Biodegradation of low-density polyethylene and polystyrene in superworms, larvae of Zophobas atratus (Coleoptera: Tenebrionidae): Broad and limited extent depolymerization (2023)

Table of Contents
Environmental Pollution Abstract Graphical abstract Introduction Section snippets Zophobas atratus larval source and test materials Survival rates with different diets and plastics consumption Conclusion CRediT authorship contribution statement Declaration of competing interest Acknowledgments References (36) Biodegradation and mineralization of polystyrene by plastic-eating superworms Zophobas atratus Sci. Total Environ. Ubiquity of polystyrene digestion and biodegradation within yellow mealworms, larvae of Tenebrio molitor Linnaeus (Coleoptera: Tenebrionidae) Chemosphere Biodegradation of polystyrene wastes in yellow mealworms (larvae of Tenebrio molitor Linnaeus): factors affecting biodegradation rates and the ability of polystyrene-fed larvae to complete their life cycle Chemosphere Anovel clean production approach to utilize crop waste residues as co-diet for mealworm (Tenebrio molitor) biomass production with biochar as byproduct for heavy metal removal Environ. Pollut. Generation of high-efficient biochar for dye adsorption using frass of yellow mealworms (larvae of Tenebrio molitor Linnaeus) fed with wheat straw for insect biomass production J.Clean. Prod. Larval dispersal and cannibalism in a natural population of Zophobas atratus (Coleoptera: Tenebrionidae) Anim. Behav. Biological degradation of plastics: a comprehensive review Biotechnol. Adv. Damage characteristics produced by insect pests in packaging film J.Stored Prod. Res. Changes in the gut microbiome and enzymatic profile of Tenebrio molitor larvae biodegrading cellulose, polyethylene and polystyrene waste Environ. Pollut. Polyethylene bio-degradation by caterpillars of the wax moth Galleria mellonella Curr. Biol. Molecular weight changes and polymeric matrix changes correlated with the formation of degradation products in biodegraded polyethylene J.Environ. Polym. Degrad. Environmental and microbiological problems arising from recalcitrant molecules Microb. Ecol. Isolation and molecular characterization of polyvinyl chloride (PVC) plastic degrading fungal isolates J.Basic Microbiol. Ecology of the plastistishere Nat. Rev. Microbiol. Complete mitochondrial genome of the super mealworm Zophobas atratus (Fab.)(Insecta: Coleoptera: Tenebrionidae) Mitochondrial DNA Part B Accumulation and fragmentation of plastic debris in global environments Philos. Trans. R. Soc. Lond. B Biol. Sci. The studies on waste biodegradation by Tenebrio molitor Fate of hexabromocyclododecane (HBCD), a common flame retardant, in polystyrene-degrading mealworms: elevated HBCD levels in egested polymer but no bioaccumulation Environ. Sci. Technol. Cited by (67) Adsorption and desorption mechanisms of oxytetracycline on poly(butylene adipate-co-terephthalate) microplastics after degradation: The effects of biofilms, Cu(II), water pH, and dissolved organic matter Biological effects on the migration and transformation of microplastics in the marine environment Recent advances and challenges in the biotechnological upcycling of plastic wastes for constructing a circular bioeconomy Microplastics in multimedia environment: A systematic review on its fate, transport, quantification, health risk, and remedial measures The interplay of larval age and particle size regulates micro-polystyrene biodegradation and development of Tenebrio molitor L. Unveiling the potential of Lichtheimia ramosa AJP11 for myco-transformation of polystyrene sulfonate and its driving molecular mechanism Recommended articles (6) Changes in the gut microbiome and enzymatic profile of Tenebrio molitor larvae biodegrading cellulose, polyethylene and polystyrene waste A polystyrene-degrading Acinetobacter bacterium isolated from the larvae of Tribolium castaneum Ubiquity of polystyrene digestion and biodegradation within yellow mealworms, larvae of Tenebrio molitor Linnaeus (Coleoptera: Tenebrionidae) Biodegradation of polystyrene wastes in yellow mealworms (larvae of Tenebrio molitor Linnaeus): Factors affecting biodegradation rates and the ability of polystyrene-fed larvae to complete their life cycle Biodegradation of polypropylene by yellow mealworms (Tenebrio molitor) and superworms (Zophobas atratus) via gut-microbe-dependent depolymerization Biodegradation of polylactic acid by yellow mealworms (larvae of Tenebrio molitor) via resource recovery: A sustainable approach for waste management FAQs

