171 | ISO 9001:2008 Certified Journal | Page 210
II. PROPOSED SETUP
1. Experimental Set-up
The moving bed biofilm reactor(MBBR) technology is an
attached growth biological treatment process based on a
continuously operating, non-clogging biofilm reactor with
low head loss, a high specific biofilm surface area, and no
requirement for backwashing. MBBR is often designed as
aerobic system. Sample will collected from STP plant
which is located in our college campus and its parameters
will be evaluated prior to treatment. Dimension of tank is
36*12*18. The moving bed biofilm reactor (MBBR) setup
proposed for this study will be made up of plastic
containing two compartments. The inlet arrangement
given at top of tank. The outlet is provided at lower level
than inlet. The proposed experimental set-up for moving
bed biofilm can be made as shown in figure.
Fig1 : Experimental setup
Aerator:
Fish tank aerator is used to provide the necessary amount
of air required by the bacterial to survive and to make the
treatment process aerobic.
For waste water treatment in lab scale model, the fish tank
aerator of 3.5 – 5 lit/min is used for aeration.
Fig2 : Blower (Aerator)
Types of MBBR carrier used are:
Fig3 : Mutag biochip 25TM Fig4: BI16
Fig5: PP22
2. Process Description:-
Here we have carried out a laboratory scale study by
conducting a series of experiments using different size and
shape of MBBR carriers to treat sewage water of an
educational complex. Experimental set-up was constructed
and MBBR media(carrier) were placed into suspended
state, maintained by continuous aeration flow. HRT of 4hrs
and 12hrs was maintained to treat the water.
The MBBR process uses floating plastic carriers within the
aeration tank to increase the amount of microorganism to
treat the wastewater. this microorganism consumes
organic material the carrier provides increased surface
area for biological microorganisms to grow in the aeration
tank. The media will be in continuous suspension from the
aeration system that adds oxygen at the bottom of the
aeration tank. After treatment final treated effluent will be
taken outside through outlet.
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 05 Issue: 06 | June 2018 www.irjet.net p-ISSN: 2395-0072
© 2018, IRJET | Impact Factor value: 6.171 | ISO 9001:2008 Certified Journal | Page 211
The process followed is as follows:
Fig6: Process Flowchart
III. RESULTS
1. Characteristics of influent:
pH 6.5
Color Blueish black
BOD 205.8
2. Characteristics of effluent:
Sr. Name of
carrier
HRT BOD Efficiency
1 BI16 4 hrs. 62.1 69.82%
12 hrs. 46.5 77.29%
2 PP22 4 hrs. 78.8 62.13%
12 hrs. 58.5 71.32%
3 Mutag
biochip
25TM
4 hrs. 54.2 75.12%
12 hrs. 32.1 84.40%
The performance evolution of MBBR was studied for the
different HRT values i.e. 4hrs and 12hrs. While evaluating
the performance BOD parameter were analyzed.
Media 1- BI16
The micro-organisms present in the wastewater uses the
atmospheric oxygen for their survival. The lack of oxygen
leads to the decrease in the removal efficiency. The BOD
removal efficiencies under constant aeration flow rate for
the retention time of 4 hrs. and 12 hrs. is seen up to
69.82% and 77.29% respectively. The BOD removal
efficiency is shown as below.
Media 2-PP22
The micro-organisms present in the wastewater uses the
atmospheric oxygen for their survival. The lack of oxygen
leads to the decrease in the removal efficiency. The BOD
removal efficiencies under constant aeration flow rate for
the retention time of 4 hrs and 12 hrs is seen up to 62.30%
and 71.32% respectively. The BOD removal efficiency is
shown as below.
Media 3- Mutag biochip 25TM
The micro-organisms present in the wastewater uses the
atmospheric oxygen for their survival. The lack of oxygen
leads to the decrease in the removal efficiency. The BOD
removal efficiencies under constant aeration flow rate for
the retention time of 4 hrs and 12 hrs. is seen up to
75.12% and 84.40% respectively. The BOD removal
efficiency is shown as below.
65
70
75
80
4 12
Removal efficiency
removal
efficiency
55
60
65
70
75
4 12
Removal efficiency
removal
efficiency
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 05 Issue: 06 | June 2018 www.irjet.net p-ISSN: 2395-0072
© 2018, IRJET | Impact Factor value: 6.171 | ISO 9001:2008 Certified Journal | Page 212
Comparison between BOD efficiency:
IV. CONCLUSION
The characteristics of the wastewater of have been
obtained from the test conducted in laboratory. according
to the observed value of various characteristics, it is seen
that the wastewater has potential to pollute the water
body considerably if disposal without treatment. It is
essential to reduce the pollutant contains of wastewater
for its safe disposal to water body under permissible limits
specified by BIS.
