WW / PAMPROCESS DUTY FILES
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SHIFT NOTE 05 / ACTIVE DOSE

How to Calculate PAM Dose for Sludge Dewatering

Calculate active PAM dose from sludge flow, feed solids and product active content, then judge cake, capture, throughput and recycle quality together.

INPUT
stream data
CHECK
active basis
OUTPUT
measured result
Belt filter press producing conditioned wastewater sludge cake
SHIFT NOTE 05 / ACTIVE DOSE
SHIFT INDEX01Use dry solids as the denominator02Convert product to active polymer03Close the time basis04Calibrate every feed05Build a controlled dose curve06Measure more than cake dryness07Check density and concentration assumptions08Track uncertainty around a dose point09Calculate treatment cost10Keep a verified reference run11Define adjustment rules
01

Use dry solids as the denominator

Sludge flow changes do not necessarily match solids loading. A dose reported only as pump speed or solution flow cannot be compared across shifts.

Calculate dry-solids mass flow from wet flow, density when needed and measured solids concentration.

02

Convert product to active polymer

Dry powder, emulsion and solution products contain different active fractions. Multiply delivered product mass by active content before comparing dose.

Keep the assumed active fraction with the calculation and verify it against current product documentation.

03

Close the time basis

Use consistent units and the same averaging period for sludge flow, solids and polymer feed. Short grab samples may not represent a fluctuating shift.

Pair dose calculations with feed samples taken during a stable run.

04

Calibrate every feed

Check powder feeder mass delivery, solution water flow, tank volume and metering-pump output. A controller percentage is not a verified mass rate.

Repeat calibration after maintenance, product-form change or major viscosity change.

05

Build a controlled dose curve

Step active dose through under-conditioned, useful and over-conditioned regions while holding machine settings as stable as possible.

Allow the press or centrifuge to reach steady response before collecting cake and liquid samples.

06

Measure more than cake dryness

Record cake solids, solids capture, filtrate or centrate quality, throughput, drainage and operating stability. A dry cake with poor capture can increase recycle load.

Use several samples and report variability rather than selecting one favorable point.

07

Check density and concentration assumptions

A quick calculation often treats sludge density as water, but concentrated or mineral-rich residuals may justify a measured value. Solids tests also need consistent sampling and laboratory method.

State every assumption with the result and update the calculation when verified data become available.

08

Track uncertainty around a dose point

Feed solids, polymer concentration and pump delivery each contribute uncertainty. A single calculated value should not be reported with more precision than the underlying measurements support.

Use a practical range and repeat the calculation across several stable periods before changing the supply specification.

09

Calculate treatment cost

Multiply active consumption by delivered active-polymer cost, then include disposal volume, throughput, wash water, energy and recycle consequences.

The economic operating point may be a stable plateau rather than the absolute driest cake.

10

Keep a verified reference run

Retain one recent run with confirmed feed solids, calibrated polymer rate, machine settings, cake and liquid results. Use it when the process drifts or a new lot arrives.

A reference run reduces the temptation to compare a new product against an undocumented best-case memory.

11

Define adjustment rules

Link dose adjustments to feed solids, drainage, capture and recycle indicators. Do not let polymer flow become the automatic response to every machine problem.

Set a reference condition and trigger a new screen when sludge characteristics leave the approved window. Review the calculation after feeder or laboratory-method changes.

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