Environmental Pollution

Volume 266, Part 1,

November 2020

, 115206

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Abstract

Larvae of Zophobas atratus (synonym as Z.morio, or Z.rugipes Kirsch, Coleoptera: Tenebrionidae) are capable of eating foams of expanded polystyrene (EPS) and low-density polyethylene (LDPE), similar to larvae of Tenebrio molitor. We evaluated biodegradation of EPS and LDPE in the larvae from Guangzhou, China (strain G) and Marion, Illinois, U.S. (strain M) at 25°C. Within 33 days, strain G larvae ingested respective LDPE and PS foams as their sole diet with respective consumption rates of 58.7±1.8mg and 61.5±1.6mg 100 larvae−1d−1. Meanwhile, strain M required co-diet (bran or cabbage) with respective consumption rates of 57.1±2.5mg and 30.3±7.7mg 100 larvae−1 d−1. Fourier transform infrared spectroscopy, proton nuclear magnetic resonance, and thermal gravimetric analyses indicated oxidation and biodegradation of LDPE and EPS in the two strains. Gel permeation chromatography analysis revealed that strain G performed broad depolymerization of EPS, i.e., both weight-average molecular weight (Mw) and number-average molecular weight (Mn) of residual polymers decreased, while strain M performed limited extent depolymerization, i.e., Mw and Mn increased. However, both strains performed limited extent depolymerization of LDPE. After feeding antibiotic gentamicin, gut microbes were suppressed, and Mw and Mn of residual LDPE and EPS in frass were basically unchanged, implying a dependence on gut microbes for depolymerization/biodegradation. Our discoveries indicate that gut microbe-dependent LDPE and EPS biodegradation is present within Z.atratus in Tenebrionidae, but that the limited extent depolymerization pattern resulted in undigested polymers with high molecular weights in egested frass.

Introduction

Due to mass-production, durability, and miss management, plastic waste has become a major worldwide environmental concern (Barnes etal., 2009). In 2018, the annual production of plastic waste had increased to over 359 million of tons (Plastics Europe., 2019). The major plastic wastes in environments include polyethylene (PE), polypropylene (PP), polystyrene (PS), polyvinyl chloride (PVC), polyethylene terephthalate (PET) and polyurethane (PUR) (Plastics Europe., 2019; Wu etal., 2017). These polymers are classified into hydrolyzable plastics (PUR and PET) and non-hydrolyzable plastics (PE, PP, PS and PVC). Non-hydrolyzable plastics is more resistant to enzymatic depolymerization or degradation (Amaral-Zettler etal., 2020; Inderthal etal., 2020).

Non-hydrolyzable polymers PE, expressed as [CH2–CH2]n, and PS, expressed as [-CH-(C6H5) CH2-]n, account for 36.7% and 7.0% of petroleum-based plastic products, respectively (Ho etal., 2018). Since the 1970s, numerous studies have been conducted regarding the biodegradation of PE and PS in the environment; the focus has largely been on biodegradation via various environmental materials such as bacteria, fungi and mixed microbial cultures from contaminated sites, sludge and soil (Alexander, 1975; Ho etal., 2018; Kaplan etal., 1979; Kong etal., 2019; Lee etal., 1991; Mor and Sivan, 2008; Shah etal., 2008). As is well known, however, the biodegradation rates by these cultures are extremely slow.