The research study highlights the performance of different
type of MBBR reactor. There are two parameters are
studied to achieve the desired objectives suggested as per
the standards. It is seen that the HRT has the greater
impact on the cost of operation as well as maintenance.
The carrier circulation is affected due to flow rate. As
retention time decreases the flow rate increases which
lead to rapid circulation of carriers.
1.The MBBR technique is suitable for the BOD removal
efficiently.
2. The MBBR technique gives the more efficiency than
other conventional method.
V. REFERENCES
[1] PICULELL,M.A.R.I.A.(2016). “ New Dimensions Of
Moving Bed Biofilm Carriers: Influence of biofilm
thickness and control possibilities”, Lund: Department
Of Chemical Engineering, Lund University
[2] H. Ødegaard “ The Moving Bed Biofilm Reactor”, Water
Environmental engineering And Reuse of Water
Hokkaido press P 250-3.5
[3] Hallvard Ødegaard “ Advanced compact waste
treatment based on coagulation and moving bed
biofilm processes”, faculty of civil and
environmental,Norway University of science and
technology (NTNU),N-7491 Trondheim,norway
[4] Daniel Vieira Minegatti De Olivrira, Marcio Dias
Rabelo, Yuri Nascimento Nariyoshi:- Evaluation of a
MBBR (moving bed biofilm reactor) pilot plant for
treatment of pulp and paper mill wastewater”,
International Journal Of Environmental Monitoring
And Analysis 2014; 2(4): 220-225
[5] Pal shailesh R, Dr. Dipak S.Vyas , Arti N pamnani “
STUDY THE EFFICIENCY OF MOVING BED BIOFILM
REACTOR (MBBR) FOR DAIRY WASTEWATER
TREATMENT “, Voi-2 Issue -3 2016 IJARIIE-ISSN(0)-
2395-4396
[6] K.Vaidhegil P. Sandhiya M. Santhiya “ Moving Bed
Biofilm Reactor- Anew Perspective In Pulp and Paper”,
waste Water Treatment K.Vaidhegiet al. int. Journal of
Engineering Research and Application ISSN :2248-
9622,Vol.6, Issue 6,(Part-4) June2016, pp.09-13
[7] Waste Water Engineering (Treatment , Disposal &
Reuse )-Metcalf & Eddy.
[8] Bruce E.Rittmann Environmental Biotechnology in
Water and Wastewater Teatment Journal
Environmental Engineering Vol.136(2010) 348-353
70
75
80
85
90
4 12
Removal efficiency
removal
efficiency
0
10
20
30
40
50
60
70
80
90
media 1 media 2 media 3
4hrs
12hrs

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IRJET- Performance Evolution of different MBBR Media in Waste Water Treatment.

  • 1. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 05 Issue: 06 | June 2018 www.irjet.net p-ISSN: 2395-0072 © 2018, IRJET | Impact Factor value: 6.171 | ISO 9001:2008 Certified Journal | Page 209 Performance evolution of different MBBR media in wastewater treatment Shriyesh Mane 1, Rohan Kotwal2, Sujit Mandave3, Nikita Landge4, Hema Kedari5, Prof. Sachin Mane6 1,2,3,4,5,6 Savitribai Phule Pune University, D. Y. Patil College of Engineering, Akurdi, Pune, India ABSTRACT: The moving bed biofilm reactor (MBBR) is a biological wastewater treatment process in which microorganisms grow as biofilm on suspended carriers. Conventionally, MBBRs are mainly designed and optimized based on the carrier surface area, neglecting the dynamic relationship between carrier design, reactor operation and biofilm characteristics, such as biofilm thickness and the composition of the microbial community. This paper evaluates performance of MBBR process for commercial waste water. We have used three different types of MBBR carriers viz. BI16, PP22, Mutag biochip 25TM. This study also compares percentage of BOD removal for different types of MBBR. The efficiency has been improved by improving the surface area per unit volume of the carrier element. It is suggested that the Moving Bed Biofilm Reactor technology could be used an ideal and efficient option for the treatment of domestic and industrial waste water, when the available area is minimum. Key Words: Wastewater treatment, moving bed biofilm reactor (MBBR), biochemical oxygen demand (BOD), Hydraulic retention time(HRT), Bio-film media, STP INTRODUCTION Water is one of the basic necessities of life. Wastewater has to be treated efficiently. The capacity and effluent quality of treatment plants must improve in order to meet the increased wastewater load, caused by growing populations. In addition to this, treatment plants often need to be compact, odor-free and almost invisibly incorporated into the city environment. In the recent year, the treatment of waste water is considered to be very essential before its discharge to the environment, as it