Polypropylene Contamination in Post-Consumer Polyolefin Waste: Characterisation, Consequences and Compatibilisation
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polymers Article Polypropylene Contamination in Post-Consumer Polyolefin Waste: Characterisation, Consequences and Compatibilisation Erdal Karaagac, Mitchell P. Jones , Thomas Koch and Vasiliki-Maria Archodoulaki * Institute of Materials Science and Technology, Faculty of Mechanical and Industrial Engineering, Technische Universität Wien, 1060 Vienna, Austria; erdal.karaagac@tuwien.ac.at (E.K.); mitchell.jones@tuwien.ac.at (M.P.J.); thomas.koch@tuwien.ac.at (T.K.) * Correspondence: vasiliki-maria.archodoulaki@tuwien.ac.at Abstract: Plastic recycling strikes a balance between functional, mass producible products and envi- ronmental sustainability and is pegged by governments for rapid expansion. However, ambitious targets on recycled material adoption across new markets are at odds with the often heterogenous properties of contaminated regranulates. This study investigated polypropylene (PP) contamination in post-consumer low-density polyethylene (PE-LD) and mixed polyolefin (PO) regranulates. Cali- bration curves were constructed and PP content, its effect on mechanical properties and property recovery in compatibilised material assessed. FT-IR band ratios provided more reliable estimations of PP content than DSC melt enthalpy, which suffered considerable error for PP copolymers. PE-LD regranulates contained up to 7 wt.% PP contamination and were considerably more brittle than virgin PE-LD. Most mixed PO regranulates contained 45–95 wt.% PP and grew more brittle with increasing PP content. Compatibilisation with 5 wt.% ethylene-based olefin block copolymer resulted Citation: Karaagac, E.; Jones, M.P.; Koch, T.; Archodoulaki, V.-M. in PE-LD blends resembling virgin PE-LD and considerable improvements in the properties of mixed Polypropylene Contamination in PO blends. These results illustrate the prevalence of PP in recycled PE, challenges associated with its Post-Consumer Polyolefin Waste: quantification, effect on mechanical properties, and compatibilisation viability, thereby representing Characterisation, Consequences and an important step towards higher quality regranulates to meet the recycling demands of tomorrow. Compatibilisation. Polymers 2021, 13, 2618. https://doi.org/10.3390/ Keywords: post-consumer waste; mechanical recycling; polyethylene; polypropylene; contamination; polym13162618 composition; tensile properties; impact properties; compatibilisation Academic Editors: Sheila Devasahayam, Raman Singh and Vladimir Strezov 1. Introduction With growing emphasis and legislative action on improving environmental sustain- Received: 22 June 2021 Accepted: 4 August 2021 ability, plastic recycling has become a forerunner in the race to optimise waste management Published: 6 August 2021 practices, reduce reliance on fossil fuels and adopt closed loop circular economy principles across the globe. The European Commission aims to increase the use of recycled plastics in Publisher’s Note: MDPI stays neutral new products to 10 million tons/year by 2025 [1] and recycle 55% of all plastic packaging with regard to jurisdictional claims in waste across the EU by 2030 [2]. Polyolefins (PO), such as polyethylene (PE) and polypropy- published maps and institutional affil- lene (PP), are popular packaging materials and represent more than half of the 29 million iations. tons of plastic waste collected in the EU each year [3,4]. Such numbers very effectively illustrate the importance PO will play in meeting new recycling targets. However, to do so, the use of these recycled plastics will need to be expanded to new applications for which recycled material hasn’t traditionally been suitable due to issues with material properties Copyright: © 2021 by the authors. stemming from contamination [4]. Licensee MDPI, Basel, Switzerland. Recycled plastics often contain both inorganic and polymer-based contamination, This article is an open access article which results in mechanical properties that diverge from application-specific targets and distributed under the terms and limit their use to sectors utilising lower grade materials, such as agriculture and construc- conditions of the Creative Commons tion [5]. This contamination often results from flawed sorting practices, which struggle Attribution (CC BY) license (https:// to economically separate materials with very similar characteristics, such as polymers of creativecommons.org/licenses/by/ very similar density [6]. PP is a common contaminant in both low-density polyethylene 4.0/). (PE-LD) and mixed PO regranulates [7]. Several recent studies generically characterise Polymers 2021, 13, 2618. https://doi.org/10.3390/polym13162618 https://www.mdpi.com/journal/polymers
Polymers 2021, 13, 2618 2 of 12 selected PE regranulates, providing differential scanning calorimetry (DSC) thermograms and Fourier transform infrared (FT-IR) spectra, as well as thermal degradation and me- chanical properties, such as tensile, impact, fracture toughness, and hardness [4,8–10]. The effect of contamination on recycled polyolefins, including that from other polyolefins, and methodologies for the identification of such contaminants are also thoroughly documented in the literature [11–16]. However, a structured investigation centered on the characterisa- tion of the PP constituent of PP contaminated PE blends, its effect on mechanical properties, and improvements possible through compatibilisation is clearly lacking. This study aimed to investigate PP contamination in post-consumer PE-LD and mixed PO regranulates using the PP content as a base parameter and reference point for analysis rather than arbitrarily characterising these very heterogenous and often incomparable ma- terials. DSC-based melt enthalpy and FT-IR band ratios were used to construct calibration curves to estimate blend PP content across a range of different PP types and their reliability contrasted. Tensile and tensile impact mechanical properties were then assessed and the influence of the PP content on these properties investigated. Finally, the regranulates were compatibilised to improve their mechanical properties and achieve a viable recycled substitute for virgin PE. 2. Materials and Methods 2.1. Materials Film grade 290E low density polyethylene (PE-LD) (Dow Chemical Company, Mid- land, MI, U.S.A), blow moulding grade Hostalen GF4750 high density polyethylene (PE- HD) (LyondellBasell, Rotterdam, The Netherlands) and injection moulding grade HF700SA polypropylene (PP) (Borealis, Vienna, Austria) were purchased as reference materials and used to construct melting enthalpy and FT-IR band ratio calibration curves for calculating PP content in PE-LD and mixed PO blends. HD601CF film grade, HC600TF thermoforming grade and HA104E extrusion grade homopolymer PP, BA202E extrusion grade block- and RD208CF random copolymer PP were purchased from Borealis (Vienna, Austria) to inves- tigate the effect of various types of PP common in regranulates on melting enthalpy and FT-IR band ratio calibration curves. P01-1,2,3, P03-1,2,3, and P05-1,2,3 PE-LD regranulates were provided by Walter Kunststoffe Regranulat (Gunskirchen, Austria). Purpolen PE Grau (PPE), Purpolen PP Grau (PPP), Dipolen H (DPH), Dipolen PP Grau (DPP), Dipolen S Grau (DPS), and Dipolen SP Grau (DSP) mixed PO regranulates were provided by MTM Regranulat (Niedergebra, Germany). INFUSE ethylene-based olefin block copolymer with glass transition and melting temperatures of −65 ◦ C and 118 ◦ C, respectively, and a tensile elongation at break of 1000% was provided by Dow Chemical Company (Midland, MI, USA) for use as compatibiliser. All materials were used as received. 