ce 428 -designactivated sludge system

4
CE 428 Water and Wastewater Treatment Design Dr. S. K. Ong Design of Completely Mixed Activated Sludge System Design a completely mixed activated sludge and secondary settling facility to treat 5.71 mgd (0.25 m 3 /s) of settled wastewater with 250 mg/L BOD 5 . The effluent is to have 20 mg/L of BOD 5 or less. Assume temperature at 20 o C. (i) Influent volatile suspended solids to reactor are negligible (ii) ratio of mixed liquor VSS (MLVSS) and mixed liquid suspended solids (MLSS) = 0.8 (iii) Return sludge concentration = 10,000 mg/L SS (iv) MLVSS = 3,500 mg/L in aeration tank (v) Design mean cell residence time c = 10 d (vi) Effluent contains 22 mg/L of biological solids, 65% is biodegradable (vii) BOD 5 = 0.68 BOD L (viii) Wastewater contains adequate nitrogen, phosphorus and trace nutrients for biological growth (ix) Peak hourly flow rate is 2.5 times the average flow rate 1. Estimate the concentration of soluble BOD 5 in the effluent using the following relationship Effluent BOD 5 = soluble BOD 5 + BOD 5 of effluent suspended solids (a) determine BOD 5 of the effluent suspended solids i. Biodegradable portion of effluent biological solids is 0.65(22 mg/L) = 14.3 mg/L ii. Ultimate BOD L of the biodegradable effluent solids is (14.3) (1.42 mg O 2 consumed/mg cell oxidized) = 20.3 mg/L iii. BOD 5 of effluent suspended solids = 20.3 0.68 = 13.8 mg/L (b) Effluent soluble BOD 5 escaping treatment is given by: 20 mg/L = S + 13.8 mg/L S = 6.2 mg/L 2. Treatment efficiency, E = (S o – S) 100/ S o Efficiency of soluble BOD 5 is (250 – 6.2) 100/250 = 97.5 %

Upload: 8925138229

Post on 04-Oct-2015

217 views

Category:

Documents


5 download

DESCRIPTION

12345

TRANSCRIPT

Design of Completely Mixed Activated Sludge System (adapted from Metcalf and Eddy)

CE 428 Water and Wastewater Treatment Design

Dr. S. K. Ong

Design of Completely Mixed Activated Sludge SystemDesign a completely mixed activated sludge and secondary settling facility to treat 5.71 mgd (0.25 m3/s) of settled wastewater with 250 mg/L BOD5. The effluent is to have 20 mg/L of BOD5 or less. Assume temperature at 20o C.

(i) Influent volatile suspended solids to reactor are negligible

(ii) ratio of mixed liquor VSS (MLVSS) and mixed liquid suspended solids (MLSS) = 0.8

(iii) Return sludge concentration = 10,000 mg/L SS

(iv) MLVSS = 3,500 mg/L in aeration tank

(v) Design mean cell residence time (c = 10 d

(vi) Effluent contains 22 mg/L of biological solids, 65% is biodegradable

(vii) BOD5 = 0.68 BODL(viii) Wastewater contains adequate nitrogen, phosphorus and trace nutrients for biological growth

(ix) Peak hourly flow rate is 2.5 times the average flow rate

1. Estimate the concentration of soluble BOD5 in the effluent using the following relationship

Effluent BOD5 = soluble BOD5 + BOD5 of effluent suspended solids

(a) determine BOD5 of the effluent suspended solids

i. Biodegradable portion of effluent biological solids is 0.65(22 mg/L) = 14.3 mg/L

ii. Ultimate BODL of the biodegradable effluent solids is (14.3)( (1.42 mg O2

consumed/mg cell oxidized) = 20.3 mg/L

iii. BOD5 of effluent suspended solids = 20.3 ( 0.68 = 13.8 mg/L

(b) Effluent soluble BOD5 escaping treatment is given by:

20 mg/L = S + 13.8 mg/L

S = 6.2 mg/L

2.Treatment efficiency, E = (So S) ( 100/ So

Efficiency of soluble BOD5 is (250 6.2) ( 100/250 = 97.5 %

Overall plant efficiency is (250 20) ( 100/250 = 92%

3.Compute reactor volume, use:

V = 1.24 million gallons or 4694 m3

Based on the sizes of aeration tank:

select two aeration tanks with depth of 6 m.

