1 Introduction

A wide variety of medicinal devices (MDs) used in hospitals are made of flexible plasticized polyvinyl chloride (PVC). Polyvinyl chloride is a polymer in which chlorine resembles more than 50% of its content. However due to the low cost and well performance of di-2-ethylhexyl phthalate (DEHP) and other phthalate plasticizers they are still commonly used in several applications. DEHP is used to soften the rigid PVC and increase its flexibility and workability but it is not chemically bound in plastic materials and they can be leaked into the environment easily (Fierens et al. 2012; Pradeep and Benjamin 2012). Plasticizers are added to PVC to make the plastics flexible, which are the most required properties for medicinal products (Koch et al. 2003; Zhang et al. 2009). Harmful effect of using phthalates as plasticizers in PVC is that it acts as simulators for the performance of human natural hormone system. Inoue et al. (2003) and Vesterberg et al. (2005) stated that DEHP is not chemically bound to the PVC polymer; it may be leaked when PVC medicinal devices come into contact with blood, urine and drugs. They also showed that DEHP from medicinal tubing is leaked into drug solutions in different quantities. DEHP is a developmental and reproductive poison in animals and supposed to be endocrine modulator in humans. DEHP may transfer from PVC storage bags to blood and blood products such as plasma, platelets and red blood cells (RBCs). Leaching of DEHP and mono-2-ethylhexyl phthalate (MEHP) into RBC units depends on the storage period (Münch et al. 2020). DEHP is hydrolyzed quickly into MEHP in human. For this reason, both DEHP (leaked from blood bags) and MEHP levels in blood products should be measured. DEHP pollution originating in several laboratory products, room air and plastic tubing may pose the contamination risk and therefore an over-estimation of DEHP levels (Inoue et al. 2005). In general population, a widespread exposure to DEHP is found. Toxic kinetic and metabolic information on DEHP in humans are very important not only for the toxicological assessment of DEHP but also for exposure assessments based on human bio monitoring information (Koch et al. 2006). Since transformation of DEHP to MEHP takes place firstly in the intestinal tract, ingestion of DEHP may be more dangerous than exposure intravenously. A number of studies displayed that DEHP causes liver cancer in laboratory animals (Gonzalez et al. 1998). It can be occurred through peroxisome proliferation induction, leading to oxidative stress and production of electrophilic free radicals, which leading to DNA damage indirectly (Silva et al. 2006). This involves the propagation of cellular organelles that contain enzymes showing catalytic activity toward fatty acids oxidation and the cholesterol biosynthesis in the liver (Dzehekova-stojkova et al. 2001; Reddy and Lalwai 1983).

Common techniques for degradation of plastic materials are incineration, land filling, hydrolysis, photodecomposition, recycling, and biodegradation (Hopewell et al. 2009; Savinova et al. 2022). Hydrolysis pathway chiefly occurs in aquatic environment but sometimes, no complete degradation of PAEs occurs. Photodecomposition is very slow (the half-life ranges from many years to many centuries) (Savinova et al. 2022). Land filling and incineration techniques need huge amount of space and are harmful to the environment. However, recycling technique is an effective method making plastic can be reused. Nevertheless, biodegradation is an environmental friendly technique that degrades a large number of pollutants using different microbial enzymes in a relatively short time (Purnomo et al. 2013; Yastrebova et al. 2019). The DEHP metabolic breakdown by microorganisms is considered to be one of the main techniques of ecological decomposition for this widespread contaminant due to its low rate of photolysis and hydrolysis. Plastics are stated to be decomposed in about 1000 years under the natural environment (Sangale et al. 2012). This slow rate of plastic wastes natural deterioration performs environmental threatens. Among the different common techniques to manage with the plastic wastes, biodeterioration technique by algae, actinomycetes, bacteria and fungi is considered as the most established and ecofriendly technique (Rutkowska et al. 2002). Biodeterioration of plastic wastes leads to complete degradation of the plastic into nonpoisonous materials as water, CH4, CO2, and other biological materials. Agaricus bisporus, Aspergillus flavus, Aspergillus glaucus, Aspergillus nidulans, Aspergillus nomius, Aspergillus oryzae, Bjerkandera adusta, Cladosporium cladosporioides, Penicillium griseofulvum, Phanerochaete chrysosporium, Pleurotus abalones, Pleurotus eryngii, Pleurotus ostreatus, etc., displayed efficient remediation of plastics (Srikanth et al. 2022).