2.2. Prepatation of Virgin, Regranulate and Compatibilised Blends Blends of virgin PE-LD and PP used to construct melting enthalpy and FT-IR band ratio calibration curves for PE-LD regranulates were prepared using a HAAKE MiniLab II twin-screw extruder (Thermo Scientific, Waltham, MA, USA) running at 180 ◦ C with a screw speed of 100 rpm and dwell time of 5 min. These lower temperature conditions were selected to minimize material degradation during extrusion. PP contents of 2, 5, 8, 10, 12, 15, 20, and 25 wt.% were weighed and hand mixed with PE-LD prior to extrusion. Melt mass-flow rates were calculated in accordance with ISO 1133-1:2011 [17]. Virgin PE-HD and PP blends were used to construct melting enthalpy and FT-IR band ratio calibration curves for mixed PO regranulates. These were prepared using an Extron- Mecanor SWL0914-1 single screw extruder (Toijala, Finland) with a nozzle temperature of 200 ◦ C running at 75 rpm. PE-HD blends with a PP content of 2, 8, 10, 20, 30, 40, 50 60, 70, 80, 90, 92, 95, and 98 wt.% were weighed, hand mixed and extruded twice. Pure PE-HD and PP references were also prepared under the same conditions. An overview of the calibration curves used in this study, the materials, and sample compositions used to
Polymers 2021, 13, 2618 3 of 12 generate them and the regranulates subsequently assessed with each curve, is provided in Table 1. Table 1. Overview of the calibration curves utilised in this study, the materials and sample com- positions used to generate them and the regranulates that were subsequently analysed using each respective calibration curve. Regranulates Calibration Curve Material Sample Compositions Analysed with Curve PE-LD 290E PP 601CF PP HC600TF PE-LD with 2, 5, 8, 10, 12, 15, 20 PP type P01 (Table 2) PP HA104E and 25 wt.% PP PP BA202E PP RD208CF PE-LD 290E PE-LD with 2, 5, 8, 10, 12, 15, 20 P01, P03, P05 PE-LD regranulate PP HF700SA and 25 wt.% PP (Table 3) PE-HD with 2, 8, 10, 20, 30, 40, PPE, PPP, DPH, Mixed PO PE-HD GF4750 50 60, 70, 80, 90, 92, 95 and DPP, DPS, DSP regranulate PP HF700SA 98 wt.% PP (Table 3) PE-LD (P01, P03 and P05) and mixed PO (PPE, PPP, DPH, DPP, DPS and DSP) re- granulates were again prepared using a HAAKE MiniLab II twin-screw extruder (Thermo Scientific, Waltham, MA, USA). Extruded plastic was collected from the die, cut into small pieces and compression moulded into sheets at 190 ◦ C using a Collin P 200 P laboratory press. Preheating was completed at 150 ◦ C and 8 bar (hydraulic press pressure) for 10 min, heating from 150–190 ◦ C at 22 bar for 8 min, followed by compression at 190 ◦ C and 30 bar for 5 min. Samples were then cooled from 190 ◦ C to 30 ◦ C over 20 min at 10 K/min and 35 bar. Blends compatibilised with 5 wt.% ethylene-based olefin block copolymer were prepared in the same way. The compatibiliser and its content (5 wt.%) were selected based on an extensive study of PE-HD compatibilisation, recommending its use in quantities of 4–8 wt.% [7]. 2.3. Melting Enthalpy and FT-IR Band Ratio Characterisation and Calibration Curve Generation Melting enthalpy was assessed using a TA Instruments Q 2000 differential scanning calorimeter (DSC) (New Castle, DE, USA). An ~8 mg sample mass of each polymer blend was deposited in an alumina testing pan and sealed. Samples were heated to 200 ◦ C at 10 K/min, cooled at the same rate to room temperature, and then reheated under the same heating conditions as previously described. A nitrogen atmosphere was maintained at all times using a flow rate of 50 mL/min. The melting enthalpy ∆Hm of the second heating run was analysed using TA Instruments Universal Analysis 2000 (v. 4.5A, b. 4.5.0.5). Analysis was based on four replicate specimens for each sample type. The use of calibration curves based on DSC melting enthalpy to calculate the composi- tion of polyolefin blends is documented in the literature [13–16]. Melting enthalpy-based calibration curves were constructed based on the known PP content of the series of virgin PE-LD/PP and PE-HD/PP blends (X axis) and the melting enthalpy (J/g) defined as the area under the melting peak on the second heating run (Y axis). A linear fit was applied to the resulting points using OriginPro 2019b (v. 9.6.5.169) and the equation noted. The PP content of PE-LD and mixed PO regranulates could then be calculated by measuring their melting enthalpies using DSC and substituting these values into the equation to provide a solution. IR spectra were recorded using a Bruker TENSOR 27 Fourier transform infrared (FT- IR) instrument in attenuated total reflection (ATR) mode. Three spectra were recorded from different portions of four individual samples to verify homogeneity. Spectra were recorded from 4000 to 400 cm−1 .
Polymers 2021, 13, 2618 4 of 12 FT-IR band ratio-based calibration curves enabling the calculation of the PP content in PE-LD regranulates were constructed based on the absorbance bands (amplitude) of the series of virgin PE-LD/PP blends of known composition at 1376 cm−1 and 1461 cm−1 . This process is documented in ASTM D7399-18:2018 [18] and the literature [13,15,19]. The known PP content of each virgin blend (X axis) was plotted against the ratio of these bands (1376 cm−1 /1461 cm−1 ) (Y axis), a linear fit applied to the resulting points, the equation noted and used as previously described. The same procedure was completed for the series of virgin PE-HD/PP blends to produce a calibration curve for mixed PO regranulates with the only exception that the absorbance (amplitude) at the bands 720 cm−1 and 1168 cm−1 were used in the ratio 1168 cm−1 /(1168 cm−1 + 720 cm−1 ). 