Task 3: Optimization of IETS (CO3, PO3)
Propose the mass balance for each unit operation to comply with Standard A, IER2009. Selection on percentage removal must be cited from valid references
Based on the proposed mass balance, propose the upgrading of IETS based on the optimization of IETS treatment processes (e.g chemical dosage, the need of additional instrument, bacteria, etc.) and performance monitoring frequency based on parameters available at each of unit operation to achieve compliance of Standard A. Your proposal should also consider the analysis on preventive action on IETS problem as your explanation in Task 2
Propose the Block Flow Diagram inclusive the summary of proposed mass balance for overall unit operation.
Propose the Process Flow Diagram (PFD) of IETS (inclusive pump, compressor, blower, etc.)
Proposed Answer Task 3
Below will be provide a calculation of mass balance of every unit operation with upgraded IETS. Summary of IECS data for incoming wastewater from table 1 will be used with addition of flocculation solution into the flocculation tank which is by adding 0.1% of H2O2 with oxygenation of 30 – 40% in wastewater level, pH of 7.7 and temperature of 19oC. This method can reduce the Ammoniacal Nitrogen up to 80% (Jóźwiakowski et al., 2017), BOD5 up to 90% (Jóźwiakowski et al., 2017), COD up to 58% (Houtmeyers et al., 1977). Since the parameters such as pH and temperature in IETS in company M are different from the stated value, therefore the percentage removal will be lower than in the cited values. Inlet of 3m3/hr with continuous flow will be used for mass balance calculation
Mass Balance of each unit operations:
Collection Pit
Collection Pit
Assumptions:
No parameter changes during this process
Inlet of 3m3/hr with 24hours flow of incoming wastewater.
Summary table in collection pit process
Parameter
|
Proposed removal percent (%)
|
Value
|
Inlet
|
Outlet
|
pH
|
-
|
5.6
|
5.6
|
BOD5, mg/L
|
-
|
500
|
500
|
COD, mg/L
|
-
|
1500
|
1500
|
TSS, mg/L
|
-
|
200
|
200
|
NH4N, mg/L
|
-
|
30
|
30
|
Equalization Tank
Equalization Tank
Assumptions:
Inlet is from outlet collection pit
Only helps to regulate and steady the flowrate of wastewater.
No parameter changes
Summary table for equalization process
Parameter
|
Proposed removal percent (%)
|
Value
|
Inlet
|
Outlet
|
pH
|
-
|
5.6
|
5.6
|
BOD5, mg/L
|
-
|
500
|
500
|
COD, mg/L
|
-
|
1500
|
1500
|
TSS, mg/L
|
-
|
200
|
200
|
NH4N, mg/L
|
-
|
30
|
30
|
Coagulation Tank
Coagulation Tank
Coagulant solution
Assumptions:
Inlet from outlet of equalization tank.
FeCl3 with pH of 1.8, 200mg/L of concentration dose
COD and TSS removal is up to 60% and 91% respectively (Abu Bakar & Abdul Halim, 2013).
pH value outlet decreased to 5.2.
Summary table for coagulation process
Parameter
|
Proposed removal percent (%)
|
Value
|
Inlet
|
Outlet
|
pH
|
-
|
5.6
|
5.2
|
BOD5, mg/L
|
-
|
500
|
500
|
COD, mg/L
|
40
|
1500
|
900
|
TSS, mg/L
|
60
|
200
|
80
|
NH4N, mg/L
|
-
|
30
|
30
|
Calculation:
COD concentration
COD outlet stream:
COD =
COD = 900
Mass loading of COD
Inlet stream = 3
Inlet stream = 108
Outlet stream = 108
Outlet stream = 64.8
TSS concentration
TSS outlet stream =
TSS outlet stream = 80
Mass loading of TSS
Inlet stream = 3
Inlet stream = 14.4
Outlet stream = 14.4 x
Outlet stream = 5.76
pH Adjustment Tank
NaOH solution
Assumptions:
pH value of wastewater increased from 5.2 to 7.1 with addition of NaOH solution at concentration of 0.02M (Tian et al., 2018).
Other parameters do not changes.
Summary table for pH adjustment process
Parameter
|
Proposed removal percent (%)
|
Value
|
Inlet
|
Outlet
|
pH
|
-
|
5.2
|
7.1
|
BOD5, mg/L
|
-
|
500
|
500
|
COD, mg/L
|
-
|
900
|
900
|
TSS, mg/L
|
-
|
80
|
80
|
NH4N, mg/L
|
-
|
30
|
30
|
Flocculation Tank
Flocculation Tank
H2O2 Solution
Assumptions:
Inlet will be from outlet of pH adjustment tank.
0.1% of Hydrogen Peroxide, H2O2 with oxygenation of 30 – 40% level will be added to the flocculation process.
