| Brand Name: | BLUWAT |
| Model Number: | Blufloc Emulsion |
| MOQ: | 1000kgs |
| Price: | negotiable |
| Delivery Time: | 5-10days |
High-molecular-weight liquid polymer grades for paper mill sludge containing fibers, fillers, fines, coating pigments, starch, and biological solids, supporting faster drainage, stronger solids capture, and more consistent mechanical dewatering.
Paper mill sludge can contain highly variable ratios of fiber, clay, calcium carbonate, coating pigment, starch, and biological solids. Grade changes and production upsets can quickly alter its charge demand, floc structure, drainage, and final dewatering behavior.
A cationic emulsion can capture anionic fines and biological material, but the polymer should be selected according to whether the feed is predominantly primary fiber sludge, secondary biological sludge, or a changing blend of both.
Blufloc cationic PAM emulsion conditions paper mill sludge containing fibers, fillers, fines, coating pigments, starch, and biological solids before mechanical dewatering.
Multiple charge grades support screening for faster drainage, stronger solids and fiber capture, resilient floc, clearer filtrate, and more consistent cake formation as mill production changes.
Furnish, filler, coating, retention chemistry, and the primary-to- biological sludge ratio can all change the optimum CPAM grade and dose.
Clay, calcium carbonate, coating pigment, and short fibers can escape into filtrate when charge and bridging are insufficient.
Furnish, paper grade, filler loading, broke, and coating changes can quickly alter drainage and cake formation.
Secondary sludge and dissolved anionic material can raise cationic demand and increase polymer use in blended feeds.
Transfer pumps, fan pumps, recirculation, and excessive mixing can break conditioned floc and reduce solids capture.
Cationic groups adsorb onto anionic fibers, mineral fines, coating particles, starch-related solids, and microbial material. Long polymer chains then bridge these components into drainable floc.
Cationic sites adsorb onto negatively charged fiber surfaces, filler particles, coating fines, and biological solids, reducing electrostatic repulsion.
High-molecular-weight chains connect destabilized particles, creating larger, open floc that can retain fines while allowing water to drain.
The selected grade should form floc that survives realistic transfer shear, releases water efficiently, and limits fiber and filler loss to filtrate.
Compare adjacent grades on representative primary, secondary, and blended sludge using the same active-mass basis, dilution water, preparation procedure, pH, temperature, feed solids, shear, and dewatering method.
| Grade | Base | Molecular Weight | Charge | Suggested Screening Role |
|---|---|---|---|---|
| EC 8040 | Oil-based | High | Medium | Starting candidate for fiber- and filler-rich primary sludge. |
| EC 8050 | Oil-based | High | High | Broad starting candidate for blended paper mill sludge. |
| EC 8060 | Oil-based | High | Very high | Candidate for biological-rich or highly anionic sludge. |
Adjacent grades support changing fiber-to-biosolids ratios and variable anionic demand.
Correct conditioning can improve filtrate clarity and limit the loss of fibers, filler fines, and biological solids.
Fast emulsion activation supports continuous mill operation and controlled response to production changes.
Grades can be screened for belt press, screw press, and centrifuge operation under representative shear.
Screening can be linked to paper grade, furnish, coating, ash, and primary-to-biological sludge contribution.
Identify the primary fiber, secondary biological, and blended sludge contribution. Note the current paper grade, furnish, filler, coating, and upstream retention chemistry.
Record ash, feed solids, pH, temperature, dilution-water quality, and the current furnish or coating grade where these data are available.
Compare adjacent cationic charges on the same active-mass basis. Observe drainage, floc resilience, filtrate solids, fiber capture, and cake formation.
Trial the best two candidates while feed solids, paper grade, machine settings, preparation, and dose calibration remain as stable as practical.
Create separate grade or dose setpoints for fiber-rich and biological-rich operating periods when one setting cannot consistently cover both conditions.
EC 8040 can be an efficient starting candidate for fiber-rich primary sludge that already forms structure.
EC 8050 is a broad starting point for blended paper mill sludge containing both fibers and biological material.
Include EC 8060 when secondary sludge, soluble anionic material, or high biological content raises charge demand.
Neat-emulsion price per kilogram can be misleading when products differ in active content, preparation efficiency, activation, working dose, and equipment throughput.
The comparison should also include machine throughput, cake or underflow quality, filtrate TSS, fiber loss, floc survival, operator adjustment, and downstream disposal cost.
If drainage, capture, or cake performance follows paper-grade changes, sample the sludge during every major furnish, filler, or coating condition. A single average sample can conceal the need for two distinct operating windows.
Check whether a retention-aid, strength-agent, sizing, broke, or coating-chemistry change upstream is also altering sludge charge, ash content, and the fines entering wastewater treatment.
Inspect emulsion activation, dilution water, injection point, mixing, transfer and fan pumps, feed-solids consistency, and dewatering-machine settings before concluding that the selected grade is no longer suitable.
Confirm the required commercial grade specification and order documentation before production and shipment.
Shortlist products using representative primary, secondary, and blended sludge under realistic pH, temperature, solids, ash, dilution-water chemistry, and transfer shear.
Provide make-down, dilution, activation, dosing, injection, and scale-up guidance for the selected grade.
Review trial data and adjust charge level, dose, addition point, mixing, transfer, machine settings, or production-linked operating windows.
No. Fiber-rich primary sludge may perform well with moderate charge, while biological-rich sludge and highly anionic blends often require higher charge.
Possibly, but coating pigments, filler loading, furnish, and wet-end chemistry can change the optimum charge and dose. Confirm performance with representative samples.
Record feed solids, ash or sludge type, primary-to-biological contribution, paper grade, filtrate TSS, fiber loss, cake solids, throughput, and active polymer mass.
Dewatering polymer mainly conditions the sludge. Any fiber- recovery or process-return strategy should be evaluated separately with the production, wastewater, and product- quality teams.
For paper mill primary, secondary, and blended sludge dewatering, Bluwat can screen adjacent PAM emulsion grades, review preparation and dosing conditions, and help define a controlled plant-trial plan using filtrate TSS, fiber loss, cake solids, throughput, floc resilience, and active polymer cost per dry ton as agreed performance indicators.