METHOD FOR REDUCING THE MICROBIOLOGICAL LOADING OF CONTAINER PRODUCTS
20180297302 ยท 2018-10-18
Inventors
Cpc classification
B29C49/46
PERFORMING OPERATIONS; TRANSPORTING
B29L2031/712
PERFORMING OPERATIONS; TRANSPORTING
B29C49/42802
PERFORMING OPERATIONS; TRANSPORTING
B65B55/02
PERFORMING OPERATIONS; TRANSPORTING
B29C49/0021
PERFORMING OPERATIONS; TRANSPORTING
B29C71/04
PERFORMING OPERATIONS; TRANSPORTING
B29C2049/4664
PERFORMING OPERATIONS; TRANSPORTING
A61L2202/23
HUMAN NECESSITIES
International classification
B29C71/04
PERFORMING OPERATIONS; TRANSPORTING
B29C49/46
PERFORMING OPERATIONS; TRANSPORTING
B65B55/02
PERFORMING OPERATIONS; TRANSPORTING
Abstract
The invention relates to a method for reducing the microbiological loading of container products consisting at least partially of at least one plastic material, in which, as part of a first production process, a plastic granulate (29) is fed to an extruder device (19), which melts the granulate (29), which, as part of a further subsequent production process, is forwarded onto a blowmolding, filling and sealing machine for obtaining the respective container product, characterised in that, at least in parts of the first production process, the respective used plastic material undergoes at least one of the following treatment steps: high-energy radiation and/or plasma treatment and/or a gas having a sterilizing effect.
Claims
1. A method for reducing the microbiological impact of container products (11), which are at least partially made from at least one plastic material, in which, as part of a first production chain, a plastic granulate (29) is supplied to an extruder device (19), which melts the granulate (29) which, as part of an additional subsequent production chain, is transferred to a blow molding, filling and sealing production machine (1) for receiving the respective container product (11), characterized in that at least in parts of the first production chain the respective plastic material used is subjected to at least one of the following treatment steps: a high-energy radiation and/or a plasma treatment and/or a gas having a sterilizing effect.
2. The method according to claim 1, characterized in that the high-energy radiation is applied as radiation, gamma radiation, UV radiation, monochromatic UV radiation, X-rays, or a sequence of rapid light flashes to the in particular granulate-form plastic material.
3. The method according to claim 1, characterized in that for the plasma treatment an atmospheric plasma is used for the in particular granulate-form plastic material.
4. The method according to one of the preceding claims claim 1, characterized in that as a gas having a sterilizing action ozone, hydrogen peroxide ethylene oxide or nitrogen dioxide is used for the in particular granulate-form plastic material.
5. The method according to claim 1, characterized in that the respective treatment step takes place when the plastic granulate (29) is still brought together in pouch-like packages (37), after the opening of which the supply of the granulate (29) to the extruder device (19) takes place in the context of the first production chain.
6. The method according to claim 1, characterized in that the respective treatment step takes place when the plastic granulate (29), in the context of a separation within the first production chain, preferably in the context of a planar filling-type or hopper-type supply (27), is supplied to the screw conveyor (21) of the extruder device (19).
7. The method according to claim 1, characterized in that the respective treatment step takes place in such a way that the plastic granulate (29) separated by means of movement is treated at least along a part of its surface with a small infiltration depth of preferably a few micrometers.
8. The method according to claim 1, characterized in that as plastic materials to be treated thermoplastics, in particular polymers, such as PE, HDPE, PP, PET, COC, COP, EVOH and PA are used, preferably easily extrudable materials, such as Low Density Polyethylene (LDPE), PP or HDPE.
9. The method according to claim 1, characterized in that the individual production steps, in a sterile manner, lead to production cycle times for a low-germ, filled and closed container product (11) of 2 to 4 seconds.
10. The method according to claim 1, characterized in that, by means of the extruder device (19) a coextrusion method is realized, which leads to a multi-layer construction of the wall of the closed and filled container product (11) and in that only the polymer forming the inner wall of the thus coextruded container (11) is subjected to one of the preceding treatment steps for reducing biological contaminants.
Description
[0023] The method according to the invention is described in greater detail below with reference to a device according to the figures.
