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Klebsiella pneumoniae in the intestines of Musca domestica larvae can assist the host in antagonizing the poisoning of the heavy metal copper

Abstract

Background

Musca domestica larvae are common saprophytes in nature, promoting the material—energy cycle in the environment. However, heavy metal pollution in the environment negatively affects their function in material circulation. Our previous research found that some intestinal bacteria play an important role in the development of housefly, but the responses of microbial community to heavy metal stresses in Musca domestica is less studied.

Results

In this study, CuSO4, CuSO4Klebsiella pneumoniae mixture and CuSO4K. pneumoniae phage mixture were added to the larval diet to analyze whether K. pneumoniae can protect housefly larvae against Cu2+ injury. Our results showed that larval development was inhibited when were fed with CuSO4, the bacterial abundance of Providencia in the intestine of larvae increased. However, the inhibition effects of CuSO4 was relieved when K. pneumoniae mixed and added in larval diets, the abundance of Providencia decreased. Electron microscope results revealed that K. pneumoniae showed an obvious adsorption effect on copper ion in vitro.

Conclusions

Based on the results we assume that K. pneumoniae could adsorb Cu2+, reduce Cu2+ impact on gut community structure. Our study explains the role of K. pneumoniae antagonizing Cu2+, which could be applied as a probiotic to saprophytic bioantagonistic metal contamination.

Peer Review reports

Background

In recent years, ecological and global public health issues associated with metal environmental pollution have received increasing attention [1]. When certain metals like iron (Fe), copper (Cu), nickel (Ni) and zinc (Zn) exceed certain thresholds, they are toxic to organisms [2]. Copper (Cu) is a crucial trace element for poultry and ruminant production and involves various physio-chemical or chemico-physiological processes and metabolisms in animal growth [3]. Copper sulfate (CuSO4) is commonly used as an additive in animal feed to promote growth and prevent copper deficiencies in the animals. It can also be used as a disinfectant to prevent the occurrence of diseases [4]. However, over-application of Cu2+ as a feed additive in poultry and livestock production systems would result in excessive Cu2+ entering the environment. Research has shown that Cu, Zn, Cd, Pb, Cr and Ni have been detected in poultry and livestock manure [5], and some of which even exceed the national heavy metal limit for animal feed [6]. Due to their bioaccumulation and nondegradable property, these metals combined with animal waste and urine to form organic compost. Heavy metals cannot be degraded during composting [7], and eventually, Cu may accumulate in aquatic foods, plants (fruits, crops, and vegetables), and drinking water and endanger human health [8].

With the rapid development of poultry and livestock farming around the world, biotransformation of saprophytic insects has emerged as a promising approach for sustainable livestock and poultry manure management in addition to traditional manure treatment techniques [9]. M. domestica larvae are resource-based insects that thrive in feces and organic matter. It can be used as an efficient method for the biotransformation of pig manure and is regarded as a sustainable substitute for pig manure management [10]. However, heavy metal residues in feces have adverse effects on larval growth and biological functions of their transformation ability [11]. Therefore, it is of great importance to investigate toxicity mechanism of heavy metals and the adaptation mechanism of M.domestica larvae for improving the efficiency of M.domestica larval biotransformation.

The heavy metals in the environment enter the insect through food intake and mainly accumulate in the insect intestine. Insects harbor diverse microorganisms in the gut, complex environments where gut microbes interact and compete with microorganisms from the outside world, providing their host with physiological and ecological advantages [12, 13]. Gut microbiota, especially some beneficial flora, play an important role in maintaining the normal physiological function of the host [14]. However, how the gut microbial community responses to heavy metal and the role specific bacteria played when M.domestica larvae encountered heavy metal stress has been little studied.

Some studies have shown that metals have a significant effect on the intestinal community structure of insects, fish and animals. Exposure to cadmium can lead to a decrease in the abundance of Bifidobacteria and Prevotella in the intestine, thereby leading to lipid metabolism disorders and fat accumulation in the liver of mice [15]. The intestinal flora of Hermetia illucens L. exposed to Cu2+ and Cd2+ changed significantly [16]. Honeybees subtly change the overall composition of the microbiome and metabolic group of honeybees after exposure to Cd2+ [17]. Cd2+ treatment significantly changed the richness and diversity of the microbiota in zebrafish and was reported to be harmful to zebrafish health by altering its gut community structure [18]. The relative abundance of Aeromonas decreased in the intestinal community structure of Bufo gargarizans tadpoles after exposed to Cr2+ indicating that Aeromonas were susceptible to Cr2+ stress [19]. At present, there is a lack of detailed reports on the toxicity mechanism of heavy metals and their interactions with intestinal flora on houseflies.

Our previous studies have shown that intestinal probiotics in M.domestica larvae can promote larval growth. Klebsiella pneumoniae is one of our identifed beneficial bacteria that is essential for the growth and development of M.domestica larvae [20]. Therefore, in this paper, we analyzed the effects of heavy metals on the gut flora of houseflies and the beneficial bacteria K. pneumoniae played when larvae face heavy metal stress.

The interactions between K. pneumoniae and Cu2+ was investigated, and the microecological mechanism of K. pneumoniae antagonizing metals was further analyzed. We found that when M.domestica larvae encounter Cu2+ stress, K. pneumoniae, as a beneficial bacterium in the intestinal community, can alleviate the host damage caused by Cu2+ through adsorption of Cu2+. An antagonistic relationship between the beneficial bacteria in the gut of M.domestica larvae and heavy metals was found in this study, which provided a new possibility for the control of heavy metal pollution in the ecological environment.