This study aimed at isolation and identification of fungi from heavily plastic polluted soil and investigating their activity in degradation of DEHP plasticizer in both blood and urine bags.

2 Materials and Methods

2.1 Collection of Soil Samples

Soil samples were collected randomly from different sites of heavily plastic polluted areas (10 cm depth) in Garbage dumps in Fifth assembly.

2.2 Extraction and Determination of DEHP Concentration in Soil, Urine and Blood Bags

One gram of soil and plastic pieces (urine or blood bags) was immersed in n-hexane and left for two days then the concentration of DEHP was determined using spectrophotometer at wavelength 275 nm with standard curve of commercial DEHP (Pradeep and Benjamin 2012).

2.3 Isolation of DEHP Degrading Fungi from Plastic Polluted Soil by Soil-Plate Method

Soil-plate method was used to isolate DEHP degrading fungi from plastic polluted soil. Two isolation media (Martin’s and Sabouraud’s media) were used, where filtered-sterilized DEHP was substituted carbon source in these media. Sabouruad’s medium is composed of (g\L): glucose 40, peptone 10 and agar 18; while martin’s medium composed of (g\L): glucose 10, peptone 5, KH2PO4 1, MgSo4.7H2O 0.5 and agar 18. Soil samples (1 g) were added into sterilized petri dishes then media were poured and incubated at 27 °C for five days. Pure cultures of the growing fungi were obtained by repeated sub-culturing then maintained on the same media in refrigerator.

2.4 Morphological Identification of Isolated Fungi

The isolated fungal species were identified morphologically and microscopically according to Moubasher (1993). Cultures of 4 days old were examined for the phenotypic properties as shapes and colors of colonies, and then light microscope (5, 10 & 40X) was used for the examination of conidiophores and spores.

2.5 Artificial Inoculation of Urine and Blood Bags Pieces with Isolated Fungi

One gram of plastic pieces from blood and urine bags were putted in 50 ml of liquid martin media (pH 6.8) then inoculated with the fungal species isolated from polluted soil and incubated at 27 °C for 20 days.

2.6 Determination of Fungal Dry Biomass, pH of the Media and DEHP Percentage

Dry biomasses of fungi were determined at five days’ intervals after drying in oven until constant weight. The pH values of the media were also measured using pH meter. Furthermore, the percentages of DEHP were determined. Plastic pieces were washed with distilled water and left to dry then moved into n-hexane for two days. Then, the percentage of DEHP was determined by using spectrophotometer at wavelength 275 nm.

2.7 Examination of the Urine and Blood Bags Pieces Using the Scanning Electron Microscope (SEM)

The surface of the plastic pieces were examined before and after treatment with fungal species using scanning electron microscope (model: JSM-5500 LV; JEOL Ltd-japan) and high vacuum mode.

2.8 Molecular Identification of Fungi

The most active DEHP metabolizing fungal species were further identified by amplification and sequencing of internal transcribed spacer (ITS) region. Briefly, genomic DNA was isolated and purified using Wizard Genomic DNA purification Kit (Promega Corporation, USA) according to manufacture instructions. Polymerase chain reactions (PCR) were prepared to a final volume of 50 µl containing reaction buffer, 1.5 mM MgCl2, 200 µM of each dNTPase, 2.5 unit of Dream Taq DNA polymerase (Thermo Scientific, USA), 30 ng DNA template and 50 pmol of each primer (ITS1 and ITS4). An initial denaturation step for 5 min at 95 °C was followed by 30 cycles of denaturation at 94 °C for 40 s, annealing at 58 °C for 40 s and extension at 72 °C for 40 s, with a final extension at 72 °C for 10 min. The amplicons were purified using GeneJET™ PCR Purification Kit according the manufacture protocol. The nucleotide sequences of the purified PCR products were determined at macrogen (Seoul, South Korea). The sequences were analyzed by BLAST tool and were submitted to the GenBank. Phylogenetic trees in the context of ITS sequences were conducted. Accession numbers of the identified fungal species were also obtained.

