Sorting and recycling centers
PE, PP and PS-rich residual streams after mechanical sorting can be assessed for pyrolysis suitability.
Start with polymer and contaminant testing, then define suitable feedstocks, exclusions, pretreatment and output validation.
Different plastics are not one feedstock; chlorine-bearing and flame-retarded materials need particular caution.
Plastic recycling industry
Plastic pyrolysis is mainly considered for streams that are difficult to recover at stable value through conventional mechanical recycling but remain identifiable and manageable. Polymer type, chlorine, moisture, flame retardants, metals and dirt affect pretreatment, wax management, condensation, corrosion and output quality.
PE, PP and PS-rich residual streams after mechanical sorting can be assessed for pyrolysis suitability.
Agricultural film, packaging film and woven bags require dirt, moisture, densification and feeding controls.
Known-origin production scrap makes it easier to establish a repeatable feedstock specification.
Sampling, analysis and sorting must control PVC, PET, flame-retarded and other unsuitable components.
01
Build the feedstock list by source, polymer, physical form and contamination.
02
Shred, wash, dewater, densify and remove metals and unsuitable components.
03
Configure storage, metering and closed feeding for film, lumps or granules.
04
Manage temperature, residence time, wax-forming components and cleaning intervals.
05
Manage heavy fractions, staged condensation, process gas and safety controls.
06
Test condensate, solids and gas conditions before defining upgrading, use or disposal.
Test chlorine, boiling range, water and stability before confirming fuel or chemical-feedstock outlets.
Some plastics create waxy material that must be managed in heating, piping, separation and cleaning.
It may be evaluated for process heating after treatment; the project defines surplus-gas handling.
Quantity and composition vary with feedstock and require testing before reuse or disposal.