2.4. Tensile (Impact) Mechanical Testing of the Virgin, Regranulate and Compatiblised Blends Dog bone shaped tensile test specimens were cut from compression moulded sheets (1.8–1.9 mm thick) according to type 5A, ISO 572-2:2012 [20]. Seven replicate tests were performed for each sample type at 23 ◦ C and a testing velocity of 10 mm/min using a Zwick 050 universal testing system equipped with a 1 kN load cell and extensometer. Tensile modulus and elongation at break were calculated using the ZwickRoell testXpert III software. It is important to note that a constant speed of 10 mm/min was used over the entire tensile testing range rather than testing as two distinct segments as suggested in ISO 572-2:2012. The strain rate calculated based on the narrow parallel part of the specimen (0.4 min−1 ) is subsequently 40 times higher than the strain rate of the special ‘modulus segment’ described in ISO 572-2:2012 (0.01 min−1 ). Tensile impact test specimens were cut from compression moulded sheets (1.1–1.2 mm thick) according to method A, ISO 8256:2004 [21]. Seven replicate tests were performed for each sample type at 23 ◦ C using an Instron CEAST 9050 impact pendulum equipped with a 2 J hammer and 15 g crosshead mass. Tensile impact strength (atN , kJ/m2 ) was calculated based on the corrected impact work (Ec , J), distance between notches (x, mm), and thickness of the narrow parallel test specimen section (h, mm) (Equation (1)). Ec atN = ·103 (1) x·h 2.5. Thermal Degradation Analysis of the Regranulate The thermal degradation properties and inorganic filler content of PE-LD (P05) and mixed PO (PPE, PPP, DPH, DPP, DPS, and DSP) regranulates were assessed using TA Instruments thermogravimetric analysis (TGA) Q500. Regranulate samples of ~10 mg were placed in an alumina crucible and heated from 30 to 600 ◦ C at a heating rate of 10 K/min in an air atmosphere. 2.6. Morphological and Elemental Analysis of the Regranulate and Compitablised Blends Scanning electron microscopy (SEM) imaging and energy dispersive X-ray spec- troscopy (EDS) elemental analysis were used to investigate the fracture surfaces of the tensile impact tested PE-LD (P05) and mixed PO (PPE, PPP, DPH, DPP, DPS, and DSP) regranulate specimens and composition of inorganic regranulate residues following TGA, respectively. A Philips XL30 scanning electron microscope was used for the tensile impact tested samples while a ZEISS EVO 10 scanning electron microscope fitted with a ZEISS SmartEDS system was used for the inorganic regranulate residues. 3. Results and Discussion 3.1. Characterisation of Polypropylene Contamination in Post-Consumer Waste DSC thermograms of virgin blends of known composition (neat PE-LD, PE-LD with 2, 5, 8, 10, 12, 15, 20, 25 wt.% PP and neat PP) indicated increasing area under the melting peak (melting enthalpy) at 161 ◦ C, which is associated with PP, as the PP content increased (Figure 1). P01,03,05 PE-LD regranulates exhibited melting peaks at 109 ◦ C and 125 ◦ C,
3. Results and Discussion 3.1. Characterisation of Polypropylene Contamination in Post-Consumer Waste DSC thermograms of virgin blends of known composition (neat PE-LD, PE-LD with Polymers 2021, 13, 2618 2, 5, 8, 10, 12, 15, 20, 25 wt.% PP and neat PP) indicated increasing area under the melting 5 of 12 peak (melting enthalpy) at 161 °C, which is associated with PP, as the PP content increased (Figure 1). P01,03,05 PE-LD regranulates exhibited melting peaks at 109 °C and 125 °C, indicatingthat indicating thatthey theyprimarily primarilycomprised comprisedPE-LD PE-LD and and PE-LLD PE-LLD [22]. [22]. An An additional additional melting melting peak at at 161 161 °C◦ C suggested a smaller peak smaller quantity quantityof ofPP PPpresent presentasascontamination. contamination.The Thearea under area un- the the der PP melting PP melting peakpeak varied considerably varied by PE-LD considerably regranulate, by PE-LD rangingranging regranulate, from thefrom shortest the and narrowest shortest peak associated and narrowest with P01 with peak associated to theP01 highest to theand widest highest andpeak for P05. widest peakMixed PO for P05. regranulates Mixed (PPE, PPP, DHP, PO regranulates (PPE, DPP, PPP,DPS and DHP, DSP)DPS DPP, exhibited and DSP)sizable meltingsizable exhibited peaks between melting 125–132 ◦ C and at 161 ◦ C attributable to PE-HD and PP, respectively. PPE exhibited the peaks between 125–132 °C and at 161 °C attributable to PE-HD and PP, respectively. PPE largest area exhibited theunder largestthe melting area under peak associated the melting peakwith PE-HDwith associated andPE-HD the smallest and theassociated smallest with PP, while PPP and DPP had the smallest area under the PE-HD melting associated with PP, while PPP and DPP had the smallest area under the PE-HD melting peak and the largest peak andunder the PPunder the largest peak. the PP peak. 2 2 VIRGIN PE-LD REGRANULATES 3 MIXED PO REGRANULATES PE-LD PP PE-LLD PE-HD Tm = 109 °C Tm = 161 °C PE-LD Tm = 125 °C Tm = 125-132 °C Heat flow (W/g) Heat flow (W/g) 2 Heat flow (J/g) 1 1 Tm = 109 °C PP PP Tm = 161 °C Tm = 161 °C 1 0 0 0 -1 PPE PE-LD -1 PPP PP -1 P01-1 DPH -2 -2 DPP 10 K/min 10 K/min P03-1 10 K/min DPS Exothermic Exothermic P05-1 Exothermic DSP -3 -3 -2 0 50 100 150 200 0 50 100 150 200 0 50 100 150 200 Temperature (°C) Temperature (°C) Temperature (°C) (a) (b) (c) 3 0.8 BLENDS P01-1 PPE 0.55 P03-1 PPP 2 wt.% PP Heat flow (W/g) Heat flow (W/g) Heat flow (W/g) P05-1 DPH 5 wt.% PP 0.7 DPP 8 wt.% PP 2 10 wt.% PP DPS 0.6 12 wt.% PP DSP 0.50 15 wt.% PP 20 wt.% PP 0.5 25 wt.% PP 1 0.4 0.45 0 130 140 150 160 170 180 190 140 150 160 170 180 100 120 140 160 180 Temperature (°C) Temperature (°C) Temperature (°C) (d) (e) (f) Figure Figure1. 1.Differential Differential scanning scanning calorimetry calorimetry (DSC) thermograms of (DSC) thermograms of (a) (a) virgin virgin PE-LD PE-LDand andpolypropylene polypropylene(PP)(PP)with with(d) (d)magni- mag- nification fication ofofPP PPmelting meltingpeak peak(T(T m m = 161 ◦°C) illustrating melt enthalpy differences by blend PP content (2, 5, 8, 10, 12, 15, 20 = 161 C) illustrating melt enthalpy differences by blend PP content (2, 5, 8, 10, 12, 15, 20 and 25 wt.%), (b) P01,03,05 PE-LD regranulates with (e) magnification of PP melting peak (T m = 161 °C) ◦ and and 25 wt.%), (b) P01,03,05 PE-LD regranulates with (e) magnification of PP melting peak (Tm = 161 C) and (c) PPE, PPP, (c) PPE, PPP, DPH, DPP, DPS and DSP mixed PO regranulates with (f) magnification of PE-HD (Tm = 125–132 ◦°C) and PP (Tm = 161 °C) DPH, DPP, DPS and DSP mixed PO regranulates with (f) magnification of PE-HD (Tm = 125–132 C) and PP (Tm = 161 ◦ C) melting peaks. melting peaks. FT-IR FT-IR spectra spectraof of virgin virgin blends blendsof of known knowncomposition compositionindicated indicatedincreasing increasingbandbandin- in- tensity tensity at at 1376 1376 cm cm−,1 ,which −1 whichisisassociated associated with with −CH −CH3 3plane planebending, bending,with withincreasing increasing PP PP content content (Figure (Figure 2). 2). The band intensity The band intensity atat 1461 1461cmcm−−11 associated with − associated with −CH CH22plane plane bending bending simultaneously decreased. P01,03,05 PE-LD regranulates exhibited simultaneously decreased. P01,03,05 PE-LD regranulates exhibited the same 1376 the same 1376 cmcm−−11 band bandininaddition additiontotoaalight lightshoulder shoulderatat3200–3500 3200–3500cm cm−associated −1 1 associatedwith -OH with -OHandandbands at bands 1565–1600 cm −1 resulting − 1 from–NH stretching. These bands could at 1565–1600 cm resulting from–NH stretching. These bands could indicate traces ofindicate traces of poly- amide, polyester, polyamide, or low polyester, or molecular low molecular weight contaminants weight contaminants [23].[23]. Mixed PO regranulates Mixed PO regranulatesex- hibited bands at 1168 cm −1−attributable 1 to −CH wagging in PP exhibited bands at 1168 cm attributable to −CH3 wagging in PP and 720 cm resulting 3 and 720 cm −11 resulting − from–CH from–CH22−rocking −rockingininPE-HD PE-HD[24]. [24].