In recent years, a more promising method of plastic biodegradation has garnered attention by researchers. Larvae and adult insects belonging to the families of darkling beetles (Coleoptera: Tenebrionidae) and pest moths (Lepidoptera: Pyralidae) have been reported to be capable of chewing and penetrating plastic materials such as PE and PS since the 1950s (Riudavets etal., 2007). Yang etal. (2014) isolated two gut bacterial strains degrading low-density polyethylene (LDPE) film from the larvae of Indian mealmoths (Plodia interpunctella). Analysis of the bacterial strains, i.e. Enterobacter asburiae YT1 and Bacillus sp. YP1, suggested that the LDPE-eating larvae could digest LDPE (Yang etal., 2014). So far, larvae of other moths in the Pyralidae family reported to be able to degrade PE include greater waxworms (Galleria mellonella) (Bombelli etal., 2017) and lesser waxworms (Achroia grisella) (Kundungal etal., 2019). Significant progress has been achieved in research on larvae of yellow mealworms (Tenebrio molitor Linnaeus 1758, Coleoptera: Tenebrionidae) since 2015. The larvae of the T.molitor strain obtained from Beijing, China was reported to be capable of depolymerizing and mineralizing EPS via gel permeation chromatography (GPC) analysis, 13C labeled PS tracer tests, as well as other methods (Yang etal., 2015a). The PS depolymerization/biodegradation was gut-microbe-dependent based on the fact that depolymerization stopped after the suppression of gut microbes by antibiotics gentamicin. The presence of a PS-degrading gut bacterial strain was supported by isolating PS-degrading gut bacterial Exiguobacterium strain YT2 (Yang etal., 2015b). Follow-up tests further indicated the ubiquity of PS depolymerization/biodegradation in T.molitor larvae around world. Furthermore, the research concluded that the PS degradation rate can be enhanced by feeding the normal co-diet (bran) (Yang etal., 2018a; Yang etal., 2018b). The larvae of T.molitor are capable of depolymerizing and biodegrading LDPE (Brandon etal., 2018) as well as consuming PVC and polylactide (PLA) (Bożek etal., 2017). Another member in Tenebrio genus, dark mealworms (larvae of Tenebrio obscurus), also biodegraded EPS, and based on antibiotic gentamicin tests, the depolymerization is also gut-microbe dependent (Peng etal., 2019).

It is unclear whether other members of darkling beetles with plastic chewing behaviors also have the capability of depolymerizing/biodegrading plastics. We have tested superworms (also known as King Worms or Morio Worms), i.e. the larvae of Zophobas atratus Fabricius 1775 (Coleoptera: Tenebrionidae), for the studies on biodegradation of plastics. Zophobas atratus, also known as Zophobas morio Fabricius 1776 and Zophobas rugipes Kirsch, is native to Southern USA and South America (Bai etal., 2019; Kim etal., 2015; Tschinkel, 1981). Z.atratus larvae are commercially marketed as a well-known feed resource for animals around world. The larvae have 6 small legs, two rudimentary hind prolegs, 13 knots with yellow-brown rings at the joints, and a dark spot on the worm head as well as dark stripes at the end of the worm tail. Z.atratus larvae can be 1.5 to 3 times larger in size than the larvae of T.molitor and T.obscurus, and can grow to 5.0–6.0cm long (Fig.S1a). Z.atratus larvae have higher nutritive value, stronger vitality, and are more resistant to hunger and thirst than T.molitor and T.obscurus but otherwise, they exhibit similar life stage from larva to pupa to adult (Figs.S1b and S1c). However, Z.atratus larvae tend to cannibalize the pupae and larvae of their own species (Tschinkel, 1981). Previous research on plastic (PS, PE etc.) consumption by Z.atratus larvae was reported by Miao and Zhang (2010), who tested a larval strain from ShanXi, China (Miao and Zhang, 2010). The researchers did not confirm biodegradation of LDPE but found changes in physical properties of residual PS in frass. Recently, Yang etal. (2020) tested Z.atratus larvae from Beijing, China and characterized egested frass and found the larvae ingested, depolymerized and biodegraded PS; EPS depolymerization was significantly inhibited under suppression of gut microbiota by mixed antibiotics (Yang etal., 2020). The capacity of PE depolymerization/biodegradation in Z.atratus larvae has remained unknown, and the ubiquity of PS depolymerization/biodegradation in Z.atratus larvae requires more tests with Z.atratus larvae from different geographical sources.

