A device for recycling a plastic container includes a housing with an opening to receive the plastic container. A moving part is movably arranged within the housing on which, in a first position of the moving part, the plastic container is placed such that a first portion of the plastic container is arranged inside the housing and a second portion of the plastic container is arranged outside the housing. An ultraviolet (UV) light device including a UV light emitter and a UV light detector is arranged in proximity to the opening and configured such that a UV light beam emitted by the UV light emitter radiates through the plastic container which is detected by the UV light detector. A controller is in communication with the UV light device and the moving part. The moving part is configured to move to a second position in which the plastic container is entirely placed inside the housing in response to a control signal from the controller indicating that the plastic container can be recycled. A first cutter is rotatably arranged in the housing and configured to separate an upper portion of the plastic container from an intermediate portion of the plastic container. A second cutter is rotatably arranged in the housing and configured to separate a lower portion of the plastic container from the intermediate portion of the plastic container. A third cutter is rotatably arranged in the housing and configured to cut the intermediate portion of the plastic container in an axial direction such that the intermediate portion, when it is rolled out to a flat form, has a rectangular shape. A mold unit has a first press mold part and a second press mold part. A robot unit is configured to roll out the intermediate portion of the plastic container, to move the intermediate portion of the plastic container to the mold unit, and to place the intermediate portion of the plastic container between the first press mold part and the second press mold part.

The invention relates to a process for the production of a recyclable product (1, 8, 9) made from a first material, wherein before or during the production of the product (1, 8, 9) a first marking material is added to the first material and the product (1, 8, 9) is produced from the first material with the admixed marking material, wherein the first marking material can be automatically detected in a recycling plant in the first material of the product (1, 8, 9) after the production thereof. The invention also relates to a process for the recycling of a product (1, 8, 9), wherein the product (1, 8, 9) is manufactured from a first material, to which a first marking material is added, wherein the product (1, 8, 9) or pieces (22) of the product (1, 8, 9) are separated from one another and/or from other objects in a recycling plant, in that the first marking material is detected in the first material of the product (1, 8, 9) or the pieces (22) of the product (1, 8, 9), and the product (1, 8, 9) or the pieces (22) of the product (1, 8, 9) are separated from one another and/or other objects, in which no marking material or a different, second marking material is detected. The invention also relates to a recyclable product and a recycling plant.

The method of uniquely identifying a product for subsequent recycling includes marking a surface of the product with a first trace signature being representative of the manufacturer of the product.

A method for sorting flexible polyurethane foams including: a) providing two or more calibration samples of conventional flexible polyurethane foams, two or more calibration samples of high resilience (HR) flexible polyurethane foams, and two or more calibration samples of viscoelastic flexible polyurethane foams, and obtaining a mid-infrared (MIR) spectrum of each calibration sample; b) carrying out a spectral pre-processing of the spectra of all the calibration samples and, then a first PCA to define a first library; c) carrying out a spectral pre-processing of the infrared spectra of conventional and HR calibration samples and, then a second PCA to define a second library; d) obtaining the MIR spectrum of a sample of polyurethane foam and, based on the first and second libraries, classifying the sample of polyurethane foam as a conventional, HR or viscoelastic polyurethane foam, or as a foam that is neither a conventional, a HR or a viscoelastic polyurethane foam.

Mixed-plastics polypropylene blend including mainly polypropylene being benzene free with defined CIELAB color.

Apparatus and methods for identifying substances in a material include at least one light source configured to irradiate a sample of the material with light of at least one wavelength. A detector is configured to detect light re-emitted or transmitted by the sample. An analysis device analyzes the detected light by UV/VIS spectroscopy, fluorescence spectroscopy, Raman spectroscopy, or absorption spectroscopy, and generates a first identification result for at least one substance of the sample. Further, the analysis device generates a second identification result in response to the first identification result being an ambiguous identification result. The second identification result may be generated by fluorescence light decay time analysis (FLZA). At least one substance is at least partially identified based on the first identification result or based on the first and second identification results.

The present invention comprises a method of shredding treated medical waste, cleaning it of all traces of biological gunk, and sorting it into separate components for recycling. To clean biological gunk from materials, all materials must be first shredded into small parts to expose the interior. The cleaning is performed by submerging the gunk coated materials into a caustic solution that breaks down and dissolves the gunk off of the materials. The caustic solution may comprise sodium hydroxide, potassium hydroxide, or a similar chemical, which is highly effective in producing a corrosive chemical that can break down blood, bone marrow, urine, unused medication, food waste, organs, tissues and any other biologic materials. After all of the biological material is removed from the cleaned materials, they are sorted into component materials, such as plastics, metals, rubbers, glass, etc.

A plastic item, such as a beverage bottle, conveys two distinct digital watermarks, encoded using two distinct signaling protocols. A first, printed label watermark conveys a retailing payload, including a Global Trade Item Number (GTIN) used by a point-of-sale scanner in a retail store to identify and price the item when presented for checkout. A second, plastic texture watermark conveys a recycling payload, including data identifying the composition of the plastic. The use of two different signaling protocols assures that a point-of-sale scanner will not spend its limited time and computational resources working to decode the recycling watermark, which lacks the data needed for retail checkout. In some embodiments, a recycling apparatus makes advantageous use of both types of watermarks to identify the plastic composition of the item (e.g., relating GTIN to plastic type using an associated database), thereby increasing the fraction of items that are correctly identified for sorting and recycling. A great number of other features and arrangements are also detailed.

A method of manufacturing a plurality of colors of bulked continuous carpet filament from a single multi-screw extruder which, in various embodiments, comprises: (A) passing PET through an extruder that melts the PET and purifies the resulting PET polymer melt; (B) adding a liquid colorant to the polymer melt using a liquid metering system; (C) using one or more static mixers (e.g., up to forty static mixers) to substantially uniformly mix (e.g., homogeneously mix) the polymer melt and the liquid colorant; and (D) feed the uniformly mixed and colored polymer melt into a spinning machines that turns the polymer into filament for use in manufacturing carpet, rugs, and other products.

Various processes and configuration are provided for a chemical recycling facility that can lower the carbon footprint and global warming potential of the facility. More particularly, we have discovered numerous ways for reducing the carbon footprint of the facility by: (i) recycling at least a portion of the residual heat energy from the pyrolysis effluent back upstream to the pyrolysis process and waste plastic liquification stage; (ii) recovering at least a portion of the carbon dioxide from at least a portion of the pyrolysis flue gas and/or the pyrolysis gas; (iii) feeding at least a portion of the pyrolysis gas at a cracker facility at a position downstream of a cracker furnace; (iv) using at least a portion of a demethanizer overhead stream as a fuel in a pyrolysis facility and/or a cracking facility; and (v) providing a chemical recycling facility that contains a pyrolysis facility co-located with a cracking facility. Thus, the global warming potential of the chemical recycling facility may be optimized and lowered due to the processes and configurations described herein.