Polymers2021, Polymers 2021,13, 13,2618 x FOR PEER REVIEW 66 of 12 of 12 VIRGIN PE-LD REGRANULATES MIXED PO REGRANULATES DSP Absorbance Absorbance Absorbance DPS P05-1 DPP PE-LD DPH P03-1 PPP PP P01-1 PPE 3500 3000 2500 2000 1500 1000 500 3500 3000 2500 2000 1500 1000 500 3500 3000 2500 2000 1500 1000 500 Wavenumber (cm ) -1 -1 Wavenumber (cm-1) Wavenumber (cm ) (a) (b) (c) PE-LD BLENDS P01-1 PPE 2 wt-% PP P03-1 PPP 5 wt-% PP DPH P05-1 Absorbance 8 wt-% PP Absorbance DPP Absorbance 10 wt-% PP DPS 12 wt-% PP 15 wt-% PP DSP 20 wt-% PP 25 wt-% PP PP 1600 1550 1500 1450 1400 1350 1500 1450 1400 1350 1200 1180 1160 1140 750 720 690 660 -1 Wavenumber (cm -1 ) Wavenumber (cm-1) Wavenumber (cm-1) Wavenumber (cm ) (d) (e) (f) Figure 2. Figure 2. Fourier Fourier transform transform infrared infrared (FT-IR) (FT-IR) spectra spectra of of (a) (a) virgin virgin PE-LD PE-LD and and polypropylene polypropylene (PP) (PP) with with (d) (d) magnification magnification illustrating differences in the 1376 cm (−CH3 plane bending) and 1461 cm (−CH2 plane bending) bands by illustrating differences in the 1376 cm − −1 (−CH3 plane bending) and 1461 cm 1 −−1 1 (−CH 2 plane bending) bands blend PP PP by blend content (0, 2, 5, 8, 10, 12, 15, 20, 25 and 100 wt.%), (b) P01,03,05 PE-LD regranulates with (e) magnification content (0, 2, 5, 8, 10, 12, 15, 20, 25 and 100 wt.%), (b) P01,03,05 PE-LD regranulates with (e) magnification of 1376 cm 1 of 1376 cm−−1 (−CH3 plane bending) and 1461 cm (−CH2 plane bending) bands and (c) PPE, PPP, DPH, DPP, DPS and DSP mixed PO −1 (−CH3 plane bending) and 1461 cm−1 (−CH2 plane bending) bands and (c) PPE, PPP, DPH, DPP, DPS and DSP mixed PO regranulates with (f) magnification of 1168 cm−1 (−CH3 wagging) and 720 cm−1 (−CH2−rocking) bands. regranulates with (f) magnification of 1168 cm−1 (−CH3 wagging) and 720 cm−1 (−CH2 −rocking) bands. Melting enthalpy-based Melting enthalpy-based calibration calibrationcurves curveswere werealmost almost identical identical forfor all all virgin homo- virgin ho- polymer PPs (HD601CF, HC600CF, and HA104E) used mopolymer PPs (HD601CF, HC600CF, and HA104E) used to simulate contaminantsto simulate contaminants in PE- in LD (Figure PE-LD 3, Table (Figure 2). Block 3, Table copolymer 2). Block copolymerPP BA202E PP BA202E also exhibited a similar also exhibited curve. curve. a similar How- ever, random However, randomcopolymer copolymer PP PPRDRD 208CF 208CF hadhada aradically radicallydifferent differentgradient gradient to to the other the other curves. This discrepancy can be explained by the differing degree of curves. This discrepancy can be explained by the differing degree of crystallinity betweencrystallinity between the homopolymer the homopolymer (~43–45%), (~43–45%),block–(~37), block–(~37),and andrandom randomcopolymer copolymer PPs (~34%), PPs (~34%), which whichaf- fects the melting enthalpy. This makes quantification of the PP affects the melting enthalpy. This makes quantification of the PP content in P01,03,05content in P01,03,05 PE- LD regranulates, PE-LD regranulates, potentially potentiallycontaminated contaminated with with anyanytype typeofofPP,PP, challenging challenging using using the the melting enthalpy. melting enthalpy. Estimated EstimatedPP PPcontent contentininP01 P01PE-LD PE-LD regranulate regranulate ranged ranged fromfrom3.43.4 to 8.9 to wt.% 8.9 using wt.% thisthis using method method based on on based thethe different differentPP PPtypes. types. FT-IR-basedvalues FT-IR-based valueswereweregenerally generallyslightly slightly higher higher than than those those based based on the on the melting melting en- enthalpy, a phenomenon also noted in other studies [15] and most thalpy, a phenomenon also noted in other studies [15] and most likely due to the migration likely due to the mi- gration of of PP PP to the to thesurface material material surface during during compression compression moulding. Homopolymer moulding. Homopolymer (HD601CF), (HD601CF), block–(PP block–(PP BA202E), andBA202E), random and random(PP copolymer copolymer RD 208CF) (PPPP RD 208CF) PP calibration calibration curves were curvesbetter much were aligned much betterwhenaligned when using the FT-IRusing band the ratio FT-IR1376band −1 /1461 cmratio 1376cm cm−−11/1461 . Thecm −1. esti- The estimated mated PP contentPPincontent PE-LD in PE-LD regranulate regranulate ranged from ranged 3.7 to from 3.7 to 5.3 wt.% 5.3 wt.% across across the the different PP different types. ThisPPmakes types.FT-IR This more makes FT-IR for suitable more suitablethe estimating forPP estimating content inthe PP content P01,03,05 PE-LD in regranulates. P01,03,05 PE-LD Theregranulates. similarity between the FT-IR The similarity band ratio-based between the FT-IR band calibration ratio-basedcurves also calibra- allows the provision tion curves also allows of the a generic equation provision for calculating of a generic equationblend PP contentblend for calculating independent PP content of PP type (Equation independent of PP(2)), typewhich is useful (Equation (2)), since whichthe type ofsince is useful PP contamination the type of PPin regranulates contamination is inoften unknown. regranulates is This oftenmethod unknown.is also advantageous This method is also as itadvantageous is faster than DSC-based as it is faster melting than enthalpy DSC-based experiments and is non-destructive. melting enthalpy experiments and is non-destructive. = y= 0.014 0.014x + 0.098, + 0.098, R2 R=2 =0.91 0.91 (2) (2)