Reasults

Effects of the interaction of Cu2+Klebsiella pneumoniae and its phage mixture on the growth and development of Musca domestica larvae

In order to verify the interaction between metals and K. pneumoniae in the organism, we added Cu2+K. pneumoniae to the M.domestica larvae and observed their effects on the growth and developmental ability. Based on the previous investigations [21,22,23], the common range of metal content of copper (Cu) was detected in the feces of poultry and livestock and within this range 300 μg/mL and 600 μg/mL of CuSO4 were selected for the subsequent experiments.After analysis, we found that Cu2+ inhibited the growth and development of M.domestica larvae and died at 600 µg/mL (Fig. 1A). Therefore, we selected 300 µg/mL CuSO4 for follow-up experiment. The results showed that the body weight (14.1 mg) and length (8 mm) of M.domestica larvae fed CuSO4 (Cu) were significantly lower than those of the control group (Lb). The growth and development of M.domestica larvae exposed to 300 μg/mL were significantly inhibited (Fig. 1B), and the pupation rate was significantly reduced (Fig. 1C). The body weight and length of M.domestica larvae fed CuSO4K. pneumoniae (CuK) were significantly higher than those of the Lb group. Compared with the Cu group, the body weight increased significantly and the inhibition of M.domestica larval development was significantly alleviated (Fig. 1B), and the pupation rate and eclosion rate increased significantly (Fig. 1 C and D). When CuSO4K. pneumoniae and its phage were fed together (CuP), the body weight and length of M.domestica larvae were significantly reduced compared with Lb group (Fig. 1B). Compared with Cu group, there was no significant difference in pupation rate and eclosion rate of M.domestica larvae (Fig. 1 C and D).

Fig. 1
figure 1

Effects of different groups on the growth and development of housefly larvae. A The body weight and body length of housefly larvae fed 300 μg/mL and 600 μg/mL CuSO4. B The body weight and body length of housefly larvae in different experimental groups. C Pupation rate in different experimental groups. D Eclosion rate of different experimental groups Abbreviations: Lb, Luria–Bertani medium; Cu, CuSo4; K, K. pneumoniae solution; CuK, Mixed solution of K. pneumoniae and CuSO4; P, K. pneumoniae phage; CuP, Mixed solution of K. pneumoniae phage and CuSO4. Asterisks indicate significant differences at *p < 0.05, **p < 0.01, ***p < 0.001,****p < 0.0001

Effects of the interaction of the heavy metal Cu2+K. pneumoniae and its phage mixture on the creeping ability of M. domestica larvae

In order to observe the effect of metal Cu2+ on M.domestica larvae from the whole aspect of K. pneumoniae, we examined their crawling ability. The results showed that feeding the mixture of CuSO4K. pneumoniae phage could significantly inhibit the creeping ability of M.domestica larvae, and feeding CuSO4K. pneumoniae could significantly promote the creeping ability of M.domestica larvae (Fig. 2A and B).

Fig. 2
figure 2

The creeping ability of housefly larvae fed with different groups. A The creeping trajectory of housefly larvae in solid agar medium. B Analysis of the creeping distance of housefly larvae. Abbreviations: Lb, Luria–Bertani medium; Cu, CuSo4; K, K. pneumoniae solution; CuK, Mixed solution of K. pneumoniae and CuSO4; P, K. pneumoniae phage; CuP, Mixed solution of K. pneumoniae phage and CuSO4. Asterisks indicate significant differences at *p < 0.05, **p < 0.01

Analysis of intestinal damage in M. domestica larvae

In order to verify more visually that metallic Cu2+ causes damage to intestinal tissues and whether the addition of K. pneumoniae attenuates this damage, we conducted trypan blue staining experiments. Meanwhile, the damaged domestic fly larvae under different application conditions were observed through tissue sections. Trypan blue staining was used to identify intestinal cell damage in M.domestica larvae exposed to Cu2+- K. pneumoniae and its phage mixture. Positive trypan blue staining was only observed in Cu group, CuK group, P group, CuP group including indicating that these treatments induced gut damage in M.domestica larvae (Fig. 3A).In the intestinal tissue sections of M. domestica larvae, we could obviously observe that the intestinal mucosa of M. domestica larvae in Cu group was irregular, while this phenomenon was significantly alleviated in CuK group (Fig. 3B).

Fig. 3
figure 3

Intestinal damage of housefly larvae fed by different groups. A Positive trypan blue staining was present in the Cu, CuK, P, and CuP groups. No signs of tissue damage were observed in the Lb and K larvae. B Damaged tissue sections of domestic fly larvae in different experimental groups (100 ×). Abbreviations: Lb, Luria–Bertani medium; Cu, CuSo4; K, K. pneumoniae solution; CuK, Mixed solution of K. pneumoniae and CuSO4; P, K. pneumoniae phage; CuP, Mixed solution of K. pneumoniae phage and CuSO4. Asterisks indicate significant differences at *p < 0.05, **p < 0.01, ***p < 0.001,****p < 0.0001

Analysis of the microbial diversity index of Musca domestica larvae under the interaction of Cu2+K. pneumoniae and its phage mixture

In order to study the mechanism of the anti-metal ability of K. pneumoniae on the growth and development of M.domestica larvae, we used 16S rRNA gene sequencing technology to analyze the changes in gut flora, and then verified it at the molecular level. Firstly, a total of 966,413 high-quality reads were measured from the original data after mass filtration. On the basis of 99% sequence homology, 61,480 OTUs were detected in all samples. The α-diversity of the intestinal microbiota was estimated by the community diversity index (Shannon) and richness index (ACE, Chao1) for the six groups. The results of the analysis using ACE and Chao1 index showed that there was no significant difference in microbial richness among the experimental groups compared with Lb, however, in the CuP group, the Chao1 index increased, and the intestinal microflora richness of M.domestica larvae increased (Fig. 4A). B). The Shannon as indicators of diversity in the OTUs in samples, indicated that there was no significant difference in the intestinal microflora diversity of M.domestica larvae between the Cu and CuK groups and the Lb groups; however, in the P and CuP groups, the Shannon index increased the intestinal flora diversity of M.domestica larvae (Fig. 4C).

