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Explora: Environment
            and Resource                                                                     Enzymatic degradation



            United  Nations Agenda 2030. Our proposed enzymatic   serum albumin as the standard.  The crude enzyme
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            approach  holds promise for  application in decentralized   concentration was measured at 10 mg/mL (20% purity). To
            waste treatment  facilities,  bioreactors for  plastic waste   reduce the concentration for further assays, 10 mL of the
            remediation, and as a pre-treatment step to accelerate   extract was diluted with an equal volume of distilled water,
            subsequent biodegradation. More importantly, such eco-  resulting in a final protein concentration of 5  mg/mL,
            friendly strategies can reduce the environmental footprint   while maintaining the purity at 20%.
            of incineration and landfilling, which aligns with circular
            economy principles and global sustainability targets.  2.4. Incubation of PE samples
                                                               2.4.1. Isolation of LDPE film in the single-enzyme
            2. Materials and methods                           system
            2.1. Materials                                     The pre-weighed LDPE films (0.5 × 0.5, 1 × 1, and 2 ×
            Low-density PE (LDPE) samples (PWS) were collected   2 cm) were aseptically transferred into three pre-labeled
            from dumpsites within Gidan Kwano village (Nigeria).   100  mL  conical  flasks,  respectively.  About  20  mL  of  the
            Enzymes used were produced at the Step B Laboratory,   prepared degrading enzyme was added to each conical
            Centre for Genetic Engineering and Biotechnology,   flask and thoroughly mixed with the LDPE samples. For
            Federal University of Technology, Minna (FUTMinna),   assessing the effect of different enzyme concentrations, the
            Bosso Campus, Nigeria. The incubation media used   prepared LDPE strips (1 × 1 cm each) were transferred into
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            for  the LDPE samples  and  all  analytical  chemicals were   two pre-labeled 100 mL conical flasks, respectively.  Then,
            procured from the Department of Chemical Engineering,   100% pure Lip and a 50% diluted Lip solution were added
            FUTMinna (Nigeria).                                separately to each flask and thoroughly mixed with the
                                                               LDPE samples. To minimize heat dissipation and preserve
            2.2. Preparation of PE films                       a sanitized environment, a foil stopper was used to seal
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            The LDPE samples were cut into 0.5 × 0.5, 1 × 1, and 2 ×   the conical flasks.  The procedure was repeated for Lac.
            2 cm strips and weighed using a digital weighing balance   After 10 days of incubation, samples were collected, and
            (MAB220, Wensar, India), as previously reported. 49,51  The   the LDPE films were cleaned with ethanol and distilled
            samples  underwent a  rigorous cleaning process, which   water, then allowed to air-dry naturally. Following that,
            involved immersion in a solution of 70% ethanol for   the LDPE samples were evaluated to determine their
            30  min, followed by washing with distilled water, and   level of biodegradability. After 30  days, the process was
            drying in an oven at 50°C for 20 min.              terminated. The 30-day incubation period was selected to
                                                               allow sufficient time for measurable enzymatic degradation
            2.3. Production of degrading enzymes               of LDPE by Lac and Lip.
            Ab initio, the medium was prepared through the following   2.4.2. Isolation of LDPE film in the two-enzyme system
            steps. First, the Sabouraud Dextrose Agar was prepared by
            dissolving 20 g of the powdered non-synthetic medium in   The pre-weighed LDPE films (0.5 × 0.5 and 2 × 2 cm) were
            two separate 2000 mL conical flasks labeled “Lipase” and   transferred into two pre-labeled 100  mL conical flasks,
            “Laccase,” respectively,  each  containing  distilled water.    respectively. Lip and Lac enzymes (20 mL) were added to
                                                         52
            For the Lip medium, 2  mL of olive oil (0.1% substrate   each conical flask and thoroughly mixed with the LDPE
            concentration) was added. For the Lac medium, 2  mL   samples.  For  assessing  the  effect  of  different  enzyme
            of guaiacol (0.1% substrate concentration) was added.    concentrations, the prepared LDPE strips (1 × 1 cm) were
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            Both media were sterilized in an autoclave at 121°C for   transferred into two pre-labeled 100  mL conical flasks,
            3  h under a pressure of 1.5  N/m. After autoclaving, the   respectively.  The Lip-Lac enzyme mixture at 100% and
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            medium was removed from the autoclave and allowed   50% concentrations was added to the two conical flasks,
            to cool before inoculation. The 72-h-old broth culture of   respectively. To minimize heat dissipation and preserve a
            A. flavus (5 mL) was inoculated into 1 L of each medium   sanitized environment, a foil stopper was used to seal the
            and incubated for 5 days on a shaker incubator at ambient   conical flasks.  The solution was gently stirred to obtain
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            or room temperature (25–28°C ± 2°C). After 5  days,   a homogeneous mixture. The LDPE films were cleaned
            crude enzymes were readily produced. The crude enzyme   using ethanol and distilled water, then allowed to air-
            solutions were centrifuged at 4000 rpm using a high-speed   dry naturally. Biodegradation of the LDPE samples was
            refrigerated centrifuge. The supernatants contained the   analyzed after 10 days of incubation. Following that, the
            crude enzymes, while the sediments consisted of fungal   LDPE samples were evaluated to determine their level of
            spores. The Bradford protein assay was used to quantify   biodegradability. The process was terminated after 30 days,
            the total protein content in the crude extract, using bovine   in accordance with Yang et al. 56


            Volume 2 Issue 3 (2025)                         3                           doi: 10.36922/EER025220042
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