1. Introduction
The development of novel food packaging with ecological character is rapidly increasing. Huge efforts are being made to reduce food waste and to close the product life cycle by extending the shelf life of food, using its waste for other processing and reusing primary or secondary packaging, either for food contact or for other purposes. Moreover, there is great scientific evidence in the application of various sources of food waste for the production of food packaging materials, using various natural biopolymers from the food waste industry. Accordingly, with the development of new extraction methods, e.g., microwave assisted extraction (MAE), ultrasound assisted extraction (UAE), pulsed electric extraction (PEE), accelerated solvent extraction, which are described as natural and consumer friendly, and various fruit pomace have been investigated as sources of natural pigments, dyes, antioxidants and antimicrobials. In this respect, experiments have been undertaken in their application as a source of active ingredients or functional packaging. The term “functional” refers to either an active or intelligent character, such as an antioxidant film that stops or slows the oxidation of packaged fatty products, or an intelligent sensor capable of detecting the presence of progressively formed volatile amines in spoiled foods. These include conductometric [
1] and pH sensitive components incorporated into the packaging material as carriers [
2]. Antioxidant compounds could scavenge the free radicals and prevent the degradation of the packed food, resulting in longer shelf-life. In dark fruits, the abundant color pigments, polyphenols, are mainly responsible for the antioxidant effect. At the same time, these pigments can be used as pH sensitive colorants, so that the final packaging can be equipped with active antioxidants and intelligent color recognition functions.
Since fruits are valuable foods that are mostly used fresh or processed into various products, commercial use for antioxidant extraction is not very likely. Nevertheless, by-products are great sources of the functional ingredients, although unfortunately they are often considered waste. In recent years, this aspect has increasingly changed. For example, fruit pomace, defined as leftovers after fruit processing and juicing, is increasingly being used as a source of valuable ingredients. The idea of reusing pomace has been explored in the scientific literature, but there are few references to the use of blackcurrant (
Ribes Nigrum). This fruit is also known as cassis and it has its natural origin and is cultivated in central–northern Europe. In the Burgundy region, it is known as a typical French product and is used either in Cassis de Dijon, as a liqueur, as berry juice or as a flavor enhancer for typical French products. Blackcurrant is rich in polyphenols with more than 90% anthocyanins (e.g. delphinidin-3-
O-glucoside, delphinidin-3-
O-rutinoside, cyanidin-3-
O-glucoside and cyanidin-3-
O-rutinoside [
3]). New sustainable developments are focused on the utilization of by-products for further functional applications due to the reuse of the high presence of bioactive compounds [
4,
5]. An interesting study was recently conducted on the valorization of processed berry waste in cereal-based foods to improve the nutritional profile of novel products [
6]. Similarly, blackcurrant pomace, when added as a flour substitute in the specific type of bread, can prevent the hyperglycemic effect [
7].
Sustainability is a promising topic for the food packaging sector, which can be attractive from both end-user and the technologist perspectives. Blackcurrant waste powder (BCW) has been used as an active ingredient source for the production of bio-based films. This type of film could potentially be used as a coating for products that do not have a monophasic structure, such as biscuits [
8], candies [
9], bread buns [
10], etc. Pectin (PEC) and chitosan (CS) are both classified as edible and biodegradable polysaccharides with a partially crystalline structure. They are also inexpensive and abundant natural polymers that use polymers to produce food-grade pectin or chitosan raw materials and has been well reported in the scientific literature [
11,
12]. When used as carriers of functional compounds, their intrinsic properties may change, leading to changes in barrier, thermal or mechanical film properties [
13]. Therefore, after the incorporation of novel compounds, it is advisable to evaluate all the parameters (such as antioxidant and antimicrobial efficacy, etc.) that are important for the final performance and potential use in food packaging.