3 Experimental Results

3.1 Determination of DEHP Concentration in Soil, Urine and Blood Bags

The concentration of DEHP in plastic polluted soil sample was found to be 0.92 g/l while it was found in urine bag sample to be 2.5 g/l, and in blood bags to be 2.6 g/l.

3.2 Isolation and Identification of DEHP Degrading Fungi from Plastic Polluted Soil

Only, three fungal species were isolated from the heavily plastic contaminated soil. They could metabolize DEHP and grow on media containing it as sole carbon source. They were identified morphologically as Aspergillus nidulans, Aspergillus niger and Rhizopus nigricans according to Moubasher (1993).

3.3 Determination of Fungal dry Biomass, pH of the Media and DEHP Utilization Percentage

Assaying the ability of the isolated soil fungi to grow on plastic pieces declared that the three fungal species could grow well on the plastic pieces containing medium as a sole carbon source. The growth increased as the time period was increased to reach its maximum value after 20 days of incubation (Fig. 1). Rhizopus nigricans obtained the highest dry weight followed by Aspergillus nidulans then Aspergillus niger in urine bags. Whereas in blood bags A. nidulans had the highest dry weight followed by R. nigricans then A. niger.

Fig. 1
figure 1

Dry biomasses of the three fungal species grown on media containing DEHP of urine a and blood b bags pieces as a sole carbon source at different time intervals

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The pH value of medium was altered by fungal growth on plastic pieces. The initial pH of the medium was 6.8. The value decreased to acidic side by increasing time with fungal growth. pH reached its minimum value after 20 days of A. niger incubation to be 4.7 in urine bags. In blood bags, pH was altered to 2.5 after 20 days of A. nidulans incubation (Fig. 2).

Fig. 2
figure 2

pH profile of the media containing DEHP of urine a and blood b bags pieces as a sole carbon source after the growth of the three fungal species at different time intervals

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The concentration of DEHP extracted from plastic pieces of urine and blood bags was determined using UV spectrophotometer after growth of the three fungal species. The decline in DEHP extracted from both blood and urine bags gradually increased as the incubation period was increased with maximum decline after 20 days of incubation for the three fungal species (Fig. 3). In case of urine bags, A. niger was the most DEHP degrading fungal species followed by R. nigricans and A. nidulans with about the same efficacy. Also, A. niger was the most DEHP degrading fungal species followed by A. nidulans then R. nigricans in case of blood bags.

Fig. 3
figure 3

Percentage of DEHP extracted from urine a and blood b bags pieces after the growth of the three fungal species at different time intervals

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3.4 Examination of Blood and Urine Plastic Surface by Scanning Electron Microscope (SEM) Before and After Treatment with Fungi

Before fungal treatment, uniform plastic network was observed in both urine and blood bags. After fungal treatment, the metabolization of DEHP made a microporous network on the plastic surfaces of either urine or blood bag pieces. A. niger was the most efficient in utilizing DEHP followed by A. nidulans then R. nigricans in urine bags, while Aspergillus nidulans was the most effective in blood bags pieces (Figs. 4 and 5).

Fig. 4
figure 4

Examination of urine bags plastic surfaces under scanning electron microscope before and after treatment with fungi a before fungal treatment b after treatment with A. nidulans c after treatment with A.niger d after treatment with R. nigricans

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Fig. 5
figure 5

Examination of blood bags plastic surfaces under scanning electron microscope before and after treatment with fungi a before fungal treatment b after treatment with A. nidulans c after treatment with A.niger d after treatment with R. nigricans

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3.5 Molecular identification of fungi

The most DEHP degrading fungi (A. niger and A. nidulans) were further identified by amplification and sequencing of ITS region. BLAST result showed 100% similarity with that of A. niger which got accession number of MZ832174 (Fig. 6), and 100% similarity with that of A. nidulans which got accession number of MT919276 (Fig. 7).