Fig. 4
figure 4

Violin plot of Microbial Species Richness (A, B) and Species Diversity (C) indices of Musca domestica larvae exposed to different experimental groups (A) ACE index, (B) Chao1 index, (C) Shannon index. Abbreviations: Lb, Luria–Bertani medium; Cu, CuSO4; K, K. pneumoniae solution; CuK, mixed solution of K. pneumoniae and CuSO4; P, K. pneumoniae phage; CuP, mixed solution of K. pneumoniae phage and CuSO4. Asterisks indicate significant differences at *p < 0.05, **p < 0.01, ***p < 0.001,****p < 0.0001

Analysis of the composition and structure of the gut flora of Musca domestica larvae under the interaction of Cu2+K. pneumoniae and its phage mixture

To analyze the influence of the Cu2+K. pneumoniae and its phage mixture on the gut microbiota of M.domestica larvae. The gut community structure of the larvae in different groups was analyzed. At the phylum level, Proteobacteria was the dominant intestinal flora in all samples. The abundance of Proteobacteria in the Cu group (99.44%) was higher than that in the Lb group, and that in the CuK group (98.29%) was lower than that in the Lb group and K group. When fed Klebsiella phage, the abundance of Proteobacteria increased (98.15%), and that of the CuP group (99.12%) increased and was higher than that of the Lb group, Cu group and P group (Fig. 5A). At the genus level, the community structure of gut microflora in the different groups was significantly different from that in the Lb groups. We found that compared with the Lb group, Klebsiella and Enterobacter in the intestinal tract of M.domestica larvae in the Cu group increased, while the relative abundance of Koukoilia and Proteus decreased significantly. In the CuK group, we found that compared with the Lb group and Cu group, the abundance of Klebsiella and Bordetella in the intestine of M.domestica larvae increased significantly, while compared with the K group, the abundance of Klebsiella and Enterobacter increased, and the relative abundance of Paenalcaligenes and Provincia decreased. In the CuP group, compared with those in the Lb and Cu groups, the abundances of Enterobacter and Klebsiella increased significantly. Compared with those in the P group, the abundances of Enterobacter, Klebsiella and Bordetella increased significantly, and the relative abundances of Paenalcaligenes, Koukoilia, Proteus and Provincia decreased (Fig. 5B). This is consistent with the heatmap analysis, through the analysis, we found that in the Cu group, Klebsiella and Enterobacter increased significantly, but in the CuK group, the Klebsiella increased more significantly, in the Group P, the abundance of Klebsiella bacteria decreased significantly, while in the CuP group, Klebsiella and Enterobacter increased significantly (Fig. 5C).

Fig. 5
figure 5

Relative abundances of bacterial components in samples of housefly larvae fed different feeds. A The relative abundances of bacteria at the phylum level. B The relative abundances of bacteria at the genus level. C Heatmaps of the relative abundances and distributions of bacterial genera in housefly larvae. Heatmaps are based on the composition of bacterial genera of the different feeding groups, with each genus color coded, as shown in the panel. Abbreviations: Lb, Luria–Bertani medium; Cu, CuSo4; K, K. pneumoniae solution; CuK, Mixed solution of K. pneumoniae and CuSO4; P, K. pneumoniae phage; CuP, Mixed solution of K. pneumoniae phage and CuSO4

We further analyzed the structural differences of the gut microflora in the different samples. Principal co-ordinate analysis (PCoA) showed that the gut microflora structure of M.domestica larvae every group was significantly different compare with Lb groups. The gut flora in the K and CuK groups clustered together, the Cu group and CuP group clustering together, and the gut flora in the Lb group and P group clustered together separately (Fig. 6A). UPGMA tree analysis provides further evidence to support the cluster analysis of different samples (Fig. 6B). The Venn diagram revealed the common and unique OTUs in all samples, the Venn diagrams also showed the differences in gut microflora samples of M.domestica larvae (Fig. 6C).

Fig. 6
figure 6

Differences in bacterial community structures and relationships between the feeding groups. A Principal coordinate analysis (PCoA) of bacterial community structures of the six groups. Each symbol represents one sample of intestinal bacteria. B Unweighted pair group method with arithmetic mean (UPGMA) evolutionary tree analysis of samples. C Venn diagram analysis of unique and shared OTUs of the intestinal bacteria in housefly larval samples. The number represents the number of unique OTUs in each sample and common OTUs shared by two or more samples. Abbreviations: Lb, Luria–Bertani medium; Cu, CuSO4; K, K. pneumoniae solution; CuK, mixed solution of K. pneumoniae and CuSO4; P, K. pneumoniae phage; CuP, mixed solution of K. pneumoniae phage and CuSO4

Analysis of the intestinal flora interaction of M. domestica larvae under the interaction of Cu2+Klebsiella pneumoniae and its phage mixture

To study the effect of feeding in different groups on the interactions of gut microflora of M.domestica larvae, we first constructed a related network of M.domestica larvae gut microflora (Fig. 7). The results showed that the CuK group significantly changed the interaction between the intestinal flora of silkworm larvae. Compared with the Lb group, the total number of nodes of the interaction network in the intestinal microflora of the Cu group increased, the average path distance increased, the average aggregation decreased, the positive correlation intensity decreased, the negative correlation intensity increased, and the negative correlation increased, which decreased the interaction stability of the intestinal microflora of M.domestica larvae. In the CuK group, compared with the Lb group, the total number of nodes increased, the average path distance increased, the average clustering coefficient decreased, the positive correlation decreased, the negative correlation increased, and the stability of intestinal microflora of M.domestica larvae decreased; compared with the Cu group, the total number of nodes decreased, the average path distance increased, the average clustering coefficient decreased, the positive correlation increased, the negative correlation decreased, which made the interactions of gut microflora of M.domestica larvae more stable. In the CuP group, compared with the Lb group, the total number of nodes increased, the average path distance increased, the average clustering coefficient increased, and the positive correlation increased, but the negative correlation decreased, which made the interactions of gut microflora of M.domestica larvae more stable. Compared with the Cu group, the summary points increased, the average path distance increased, the average clustering coefficient increased, the positive correlation increased, and the negative correlation decreased, which made the interactions of gut microflora of M.domestica larvae more stable (Table 1).