BOD5 removal up to 90% (Jóźwiakowski et al., 2017).
COD removal up to 58% (Houtmeyers et al., 1977).
Removal of Ammoniacal Nitrogen up to 80% (Jóźwiakowski et al., 2017).
Parameter
|
Proposed removal percent (%)
|
Value
|
Inlet
|
Outlet
|
pH
|
-
|
5.2
|
7.1
|
BOD5, mg/L
|
65
|
500
|
175
|
COD, mg/L
|
40
|
900
|
540
|
TSS, mg/L
|
-
|
80
|
80
|
NH4N, mg/L
|
70
|
30
|
9
|
Calculation:
BOD5 concentration
BOD5 outlet stream:
BOD5 =
BOD5 = 175
Mass loading of BOD5
Inlet stream = 3
Inlet stream = 36
Outlet stream = 36
Outlet stream = 12.6
COD concentration
COD outlet stream:
COD =
COD = 540
Mass loading of COD
Inlet stream = 3
Inlet stream = 38.88
Outlet stream = 38.88
Outlet stream = 23.33
NH4N concentration
NH4N outlet stream:
NH4N =
NH4N = 9
Mass loading of NH4N
Inlet stream = 3
Inlet stream = 2.16
Outlet stream = 2.16
Outlet stream = 0.65
Primary Clarifier
Primary Clarifier
Assumptions:
Inlet wastewater is from outlet of flocculation tank.
BOD removal range of 25 – 40% (Tchobanoglous et al., 2014).
TSS removal range of 50 – 75% (Tchobanoglous et al., 2014).
Summary table for Primary Clarifier process
Parameter
|
Proposed removal percent (%)
|
Value
|
Inlet
|
Outlet
|
pH
|
-
|
7.1
|
7.1
|
BOD5, mg/L
|
30
|
175
|
122.5
|
COD, mg/L
|
-
|
540
|
540
|
TSS, mg/L
|
60
|
80
|
32
|
NH4N, mg/L
|
-
|
9
|
9
|
BOD5 concentration
BOD5 outlet stream:
BOD5 =
BOD5 = 122.5
Mass loading of BOD5
Inlet stream = 3
Inlet stream = 8.82
Outlet stream = 8.82
Outlet stream = 6.17
TSS concentration
TSS outlet stream =
TSS outlet stream = 32
Mass loading of TSS
Inlet stream = 3
Inlet stream = 5.76
Outlet stream = 5.76 x
Outlet stream = 2.3
Treated Water Holding Tank No. 01
Treated Water Holding Tank No. 01
Assumptions:
Inlet water is from outlet of Primary Clarifier tank.
No parameters will be changing during this process.
Summary table for Treated Water Holding Tank No.01 process
Parameter
|
Proposed removal percent (%)
|
Value
|
Inlet
|
Outlet
|
pH
|
-
|
7.1
|
7.1
|
BOD5, mg/L
|
-
|
122.5
|
122.5
|
COD, mg/L
|
-
|
540
|
540
|
TSS, mg/L
|
-
|
32
|
32
|
NH4N, mg/L
|
-
|
9
|
9
|
Aeration Tank
Aeration Tank
Assumptions:
Aeration tank inlet is from outlet of treated water holding tank no. 01.
BOD removal efficiency is up to 60% (Sikumaran et al., 2015).
COD removal efficiency is up to 58% (Sikumaran et al., 2015).
TSS removal efficiency is up to 80% (Sikumaran et al., 2015).
Parameter
|
Proposed removal percent (%)
|
Value
|
Inlet
|
Outlet
|
pH
|
-
|
7.1
|
7.1
|
BOD5, mg/L
|
45
|
122.5
|
67.38
|
COD, mg/L
|
42
|
540
|
313.2
|
TSS, mg/L
|
55
|
32
|
14.4
|
NH4N, mg/L
|
-
|
9
|
9
|
Summary of Aeration Tank process
BOD5 concentration
BOD5 outlet stream:
BOD5 =
BOD5 = 67.38
Mass loading of BOD5
Inlet stream = 3
Inlet stream = 4.85
Outlet stream = 4.85
Outlet stream = 2.67
COD concentration
COD outlet stream:
COD =
COD = 313.2
Mass loading of COD
Inlet stream = 3
Inlet stream = 38.88
Outlet stream = 38.88
Outlet stream = 22.55
TSS concentration
TSS outlet stream =
TSS outlet stream =
Mass loading of TSS
Inlet stream = 3
Inlet stream = 5.76
Outlet stream = 5.76 x
Outlet stream = 2.59
Secondary Clarifier
Secondary Clarifier
Assumptions:
Secondary clarifier inlet is from outlet of aeration tank.
BOD removal percent is up to 40% (Tchobanoglous et al., 2014).