Depolymerization has been defined as the process of converting a polymer into a monomer or a mixture of monomers and recently is also described as a process of breaking down a polymer into fragments or compounds with smaller molecules. Hydrolyzable polymers (e.g. PET, PUR) can be hydrolyzed via enzymes (hydrolase, cutinases, lipases, etc.) to monomers or a mixture of monomers which are then further biodegraded; but non-hydrolyzable polymers (PS, PE etc.) are much more resistant to hydrolysis and require oxidative cleavage of backbone C–C bonds via enzymes with high redox potential (Amaral-Zettler etal., 2020; Inderthal etal., 2020). GPC analysis has been a key tool in evaluating polymer depolymerization, the primary and essential step of biodegradation. GPC analysis provides the information of the number-average molecular weight (Mn), the weight-average molecular weight (Mw) and molecular weight distribution (MWD), which are considered as a major indication of polymer modification, depolymerization and degradation (Albertsson etal., 1998; Yang etal., 2018a). To date, a commonly observed depolymerization pattern during plastics biodegradation has been broad depolymerization (BD), i.e., the decrease in both Mn and Mw of the plastic polymer, as well as a shift of MWD towards lower molecular weight, which is evidence of chain scission by enzymatic depolymerization or microbial attack (Ali etal., 2014; Brandon etal., 2018; Peng etal., 2019; Yang etal., 2018a; Yang etal., 2018b; Yang etal., 2015a, b). However, we questioned whether other patterns would be present if the depolymerizing enzyme(s) had limited capacity of breaking down polymers, or were incapable of scissing of long molecular chains or complicated polymers.

In this study, we tested LDPE and EPS consumption/biodegradation in Z.atratus larvae obtained from Guangdong, China and Marion, Illinois, USA in order to verify the ubiquity of PS biodegradation and to investigate feasibility of PE degradation in Z.atratus larvae. Results indicated that both EPS and LDPE were biodegraded via different depolymerization patterns, and the depolymerization/biodegradation of LDPE and EPS in Z.atratus larvae was gut microbiome dependent.

Section snippets

Zophobas atratus larval source and test materials

In this study, two geographic sources of Z.atratus larvae (approximately 5cm in length) were investigated. Z.atratus larvae purchased from the Guangzhou Insect Breeding Plant (Guangdong, China) were named as strain G. Meanwhile, Z.atratus larvae purchased from Petco Animal Supplies, Mountain View, California, USA (supplied by Timberline Fisheries, Marion, Illinois, USA) were named as strain M. Both strains are identified as Zophobas atratus based on morphology and coloration (Fig.1 and

Survival rates with different diets and plastics consumption

Z.atratus larvae from both sources ate LDPE and EPS foams as they were fed (Fig.1a–d), then egested particle-like-frass with yellow or brown color (Figs.S3 and S4) which were larger than those derived from T.molitor larvae (Brandon etal., 2018; Peng etal., 2019). The larvae of strain G ate both PE-1 and PS-1 foam without adaptation but strain M required a co-diet (cabbage leaf and bran) for adaptation. For the larvae of strain G, the SRs with respective diet treatments maintained at a

Conclusion

The results demonstrate that Zophobas atratus larvae, another species of darkling beetles (Coleoptera: Tenebrionidae) from two different geographical locations (strain G from China and strain M from the USA) have the capacity of depolymerizing/biodegrading both non-hydrolyzable plastics LDPE and EPS. Antibiotics gentamicin inhibited depolymerization of both LDPE and EPS, indicating that the biodegradation of both LDPE and EPS in the both larvae was gut microbe dependent similar to previous

CRediT authorship contribution statement

Bo-Yu Peng: Methodology, Investigation, Data curation, Validation, Writing - original draft. Yiran Li: Methodology, Investigation, Data curation, Validation, Writing - original draft. Rui Fan: Methodology, Investigation, Data curation, Validation, Writing - original draft. Zhibin Chen: Methodology, Investigation. Jiabin Chen: Methodology, Investigation. Anja M. Brandon: Methodology, Investigation, Writing - review & editing. Craig S. Criddle: Conceptualization, Investigation, Writing - review &

Declaration of competing interest

The authors declare no competing financial interest.