Fig. 7
figure 7

Intestinal bacterial cooccurrence microbiome networks between different processing groups. Network analysis of different groups. Each point in the figure represents a species, and species with correlations are connected by a line. Red lines represent positive correlations, green lines represent negative correlations, and the intensity of the line represents the level of correlation. B NetShift analysis of different groups. Potential “driver taxa” of infection based on bacterial network analysis of the experimental group (P, K, CuP, CuK, and Cu) and the control groups (Lb), marked as P vs. Lb, K vs. Lb, CuP vs. Lb, CuK vs. Lb, respectively. Node sizes are proportional to their scaled NESH (neighbor shift) score (a score identifying important microbial taxa of microbial association networks), and those nodes colored red were important driver taxa. As a result, large red nodes denote particularly important driver taxa under different conditions. Line colors indicate node (taxa) connections as follows: red edges, association present only in experimental groups; green edges, association present only in control groups; blue edges, association present in both the experimental and control groups. Abbreviations: Lb, Luria–Bertani medium; Cu, CuSO4; K, K. pneumoniae solution; CuK, mixed solution of K. pneumoniae and CuSO4; P, K. pneumoniae phage; CuP, mixed solution of K. pneumoniae phage and CuSO4

Table 1 Co-occurrence network indices of different groups

In all samples, there was a high degree of connectivity within Proteobacteria, especially the interactions between Proteobacteria (89.25%). In the Cu group, the interaction between Proteobacteria (91.4%) was enhanced, the interaction between Firmicutes (6.99%) and Proteobacteria was enhanced, and the interaction between Actinobacillus (1.61%), Proteobacteria and Firmicutes was significantly weakened. In the CuK group, compared with the Lb group and Cu group, the interaction between Proteobacteria (90%) was enhanced, the interaction between Firmicutes (2.35%) and Proteobacteria was weakened, and the interaction between Actinobacillus (5.29%), Bacteroides (2.35%) and Proteobacteria was significantly enhanced. In the CuP group, compared with the Lb group and the Cu group, the interaction between Proteobacteria (94.92%) was enhanced, and the interaction between Firmicutes (3.52%), Bacteroides (1.17%), Actinobacillus (0.39%) and Proteobacteria was weakened (Fig. 7A). The Netshift analysis revealed that Proteus, Bordetella, Morganella and Paenochrobactrum were the potential key bacterial groups in the Cu group. In the K group, Koukoulia, Leucobacter, Alcaligenes and Klebsiella were the potential key bacterial groups in the initial microbiomes of M.domestica larvae. Koukoulia, Leucobacter, Arthrobacter, Klebsiella and Alcaligenes were the potential key bacterial groups in the CuK group initial microbiomes of M.domestica larvae. In the P group, Morganella, Proteus and Kerstersia were the potential key bacterial groups in the initial microbiomes of M.domestica larvae. Koukoulia, Leucobacter, Arthrobacter, Klebsiella and Alcaligenes were the potential key bacterial groups in the CuP group initial microbiomes of M.domestica larvae (Fig. 7B).

Analysis of electron microscope results

The in vivo model of M.domestica larvae showed that the addition of K. pneumoniae could alleviate the damage caused by Cu2+ to M.domestica larvae, We inferred that the metal adsorption of K. pneumoniae could reduce the effect of heavy metals on intestinal flora and then played a useful regulatory role. To verify our hypothesis, we carried out in vitro verification experiments to verify the relationship between K. pneumoniae and Cu2+. K. pneumoniae was cultured in different concentrations of Lb-Cu2+ medium (Lb-Cu medium). The results showed that in Lb-Cu medium containing different concentrations of Cu2+, the growth of K. pneumoniae was significantly inhibited with increasing Cu2+ concentration (Fig. 8A). The scanning electron microscopy (SEM) results showed that Cu2+ was obviously adsorbed on K. pneumoniae (Fig. 8B). The cytoplasm of K. pneumoniae inoculated in Lb-Cu medium was obviously damaged (Fig. 8C).

Fig. 8
figure 8

A K.pneumoniae was inoculated in different concentrations of Lb-Cu medium, and the growth of bacteria was measured under OD600 absorbance conditions. B Scanning electron microscope (SEM) image (10,000 ×) (C) Transmission electron microscope (TEM) image (25,000 ×). Abbreviations: K, K. pneumoniae solution; CuK, mixed solution of K. pneumoniae and CuSO4; CuP, mixed solution of K. pneumoniae phage and CuSO4

Analysis of the immune function of M. domestica larvae

To further verify the antagonistic effect of K. pneumoniae on M.domestica larvae caused by Cu2+, we measured phenoloxidase (PO) activity in different experimental groups. We found that compared with the Lb group, there was no difference in phenoloxidase activity and no melanization in the hemolymph of larvae on Day 1. The hemolymph PO activity of larvae on the Day 2 for the Cu and CuP groups was significantly inhibited, and there was no melanization in larval hemolymph. There was no significant difference in PO activity between the CuK group and Lb group and no melanization in larval hemolymph. The activity of PO in the hemolymph of the larvae in the Day 4, Cu, P and CuP groups was significantly inhibited, and there was no melanization in the hemolymph of the larvae. There was no significant difference in the PO activity between the CuK group and the Lb group (Fig. 9). These results showed that the immunity of M.domestica larvae decreased after feeding CuSO4K. pneumoniae alleviated the damage caused by Cu2+ to M.domestica larvae.