The aim of this study was to analyze how the incorporation of lyophilized and ground blackcurrant pomace powder affects the physical and chemical (color, thickness, and water vapor permeability), mechanical (tensile strength, Young’s modulus, and elongation at break), thermal (differential scanning calorimetry) and surface (spectroscopy) of pectin and chitosan-based films. In addition, investigations were carried out on the antioxidant character, as well as on color changes after exposure to different pH values, which should provide information on the possible use as active or intelligent (indicator) packaging films.
3. Materials and Methods
3.1. Materials and Reagents
Chitosan (CS) (France Chitin, Orange, FR, type 652, Mw 165 kDa, DA > 85%) and pectin (PEC) powder (citrus 121 grade, CAS 9000-69-5, Fisher Scientific, Leicestershire, UK) were used for film preparation. Blackcurrant fruit (BC) (Ribes nigrum) was purchased frozen, from a local supermarket, packed in polyethylene bags and stored at −18 °C. The BC was pressed and the fruit pomace was used for the preparation of active powder (BCW). Acetic acid (glacial 100%, Merck, Darmstadt, Germany), pure ethanol (96%, Gram mol, Zagreb, Croatia), deionized water and glycerol (Fluka Chemical, 98% purity, Neu Ulm, Germany) were used for film forming solutions (FFS). Commercial pH buffers (KEFO, Sisak, Croatia) were used for the evaluation of pH sensor properties. All chemicals were used as received.
3.2. Preparation of Blackcurrant Powder
BC pomace was lyophilized (frozen samples at −80 °C, lyophilization during 48 h) (ScanCool SCL210P, Labo-GeneTM, Lynge, Denmark). Lyophilized material was ground using a household blender. Particles that passed through a sieve with a nominal mesh aperture of 180 microns were collected and kept refrigerated before being used for film preparation.
3.3. Film Preparation
CS and PEC powders were dissolved in 1% (v/v) aqueous acetic acid solution and distilled water to obtain 2 and 3% (w/v) suspensions (FFS), respectively. These solutions were continuously stirred for 2 h at room temperature (23 ± 2 °C), until all the powder was dissolved. Then, 30% (w/w of solution) glycerol was added to the FFS for 30 min with stirring at 1200 rpm. Blackcurrant waste powder (BCW) was added to the FFS (at concentrations of 10 and 20%, w/w) with stirring at 1200 rpm. The enriched film forming dispersion was optimized for 2 h. The pH for CS and PEC solutions were 4.60 and 4.20, respectively. An exact amount of FFS (20 g) was then poured into a glass Petri dish (20 cm diameter) and dried for 24 h (Memmert HPP110, Memmert, Buechenbach, Germany) at 30 °C and 50% RH. The dry films were peeled off and conditioned in a controlled atmosphere at 50% RH and 25 °C until used.
3.4. Physical and Chemical Characterization of Films
3.4.1. Film Thickness
The thickness of all film samples was measured with a digital micrometer with an accuracy of 1 µm (Digimet, HP, Helios Preisser, Gammertingen, Germany). An average of 10 values was used for further calculations.
3.4.2. Water Vapor Permeability (WVP) Measurements
The WVP of films was measured gravimetrically ([
41] adapted to edible materials by [
42]). Differential relative humidity (RH) (ΔRH70) was used by adding the distilled water (100% RH) to the permeation cell (cup) and exposing it to 30% RH in a ventilated climatic chamber (Memmert HPP110, Memmert, Buechenbach, Germany), at 25 ± 1 °C. The water vapor permeability, WVP (g m
−1 s
−1 Pa
−1) was calculated at the steady state of the permeation process, i.e., at a constant weight change of the cell, according to Equation (1):
where Δm/Δt is the weight of moisture loss per unit of time (g s
−1), A is the film area exposed to the moisture transfer (9.08 × 10
−4 m
2), x is the film thickness (m), and Δp is the water vapor pressure difference between the two sides of the film (Pa).
For all the samples, 5 replicates were performed.