Acknowledgments

We gratefully acknowledge support from the National Science Fund for Distinguished Young Scholars of China (No. 51625804) and also appreciate the support by the Woods Institute for Environment at Stanford University (Award 1197667-10-WTAZB). We thank Professors Zheng Shen, Dr. Huaqiang Chu and Dr. Minyan Gu, Tongji University, for assistance in laboratory research at Tongji University; Dr. Shan-Shan Yang, Harbin Institute of Technology for help in laboratory research at Stanford University; Ms.

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      Ubiquity of polystyrene digestion and biodegradation within yellow mealworms, larvae of Tenebrio molitor Linnaeus (Coleoptera: Tenebrionidae)

      Chemosphere, Volume 212, 2018, pp. 262-271

      Academics researchers and “citizen scientists” from 22 countries confirmed that yellow mealworms, the larvae of Tenebrio molitor Linnaeus, can survive by eating polystyrene (PS) foam. More detailed assessments of this capability for mealworms were carried out by12 sources: five from the USA, six from China, and one from Northern Ireland. All of these mealworms digested PS foam. PS mass decreased and depolymerization was observed, with appearance of lower molecular weight residuals and functional groups indicative of oxidative transformations in extracts from the frass (insect excrement). An addition of gentamycin (30 mg g−1), a bactericidal antibiotic, inhibited depolymerization, implicating the gut microbiome in the biodegradation process. Microbial community analyses demonstrated significant taxonomic shifts for mealworms fed diets of PS plus bran and PS alone. The results indicate that mealworms from diverse locations eat and metabolize PS and support the hypothesis that this capacity is independent of the geographic origin of the mealworms, and is likely ubiquitous to members of this species.

    • Research article

      Biodegradation of polystyrene wastes in yellow mealworms (larvae of Tenebrio molitor Linnaeus): Factors affecting biodegradation rates and the ability of polystyrene-fed larvae to complete their life cycle

      Chemosphere, Volume 191, 2018, pp. 979-989

      Commercial production of polystyrene (PS) -a persistent plastic that is not biodegradable at appreciable rates in most environments-has led to its accumulation as a major contaminant of land, rivers, lakes, and oceans. Recently, however, an environment was identified in which PS is susceptible to rapid biodegradation: the larval gut of Tenebrio molitor Linnaeus (yellow mealworms). In this study, we evaluate PS degradation capabilities of a previously untested strain of T.molitor and assess its survival and PS biodegradation rates for a range of conditions (two simulated food wastes, three temperatures, seven PS waste types). For larvae fed PS alone, the %PS removed in the short (12–15h) residence time of the mealworm gut gradually increased for 2–3 weeks then stabilized at values up to 65%. Thirty two-day survival rates were >85% versus 54% for unfed larvae. For mealworms fed ∼10% w/w PS and ∼90% bran, an agricultural byproduct, rates of PS degradation at 25°C nearly doubled compared to mealworms fed PS alone. Polymer residues in the frass showed evidence of partial depolymerization and oxidation. All of the tested PS wastes degraded, with the less dense foams degrading most rapidly. Mealworms fed bran and PS completed all life cycle stages (larvae, pupae, beetles, egg), and the second generation had favorable PS degradation, opening the door for selective breeding.

    • Research article

      Biodegradation of polypropylene by yellow mealworms (Tenebrio molitor) and superworms (Zophobas atratus) via gut-microbe-dependent depolymerization