Fig. 9
figure 9

Effects of different diets on PO activity in the hemolymph of housefly larvae. Abbreviations: Lb, Luria–Bertani medium; Cu, CuSO4; K, K. pneumoniae solution; CuK, mixed solution of K. pneumoniae and CuSO4; P, K. pneumoniae phage; CuP, mixed solution of K. pneumoniae phage and CuSO4. Asterisks indicate significant differences at *p < 0.05, **p < 0.01

Discussion

With the continuous development of industry, copper is used in a variety of industries. Cu is an essential metal for human, animals and plants, it is associated with numerous physiological and biochemical processe, and it acts as a cofactors in numerous enzymes such as laccase, cytochrome coxidase, polyphenol oxidase [24]. Cu is a basic micronutrient for insect respiration, pigmentation and oxidation, but it is toxic at certain exposure concentrations. In our study, when the concentration of Cu2+ reached 600 μg/mL, the body weight and length of M.domestica larvae were significantly inhibited, and death occurred. According to previous studies, when the concentration of Cu2+ reaches 600 μg/L, the development rate and pupation ratio of Aedes aegypti were significantly decreased; in addition to this, it has been shown that exposure to the nanoparticle Fe3O4 inhibits the growth and development of M.domestica larvae, resulting in the inability to feather properly and causing significant damage to their tissues and digestive system [25, 26]. In this study, we analyzed the alterations in the growth and development and intestinal microflora of M.domestica larvae under the influence of Cu2+K. pneumoniae and its phage mixture to observe the role of the addition and removal of K. pneumoniae in Cu2+ antagonistic. We found that when Cu2+K. pneumoniae, the damage caused by Cu2+ to the host was significantly reduced, while after the targeted removal of K. pneumoniae, the damage caused by Cu2+ to the host was more severe. The SEM and TEM results further explain that K. pneumoniae could adsorb Cu2+ to reduce the negative effect of Cu2+ on intestinal flora.

Existing studies have shown that heavy metal exposure can change the intestinal flora of insects, some researchers believe that insects can be used as biological indicators of heavy metal pollution [27]. For example, it has studies shown that heavy metals play an important impact on the intestinal flora of animals and insects such as black soldier flies, fish, Amphibia, and others [16, 28, 29]. In our study, M.domestica larvae were exposed to CuSO4, and the intestinal flora of M.domestica larvae changed significantly, mainly characterized by a significant increase in the abundance of Klebsiella and Enterobacter. Enterobacter is beneficial to M.domestica larval growth, which can inhibit the growth of some pathogenic strains in M.domestica larvae, increase the load of beneficial bacteria in the intestinal microbial community and balance the interaction of intestinal microflora in M.domestica larvae [30]. We assume that the increased Enterobacter and Klebsiella are the anti-damage bacteria produced by M.domestica larvae stimulated by Cu2+. Lactobacillus is the dominant genus of adult Drosophila, however, when Drosophila is exposed to Pb2+, Komagataeibacter becomes the main dominant genus of bacteria [31].

Beneficial bacteria play an important role in the growth and development of insects, they can participate in host metabolism, synthesize amino acids, vitamins, and nutrients, regulate hormones, physiological response, which in turn plays a regulatory role in the development process of insects [32,33,34]. The intestinal community diversity and humoral immunity of M. domestica larvae increased with the addition of E. hormaechei, K. pneumoniae, Acinetobacter bereziniae and Enterobacter cloacae during the growth and development of M. domestica larvae [35]. Candida albicans, a symbiotic bacterium in the intestinal tract of adult Bactrocera minax, it provides essential amino acids for its growth and development and can also convert urea into available nitrogen sources through metabolism, thus significantly increasing its fecundity [17]. The application of bacteria results in a significant increase in honeybee brooding, pollen and harvested honey [36]. Our study showed that after the combined application of Cu2+K. pneumoniae, the intestinal flora of M.domestica larvae change significantly, the body weight and length increased significantly, and the exercise ability returned to the normal level, which indicated that the addition of K. pneumoniae would further increase the abundance of beneficial bacteria in the intestinal tract of M.domestica larvae and antagonize Cu2+. The results of SEM showed that K. pneumoniae could aggregate and adsorb Cu2+, alleviating the damage of Cu to other beneficial bacteria in intestinal tract, which further verified the antagonism of K. pneumoniae to Cu2+ in vivo.

Bacteriophages can target and kill pathogens without affecting other bacteria [37, 38]. In our study, when M.domestica larvae were fed K. pneumoniae phage, the abundance of K. pneumoniae in the intestine of M.domestical arvae decreased significantly, and the intestinal community structure of M.domestica larvae changed. Interestingly, however, we found that the relative abundance of K. pneumoniae did not decrease, compared to the Lb and Cu groups after application of Cu2+- K. pneumoniae phages. The body weight and body length of M.domestica larvae were significantly higher than those of the Cu group. We speculate that Klebsiella phage may be resistant to bacteriophages and that Cu2+ stimulates the host to produce Klebsiella to fight against the damage of Cu2+. Zhang X et al. also found a similar phenomenon; they believe that single-use phages can establish an intestinal phage amplification model, and bacteria may soon become resistant to this phage [39], When bacteriophages are continuously added, they will not produce significant effects [40].

Beneficial bacteria not only reflect the growth and development of M.domestica larvae but also play an important role in antagonizing intestinal tissue damage and immunity. Related studies have shown that exposure to copper-containing compounds can lead to DNA damage, apoptosis, inflammation, changes in gene expression, tissue damage and gill damage in fish [41, 42]. In our study, we found that the intestinal tissue of M.domestica larvae was obviously damaged after exposure to Cu2+. PO is one of the necessary enzymes in the insect immune system to resist microbial invasion. PO plays an important role in the growth, development and immune function of insects [43]. Some studies have shown that when insects are invaded by exotic microorganisms, inactive prophenoloxidase (PPO) activates PO under the action of related serine proteases to form quinones. PPO can regulate phagocytosis, coating and blackening and participate in the immune defense process of insects [44]. At present, PO activity is used as a standard index to evaluate the immune ability of insects. In our study, we found that the PO activity decreased after feeding Cu2+ to M.domestica larvae, which indicated that Cu2+ could damage the immunity of M.domestica larvae. When we give Cu2+K. pneumoniae, the PO activity of M.domestica larvae returned to the normal level, which indicated that the addition of K. pneumoniae could prevent the damage of Cu2+ to the immune system. After the targeted removal of K. pneumoniae, PO activity was more inhibited, which further confirmed the importance of K. pneumoniae in antagonizing the immune damage caused by Cu2+.