3.4.3. Moisture Content and Water Solubility
The dry matter of the film was determined by weighing the film of the exact area (2 cm × 2 cm) before (w
i) and after (w
f) 2 h drying in an oven at 105 °C. The solubility in water (WS) was evaluated according to the literature [
16,
43]. WS gives the information about the amount of dry solids dissolved in distilled water after the films were immersed for 24 h. The procedure was as follows: (1) cutting the film samples into discs (2 cm diameter); (2) determining the initial dry weight (w
i) by drying to a constant weight at 105 °C; (3) immersing in distilled water (30 mL) and leaving for 24 h at 25 °C with periodical shaking; (4) oven drying (105 °C) the remaining film pieces to constant weight (the final weight of dry matter not dissolved in water (w
f).
WS (%) was calculated using the following equation:
Three measurements were taken for each film.
3.4.4. Mechanical Properties
A universal tensile testing machine (Stable Micro Systems Texture Analyzer TA.HD. plus, Surrey, UK) was used to determine the tensile strength (TS, MPa), the Young’s modulus (YM, MPa) and the percentage of elongation at a breakpoint (E, %) according to ASTM D882 [
44]. The film specimens were cut into a rectangular shape (1.5 × 5 cm). Prior to testing, all samples were equilibrated for 7 days at 50% of RH and at 25 °C. The equilibrated film specimens were clamped in the extension grips of the testing machine and unaxially stretched at a rate of 50 mm min
−1 until rupture. The initial distance between specimen holders was 4 cm. TS, YM, and E were plotted by computer from the stress–strain curves. Three replicates were tested for each film.
3.4.5. Film Color
Film color was measured with a colorimeter (Chroma meter CR-5, Konica Minolta, Tokyo, Japan) using the CIE-Lab color scale. The following color parameters were measured:
L* (lightness),
a* (redness) and
b* (yellowness). From the recorded parameters
L*,
a* and
b*, the total color difference Δ
E was determined according to Equation (3). It is defined that when Δ
E is more than 3, the color change can be perceived by human eye.
with
L1,
a1 and
b1—for active film,
L0,
a0 and
b0—control film (CS or PEC without active substances).
To evaluate the color changes of the pH sensing films, the above procedure was also used. Before measurements, the film samples were immersed in different pH buffers (pH 2, 4, 5, 6, 7, 8, 10, and 12) and left for 10 min. After that, all samples were collected and evaluated. All color measurements were taken at 5 different locations on the surface of each film sample.
3.4.6. FTIR Analysis
Fourier transform infrared (FTIR) spectroscopy was carried out using an FTIR spectrometer (PerkinElmer Frontier, Llantrisant, UK). FTIR spectra were recorded in the frequency range from 4000 to 400 cm−1 using ATR (attenuated total reflectance) with a ZnSe crystal. For each measurement, 64 scans were taken with a resolution of 4 cm−1. The spectra were recorded in duplicate. The aim of this analysis was to determine the molecular level modifications induced by the incorporation of BCW into the polymer chains.
3.4.7. Differential Scanning Calorimetry (DSC) Analysis
Thermal behavior was checked by differential scanning calorimetry (DSC), using Mettler Toledo DSC822e calibrated with indium (Mettler Toledo, Greifensee, Switzerland). The film samples were preconditioned at 53% RH in a climatic chamber for at least 48 h before analysis. About 10 mg of the studied film samples were hermetically sealed in an aluminum pan and heated (two runs: 1st from 0 to 220 °C and 2nd to 350 °C) at a rate of 10 °C min
−1. An empty aluminum pan was used as a reference. The peak points of specific temperature and heats of fusion were calculated from DSC thermograms using TA Universal Analysis Software (New Castle, DE, USA). According to the author’s previous experiences [
18] and preliminary results (not shown), it was expected that the greatest changes would be observed after incorporation of the highest extract concentrations, 20% BCW in this study, therefore only these film formulations were tested.