      Science of The Total Environment, Volume 756, 2021, Article 144087

      Polypropylene (PP), a fossil-based polyolefin plastics widely used worldwide, is non-hydrolyzable and resistant to biodegradation as a major source of plastic pollutants in environment. This study focused on feasibility of PP biodegradation in the larvae of two species of darkling beetles (Coleoptera: Tenebrionidae) i.e., yellow mealworms (Tenebrio molitor) and superworms (Zophobas atratus) using PP foam with number-, weight-, and size-average molecular weights (Mn, Mw, and Mz) of 109.8, 356.2, and 765.0kDa, respectively. The tests were conducted in duplicates with respective larvae (300T. molitor and 200 Z. atratus each incubator) at 25°C and 65% humidity for over a 35-day period. The larvae of T. molitor and Z. atratus fed with PP foam as sole diet consumed PP at 1.0±0.4 and 3.1±0.4mg 100 larvae−1days−1, respectively; when fed the PP foam plus wheat bran, the consumption rates were enhanced by 68.11% and 39.70%, respectively. Gel permeation chromatography analyses of the frass of T. molitor and Z. atratus larvae fed PP only indicated that Mw was decreased by 20.4±0.8% and 9.0±0.4%; Mn was increased by 12.1±0.4% and 61.5±2.5%; Mz was decreased by 33.8±1.5% and 32.0±1.1%, indicating limited extent depolymerization. Oxidation and biodegradation of PP was confirmed through analysis of the residual PP in frass. Depression of gut microbes with the antibiotic gentamicin inhibited PP depolymerization in both T. molitor and Z. atratus larvae. High throughput 16S rRNA sequencing revealed that Citrobacter sp. and Enterobacter sp. were associated with PP diets in the gut microbiome of Z. atratus larvae while Kluyvera was predominant in the T. molitor larvae. The results indicated that PP can be biodegraded in both T. molitor and Z. atratus larvae via gut microbe-dependent depolymerization with diversified microbiomes.

    • Research article

      Biodegradation of polylactic acid by yellow mealworms (larvae of Tenebrio molitor) via resource recovery: A sustainable approach for waste management

      Journal of Hazardous Materials, Volume 416, 2021, Article 125803

      Polylactic acid (PLA) is biodegraded rapidly under composting or thermophilic temperature but slowly under natural conditions with substantial microplastics generated. In this study, we examined the feasibility of PLA biodegradation and developed a novel approach for PLA waste management using yellow mealworms (Tenebrio molitor larvae) to achieve biodegradation and resource recovery simultaneously. Results confirmed PLA biodegradation in mealworms as sole PLA and PLA-bran mixtures (10%, 20%, 30% and 50% PLA, wt/wt). Feeding PLA-bran mixtures supported the larval development with higher survival rates and lower cannibal rates than feeding PLA only at ambient temperature. The PLA conversion efficiency was 90.9% with 100% PLA diet and was around 81.5–86.9% with PLA-bran mixtures. A peak insect biomass yield was achieved at a PLA ratio of 20%. PLA biodegradation was verified via detection of chemical and thermal modifications. Gut microbial community analysis indicated that intestinal communities shifted with PLA biodegradation, resulting in clusters with OTUs unique to the PLA diet. Based on these findings, we propose a circular approach for PLA waste management via resource recovery of used PLA as the feedstock for insect biomass production, management of mealworm excrement waste as fertilizer, and utilization of agricultural products for PLA production.

    This paper has been recommended for acceptance by Maria Cristina Fossi.

    1

    These authors contributed equally to this work.

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    © 2020 Published by Elsevier Ltd.

    FAQs

    What is Zophobas Atratus? ›

    Zophobas atratus Fabricius (Coleoptera: Tenebrionidae) is a large neotropical beetle. It is found on fruit bat guano and organic litter in its natural environment (Tschinkel and Willson, 1971; Quennedey et al., 1995).

    What bacteria degrade polyethylene? ›

    More than 20 bacterial genera have been shown to degrade different types of PE. Those include various Gram-negative and Gram-positives species belonging to the genera Pseudomonas, Ralstonia, Stenotrophomonas, Klebsiella, Acinetobactor, etc. and Rhodococcus, Staphylococcus, Streptococcus, Streptomyces, Bacillus, etc.

    What is polythene biodegradation? ›

    The degradation of polythene begins with the attachment of microbes to its surface. Various bacteria (Streptomyces viridosporus T7A, Streptomyces badius 252, and Streptomyces setonii 75Vi2) and wood degrading fungi produced some extracellular enzymes which leads of degradation of polythene [35,36,7].

    What are the health benefits of superworms? ›

    Mealworms and superworms are rich in protein, amino acids and vitamins and minerals like potassium and iron. Plus, they have less fat and cholesterol than beef.

    Are superworms harmful? ›

    Superworms and superworm beetles are docile and do not pose a threat to humans.

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