Conclusions

In conclusion, this study revealed that K. pneumoniae helped M.domesticalarvae resist damage from Cu2+ stress by regulating intestinal microflora and adsorbed Cu2+, thereby reduced Cu2+ effect on other bacteria (especially beneficial bacteria), thus producing obvious antagonism.

Materials and methods

Materials

The houseflies used in this study were raised in the Laboratory of Vector and Vector-borne Diseases of Shandong First Medical University since 2005. Adult houseflies were fed with brown sugar and water, and the larvae were fed with wet wheat bran and milk powder [wheat bran (g): water (mL): milk powder (g) = 1:1:0.4]. Houseflies were reared in an artificial climate incubator maintained at 25 ± 1℃ and 70% relative humidity under a photo period of 12/12 h [light/dark].

Klebsiella pneumoniae was isolated from M.domestica larvae, and based on specificity, bacteriophages that could attack the bacteria were isolated [20].

A copper-containing compound (CuSO4) were purchased from Kaitong Chemical Reagent Institute, Tianjin, China. Copper (300 μg/mL) solution was prepared as mother liquor for follow-up experiments.

Experiment design

K. Pneumoniae were inoculated into Luria–Bertani liquid (Lb liquid) and cultured at 37 °C and 110 rpm in a constant temperature culture oscillator. After 24 h of cultivation, 30 mL of K. Pneumoniae (OD600 = 2.00) stock solution was used for subsequent experiments. 30 mL of K. pneumoniae phage solution was diluted 107-fold with Lb liquid for subsequent experiments. A total of 0.03537 g CuSO45H2O was dissolved separately in 30 mL of Lb liquid and 30 mL of K. pneumoniae (OD600 = 2.00) stock solution to prepare a CuSO4 solution and K. pneumoniae mixture, respectively. A total of 0.03537 g CuSO45H2O was dissolved separately in 30 mL of K. pneumoniae phage solutions to prepare CuSO4 and K. pneumoniae phage (107) solution mixtures, respectively. Sterilized wheat bran (30 g) was separately mixed with 30 mL of Lb liquid medium (group Lb), CuSO4 solution (group Cu), K. Pneumoniae (OD600 = 2.00) (group K), CuSO4-K. Pneumoniae mixture (group CuK), K. Pneumoniae phage (107) solution (group KP)and CuSO4-K. Pneumoniae phage mixture (group CuP) for larval feed and placed in a 5 mL sterile centrifuge tube with small holes on the top. As reported in our previous study [45], wheat bran (1.5 g-1.6 g) were added in a 1:1 proportion to the 5 mL centrifuge tube. The tubes were placed in an artificial climate incubator maintained and kept at a predetermined time point (1, 2, 3, 4 days). The same number of larvae were taken from each test tube, and their body length, body weight, pupal weight, pupation rate and emergence rate were recorded.

Extraction of intestinal DNA and Bioinformatics analysis

DNA extraction of the intestinal bacteria and determining changes in gut composition using Illumina MiSeq Sequencing were carried out using the same method [45]. MENAP is used to analyze the OTU data of each sample, and the network was performed using Gephi (Gephi 0.10.1, France) [46,47,48,49].

Sample preparation for scanning and transmission electron microscopy

The Luria–Bertani medium containing 300 μg/ mL Cu2+ of heavy metals was configured (named Lb-Cu). K.pneumoniae bacterial stock solution were inoculated into Lb-Cu medium and cultured for 24 h, the growth of bacteria was detected under the condition of OD600 absorption. Bacteria obtained by centrifugation were fixed overnight in 2.5% (v/v) glutaraldehyde. Then they were sectioned in 2 mm × 1 mm samples with parallel surfaces to get a flat surface of observation. Samples were observed using a scanning electron microscope (SEM) (Hitachi SU 8020, Tokyo, Japan). According to previous studies [49], samples were prepared and observed were observed by transmission electron microscope (TEM) (Hitachi, H-7650).

Determination of the crawling ability of M.domestica larvae in different experimental groups

Three 3-day-old Musca domestica larvae with good growth condition were placed on solid Agar medium. The larvae were removed after 10 min, and the creeping tracks of M.domestica larvae were photographed and recorded and then marked with Digimizer4. The length of creeping tracks was calculated. Each experimental group was repeated 3 times.

Trypan blue staining of M.domestica larvae

In this experiment, two-day-old M.domestica larvae were selected for staining to observe the intestinal damage of different experimental treatments to M.domestica larvae. Three replicates were analyzed in each group (8 larvae per replicate). The larvae of M.domestica in different groups crawled for 10 min to remove food traces in the gut of larvae. M.domestica larvae were transferred to a 1.5 mL centrifuge tube, washed thoroughly with PBS (1 ×) solution, and 1 mL of trypan blue staining solution was added and the solution was kept under shaking conditions for 30 min. The stained larvae were rinsed three times with PBS (1 ×) solution. Larval staining was eventually observed under a microscope.

Analysis of phenoloxidase activity of M.domestica larvae in different experimental groups

The same number of larvae were extracted from Lb, Cu, K, CuK, P and CuP, and the phenoloxidase (PO) activity was analyzed by the same method as reported in our previous study [35].

Statistical analysis

All data analysis was performed by IBM SPSS Statistics 20 statistical software. All data are expressed as mean ± SD. The effects of the body weight and body length of M.domestica larvae were compared by using Two-way ANOVA followed by Sidak correction. The microbial diversity index, pupation rate, pupal weight, eclosion, crawling distance and phenoloxidase activity in the hemolymph of the larvae were analyzed by one-way ANOVA. Significance analysis was performed by Sidak’s multiple comparisons test (p < 0.05).