TSS removal percent is up to 50% (Tchobanoglous et al., 2014).
Parameter
|
Proposed removal percent (%)
|
Value
|
Inlet
|
Outlet
|
pH
|
-
|
7.1
|
7.1
|
BOD5, mg/L
|
30
|
67.38
|
47.16
|
COD, mg/L
|
-
|
313.2
|
313.2
|
TSS, mg/L
|
40
|
14.4
|
8.64
|
NH4N, mg/L
|
-
|
9
|
9
|
Summary of Secondary Clarifier process
BOD5 concentration
BOD5 outlet stream:
BOD5 =
BOD5 = 47.16
Mass loading of BOD5
Inlet stream = 3
Inlet stream = 3.43
Outlet stream = 3.43
Outlet stream = 2.3
TSS concentration
TSS outlet stream =
TSS outlet stream =
Mass loading of TSS
Inlet stream = 3
Inlet stream =1.04
Outlet stream = 1.04 x
Outlet stream = 0.622
Treated Water Holding Tank No. 02
Treated Water Holding Tank No. 02
Assumptions:
Inlet water is from outlet of Secondary Clarifier tank.
No parameters will be changing during this process.
Parameter
|
Proposed removal percent (%)
|
Value
|
Inlet
|
Outlet
|
pH
|
-
|
7.1
|
7.1
|
BOD5, mg/L
|
-
|
47.16
|
47.16
|
COD, mg/L
|
-
|
313.2
|
313.2
|
TSS, mg/L
|
-
|
8.64
|
8.64
|
NH4N, mg/L
|
-
|
9
|
9
|
Summary table for Treated Water Holding Tank No. 02 process
Sand Filter
Sand Filter
Assumptions:
Inlet water is from outlet of treated water holding tank no. 02.
BOD, COD and TSS removal percent is up to 42%, 47% and 43% respectively (Saad et al., 2016).
pH value increase to 7.2 (Saad et al., 2016).
Parameter
|
Proposed removal percent (%)
|
Value
|
Inlet
|
Outlet
|
pH
|
-
|
7.1
|
7.2
|
BOD5, mg/L
|
35
|
47.16
|
30.65
|
COD, mg/L
|
38
|
313.2
|
194.18
|
TSS, mg/L
|
35
|
8.64
|
5.62
|
NH4N, mg/L
|
-
|
9
|
9
|
Summary of Sand Filter process
BOD5 concentration
BOD5 outlet stream:
BOD5 =
BOD5 = 30.65
Mass loading of BOD5
Inlet stream = 3
Inlet stream = 3.4
Outlet stream = 3.4
Outlet stream = 2.21
COD concentration
COD outlet stream:
COD =
COD = 194.18
Mass loading of COD
Inlet stream = 3
Inlet stream = 22.55
Outlet stream = 22.55
Outlet stream = 11.73
TSS concentration
TSS outlet stream =
TSS outlet stream =
Mass loading of TSS
Inlet stream = 3
Inlet stream = 0.622
Outlet stream = 0.622 x
Outlet stream = 0.40
Activated Carbon Filter
Assumptions:
Inlet water is from outlet of sand filter.
BOD and COD removal percent is up to 94% and 93% (Hami et al., 2007).
Parameter
|
Proposed removal percent (%)
|
Value
|
Inlet
|
Outlet
|
pH
|
-
|
7.2
|
7.1
|
BOD5, mg/L
|
80
|
30.65
|
6.13
|
COD, mg/L
|
80
|
194.18
|
38.84
|
TSS, mg/L
|
-
|
5.62
|
5.62
|
NH4N, mg/L
|
-
|
9
|
9
|
Summary of Activated Carbon process
BOD5 concentration
BOD5 outlet stream:
BOD5 =
BOD5 = 6.13
Mass loading of BOD5
Inlet stream = 3
Inlet stream = 2.21
Outlet stream = 2.21
Outlet stream = 0.44
COD concentration
COD outlet stream:
COD =
COD = 38.84
Mass loading of COD
Inlet stream = 3
Inlet stream =13.98
Outlet stream = 13.98
Outlet stream = 2.8
Final Discharge Value
Summary table for Final Discharge
Parameter
|
Proposed removal percent (%)
|
Value
|
Inlet
|
Outlet
|
pH
|
-
|
7.2
|
7.1
|
BOD5, mg/L
|
80
|
30.65
|
6.13
|
COD, mg/L
|
80
|
194.18
|
38.84
|
TSS, mg/L
|
-
|
5.62
|
5.62
|
NH4N, mg/L
|
-
|
9
|
9
|
Above is the full mass balance calculation of each operation units with upgraded of IETS. Inclusive of H2O2 with proper justification has shown in the flocculation tank process. Final discharge has been shown in above table to comply standard A.
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