Organic polymer materials are technical mass products, the recycling of which is getting more and more important and interesting. Due to the unregulated disposal of such materials environmental problems have been caused to an increasing degree (“plastic planet”). Furthermore recycling of polymer materials is a valuable source for organic raw materials. The predominant part of the technically used macro-molecular materials are thermoplastics, which can be reused basically by fusion and new forming; this requires however due to the incompatibility of polymeric materials among each other a high degree of sorting pureness, since already 5% contaminant deteriorates the properties to large degree. Used materials are however provided in the rarest cases in a completely separated manner, at best as waste during production processes; collected material is in general more or less mixed and has to, in particular prior to the converting to high-quality products, be sorted. A sorting is also interesting when re-used in a different way, because the corresponding processes can be exactly adjusted to the respective materials. The sorting for recycling requires a fast, efficient and less-complex detection method. There are known detection methods, which are based on the different density or on the electrostatic properties [1] of macro-molecular materials; Such methods are basically complex and accident-sensitive.
Optical methods are attractive, because they are fast and reliable and require only a comparatively small effort. The marking of polymer materials with fluorescence dyes has been described [2], to identify the respective material or the respective charge respectively using fluorescence spectra (wavelength-dependency of the fluorescence intensity) [3,4]. This method requires registering and assigning of fluorescence spectra individually for each polymer particle and is therefore basically comparatively complex. Furthermore the polymeric materials must be already marked for their sorting; this limits the method to a selective recycling. It is in particular basically unfeasible for secondary materials. It would be desirable if a sorting method could be provided also for unmarked material and therefore the complex registering of fluorescence spectra could be avoided.
The problem was to develop an optical detection system, to Identify polymer raw materials in a completely separated manner.
We have found that technical polymer raw materials (here as examples Luran, Delrin and Ultramid) astonishingly show large intrinsic fluorescences if they are stimulated optically for example in the UV-region, in particular in the UVA-region, and also in the short-wave visual range; see
Since the fluorescence decay curves can be in general described exactly with exponential functions, a similar procedure for the detection of various polymer materials is possible. It is not required at all to capture the complete exponential curve but rather two punctual or also integrated intensity measurements [5] (cumulation-summation-of single measurements, each over a defined time period) at different times are more than sufficient. When having a bi-exponential curve one requires three intensity measurements, if having pure plastics however the mono-exponential parts are relevant.
a)Fluoreszenz-Abklingkonstante;
b)zusätzlicher biexponentieller Anteil;
c)Anregungswellenlänge in nm:
d)Detektionswellenlänge in nm,
e)Bi-exponentiell ausgewertet.
Integration over each defined time period, preferably a measurement before the first half-value period and a measurement after the first half-value period is in particular advantageously because the signal-to-noise-ratio can be significantly enhanced (the fluorescent light of the probe is used more efficiently). Starting from the usual fluorescence decay times of approximately 5 ns, then this requires two measurements in time distance of 1 to 2 ns with integration times of also approximately 1 to 2 ns. Measurements with such a time resolution do not pose a problem electronically, however the measurement, procedure can be further simplified by stimulating the plastic probe not only once but periodically. It is assumed that after approximately ten half-value periods the optical stimulation is reduced to such an extent that another stimulation can be carried out undisturbed; when starting from an unfavorable case having 10 ns fluorescence decay time this is achieved after approximately 70 ns. One can optically stimulate the probe periodically with a pulse sequence of 70 ns, therefore with repeating frequency of approximately 15 MHz. The two measurements for the determination of the fluorescence decay times then do not need to have to lie within single decay time, but can lie within two subsequent pulses and the requirements for the electronic components for the evaluation are further lowered.
a)Fluoreszenz-Abklingkonstante;
b)Mittetwert, Standardabweichung s;
c)Anregungswellenlänge in nm;
d)Detektionswellenlänge in nm.