3.5. Antioxidant Properties
3.5.1. Total Phenolic Content
Total phenolic content (TPC) was determined using the modified Folin-Ciocalteu method [
45]. First, 100 µL of the appropriately diluted content was mixed with 200 µL of Folin–Ciocalteu reagent and 2 mL of distilled water. Then, 1 mL of 20% Na
2CO
3 (
w/
v) was added and kept at 50 °C for 25 min. The absorbance was measured at 765 nm using a spectrophotometer (model UV 1600PC; VWR International, Leuven, Belgium). The solvent (distilled water for PEC samples and aqueous acetic acid (1%,
v/
v) for CS samples) for extraction was used instead of fruit extract for blanks, and gallic acid (5 g L
−1) was used for the analytical curve. TPC was expressed as mg of gallic acid equivalent (GAE) g
−1 of prepared film or mg of GAE g
−1 of powdered extract. All measurements were performed in duplicate.
3.5.2. Antioxidant Activity of the Films
The reducing capacity (antioxidant activity, AOA) was determined using a modified ferric reducing antioxidant power (FRAP) method [
45]. The procedure was as follows: freshly prepared FRAP reagent was mixed with 0.3 M acetate buffer (pH = 3.6), 2,4,6-tripyridyl-s-triazine (TPTZ) solution and 20 mM FeCl
3·6H
2O solution, respectively, in a ratio of 10:1:1 (
v/
v/
v) and incubated at 37 °C. The sample (film or extract) and FRAP reagent were mixed (300 µL and 2.25 mL, respectively) and incubated for 10 min at 37 °C. The absorbance was measured at 593 nm. The blank sample was prepared using either distilled water for extracts and PEC-based samples or aqueous acetic acid for CS-based samples. The obtained results were expressed as the mg of ascorbic acid equivalents (AAE) g
−1 of the prepared films, or mg AAE g
−1 of the extract [
46]. All measurements were carried out in duplicate.
3.6. Statistical Analysis
Statistical analysis was performed using Xlstat-Pro (win) 7.5.3. (Addinsoft, New York, NY, USA). All data were ranked and the statistical differences were evaluated on the ranks using one-way analysis of variance (ANOVA) and Tukey’s multiple comparison tests. In all cases, a value of p < 0.05 confidence level is considered significant.
4. Conclusions
Novel formulations of bio-based films were successfully prepared using blackcurrant waste. Blackcurrant waste was used with the aim of obtaining both antioxidant properties and colored polyphenols to be used as color indicators of pH changes. Both study objectives were achieved to an extent that can be used for further investigation and use of the films in laboratory scale tests on real foods sensitive to oxidative stress or production of spoilage-indicating volatiles that can alter the pH of the packaging environment. Significant color changes were observed in dry films as a function of pH, providing a promising mechanism for their use as intelligent sensors for food packaging. However, further analysis and improvements need to be carried out in large-scale production. The antioxidant activity was dependent on the availability of phenols entrapped in the polymer matrix, which were derived from blackcurrant waste. The incorporation of blackcurrant waste affected some physical and chemical film properties. The water vapor permeability was significantly increased after the incorporation of the active powder, which was mainly due to the physical failures in the film matrix. The mechanical efficiency, as an integral film, was also decreased due to the incorporation of undissolved particles present in the blackcurrant waste. Spectral analysis of the film surface revealed no detectable binding between active powder and polymer chains on the film surface. However, the degradation temperatures determined by DSC were lower in the samples with blackcurrant powder, indicating a disturbance in polymer stability. A decrease of the melting temperature is related to a loss of thermal stability. The developed films are a good example of the use of food waste to produce packaging materials for environmentally conscious manufacturers. Produced composites are of great interest as they are created from abundant food by-products which, on the one hand, create environmental problem, and on the other hand, are rich in active compounds. Blackcurrant has not been widely used for the production of functional products, as are some other fruits of the berry group (such as cranberry, blueberry, etc.). Therefore, additional knowledge about its potential use is of scientific and industrial relevance.