My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
SU0003122
Environmental Health - Public
>
EHD Program Facility Records by Street Name
>
T
>
THORNTON
>
26440
>
2600 - Land Use Program
>
SA-93-26
>
SU0003122
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
5/7/2020 11:29:41 AM
Creation date
9/9/2019 10:38:07 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
RECORD_ID
SU0003122
PE
2633
FACILITY_NAME
SA-93-26
STREET_NUMBER
26440
Direction
N
STREET_NAME
THORNTON
STREET_TYPE
RD
City
THORNTON
ENTERED_DATE
11/6/2001 12:00:00 AM
SITE_LOCATION
26440 N THORNTON RD
QC Status
Approved
Scanner
SJGOV\rtan
Supplemental fields
FilePath
\MIGRATIONS\T\THORNTON\26440\SA-93-26\SU0003122\APPL.PDF \MIGRATIONS\T\THORNTON\26440\SA-93-26\SU0003122\CDD OK.PDF \MIGRATIONS\T\THORNTON\26440\SA-93-26\SU0003122\EH COND.PDF \MIGRATIONS\T\THORNTON\26440\SA-93-26\SU0003122\CORRESPOND.PDF
Tags
EHD - Public
Jump to thumbnail
< previous set
next set >
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
325
PDF
Print
Pages to print
Enter page numbers and/or page ranges separated by commas. For example, 1,3,5-12.
After downloading, print the document using a PDF reader (e.g. Adobe Reader).
View images
View plain text
Technical Description <br /> Unlike a conventional flowthrough clarifier, where the surface area must be large enough to allow <br /> L particles to settle downward in a constantly moving stream,the batch clarifier provides particle settling <br /> under completely static, quiescent conditions. This method is more efficient and economical than <br /> meeting the need in flowthrough systems for greater surface areas with increasing flow rates at larger <br /> Lcapacities. <br /> With the batch process,the static clarifier does not require this larger surface area;therefore,in design, <br /> the batch clarifier volume capacity is equal to the mixed-liquor volume, or batch, to be transferred. <br /> Surface settling rates (SSR) do apply, however, but only on a batch-by-batch basis. SSRs are based <br /> upon flow in static conditions and are thus accurate for the 24-hour period flow. The Bio-Pure batch <br /> process is unique in that longer retention times are not required to do the accurate sludge volume <br /> results obtained in the standard SSV-30 and SSV-60 tests..By staying within those basic design <br /> parameters of SSR per batch, the static condition of the batch clarification process is directly <br /> comparable to settlometer readings. <br /> Complete control of the entire process can be based upon the SSV-30 and -60 tests. If the sludge <br /> flocculates well and settles rapidly, it is possible to reprogram the system controlling microprocessor <br /> (PC) to allow for automatic sequencing of the batch cycle based upon current biomass conditions <br /> within the treatment plant.This change can increase or decrease aeration detention and the subsequent <br /> clarifier cycle surface settling rate. <br /> The clarifier has a dual-weir system for removal and return of floatables to aeration. The weir system <br /> is sized using hydraulic returnisurface area(square feet). One hundred percent of all weir wastewater <br /> is returned to aeration and thus is contained within the internal detention time ofthe treatment process. <br /> Provisions are made to ensure that any residual floatable scum is not transferred into any downstream <br /> process by SNT pump elevation control. <br /> FLOW EQUALIZATION <br /> Widely fluctuating influent flow rates are typical at nearly all wastewater treatment plants. This <br /> fluctuation can result in a loss of treatment efficiency. With higher degrees of treatment constantly <br /> being required, some method of flow equalization is a design necessity. <br /> The objective offlow equalization is to level offthe daily flow variations in order to achieve a constant, <br /> �. batched flow rate at the downstream treatment process steps. This is accomplished by storing influent <br /> which is in excess ofthe daily flow-rate average,and then discharging it to the system when the influent <br /> flow rate is less than that average. By achieving this objective, overall treatment plant efficiency is <br /> dramatically improved. <br /> Several methods are available for determining equalization volume;all require generating a daily flow <br /> pattern record. If possible, this should be based upon actual plant data. If actual flow data are not <br /> available, which is frequently the case, existing communities, developments, institutions, etc., with <br /> similar flow characteristics should be studied. <br /> r <br /> 15 <br />
The URL can be used to link to this page
Your browser does not support the video tag.