Polymers 2021, 13, x FOR PEER REVIEW 7 Polymers 2021, 13, 2618 7 of 12 PP content (wt.%) PP content (wt.%) 0 5 10 15 20 25 30 35 0 5 10 15 20 25 25 30 PP TYPES Crystallinity FOR PE-LD REGRANULATES 45.4% PP HD601CF 44.0% 0.6 Melt enthalpy (J/g) 20 Melt enthalpy (J/g) 25 PP HC600TF PP HA104E R2 > 0.99 42.7% Melting enthalpy 37.3% 2nd heating run Band ratio 20 PP BA202E PP RD208CF 15 y=0.88x-0.70, R2 = 0.99 0.4 15 10 10 33.9% 5 FTIR band ratio 0.2 5 1376 cm-1 / 1461 cm-1 2 y=0.02x+0.10, R = 0.97 0 Melting enthalpy 0 2nd heating run 0.0 (a) (b) 0.6 PP TYPES Crystallinity FOR MIXED PO REGRANULATES 200 PP HD601CF 45.4% 1.0 Melt enthalpy (J/g) 0.5 2 PP BA202E R > 0.99 37.3% Melting enthalpy PP RD208CF 33.9% 150 2nd heating run Band ratio Band ratio y=1.87x-6.69, R2 = 0.99 0.4 100 0.5 0.3 0.2 50 FTIR band ratio 1168 cm-1 / 1168 cm-1 + 720 cm-1 y=0.009x-0.008, R2 = 0.99 0.0 0.1 FTIR band ratio 0 1376 cm-1 / 1461 cm-1 0 5 10 15 20 25 30 35 0 20 40 60 80 100 PP content (wt.%) PE / PP content (wt.%) (c) (d) Figure 3. Calibration Figure 3. curves constructed Calibration based on (a)based curves constructed differential scanning calorimetry on (a) differential (DSC) melting scanning calorimetry enthalpy (DSC) melt- and (c) Fourier transform infrared (FT-IR) band ratios (1376 cm −1/1461 cm−1) of virgin PE-LD blends of ing enthalpy and (c) Fourier transform infrared (FT-IR) band ratios (1376 cm /1461 cm 1 ) of − 1known composition. − DSC melting enthalpy-based curves vary considerably by polypropylene (PP) type (especially BA202E block- and RD208CF virgin PE-LD blends of known composition. DSC melting enthalpy-based curves vary consider- random copolymers) and crystallinity, while FT-IR band ratio-based curves are less affected. Calibration curves for deter- ably by polypropylene (PP) type (especially BA202E block- and RD208CF random copolymers) mining PP content in (b) PE-LD and (d) mixed PO regranulates are constructed based on DSC melt enthalpy and FT-IR and cm band ratios 1376 crystallinity, −1/1461 cm−1while FT-IRregranulates for PE-LD band ratio-based curves and 1168 are less cm−1/(1168 cmaffected. −1 + 720 cm Calibration −1) for mixedcurves for PO regranulates. determining PP content in (b) PE-LD and (d) mixed PO regranulates are constructed based on DSC melt enthalpy −1 /1461 cm−1 for PE-LD regranulates and Table and FT-IR 2. Melt band ratios mass-flow 1376 cm rate (MFR, g/10 min) for 2.16 kg at 230 °C, degree of crystallinity (% − 1 1168 cm /(1168 − 1 cm + 720 − 1 cmequations ) for mixed PO regranulates. calibration curve for virgin homopolymer, block- and random copolymer polypropy (PP) and calculated PP content for P01 PE-LD regranulate by PP type based on the melting ent and FT-IRrate Table 2. Melt mass-flow band ratio g/10 (MFR, min) for 2.16 kg at 230 ◦ C, degree of crystallinity (%) and methods. calibration curve equations for virgin homopolymer, block- MFRand random (g/10 copolymer polypropylenes PP in P Crystallinity Method (PP) and calculated PP contentType for P01 PE-LD Material regranulate by PP type based Equation min) (%) on the melting enthalpy (wt.% and FT-IR band ratio methods. Homo PP HD601CF 8.0 45.4 ± 1.5 = 0.88x − 0.72 3.88 ± 0 PP MFR HC600TFCrystallinity 2.8 44.0 ± 1.6 = 0.87x PP − in0.25 P01 3.40 ± 0 Method Melting Type Material Equation PP HA104E (g/10 min) 0.8 (%) 42.7 ± 0.5 = 0.88x(wt.%) − 0.35 3.47 ± 0 enthalpy Homo Block PP HD601CF PP 8.0 BA202E 45.4 ± 0.31.5 y37.3 = 0.75x ± 0.2− 0.72 = 0.88x 3.88−±0.41 0.26 4.15 ± 0 Melting PP Random HC600TF 2.8 PP RD208CF 44.0 ± 8.01.6 ± 0.1− 0.25 = 0.87x y33.9 3.40+±0.12 = 0.29x 0.09 8.91 ± 0 enthalpy PP HA104E 0.8 42.7 ± 0.5 y = 0.88x − 0.35 3.47 ± 0.09 Block Homo PP BA202E PP HD601CF 0.3 8.00.2 37.3 ± y45.4 = 0.017x ± 1.5− 0.41 = 0.75x +0.14 4.15 ± 0.10 3.69 ± 0 FT-IR bandPP RD208CF Random Block BA202E 33.9 ± PP 8.0 0.30.1 = 0.29x y37.3 ± 0.2+ 0.12 8.91 ± = 0.013x +0.39 0.11 3.85 ± 0 ratio 45.4 ± = 0.017x y33.9 3.69 ± FT-IR band Homo PP Random HD601CF 8.0 PP RD208CF 8.01.5 ± 0.1+ 0.10 = 0.015x +0.90 0.08 5.30 ± 0 Block PP BA202E 0.3 37.3 ± 0.2 y = 0.013x + 0.11 3.85 ± 0.87 ratio Random PP RD208CF 8.0 33.9 ± 0.1 y = 0.015x + 0.08 5.30 ± 0.90 Generic PP calibration curves for P01,03,05 PE-LD regranulates based on both m ing enthalpy and FT-IR band ratios are provided in Figure 3. Similar curves are prov Generic PP calibration curves for P01,03,05 PE-LD regranulates based on both melting for mixed PO regranulates based on the melting enthalpy and FT-IR bands 720 cm− enthalpy and FT-IR band ratios are provided in Figure 3. Similar curves are provided 1168 cm−1, expressed as 1168 cm−1/(1168 cm−1 + 720 cm−1), of a series of virgin PE-HD (m for mixed PO regranulates based on the melting enthalpy and FT-IR bands 720 cm−1 ing enthalpy) and PP (FT-IR band ratio) blends of known composition. These calibr and 1168 cm−1 , expressed as 1168 cm−1 /(1168 cm−1 + 720 cm−1 ), of a series of virgin curves PE-HD (melting were used enthalpy) to (FT-IR and PP calculate theratio) band PP content blends in P01,03,05 of known PE-LD regranulates composition. These and PPP, DPH, DPP, DPS, and DSP mixed PO regranulates (Table 3).