Fig. 6
figure 6

Phylogenetic tree of Aspergillus niger (MZ832174)

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Fig. 7
figure 7

Phylogenetic tree of Aspergillus nidulans (MT919276)

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4 Discussion

Bioremediation is the clean of the polluted environment at minimum cost and ecofriendly techniques using microorganisms. Plastic is used in many activities and it is a good replacement of other materials such as metals or paper and it can be retained for extended period with no deterioration. Plastic is also hydrophobic so it used in situations where water content requires to be avoided. Furthermore, plastic can be softenized by adding specific materials to it such as plasticizers (Azubuike et al. 2016; Liang et al. 2008). These plasticizers can transfer from the PVC bags into infused solutions and thus come into contact with the patient (Niino et al. 2001, 2002). Some of these chemical compounds are harmful to the patient which can affect reproduction and fertility (Hauser and Calafat 2005). Other adverse effects of DEHP exposure in animal studies include inhibited or delayed ovulation, inhibited estradiol production, and produce polycystic ovaries. It also reduces kidney function, causes kidney atrophy, reduces liver function, causes respiratory distress, and decreases heart rate and blood pressure (Gonzalez et al. 1998; Silva et al. 2006). Phthalate esters (PEs) are the most commonly used plasticizers worldwide. Concerns about toxicity of PEs were found because PEs can act as endocrine disrupting chemicals which affect development and reproduction. A talented approach of PEs remediation is their biotransformation by fungal enzymes. White rot fungi are able to degrade phthalates. The efficacy of the biotransformation most probably depends on the enzymatic system of a particular species (Fedorova et al. 2021). However, there are many problems concerning their deterioration, where themanufacture rate of plastic is not balanced with the decomposition rate throughout the world (Shahnawaz et al. 2019).

In the present study, bioremediation of plastic containing the plasticizer DEHP by three fungal species were investigated. Aspergillus nidulans, Aspergillus niger and Rhizopus nigricans isolated from heavily plastic polluted soil samples were found as good utilizers of DEHP. In relation to our study, Ekanayaka et al. (2022) stated that fungal species which degrade plastic are present in 11 classes belonging to the phyla Ascomycota, Basidiomycota and Mucoromycota. Srikanth et al. (2022) reported that Aspergillus nidulans, Aspergillus flavus, Aspergillus oryzae, etc., can grow on plastics causing degradation of them.

The results of this study indicated that the dry biomass of the studied fungal species increased gradually with increasing the incubation period when grown on media containing DEHP as sole carbon source. However, the pH values of the growth media were altered to acidic side and the DEHP% decreased by increasing the incubation time indicating a continuous utilization of DEHP by the fungal species. The results of this study are compatible with earlier studies. Fu and Xiang (2020) studied the influence of Aspergillus niger, Penicillium and yeast on DEHP degradation by single factor test. They found that the optimum conditions for degradation of DEHP were at pH 5.0 and 30 °C. These fungi had the ability to degrade DEHP, where Aspergillus niger was the most able fungus to degrade DEHP (68.75% of degradation within 60 h). Aguilar-Alvarado et al. (2015) demonstrated that fungal species isolated from recycled paper wastes in a paper manufacturing were able to utilize DEHP as the sole carbon source. These fungal isolates can be used for DEHP biodegradation. Savinova et al. (2022) reported that PAEs degradation is depending on fungal enzymes. They also stated that DEHP was degraded by some fungi (Trametes hirsute and Steccherinum ochraceum) with an efficacy of > 99%. Johnson (2014) studied an experiment to determine the effect of fungal growth on the phthalate ester content of the pPVC used as the fronting material of metal building insulation. He showed that the mean content of all tested phthalate esters was decreased in case of fungal growth as compared to pieces of no fungal growth. He found that DEHP had a mean mass content of 319 ng in the pPVC without fungal growth and 278 ng in the pPVC with fungal growth (i.e., 10% decline in phthalate ester mass between the pPVC without fungal growth and pPVC with fungal growth).

In the current study, SEM images showed changes in plastic surface structure. A microporous plastic surface was formed by the decomposition of the urine and blood bags plastic pieces by the tested fungal species. Adamcová et al. (2018) studied the degradation of plastics using SEM analysis. SEM is used for examination of changes occurs in materials morphology at microscale. SEM images proved the microbial activity on bioplastic by formation of cracks and loss of surface structure smoothness.

5 Conclusion

This study obviously demonstrates that fungal species (Aspergillus nidulans, Aspergillus niger and Rhizopus nigricans) isolated from heavily plastic polluted soil can grow on and degrade the plasticizer hazardous compound DEHP contained in blood and urine bags with an efficient degree.