With a width to depth ratio of 1.0:1 to 2.2:1, select 1.5:1

Width = 6 m ( 1.5 = 9 m

Length = 4694/[2(9 ( 6)] = 43.5 mselect 45 m, add freeboard of 1 m

Volume of reactor = 45(9(6 = 2430 m34.HRT of reactor = (2430 m3) (2((264.17 gal/m3)/5.21 x 106 gal/d = 0.246 days = 5.9 hrs

5.Waste to be wasted each day to maintain sludge age of 10 days

= 170100 x 103 mg of MLVSS/day

= 1701 kg of MLVSS/day

orQwXw = 1701 (Q Qw)Xe

assume Q >> Qwthen= 1701 [(0.25 m3/s) (1000 L/m3(86400 s/d] (22 mg/L(0.8 MLVSS/MLSS/106 kg/mg

QwXw= 1701 380.16= 1321 kg MLVSS/day

Since Xw = 10,000 mg/L MLSS

In terms of MLVSS = 10,000 ( 0.8 = 8,000 mg/L MLVSS

Therefore Qw = 1321 (kg/day)/[8000 ( (kg/106 mg) ((1000L/m3)] = 165 m3/day or 0.0019 m3/s

(Q >> Qw, assumption is ok)

6. Recirculation rate

7. Oxygen requirements (no nitrification at 10 days SRT)

(a) compute the mass of BODL of the incoming wastewater that is converted to the process,

assuming that BOD5 is equal to 0.68 BODL

Mass of BODL utilized (lb O2/day) = Q(So S) (8.34/0.68

In terms of kg/d = Q(So S)/0.68

= (0.25(86,400 s/d)(250 6.2) (1000/(106 ( 0.68)

= 7,744 kg/d

Oxygen requirements (kg/d) = 7744 1.42 (1321)= 5868 kg/day

Volume of air needed is given by:

Assume oxygen transfer efficiency = 8%

Safety factor of 2 for actual design volume for sizing blowers

Air density is 0.075 lb/ft3

% by weight of oxygen in air = 23.2%

in terms of lb/day= 5868 ( 2.2 lb/day/(0.075(0.232)= 741,425 ft3/day

Air requirement= 741,425/0.08 = 9,267,813 ft3/day or 6,436 ft3/min

Design air requirements = 2 ( 6,436= 12,872 ft3/min

Check:Air volume/flow rate= 9,267,816 ft3/d/5,710,000 gal/d= 1.62 ft3/gal

Air requirement per lb of BOD5 removed = (9,267,816 ft3/d)/[(250 6.2) ((5.71) (8.34]

= 798 ft3/lb BOD5 removed

Check against Ten States Standard

Organic loading

(lb BOD5/d/1000 ft3) = 40

F/M Ratio

(lb BOD5/d/lb MLVSS) = 0.2 0.5

Organic Loading

= (0.25 m3/s)(250 mg/L) (1000 L/m3)(86,400 s/d) (2.2)/[(106)(6(45(9(2 m3)(3.28)3]

= 0.069 lb BOD5/d/ft3= 69 lb BOD5/d/1000 ft3

Does not meet Ten States Standard but meets loading rates in notes

F/M ratio = (0.25 m3/s)(250 mg/L)(1000 L/m3(86,400 s/d)/[(3500)(6(9(45(2 m3)(1000)]

= 0.32

within Ten States Standard

_1169834238.unknown

_1169834264.unknown

_1169834311.unknown

_1169834496.unknown

_1169834291.unknown

_1169834246.unknown

_1169834226.unknown