Polymers 2021, 13, 2618 8 of 12 calibration curves were used to calculate the PP content in P01,03,05 PE-LD regranulates and PPE, PPP, DPH, DPP, DPS, and DSP mixed PO regranulates (Table 3). Table 3. Melt mass-flow rate (MFR, g/10 min) for 2.16 kg at a 190 ◦ C and b 230 ◦ C, and calculated polypropylene (PP) content of PE-LD and mixed PO regranulates based on the melting enthalpy and FT-IR band ratio calibration curves. Calculated PP Content (wt.%) Type MFR Material (g/10 min) Melting FT-IR Band Enthalpy Ratio Regranulate P01-1 3.0 ± 0.9 2.7 ± 1.7 Regranulate P01-2 3.1 ± 0.8 4.6 ± 0.2 Regranulate P01–3 2.6 ± 0.8 4.5 ± 0.6 Regranulate P03-1 5.9 ± 0.5 6.5 ± 0.1 PE-LD regranulate Regranulate P03-2 0.8 a 5.6 ± 0.5 7.2 ± 0.7 Regranulate P03-3 5.7 ± 0.7 6.8 ± 0.3 Regranulate P05-1 6.1 ± 2.8 7.3 ± 1.3 Regranulate P05-2 6.4 ± 1.7 7.4 ± 0.2 Regranulate P05-3 4.6 ± 1.3 6.9 ± 2.4 Purpolen PE (PPE) 0.5 a 6.9 ± 5.3 5.5 ± 1.2 Purpolen PP (PPP) 20 b 91.4 ± 0.8 87.5 ± 3.7 Mixed PO Dipolen H (DPH) 2.5 a 70.1 ± 1.9 46.1 ± 9.0 regranulate Dipolen PP (DPP) 10 b 93.8 ± 0.3 94.9 ± 2.3 Dipolen S (DPS) 5b 67.9 ± 0.4 44.5 ± 5.5 Dipolen SP (DSP) 7b 82.3 ± 0.6 60.0 ± 9.0 Discrepancies between PP content calculated based on melting enthalpy and FT-IR band ratios of PE-LD regranulates were
Polymers 2021, 13, x FOR PEER REVIEW 9 of 12 Polymers 2021, 13, 2618 9 of 12 3.3. Effect Effect of of Polypropylene Polypropylene Contamination on Tensile and Tensile Tensile Impact Impact Properties Properties P05 PE-LD PE-LD regranulate had a higher tensile modulus ( (E t ) than virgin PE-LD (453 MPa compared to compared to 320 320MPa), MPa),aaconsiderably considerablylower lowerelongation elongation atat break break (εb(ε) b(421% ) (421% compared compared to to 620%) 2 2 620%) andand tensile tensile impact impact strength strength ( )(a(84 tN )kJ/m (84 kJ/m 2 compared compared to 115). kJ/m to 115 kJ/m 2 These ).undesir- These undesirable able properties properties result result from thefrom the ~7PPwt.% ~7 wt.% PP contamination contamination presentpresent in this PE-LD in this PE-LD blend, blend, has which which has ahigher a much much higher than E than PE-LD t PE-LD and and hinders hinders miscibilitymiscibility and and adhesion adhesion between between blend blend components components (Figure 4).(Figure 4). MFR (g/10 min) MFR (g/10 min) MFR (g/10 min) 0 5 10 15 20 0 5 10 15 20 0 5 10 15 20 3000 700 Et (MPa) PE-LD MFR eb (%) PE-LD MFR atN (kJ/m2) PP content 120 PP content MIXED PO REGRANULATES PPP 600 PE-LD PE-LD 2000 DPP P05 REGRANULATES REGRANULATES DPH 500 80 DSP P05 DPS MIXED PO REGRANULATES PPP 1000 PPE 400 MIXED PO REGRANULATES DSP DPP 40 PPE DPS P05 PE-LD 100 REGRANULATES PPE MFR PE-LD PP content DPH DPS DSP DPP PPP DPH 0 0 0 0 20 40 60 80 100 0 20 40 60 80 100 0 20 40 60 80 100 PP content (wt.%) PP content (wt.%) PP content (wt.%) (a) (b) (c) PE-LD MIXED PO REGRANULATES PE-LD MIXED PO REGRANULATES PE-LD MIXED PO REGRANULATES 3000 1200 150 Original eb (%) Original atN (kJ/m2) Virgin PE-LD Et (MPa) PPP Compatabilised Compatabilised P05 DPP 900 2000 100 PPE P05 regranulate DPH Virgin PE-LD DSP PPE DPS 600 Virgin PE-LD P05 regranulate DPP DPS PPE PPP 1000 50 DSP DPH 300 DPH DPS DSP DPP PPP Original Compatabilised 0 0 0 (d) (e) (f) Figure 4. Effect Effectof ofpolypropylene polypropylene(PP) (PP)content content(hollow (hollowmarkers) markers)and and melt meltmass-flow mass-flow rate rate(MFR, solid (MFR, markers) solid on on markers) the the (a) tensile modulus (a) tensile modulus( ), (b) elongation at break ( (Et ), (b) elongation at break ) and (c) tensile impact strength ( (ε f ) and (c) tensile impact strength ) of PE-LD and mixed PO regranulates. (atN ) of PE-LD and mixed PO Effect of 5 wt.% ethylene-based olefin block copolymer the (d) , on oncopolymer (d) (e) the andE(f) ε of PE-LD and mixed PO regran- regranulates. Effect of 5 wt.% ethylene-based olefin block t , (e) f and (f) atN of PE-LD and mixed ulates (solid markers prior to compatibilisation and hollow markers after). PO regranulates (solid markers prior to compatibilisation and hollow markers after). Compatibilisation Compatibilisation with with 55 wt.% wt.% ethylene-based ethylene-based olefin olefin block block copolymer copolymer enhanced enhanced in- in- terfacial adhesion and provided an 81% improvement in the terfacial adhesion and provided an 81% improvement in the εbb of P05 (421% to ε of P05 (421% to 762%), 762%), aa value 23% higher than even even virgin virgin PE-LD PE-LD (762% compared with 620%). The The compatibiliser compatibiliser also improved improved stress stress transfer transfer between between the thephases phasesresulting resultingininaa39% 39%increase increasein the a inthe tN of kJ/m22to P05 (84 kJ/m to118 kJ/m2)2 )and 118 kJ/m andaacomparable comparablevaluevaluetoto that that of virgin PE-LD (115 kJ/m22).). (115 kJ/m SEM SEM micrographs micrographs indicated indicated that that the the already already present present necking necking inin P05 P05 was was increased increased post- post- compatibilisation with withshear shearyielding yieldingthetheprimary primarydeformation deformation mechanism mechanism in both in both sam- samples ples (Figure (Figure 5). EThe 5). The of t of P05 P05 simultaneously simultaneously decreased decreased with compatibilisation with compatibilisation to 381a to 381 MPa, MPa, a 16% reduction 16% reduction which resulted which resulted in an Et just higher in an19% just 19% higher than virginthan PE-LD.virgin ThisPE-LD. is dueThis to theis due low to Et the low of ethylene-based of ethylene-based olefin blockolefin block which copolymer, copolymer, which encapsulates encapsulates the dispersed the dis- phase in the matrix persed phase and in the reduces matrixthe andEtreduces the Significantly, of the blends. of the blends.these results indicated Significantly, these resultsthat compatibilised P05 PE-LD regranulate exhibits competitive or better tensile indicated that compatibilised P05 PE-LD regranulate exhibits competitive or better tensile properties than even virginthan properties PE-LD evenfilms andPE-LD virgin can be films considered and cana viable recycled asubstitute. be considered viable recycled substi- tute. All mixed PO regranulates other than PPE exhibited high (≥~45 wt.%) PP contents and high melt mass-flow All mixed rates (MFR) PO regranulates other (2.5 than−20.0 PPE g/10 min) high exhibited better(≥~45 suited to injection wt.%) PP contentsthan and high melt mass-flow rates (MFR) (2.5−20.0 g/10 min) better suited to injection than
Polymers 2021, 13, x FOR PEER REVIEW 10 of 13 competitive or better tensile properties than even virgin PE-LD films and can be Polymers 2021, 13, 2618 considered a viable recycled substitute. 10 of 12 All mixed PO regranulates other than PPE exhibited high (≥~45 wt.%) PP contents and high melt mass-flow rates (MFR) (2.5−20.0 g/10 min) better suited to injection than compression moulding, compression moulding,which whichresulted resultedin in brittle tensile brittle properties. tensile Literature properties. does, does, Literature how- ever, indicate however, similar indicate properties similar in injection properties moulded in injection samplessamples moulded suggesting a more general, suggesting a more moulding method independent sensitivity of ε to the presence of mixtures general, moulding method independent sensitivity of ε to the presence of mixtures of b of polymers with different polymers withmolar massmolar different distributions in recycled materials mass distributions in recycled Blend Et increased [25].materials [25]. Blendwith increased with MFR and PP content, while ε decreased violently at elevated MFRsindi- MFR and PP content, while ε b decreased violently at elevated MFRs and PP contents, and cating PP the sensitivity contents, of this indicating theparameter sensitivitytoofthese this factors. parameteratN was also sensitive to these factors. to increasing was also MFR and PP content, dropping very quickly as PP content increased, sensitive to increasing MFR and PP content, dropping very quickly as PP content but then recovering slightly at MFR increased, ≥ 5recovering but then g/10 min and slightly at MFR ≥ PP contents ≥ 560 wt.%. g/10 min and PP contents ≥ 60 wt.