[0024] In schematic and not to scale depictions, said figures show
[0025]
[0026]
[0027]
[0028]
[0029] As can additionally be seen from
[0030] To assist with the detachment of the containers 11 from the walls of the individual molding parts 7 that move apart from one another at the output region, the demolding device 3 of the container chain 9 conveys a displacement movement, as is indicated in
[0031] This blow molding, filling and sealing production machine 1 and demolding device 3 according to
[0032] The processing temperature of polyethylene as the plastic material used is 170 C. to 200 C. and is 190 C. to 200 C. in the case of polypropylene materials, with the discharge pressure behind the extruder device 19 at the point of transition to the hose head 33 conventionally being approximately 200 bar to 400 bar.
[0033] As
[0034] One possibility for the granulate treatment according to the invention by means of the radiation source 35 consists of the application of gamma rays, which nevertheless requires a corresponding investment and safety costs. A safer option is the application of intensive ultra-short light flashes by so-called xenon lamps with a high quantity of UV-C radiation, in particular in the wavelength range of 190 nm to 290 nm by means of the radiation source 35, which is essentially described in document U.S. Pat. No. 5,786,598 A.
[0035] The use of monochromatic UV light of 193, 222, 248, 282, 308 and 354 nm wavelength is also possible, as is essentially described in the US documents 2005/0173652 A1 and 8 125 333 B2 (B. Ressler et al). Another possibility is the application of X-rays via the radiation source 35 according to the essential specifications in the WO publication 2008/129397 A8.
[0036] It has proven to be particularly advantageous for the solution according to the invention to use electron beam sources, which are often also described as beta emitters, with relatively low electron beam energy, as it is sufficient to sterilize the granulate surface with only a low depth of penetration of a few micrometers into the actual plastic material, with the beta rays being applied once again via the radiation source 35.
[0037] The desired radiation dosetypically in the range from ca. 10 to 25 kGraycan be easily adjusted by means of appropriate dimensioning of the electron beam source 35 and of the residence times of the granulate 29 in the radiation zone. In the context of the method, which is also referred to in technical parlance as an E-beam method, compact electron beamlines with 80 kV to 300 kV acceleration voltage are preferably used, with which it is frequently possible to achieve a penetration depth up to ca. 300 pm in the polymer materials typically used in the BFS process. In the case of a 300 mm radiation length on a granulate slide (not depicted), 25 kGray was achieved at just 120 kV to 150 kV acceleration voltage. In a surprising manner, known, disadvantageous chain degradation reactions were not observed even with polypropylene with the use of respective radiation via the radiation source 35 or did not in any case have a significant effect on the container quality of the individual containers 11 of the container chain 9.
[0038] Additionally or alternatively to the known radiation, a plasma treatment is also possible, with a non-thermal, atmospheric plasma preferably being used, as is described for example in the article by Tobias G. Klmpfl et al. Cold Atmospheric Air Plasma Sterilization against Spores and Other Microorganisms of Clinical Interest, published in the journal Applied and Environmental Microbiology, August 2012, Volume 78, No. 15 p. 5077-5082. In addition to the radiation source 35 or instead of same, an application device (not depicted in detail) is then employed for the atmospheric plasma to be created, which is to be introduced into or applied to the feeding hopper 27 or another feeding device for the extruder device 19. If only one plasma application process is to occur, the radiation source 35 can then be dispensed with in this respect.
[0039] It is furthermore possible to reduce the microbiological contaminants by means of chemical sterilization of the granulate. For this purpose, gases, such as ozone, hydrogen peroxide, ethylene oxide, nitrogen dioxide and other gases are used, as described for example in the CDC (Center Of Disease Control and Prevention) Guideline for Disinfection and Sterilization in Healthcase Facilities, 2008 by William A. Rutala et al. For the introduction of such gases, in the region of the feeding hopper 27 or another input device for the granulate 29 there is in turn provision of an input or application device (not depicted in detail) for said purpose.
[0040] As the depiction according to
[0041] In the context of a practical test of the solution according to the invention, for all of the exemplary embodiments materials, container sizes and machine settings were selected, which reflect the worst case concerning the mechanism of reduction of microbiological contaminants. As an example of microbiological contaminants, resistant spores of bacillus atrophaeus and bacillus pumilus were selected as test bacteria, as is standard in sterility testing. As container materials polymers which have low BFS working temperatures were additionally used, in order to keep thermal effects on the artificially added spores low. In addition, process parameters were selected which have only minimal effects on the spores but which result in container products having useable quality and standard output quantities. The throughput of polymer through the extruder 19 was thus set at the upper limit in order to thus minimize the duration of the heat effect on the artificially added spores.