Availability of data and materials

The 16 s sequence data of the microbiome were stored in the Sequence Read Archive database (BioProject accession number: PRJNA970925).

References

  1. Tchounwou PB, Yedjou CG, Patlolla AK, Sutton DJ. Molecular, clinical and environmental toxicicology Volume 3: Environmental Toxicology [Internet]. Mol. Clin. Environ. Toxicol. 2012. Available from: https://0-doi-org.brum.beds.ac.uk/10.1007/978-3-7643-8340-4

  2. Gao M, Lin Y, Shi GZ, Li HH, Yang ZB, Xu XX, et al. Bioaccumulation and health risk assessments of trace elements in housefly (Musca domestica L.) larvae fed with food wastes. Sci Total Environ Elsevier BV. 2019;682:485–93. https://0-doi-org.brum.beds.ac.uk/10.1016/j.scitotenv.2019.05.182.

    Article  CAS  Google Scholar 

  3. Hesari BA, Mohri M, Seifi HA. Effect of copper edetate injection in dry pregnant cows on hematology, blood metabolites, weight gain and health of calves. Trop Anim Health Prod. 2012;44:1041–7.

    Article  PubMed  Google Scholar 

  4. Zhu Y-G, Johnson TA, Su J-Q, Qiao M, Guo G-X, Stedtfeld RD, et al. Diverse and abundant antibiotic resistance genes in Chinese swine farms. Proc Natl Acad Sci. 2013;110:3435–40.

    Article  PubMed  PubMed Central  CAS  Google Scholar 

  5. Peng S, Zhang H, Song D, Chen H, Lin X, Wang Y, et al. Distribution of antibiotic, heavy metals and antibiotic resistance genes in livestock and poultry feces from different scale of farms in Ningxia, China. J Hazard Mater. 2022;440:129719.

  6. Nkwunonwo UC, Odika PO, Onyia NI. A Review of the Health Implications of Heavy Metals in Food Chain in Nigeria. ScientificWorldJournal. 2020;2020:6594109.

  7. Chen X, Du Z, Guo T, Wu J, Wang B, Wei Z, et al. Effects of heavy metals stress on chicken manures composting via the perspective of microbial community feedback. Environ Pollut Elsevier Ltd; 2022;294:118624. Available from: https://0-doi-org.brum.beds.ac.uk/10.1016/j.envpol.2021.118624

  8. Gao Y, Li X, Dong J, Cao Y, Li T, Mielke HW. Snack foods and lead ingestion risks for school aged children: A comparative evaluation of potentially toxic metals and children’s exposure response of blood lead, copper and zinc levels. Chemosphere. Elsevier Ltd; 2020;261:127547. Available from: https://0-doi-org.brum.beds.ac.uk/10.1016/j.chemosphere.2020.127547

  9. Rehman KU, Ur Rehman R, Somroo AA, Cai M, Zheng L, Xiao X, et al. Enhanced bioconversion of dairy and chicken manure by the interaction of exogenous bacteria and black soldier fly larvae. J Environ Manage. 2019;237:75–83.

  10. Zhu F-X, Yao Y-L, Wang S-J, Du R-G, Wang W-P, Chen X-Y, et al. Housefly maggot-treated composting as sustainable option for pig manure management. Waste Manag. 2015;35:62–7.

    Article  PubMed  Google Scholar 

  11. Kökdener M, Gündüz NEA, Zeybekoǧlu Ü, Aykut U, Yllmaz AF. The effect of different heavy metals on the development of Lucilia sericata (Diptera: Calliphoridae). J Med Entomol. 2022;59:1928–35.

    Article  PubMed  Google Scholar 

  12. Jang S, Kikuchi Y. Impact of the insect gut microbiota on ecology, evolution, and industry. Curr Opin Insect Sci. 2020;41:33–9.

    Article  PubMed  Google Scholar 

  13. Raffaelli S, Abreo E, Altier N, Vázquez Á, Alborés S. Bioprospecting the Antibiofilm and Antimicrobial Activity of Soil and Insect Gut Bacteria. Molecules. 2022;27(6):2002.

  14. Rosenfeld CS. Gut Dysbiosis in Animals Due to Environmental Chemical Exposures. Front Cell Infect Microbiol. 2017;7:396.

  15. Ba Q, Li M, Chen P, Huang C, Duan X, Lu L, et al. Sex-dependent effects of cadmium exposure in early life on gut microbiota and fat accumulation in mice Environ Health Perspect. Public Health Services US Dept Health Human Services. 2017;125:437–46.

    CAS  Google Scholar 

  16. Wu N, Wang X, Xu X, Cai R, Xie S. Effects of heavy metals on the bioaccumulation, excretion and gut microbiome of black soldier fly larvae (Hermetia illucens). Ecotoxicol Environ Saf. 2020;192:110323

  17. Rothman JA, Leger L, Kirkwood JS, McFrederick QS. Cadmium and Selenate Exposure Affects the Honey Bee Microbiome and Metabolome, and Bee-Associated Bacteria Show Potential for Bioaccumulation. Appl Environ Microbiol. 2019;85(21):e01411–19.

  18. Xia Y, Zhu J, Xu Y, Zhang H, Zou F, Meng X. Effects of ecologically relevant concentrations of cadmium on locomotor activity and microbiota in zebrafish. Chemosphere. 2020;257:127220.

  19. Yao Q, Yang H, Wang X, Wang H. Effects of hexavalent chromium on intestinal histology and microbiota in Bufo gargarizans tadpoles. Chemosphere. 2019;216:313–23. https://0-doi-org.brum.beds.ac.uk/10.1016/j.chemosphere.2018.10.147.

    Article  PubMed  CAS  Google Scholar 

  20. Zhang K, Wang S, Yao D, Zhang X, Zhang Q, Liu W,et al. Aerobic and facultative anaerobic Klebsiella pneumoniae strains establish mutual competition and jointly promote Musca domestica development. Front Immunol. 2023;14:1102065

  21. Liu WR, Zeng D, She L, Su WX, He DC, Wu GY, et al. Comparisons of pollution characteristics, emission situations, and mass loads for heavy metals in the manures of different livestock and poultry in China. Sci Total Environ. 2020;734:139023.

