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Fort Walton Beach Council agenda — 04-29-03 workshop agenda — reading text
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the pre- aeration structure. Minor " roping" of material
around the diffusers is occurring that is likely due to the fibrous material passing the
screening. Wastewater discharges from the pre- aeration basin to the primary
clarifiers. Stationary weirs control the wastewater flow from the aeration basin to
pre'-
the individual primary clarifiers. It appears the flow from the pre- aeration basin is not
equally split causing " dead zones" of unequal flows to the primary clarifiers. The
IIiI
strong presence of hydrogen sulfide ( H2S) at this location reinforced the idea that a
portion of the flow is stagnant. H2S is also known to be generated due to the long
length of pipe run from the pump stations to the headworks. Minor concrete
corrosion was noticeable at the air wastewater interface in the aerated grit chamber
and the pre- aeration basin. Figures 2- 6 and 2- 7 include photographs of the aerated
grit chamber and the pre- aeration basin.
I
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Figure 2- 4
City of Fort WaltQn Beach
Wastewater Treatment Plant Facilities Plan
Mechanical Bar Screen Photos
MechanicalBar Screen
Mechanical Bar Screen - Side View
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Figure 2- 5
City of Fort Walton Beach
Wastewater Treatment Plant Facilities Plan
Grit Cyclone and Classifier Photos
Grit Cyclone Facing West
Grit Cyclone and Classifier Facing North
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Figure 2- 6
City of Fort Walton Beach
Wastewater Treatment Plant Facilities Plan
Pre- Aeration Basin Photos
Aerated Grit Chamber and Pre- Aeration Basin Facing West
Pre- Aeration Basin Facing South
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Figure 2- 7
City of Fort Walton Beach
Wastewater Treatment Plant Facilities Plan
Pre- Aeration Basin Photos
Aerated Grifc;hambef(}3ackground) and
Pre- Aeration Basin ( For~ grol.nd) FacingNorth with Blow~rs On
Pre- Aeration Basin Facing South With Blowers Off
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III
III
2. 3. 2.2 Primary Clarifiers
ill
The purpose of the primary clarifiers is to provide a quiescent zone for settling of
heavier organic solids not removed in the screening, thus reducing the downstream 5-
day carbonaceous biochemical oxygen demand ( CBODs) and total suspended solids
TSS) load of the raw wastewater.
ta
I
The City' s WWTP has two ( 2) 65- feet diameter circular primary clarifiers, with
I operating sidewater depths of 12- feet. The concrete appears to be in good condition,
however, the bridges to the clarifier drives are corroded. The primary clarifiers have a
i total surface area of 6, 636 square feet, and have a design overflow rate at average
daily flow of approximately 678 gpd/sf. Typical overflow rates for primary clarifiers
range between 600 and 1, 000 gpd/sf. The primary criteria used when evaluating the
I primary clarifiers are configuration, hydraulic loading rates, and the detention times of
f!
III these units. Based on the design flow of 4. 50 MGD and the configuration of the
primary clarifiers, the following were determined:
FWB WWTP
Parameter At Desi n Flow
678 600 to 1, 000
Detention Time, minutes 191 90 to 150
ill
till!!
Based on the information provided above, both of these performance- limiting
ill
parameters are generally within the typical design standards used for sizing these
types of facilities. However, it should be noted that historic problems associated with
II the infiltration and inflow ( III) in the City's wastewater collection system may limit
the treatment efficiency of the primary clarifiers during high rainfall periods. During
periods of heavy rainfall, the III entering the City' s wastewater system could
significantly increase the influent flow to the City' s WWTP, thus hydraulically
i'
overloading these units. Over the past few years, the City has been identifying
II
problem areas in their wastewater collection system, and has developed a program to
reduce the III entering the system. The City' s on- going III program is addressing
I these issues, such as minimizing inflow coming from the cross connections by private
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filii
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IiIIi
III
individuals and infiltration through existing deteriorating manholes, and gravity sewer
mams.
filii
The expected CBOD5 removal through the primary clarifiers should range between
30- and 45- percent. While no infonnation is maintained at the City' s WWTP to
detennine the effectiveness of these units, there is no reason to expect that these units
are not perfonning within these limits.
it.
Each unit can be bypassed to route the flow to the other clarifier during times of
I required maintenance.
I"';'.
1,;'.
Sludge from the primary clarifiers is pumped to a gravity thickener, which in turn
The pumping
directs the sludge to the anaerobic digesters for further treatment.
facilities consist of two ( 2) sets of two ( 2) piston pumps, four ( 4) total, for the
I removal of primary sludge and scum from the two ( 2) primary clarifiers. The two ( 2)
piston pumps were installed in 1999 to replace two ( 2) problematic centrifugal
III pumps. The two ( 2) scum pumps are non- clog centrifugal type pumps. Both sets of
till pumps are in good operating condition.
Figure 2- 8 contains photographs of the primary clarifiers and Figure 2- 9 shows photos
of the primary sludge pumps.
It
III
II
Ii
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Figure 2- 8
City of Fort Walton Beach
Wastewater Treatment Plant Facilities Plan
Primary Clarifiers Photos
North Primary Clarifier
South Primary Clarifier
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Figure 2- 9
City of Fort Walton Beach
Wastewater TreatmentPlant Facilities Plan
Primary Sludge Pumps
Primary Sludge Pumps
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I'll
III 2.3.2.3 Rotating Biological Contactors ( RBCs)
From the primary clarifiers, the wastewater flows by gravity to the RBCs. The system
is made up of four ( 4) trains of five ( 5) rotating units. Each drum- shaped unit is 25
feet long and 10 feet in diameter fitted with eight ( 8) sectors of plastic media for the
treatment of organic waste streams. A total of 18 of the 20 units have four ( 4)
quadrants of plastic media; and the other two ( 2) units are a newer design having a six
I 6) quadrant configuration. Each unit rotates the media through the wastewater on a
horizontal shaft in a basin filled with wastewater that has undergone primary
I treatment. The units are powered at one