[0042] Furthermore, a BFS system of model 460 by the company rommelag, Waiblingen, Germany, was used with a cycle time for the container production of ca. 3.5 seconds. As plastic granulate 29 polymers were used such as Purell LDPE of type 1840 H from the company LyondellBasell as well as Ineos LDPE of type Eltex MED PH 23H630 with working temperatures of the extruder 19 and of the hose head 33 in the range between 160 C. and 165 C.
[0043] In order to produce the contaminated granulate samples, endospores of the bacillus atrophaeus ATTC 9372 with a D-value, D.sub.160-C=0.2850.08 min were used. In a similar manner, spores of the reference germ for the radiation sterilization, bacillus pumilus ATCC 27142, were used. The spores were evenly distributed on the granulate 29 and the spore quantity was verified in a laboratory. The concentration range was from 10.sup.3 to 10.sup.6 cfu per gram. 10 ml capacity containers 11 filled with 6 ml liquid CASO nutrient solution were produced.
[0044] For further clarification: CASO nutrient solution is a complex medium, to which is added, besides glucose, peptone proteolytically obtained from milk protein (casein peptone) and peptone proteolytically obtained from soy flour (soy flour peptone). The casein peptone is rich in free amino acids and the soy flour peptone is distinguished by a high carbohydrate and vitamin content. Such nutrient media are particularly well suited for the cultivation of fastidious microorganisms.
[0045] For each test batch, more than 12,000 container products were produced, with the analytical procedure otherwise corresponding to the contents of the above-mentioned article by Frank Leo et al Evaluation of Blow-Fill-Seal-extrusion Through Processing Polymer Contaminated with Bacterial Spores and Endotoxin.
[0046] Firstly, three reference batches, i.e. without using the methods according to the invention, were produced for the purpose of germ reduction. For this purpose, a pin wrench distributer with holes, of the kind which is standard in extrusion technology, was used as a dynamic mixer device (as shown in the book by W. Michaeli), with no granulate treatment according to the invention taking place. This resulted in a germ count reduction in particular due to thermal effects of on average 10.sup.3 cfu/gram.
[0047] In one of the tests, the polymer granulate 29 contaminated with bacillus pumilus spores was then supplied via a vibrating slide, which is comparable to the feeding hopper 27, to the extruder device 19 and was radiated with an electron beam source 35 (e-beam) from the company Comet AG, Switzerland, in a contact-free manner but only at a very small distance with different radiation doses of ca. 10, 15 or 25 or 30 kGray. At a 300 mm radiation length, 25 kGray with 140 kV acceleration voltage was achieved, the thus-created ozone was extracted by suction; the contribution of the ozone to the germicidal action was not quantified, however it is generally not undesirable. If the ozone formation is undesirable for other reasons, this can be easily achieved in that air is replaced by an inert gas atmosphere consisting of for example nitrogen, argon or carbon dioxide.
[0048] These tests showed that a rotating movement of the granules of the plastic granulate 29 and a flat fanning out of the granulate 29 is advantageous in order to prevent shadowing as much as possible and thus to expose the entire surface of the granules to the high-energy radiation by means of the respective radiation source 35.
[0049] In addition, tests were realized using the electron beam source 35 described in detail above, in which tests spores of the bacillus atrophaeus contaminated the polymer granulate 29.
[0050] The respective radiation method resulted in an improvement factor compared with the reference measurement described above of at least the factor 1000, i.e. 1000 times the quantity of biological contaminants were able to be destroyed.
[0051] All of the above-mentioned methods according to the invention for minimizing the microbiological impact have the advantage that it is not necessary to sterilize an empty plastic container or even an already filled container, but merely the still solid granulate before the melting.
[0052] When producing multi-layer containers according to the BFS method, as disclosed for example in document DE 103 47 908 A1, the use of the respective described reduction method according to the invention may suffice solely for the polymer granulate which forms the inner layer of the container 11.
[0053] A method for reducing the microbiological impact of plastic container products, produced according to the blow molding, filling and sealing method, in which, before discharge from the hose head 33, the plastic is subjected to a treatment step with gases having a sterilizing action, high-energy radiation and/or a plasma treatment, is thus not described in the prior art.