needs public health protection from water borne diseases, environmental protection of our land and water. The waste water contains about 99.7% to 99.9 % liquid waste and 0.1 % to 0.3 %of solid waste and millions of micro- organisms. The organic solid which can be undergo decomposition by micro-organism will fix the characteristics of the sewage and measured in term of BOD (biochemical oxygen demand in mg/lit). Hence the organic solids and inorganic solids are to be removed by suitable treatment technologies. The moving bed biofilm reactor (MBBR) is a biological wastewater treatment process in which microorganisms grow as biofilm on suspended carriers. This keeps check of BOD, COD, pH and many other parameters that would affect the quality of wastewater. MBBR process can be used effectively to treat water from lower concentration to higher concentration. This process promotes suspended growth as well as attached growth. Carriers are used here that helps bio-degradation of organic matter in wastewater, with the help of microbial bio-film that grows on its surface. Aeration system is used for continuous suspension of carriers. This process uses carriers of different size and shapes, covering different surface area, having different potential to form bio-film. Over last few years there has been a growing interest in biofilm process of wastewater treatment. There are several reasons for the fact that biofilm process more and more often are being favored such as:  The treatment plant requires less space.  The final treatment result is less dependent on biomass separation since the biomass concentration to be separated is at least 10 times lower.  The attached biomass become more specialized (high concentration of relevant organism) at a given point in the process train, because there is no sludge return. The desired objective of this paper is to investigate the reactor performance with respect to different size and shape of the carrier and HRT, i.e. 4hrs and 12hrs. I. OBJECTIVE • To analyze the performance of different carriers of MBBR in waste water treatment. o By changing aeration period o By changing the shape and size of carrier.
  • 2. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 05 Issue: 06 | June 2018 www.irjet.net p-ISSN: 2395-0072 © 2018, IRJET | Impact Factor value: 6.171 | ISO 9001:2008 Certified Journal | Page 210 II. PROPOSED SETUP 1. Experimental Set-up The moving bed biofilm reactor(MBBR) technology is an attached growth biological treatment process based on a continuously operating, non-clogging biofilm reactor with low head loss, a high specific biofilm surface area, and no requirement for backwashing. MBBR is often designed as aerobic system. Sample will collected from STP plant which is located in our college campus and its parameters will be evaluated prior to treatment. Dimension of tank is 36*12*18. The moving bed biofilm reactor (MBBR) setup proposed for this study will be made up of plastic containing two compartments. The inlet arrangement given at top of tank. The outlet is provided at lower level than inlet. The proposed experimental set-up for moving bed biofilm can be made as shown in figure. Fig1 : Experimental setup Aerator: Fish tank aerator is used to provide the necessary amount of air required by the bacterial to survive and to make the treatment process aerobic. For waste water treatment in lab scale model, the fish tank aerator of 3.5 – 5 lit/min is used for aeration. Fig2 : Blower (Aerator) Types of MBBR carrier used are: Fig3 : Mutag biochip 25TM Fig4: BI16 Fig5: PP22 2. Process Description:- Here we have carried out a laboratory scale study by conducting a series of experiments using different size and shape of MBBR carriers to treat sewage water of an educational complex. Experimental set-up was constructed and MBBR media(carrier) were placed into suspended state, maintained by continuous aeration flow. HRT of 4hrs and 12hrs was maintained to treat the water. The MBBR process uses floating plastic carriers within the aeration tank to increase the amount of microorganism to treat the wastewater. this microorganism consumes organic material the carrier provides increased surface area for biological microorganisms to grow in the aeration tank. The media will be in continuous suspension from the aeration system that adds oxygen at the bottom of the aeration tank. After treatment final treated effluent will be taken outside through outlet.
