DEVICE AND METHOD FOR RECYCLING POST-CONSUMER PLASTIC WASTE SHREDDED TO FLAKES AND WASHED
20250161512 · 2025-05-22
Inventors
Cpc classification
B29B17/02
PERFORMING OPERATIONS; TRANSPORTING
B29B17/0412
PERFORMING OPERATIONS; TRANSPORTING
B29B15/00
PERFORMING OPERATIONS; TRANSPORTING
A61L2202/13
HUMAN NECESSITIES
B29B2013/005
PERFORMING OPERATIONS; TRANSPORTING
International classification
B29B13/00
PERFORMING OPERATIONS; TRANSPORTING
B29B15/00
PERFORMING OPERATIONS; TRANSPORTING
B29B17/02
PERFORMING OPERATIONS; TRANSPORTING
B29B17/04
PERFORMING OPERATIONS; TRANSPORTING
Abstract
The device for recycling flakes from shredded and washed post-consumer plastic waste comprisesseen in the processing direction of the plastic wastea pre-treatment unit (2) for drying and homogenising the flakes from shredded and washed post-consumer plastic waste, a melting extruder (3) for melting the plastic waste dried and homogenized in the pre-treatment unit (2), a degassing extruder (5) having a connection (5a) to a vacuum source for degassing the plastic melt, a granulating device (6) for granulating the plastic melt, and an odour removal unit (8) to subject the granules an odour removal.
The odour removal unit (8) has a process gas feed (10) and a gas discharge (11) for discharging an exhaust gas stream, wherein the process gas feed (10) of the odour removal unit (8) is connected to an ozone source (12) or an ozone generating device (13), whereby the odour removal unit (8) may be supplied with process gas enriched with ozone.
Claims
1. A device for recycling flakes from shredded and washed post-consumer plastic waste, comprising: a pre-treatment unit for drying and homogenising the flakes from shredded and washed post-consumer plastic waste, a melting extruder arranged downstream of the pre-treatment unit for melting the plastic waste dried and homogenized in the pre-treatment unit, a degassing extruder arranged downstream of the melting extruder and having a connection to a vacuum source for degassing the plastic melt, optionally a melt filter arranged between the melting extruder and the degassing extruder for removing foreign matter from the plastic melt, a granulating device arranged downstream of the degassing extruder for granulating the plastic melt, an odour removal unit arranged downstream of the granulating device for subjecting the granules to odour removal, and optionally a drying device arranged between the granulating device and the odour removal unit for drying the granules, characterised in that the odour removal unit has a process gas feed and a gas discharge for discharging an exhaust gas stream, wherein the process gas feed of the odour removal unit is connected to an ozone source or an ozone generating device, whereby the odour removal unit may be supplied with process gas enriched with ozone.
2. A device according to claim 1, further comprising an in-line measuring device for measuring the ozone concentration of the exhaust gas stream from the odour removal unit.
3. A device according to claim 1, further comprising an adjustment device for adjusting the amount of ozone, which is supplied to the odour removal unit, in dependency on the ozone concentration of the exhaust gas stream from the odour removal unit.
4. A device according to claim 1, further comprising at least one apparatus for the at least partial depletion of ozone contained in the exhaust gas stream, wherein the apparatus is configured to deplete ozone preferably for the thermal or catalytic treatment of the exhaust gas stream or for irradiating the exhaust gas stream using electromagnetic waves.
5. A device according to claim 1, wherein the process gas to be enriched with ozone is air.
6. A device according to claim 1, wherein a the ozone concentration in the enriched process gas is at least 0.1 ppm.
7. A method for recycling flakes from shredded and washed post-consumer plastic waste, comprising: drying and homogenising the flakes from shredded and washed post-consumer plastic waste in a gas stream, in particular a hot gas stream, melting the dried and homogenized plastic waste into a plastic melt, optionally filtering out foreign matter from the plastic melt, degassing the plastic melt, granulating the plastic melt, optionally drying the granules, removing odour from the granules by way of a process gas stream, characterised by enriching the process gas stream used for removing odour from the granules with ozone or providing the process gas stream as a gas enriched with ozone.
8. A method according to claim 7, wherein the mount of ozone, which is supplied to the granules when removing the odour from the granules, is adjusted in dependency on the ozone concentration of the process gas upon removal following the odour removal treatment of the granules.
9. A method according to claim 8, wherein the ozone concentration of the process gas upon removal following the odour removal treatment of the granules is detected by way of in-line measurements and that the adjustment of the amount of ozone supplied to the granules when removing the odour from the granules is carried out in dependency on the ozone concentration measured.
10. A method according to claim 7, wherein the ozone contained in the removed process gas is depleted at least in part, wherein the depletion of ozone is preferably done by way of thermal or catalytic treatment of the process gas removed.
11. A method according to claim 7, wherein the ozone contained in the removed process gas is depleted at least in part, wherein the depletion of ozone is done by way of irradiation of the removed process gas using electromagnetic waves, wherein the electromagnetic waves are preferably UV light having a wavelength of at least 254 nm.