%. P05 PPE DPS (a) (b) (c) (Compatibilised) (Compatibilised) (Compatibilised) (d) (e) (f) Figure 5.5. SEM micrographs of the tensile impact fracture surfaces of (a,d) P05 PE-LD, (b,e) PPE and (c,f) DPS mixed PO regranulates both regranulates both before before (a–c) (a–c) and and after after (d–f) (d–f) compatibilisation compatibilisation with with 55 wt.% wt.% ethylene-based ethylene-based olefin olefin block block copolymer. copolymer. P05 P05 PE-LD regranulates PE-LD regranulates demonstrated demonstrated necking, necking, especially especially in the compatibilised in the compatibilised material, material, with shear yielding with shear yielding the the primary primary deformation mechanism. deformation mechanism. PPE PPE exhibited exhibited aa brittle brittle fracture surface with fracture surface with signs signs of of energy energy dissipating dissipating effects, effects, debonding debonding and and fibrillation before and extensive plastic deformation and strong fibrillation after compatibilisation. DPS fracture surfaces fibrillation before and extensive plastic deformation and strong fibrillation after compatibilisation. DPS fracture surfaces were macroscopically brittle both before and after compatibilisation, although compatibilised material did exhibit some were macroscopically brittle both before and after compatibilisation, although compatibilised material did exhibit some regions of microplasticity. Higher magnification micrographs illustrating the phase morphology are provided in the insets. regions of microplasticity. Higher magnification micrographs illustrating the phase morphology are provided in the insets. PPP was the stiffest mixed PO regranulate with an of 2160 MPa, almost double PPP was the stiffest mixed PO regranulate with an Et of 2160 MPa, almost double that of DPS (1100 MPa), which had the lowest . PPP’s stiffness resulted from its high PP that of DPS (1100 MPa), which had the lowest Et . PPP’s stiffness resulted from its high content (~88 wt.%), which was approximately double that of DPS (~45 wt.%). Notably, PP content (~88 wt.%), which was approximately double that of DPS (~45 wt.%). Notably, DPP while also exhibiting a high (1780 MPa) wasn’t as stiff as PPP despite containing DPP while also exhibiting a high Et (1780 MPa) wasn’t as stiff as PPP despite containing more PP (~95 wt.% compared to ~88 wt.%). PPE, DPH, DPS, and DSP all fell in the range more PP (~95 wt.% compared to ~88 wt.%). PPE, DPH, DPS, and DSP all fell in the range of of 1220–1310 MPa, 1220–1310 MPa,despite despitePPEPPEhaving havinga amuch much lower lower PPPPcontent than content thethe than other mixed other PO mixed regranulates (~6 wt.% compared to ~45–60 wt.%). This low PP content PO regranulates (~6 wt.% compared to ~45–60 wt.%). This low PP content did, however, did, however, endow endow PPEPPE with with an an εεb 38–75 38–75 times times higher higher than than all all other other mixed mixed PO PO regranulates regranulates (114% (114% compared with 1.5–3.0%, respectively) and 1.5–3.5 times higher (50.0 compared with 1.5–3.0%, respectively) and 1.5–3.5 times higher atN (50.0 kJ/m compared kJ/m 2 compared 2 to to 14.7–34.4 14.7–34.4 kJ/m kJ/m2).). 2 The relativelyhigh The relatively high mixed Et of of mixed PO regranulates PO regranulates could potentially could potentially have beenhave been attributed attributed to mineralto mineral fillers, fillers, such such ascarbonate as calcium calcium carbonate or talc. However, or talc. However, the low inorganic the low inorganic residues residues in theand in the PE-LD PE-LDmixedandPO mixed PO regranulates regranulates (0.9–2.8 (0.9–2.8 wt%) couldwt%)be could be neglected neglected due to due the to the relatively high strain rate in the region of modulus determination and relatively high strain rate in the region of modulus determination and the high crystallinity the high of the samples resulting from the lower cooling rate used during compression moulding (10 K/min), as opposed to injection moulding. Compatibilisation with 5 wt.% ethylene-based olefin block copolymer doubled the εb of PPE (114% to 231%) and increased its atN by 50% (50.1 kJ/m2 to 75.2 kJ/m2 ). SEM micrographs revealed that the previously brittle fracture surface of PPE, which showed
Polymers 2021, 13, 2618 11 of 12 signs of energy dissipating effects, debonding and fibrillation was, extensively plastically deformed following compatibilisation with strong fibrillation visible (Figure 5). Compati- bilised PPP, DPH, DPP, DPS, and DSP all exhibited slightly higher εb (~2–8%). DPS also experienced a considerable increase in atN (14.1 kJ/m2 ) following compatibilisation but DPH, DPP and DSP were restricted to small improvements (1.8–7.6 kJ/m2 ), while the atN of PPP decreased (34.3 kJ/m2 to 30.9 kJ/m2 ). Whether compatibilised or not, DPS fracture surfaces macroscopically appeared brittle, with improvements in the compati- bilised material limited to some regions of microplasticity (Figure 5). Compatibilisation also resulted in a ~13–33% reduction in Et for all mixed PO regranulates. SEM micrographs of the tensile impact fracture surfaces of the other mixed PO regranulates are provided in Supplementary Figure S2. 4. Conclusions PE-LD and mixed PO regranulates can be contaminated with any number of different PP types, which complicates blend characterisation and results in mechanical properties that diverge from application-specific targets. Variations in the crystallinity and ethylene fractions of PP copolymers affect the PP melting peak and cause low temperature shoulders that overlap the PE melting peak in DSC thermograms. This study found calibration curves constructed based on reference blends with known concentrations of virgin material and FT- IR band ratios more reliable in estimating the PP content of regranulates than those based on DSC melting enthalpy. P05 regranulate was the most highly contaminated PE-LD blend containing ~7 wt.% PP, which made it considerably stiffer and more brittle than virgin PE- LD. Most mixed PO regranulates contained 45–95 wt.% PP which also resulted in stiff and brittle tensile and tensile impact properties that only worsened with increasing PP content and MFR. Compatibilisation with as little as 5 wt.% ethylene-based olefin block copolymer considerably reduced the tensile modulus of all regranulates in addition to increasing their elongation at break and tensile impact strength. Compatibilised P05 PE-LD regranulates in fact exhibited comparable tensile and tensile impact properties to virgin PE-LD and could be a viable recycled substitute. These results demonstrate the prevalence of PP in PE regranulates, the challenges associated with its characterisation, and the significant detrimental effects that it has on tensile and tensile impact properties. Identification of this contamination and its treatment with low quantities of suitable compatibilisers could radically improve the quality of recycled plastic reentering the market across the globe, promoting consumer confidence and interest in recycled products and improved environmental sustainability. Supplementary Materials: The following are available online at https://www.mdpi.com/article/10 .3390/polym13162618/s1. Figure S1: thermogravimetric analysis of P05 PE-LD and PPE, PPP, DPH, DPP, DPS and DSP mixed PO regranulates. Figure S2: SEM micrographs of the tensile impact fracture surfaces of PPP, DPH, DPP and DSP mixed PO regranulates. Author Contributions: Conceptualization, V.-M.A. and E.K.; methodology, V.-M.A., T.K., and E.K.; formal analysis, E.K.; writing—original draft preparation, M.P.J. and E.K.; writing—review and editing, V.-M.A. and T.K.; visualization, M.P.J.; supervision, V.-M.A..; funding acquisition, V.-M.A. All authors have read and agreed to the published version of the manuscript. Funding: This research was funded by FFG, Recycling Healing of polyOlefins (RHO); project number 867903. The authors acknowledge “Open Access Funding by TU Wien” for financial support through its Open Access Funding Program. Data Availability Statement: The data presented in this study are available on request from the corresponding author. Conflicts of Interest: The authors declare no conflict of interest. The funders had no role in the design of the study; in the collection, analyses, or interpretation of data; in the writing of the manuscript, or in the decision to publish the results.