  • 3. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 05 Issue: 06 | June 2018 www.irjet.net p-ISSN: 2395-0072 © 2018, IRJET | Impact Factor value: 6.171 | ISO 9001:2008 Certified Journal | Page 211 The process followed is as follows: Fig6: Process Flowchart III. RESULTS 1. Characteristics of influent: pH 6.5 Color Blueish black BOD 205.8 2. Characteristics of effluent: Sr. Name of carrier HRT BOD Efficiency 1 BI16 4 hrs. 62.1 69.82% 12 hrs. 46.5 77.29% 2 PP22 4 hrs. 78.8 62.13% 12 hrs. 58.5 71.32% 3 Mutag biochip 25TM 4 hrs. 54.2 75.12% 12 hrs. 32.1 84.40% The performance evolution of MBBR was studied for the different HRT values i.e. 4hrs and 12hrs. While evaluating the performance BOD parameter were analyzed. Media 1- BI16 The micro-organisms present in the wastewater uses the atmospheric oxygen for their survival. The lack of oxygen leads to the decrease in the removal efficiency. The BOD removal efficiencies under constant aeration flow rate for the retention time of 4 hrs. and 12 hrs. is seen up to 69.82% and 77.29% respectively. The BOD removal efficiency is shown as below. Media 2-PP22 The micro-organisms present in the wastewater uses the atmospheric oxygen for their survival. The lack of oxygen leads to the decrease in the removal efficiency. The BOD removal efficiencies under constant aeration flow rate for the retention time of 4 hrs and 12 hrs is seen up to 62.30% and 71.32% respectively. The BOD removal efficiency is shown as below. Media 3- Mutag biochip 25TM The micro-organisms present in the wastewater uses the atmospheric oxygen for their survival. The lack of oxygen leads to the decrease in the removal efficiency. The BOD removal efficiencies under constant aeration flow rate for the retention time of 4 hrs and 12 hrs. is seen up to 75.12% and 84.40% respectively. The BOD removal efficiency is shown as below. 65 70 75 80 4 12 Removal efficiency removal efficiency 55 60 65 70 75 4 12 Removal efficiency removal efficiency
  • 4. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 05 Issue: 06 | June 2018 www.irjet.net p-ISSN: 2395-0072 © 2018, IRJET | Impact Factor value: 6.171 | ISO 9001:2008 Certified Journal | Page 212 Comparison between BOD efficiency: IV. CONCLUSION The characteristics of the wastewater of have been obtained from the test conducted in laboratory. according to the observed value of various characteristics, it is seen that the wastewater has potential to pollute the water body considerably if disposal without treatment. It is essential to reduce the pollutant contains of wastewater for its safe disposal to water body under permissible limits specified by BIS. The research study highlights the performance of different type of MBBR reactor. There are two parameters are studied to achieve the desired objectives suggested as per the standards. It is seen that the HRT has the greater impact on the cost of operation as well as maintenance. The carrier circulation is affected due to flow rate. As retention time decreases the flow rate increases which lead to rapid circulation of carriers. 1.The MBBR technique is suitable for the BOD removal efficiently. 2. The MBBR technique gives the more efficiency than other conventional method. V. REFERENCES [1] PICULELL,M.A.R.I.A.(2016). “ New Dimensions Of Moving Bed Biofilm Carriers: Influence of biofilm thickness and control possibilities”, Lund: Department Of Chemical Engineering, Lund University [2] H. Ødegaard “ The Moving Bed Biofilm Reactor”, Water Environmental engineering And Reuse of Water Hokkaido press P 250-3.5 [3] Hallvard Ødegaard “ Advanced compact waste treatment based on coagulation and moving bed biofilm processes”, faculty of civil and environmental,Norway University of science and technology (NTNU),N-7491 Trondheim,norway [4] Daniel Vieira Minegatti De Olivrira, Marcio Dias Rabelo, Yuri Nascimento Nariyoshi:- Evaluation of a MBBR (moving bed biofilm reactor) pilot plant for treatment of pulp and paper mill wastewater”, International Journal Of Environmental Monitoring And Analysis 2014; 2(4): 220-225 [5] Pal shailesh R, Dr. Dipak S.Vyas , Arti N pamnani “ STUDY THE EFFICIENCY OF MOVING BED BIOFILM REACTOR (MBBR) FOR DAIRY WASTEWATER TREATMENT “, Voi-2 Issue -3 2016 IJARIIE-ISSN(0)- 2395-4396 [6] K.Vaidhegil P. Sandhiya M. Santhiya “ Moving Bed Biofilm Reactor- Anew Perspective In Pulp and Paper”, waste Water Treatment K.Vaidhegiet al. int. Journal of Engineering Research and Application ISSN :2248- 9622,Vol.6, Issue 6,(Part-4) June2016, pp.09-13 [7] Waste Water Engineering (Treatment , Disposal & Reuse )-Metcalf & Eddy. [8] Bruce E.Rittmann Environmental Biotechnology in Water and Wastewater Teatment Journal Environmental Engineering Vol.136(2010) 348-353 70 75 80 85 90 4 12 Removal efficiency removal efficiency 0 10 20 30 40 50 60 70 80 90 media 1 media 2 media 3 4hrs 12hrs