12. A method according to claim 7, wherein the process gas to be enriched with ozone is air.
13. A method according to claim 7, wherein the ozone concentration in the enriched process gas is at least 0.1 ppm.
14. A device according to claim 6, wherein the ozone concentration in the enriched process gas is in a range between 10 ppm and 100 ppm.
15. A method according to claim 13, wherein the ozone concentration in the enriched process gas is in a range between 10 ppm and 100 ppm.
Description
[0071]
[0072]
[0073] The device for recycling flakes from shredded and washed post-consumer plastic waste, which is schematically depicted in
[0074] Downstream of the melt filter 4, a degassing extruder 5 is located having a vacuum connector 5a to a not depicted vacuum source for degassing the plastic melt, followed by a granulating device 6 for granulating the plastic melt. The granules produced in the granulating device 6 are dried in a drying centrifuge 7 and then supplied to an odour removal unit 8, where the granules are subjected to odour removal. Following the odour removal treatment, the granules are discharged from the odour removal unit 8 and may then be either directly processed or supplied to a storage silo 9.
[0075] The odour removal unit 8 has a process gas feed 10 and a gas discharge 11 for discharging an exhaust gas stream, wherein the process gas feed 10 of the odour removal unit 8 is connected to an ozone source 12, e.g. in the form of a container filled with ozone-enriched gas, e.g. ozone-enriched pressurized air, or to an ozone generating device 13, whereby ozone or ozone-enriched process gas may be supplied to the odour removal unit 8.
[0076] An adjustment device 20 serves for adjusting the amount of ozone, which is supplied to the odour removal unit 8, in dependency on the ozone concentration of the exhaust gas stream from the odour removal unit 8. Adjusting the amount of ozone to be supplied is realized, for example, by way of a control valve actuated by the adjustment device 20 in the process gas feed 10. The adjustment device 20 may be configured as an electronic control unit having a microprocessor, a main memory, a programme memory having a control algorithm stored therein and interfaces for the communication and for the actuation of actuators, such as, e.g., the control valve mentioned. The ozone generating device 13 may be configured such that it puts the ambient air under electric voltage such that the oxygen in the ambient air is reacted into ozone. The higher the electric voltage, the more ozone is generated. In this way, by controlling the electric voltage, the ozone concentration of the gas exiting the ozone generating device 13 can be controlled. The control of the ozone generating device 13 for generating and varying the electric voltage can be performed by the adjustment device 20.
[0077] Alternatively thereto, the ozone generating device 13 may operate on the basis of irradiation of aspirated ambient air with UV light, preferably having a wave length of less than 240 nm. In such an ozone generating device 13, the ozone concentration of the gas exiting the ozone generating device 13 is controlled by changing the wave length of the UV light. Also this control may be realized by using the adjustment device 20. Since UV light of shorter wave length is more energetic, therewith more ozone is produced than with irradiation using UV light of longer wave length.
[0078] The adjustment device 20 is preferably controlled by an in-line measuring apparatus 30 for measuring the ozone concentration of the exhaust gas stream from the odour removal unit 8, wherein controlling the adjustment device 20 is carried out to adjust the amount of ozone supplied to the odour removal unit 8, in dependency on the ozone concentration measured. Using such a configuration, the processes described above for the removal of odour may be carried out, while simultaneously having only little ozone-related impact onto the environment. The in-line measuring apparatus 30 can be arranged directly in or at the gas discharge 11, or it may alternatively be arranged in a distance to the gas discharge 11, but it may also have an ozone sensor, which is installed in the gas discharge 11.
[0079] At the gas discharge of the odour removal unit 8, there is optionally provided an apparatus 40 for the at least partial depletion of ozone contained in the exhaust gas stream, wherein the apparatus 40 for the depletion of ozone is configured preferably for the thermal or catalytic treatment of the exhaust gas stream or for the irradiation of the exhaust gas stream with electromagnetic waves. If the depletion of ozone by means of irradiation of the process gas removed is carried out using electromagnetic waves, then there is preferably used UV light having a wave length of at least 254 nm.
[0080] Due to its simple handling, the process gas to be enriched with ozone is preferably air. The ozone concentration in the enriched process gas should be at least 0.1 ppm and lie in a range between 10 ppm and 100 ppm.
[0081] In
[0082] In series of experiments, the process gas stream to the odour removal unit 8 was enriched with 35 ppm ozone, and in the odour removal unit 8, granules from post-consumer waste of various plastic types were each passed through with the ozone-enriched process gas for respectively 2-2.7 h. At an ozone concentration of 35 ppm and a flow rate of 1600 m.sup.3 process gas/h, the ozone amount conveyed was 120 g/h. Hence, 0.24 g ozone per kg plastic was supplied.
[0083] Subsequently, in a blind test, respectively two samples of the same plastic material, wherein one sample was passed through in a conventional manner for 2-2.7 h by hot air and the other sample was passed through for the same period of time at the same temperature by hot air containing 35 ppm ozone as process gas, were presented to a board of trained odour testers for evaluation. Thereby, the granules made from HDPE, PP and LDPE and treated with ozone were assessed as being significantly superior in regard to odour intensity and hedonics by the testers than the comparative material treated exclusively with hot air.