Polymers 2021, 13, 2618 12 of 12 References 1. European Commission. Communication from the Commission to the European Parliament, the Council, the European Economic and Social Committee and the Committee of the Regions—A European Strategy for Plastics in a Circular Economy. Available online: https://eur-lex.europa.eu/legal-content/EN/TXT/?uri=COM%3A2018%3A28%3AFIN (accessed on 15 June 2021). 2. European Commission. Directive (EU). 2018/852 of the European Parliament and of the Council of 30 May 2018 Amending Directive 94/62/EC on Packaging and Packaging Waste. Available online: https://eur-lex.europa.eu/legal-content/EN/TXT/ ?uri=celex:32018L0852 (accessed on 15 June 2021). 3. Geyer, R.; Jambeck, J.R.; Law, K.L. Production, use, and fate of all plastics ever made. Sci. Adv. 2017, 3, 1207–1221. [CrossRef] [PubMed] 4. Gall, M.; Freudenthaler, P.J.; Fischer, J.; Lang, R.W. Characterization of Composition and Structure–Property Relationships of Commercial Post-Consumer Polyethylene and Polypropylene Recyclates. Polymers 2021, 13, 1574. [CrossRef] [PubMed] 5. Kazemi, Y.; Kakroodi, A.R.; Rodrigue, D. Compatibilization efficiency in post-consumer recycled polyethylene/polypropylene blends: Effect of contamination. Polym. Eng. Sci. 2015, 55, 2368–2376. [CrossRef] 6. Archodoulaki, V.-M.; Jones, M.P. Recycling viability: A matter of numbers. Resour. Conserv. Recycl. 2021, 168, 105333. [CrossRef] 7. Karaagac, E.; Koch, T.; Archodoulaki, V.M. The effect of PP contamination in recycled high-density polyethylene (rPE-HD) from post-consumer bottle waste and their compatibilization with olefin block copolymer (OBC). Waste Manag. 2021, 119, 285–294. [CrossRef] [PubMed] 8. De Camargo, R.V.; Saron, C. Mechanical–Chemical recycling of low-density polyethylene waste with polypropylene. J. Polym. Environ. 2020, 28, 794–802. [CrossRef] 9. Satya, S.K.; Sreekanth, P.S.R. An experimental study on recycled polypropylene and high-density polyethylene and evaluation of their mechanical properties. Mater. Today Proc. 2020, 27, 920–924. [CrossRef] 10. Gall, M.; Lang, R.W.; Fischer, J.; Niehoff, A.; Schmidt, S. Characterization of post-use polyethylene and polypropylene recy- clate blends for pipe applications. In Proceedings of the 19th Plastic Pipes Conference PPXIX, Las Vegas, NV, USA, 24–26 September 2018. 11. Ragaert, K.; Delva, L.; Van Geem, K. Mechanical and chemical recycling of solid plastic waste. Waste Manag. 2017, 69, 24–58. [CrossRef] [PubMed] 12. Signoret, C.; Caro-Bretelle, A.-S.; Lopez-Cuesta, J.-M.; Ienny, P.; Perrin, D. MIR spectral characterization of plastic to enable discrimination in an industrial recycling context: II. Specific case of polyolefins. Waste Manag. 2019, 98, 160–172. [CrossRef] [PubMed] 13. Camacho, W.; Karlsson, S. NIR, DSC, and FTIR as quantitative methods for compositional analysis of blends of polymers obtained from recycled mixed plastic waste. Polym. Eng. Sci. 2001, 41, 1626–1635. [CrossRef] 14. Kisiel, M.; Mossety-Leszczak, B.; Frańczak, A.; Szcz˛ech, D. Quantitative analysis of the polymeric blends. Prog. Rubber Plast. Recycl. Technol. 2019, 35, 75–89. [CrossRef] 15. Luijsterburg, B.; Goossens, H. Assessment of plastic packaging waste: Material origin, methods, properties. Resour. Conserv. Recycl. 2014, 85, 88–97. [CrossRef] 16. Larsen, Å.G.; Olafsen, K.; Alcock, B. Determining the PE fraction in recycled PP. Polym. Test. 2021, 96, 107058. [CrossRef] 17. The International Organization for Standardization. ISO 1133-1:2011 Plastics—Determination of the Melt Mass-Flow Rate (MFR) and Melt Volume-Flow Rate (MVR) of Thermoplastics—Part 1: Standard Method; The International Organization for Standardization: London, UK, 2011. 18. ASTM International. ASTM D7399-18 Standard Test Method for Determination of the Amount of Polypropylene in Polypropylene/Low Density Polyethylene Mixtures Using Infrared Spectrophotometry; ASTM International: West Conshohocken, PA, USA, 2018. 19. Higgins, F. Determination of Percent Polyethylene in Polyethylene/Polypropylene Blends Using Cast Film FTIR Techniques; Agilent Technologies: Danbury, CT, USA, 2012. 20. The International Organization for Standardization. ISO 527-2:2012 Plastics—Determination of Tensile Properties—Part 2: Test Conditions for Moulding and Extrusion Plastics; The International Organization for Standardization: London, UK, 2012. 21. The International Organization for Standardization. ISO 8256:2004 Plastics—Determination of Tensile-Impact Strength; The Interna- tional Organization for Standardization: London, UK, 2004. 22. Kyu, T.; Hu, S.R.; Stein, R.S. Characterization and properties of polyethylene blends II. Linear low-density with conventional low-density polyethylene. J. Polym. Sci. Part B Polym. Phys. 1987, 25, 89–103. [CrossRef] 23. Garofalo, E.; Di Maio, L.; Scarfato, P.; Di Gregorio, F.; Incarnato, L. Reactive compatibilization and melt compounding with nanosilicates of post-consumer flexible plastic packagings. Polym. Degrad. Stab. 2018, 152, 52–63. [CrossRef] 24. Siesler, H.W. Infrared and Raman spectroscopy of polymers. In Practical Spectroscopy; Marcel Dekker Inc.: New York, NY, USA, 1980; Volume 4. 25. Kamleitner, F.; Duscher, B.; Koch, T.; Knaus, S.; Archodoulaki, V.-M. Long chain branching as an innovative up-cycling process of polypropylene post-consumer waste—Possibilities and limitations. Waste Manag. 2017, 68, 32–37. [CrossRef] [PubMed]
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