More productive is the measurement with a fluorescence decay process by detecting the two required integrated signals with periodic stimulation in that is time-shifted and triggered by the stimulating pulse; here a separation can be performed, for instance with two parallel running phase-sensitive detectors (PSD) with which the lintensities are measured integrating over two different time ranges of the decay curve. Finally it is not required to determine the absolute decay time, because device specific raw data can be used as long as they are sufficiently reproducible; for all used devices a very good reproducibility of the measured values and also of the raw data (for instance not corrected by deconvolution) was obtained. There have been found very small standard deviations s of 0.02 to 0.07 nanoseconds, which document a clear discrimination between various probes; see table 2. The method is significantly further simplified because of the unproblematic use also of raw data.
When considering, that a recycling-flake is in the worst case of a maximum size of 10 mm and for reliability reasons a distance of 20 mm is imposed between two flakes then at 15 MHz pulse sequence and a form feed velocity of 500 m/s (because of technology reasons one should stay below the velocity of sound) more than 200 stimulating pulses per flake are provided. When averaging these one can enhance the signal-to-noise-ratio significantly and the detection reliability can be further increased. Assuming a mass of 25 mg for a recycling-flake (the value was obtained by averaging flakes from commercially available technical recycling material), one can sort 1.5 tons of material per hour with a sorting line. This can be regarded as a realistic technological continuous sorting power, which can be managed by the described detection method. In many cases such high sorting power is not required; when requiring small sorting power, requirements of electronics and mechanics are significantly lower.
The method described here uses the intrinsic fluorescence of the materials. One can dope the polymer materials additionally with fluorescence markers; When having dope concentrations below 0.02 ppm the markers are invisible for the human eye. Markers require a minimum of light fastness; when shreddering plastics prior to the detection, this is not a serious problem because of the formation of fresh areas of fracture. For light fastened fluorescence dyes perylene derivatives and other peri-arylenes, like for example 1 to 3 can be used; for the UV/VIS—absorption—and fluorescence spectra in chloroform-solution see
We have used as short-wave, visual fluorescing perylene derivate the perylene tetracarboxylictetraisobutylester 1 [6], for middle-wave wavelengths the bisimid 2 [7] and for longer wavelengths the terrylene derivative 3 [8]—see
The describes method here has been primarily developed for the recycling of plastics, it can however be used in general for for instance manifold marking purposes, for example by replacing a barcode or QR-code markings; for the latter usually optically readable markings are required whereas fluorescence decay times can be determined also from arbitrarily light scattering objects. The marking can be attached hidden or partially hidden and can therefore for instance be used as a marking, against product counterfeiting. When introducing the marker into plastics of a plastic bottle a particular reliability regarding their identification can be obtained since neither the label nor the Inscription are necessary, which can be lost.
Using the fluorescence decay time of the intrinsic fluorescence polymer materials can be clearly identified and in this way can be sorted in a completely separated manner automatically. Because of the high velocity of the detection process possibilities for sorting devices with high material throughput are opened. Because of the use of phase-sensitive detectors and integrative measurements electronic costs for detection units are beneficial. Furthermore the polymer materials can be marked for their detection with fluorescence dyes, like for example perylene ester, peryleneimides, and terryleneimides, which are detected in different spectral regions via their fluorescence, or also via their individual fluorescence decay times in various polymer materials. Due to a binary combination of the marker a multiplication of the detection possibilities is provided. The identification can be realized via their spectral regions as well as via their individual decay times in that respective polymers.
pulsed light sources are used; preferred light sources are semiconductor light sources like laser diodes and light diodes, preferably comprising gallium nitride, or also gas discharge lamps.
Figure next spring from left to right: UVNIS—absorption—(each on the left) and fluorescence spectra (each on the right) of perylene ester 1 (buttons), the peryleneimide 2 (solid) and of terryleneimide 3 (best) in chloroform.
Number | Date | Country | Kind |
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10 2014 004 529.3 | Mar 2014 | DE | national |
Filing Document | Filing Date | Country | Kind |
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PCT/DE2015/000102 | 3/4/2015 | WO | 00 |