    Article  PubMed  CAS  Google Scholar 

  22. Zhang F, Li Y, Yang M, Li W. Content of heavy metals in animal feeds and manures from farms of different scales in Northeast China. Int J Environ Res Public Health. 2012;9:2658–68.

    Article  PubMed  PubMed Central  CAS  Google Scholar 

  23. Mu HY, Zhuang Z, Li YM, Qiao YH, Chen Q, Xiong J, et al. Heavy metal contents in animal manure in china and the related soil accumulation risks. Huanjing Kexue/Environmental Sci. 2020;41:986–96.

    Google Scholar 

  24. Shabbir Z, Sardar A, Shabbir A, Abbas G, Shamshad S, Khalid S, et al. Copper uptake, essentiality, toxicity, detoxification and risk assessment in soil-plant environment. Chemosphere. 2020;259:127436.

    Article  PubMed  CAS  Google Scholar 

  25. Neff E, Dharmarajan G. The direct and indirect effects of copper on vector-borne disease dynamics. Environ Pollut. 2021;269:116213. https://0-doi-org.brum.beds.ac.uk/10.1016/j.envpol.2020.116213. (Elsevier Ltd).

    Article  PubMed  CAS  Google Scholar 

  26. Toto NA, Elhenawy HI, Eltaweil AS, El-Ashram S, El-Samad LM, Moussian B, et al. Musca domestica (Diptera: Muscidae) as a biological model for the assessment of magnetite nanoparticles toxicity. Sci Total Environ. 2022;806:151483.

    Article  PubMed  CAS  Google Scholar 

  27. Skaldina O, Ciszek R, Peräniemi S, Kolehmainen M, Sorvari J. Facing the threat: common yellowjacket wasps as indicators of heavy metal pollution. Environ Sci Pollut Res. 2020;27:29031–42.

    Article  CAS  Google Scholar 

  28. Chang X, Li H, Feng J, Chen Y, Nie G, Zhang J. Effects of cadmium exposure on the composition and diversity of the intestinal microbial community of common carp (Cyprinus carpio L.) Ecotoxicol Environ Saf. Academic Press. 2019;171:92–8.

    CAS  Google Scholar 

  29. Mu D, Meng J, Bo X, Wu M, Xiao H, Wang H. The effect of cadmium exposure on diversity of intestinal microbial community of Rana chensinensis tadpoles. Ecotoxicol Environ Saf. 2018;154:6–12. https://0-doi-org.brum.beds.ac.uk/10.1016/j.ecoenv.2018.02.022.

    Article  PubMed  CAS  Google Scholar 

  30. Zhang Q, Wang S, Zhang X, Zhang K, Liu W, Zhang R, et al. Enterobacter hormaechei in the intestines of housefly larvae promotes host growth by inhibiting harmful intestinal bacteria. Parasites Vectors BioMed Central. 2021;14:1–15. https://0-doi-org.brum.beds.ac.uk/10.1186/s13071-021-05053-1. (Elsevier Ltd).

    Article  CAS  Google Scholar 

  31. Beribaka M, Jelić M, Tanasković M, Lazić C, Stamenković-Radak M. Life History Traits in Two Drosophila Species Differently Affected by Microbiota Diversity under Lead Exposure. Insects. 2021;12(12):1122.

  32. Mattila HR, Rios D, Walker-Sperling VE, Roeselers G, Newton IL. Characterization of the active microbiotas associated with honey bees reveals healthier and broader communities when colonies are genetically diverse. PLoS One. 2012;7(3):e32962.

  33. Janashia I, Choiset Y, Jozefiak D, et al. Beneficial Protective Role of Endogenous Lactic Acid Bacteria Against Mycotic Contamination of Honeybee Beebread. Probiotics Antimicrob Proteins. 2018;10(4):638–46.

  34. Lee JB, Park KE, Lee SA, Jang SH, Eo HJ, Jang HA, et al. Gut symbiotic bacteria stimulate insect growth and egg production by modulating hexamerin and vitellogenin gene expression. Dev Comp Immunol. Elsevier Ltd; 2017;69:12–22. https://0-doi-org.brum.beds.ac.uk/10.1016/j.dci.2016.11.019

  35. Zhang Q, Wang S, Zhang X, Zhang K, Li Y, Yin Y, et al. Beneficial bacteria in the intestines of housefly larvae promote larval development and humoral Phenoloxidase activity, while harmful bacteria do the opposite. Front Immunol. 2022;13:1–12.

    Google Scholar 

  36. Alberoni D, Baffoni L, Gaggìa F, Ryan PM, Murphy K, Ross PR, et al. Impact of beneficial bacteria supplementation on the gut microbiota , colony. 2018;1–10.

  37. Buttimer C, McAuliffe O, Ross RP, Hill C, O’Mahony J, Coffey A. Bacteriophages and bacterial plant diseases. Front Microbiol. 2017;8:1–15.

    Article  Google Scholar 

  38. Iriarte FB, Obradović A, Wernsing MH, Jackson LE, Balogh B, Hong JA, et al. Soil-based systemic delivery and phyllosphere in vivo propagation of bacteriophages: Two possible strategies for improving bacteriophage persistence for plant disease control. Bacteriophage. 2012;2:215–24. https://0-doi-org.brum.beds.ac.uk/10.4161/bact.23530.

    Article  PubMed  PubMed Central  Google Scholar 

  39. Zhang X, Wang S, Zhang Q, Zhang K, Liu W, Zhang R, et al. The expansion of a single bacteriophage Leads to bacterial disturbance in Gut and reduction of larval growth in Musca Domestica. Front Immunol. 2022;13:1–13.

    Google Scholar 

  40. Gogokhia L, Buhrke K, Bell R, Hoffman B, Brown DG, Hanke-Gogokhia C, et al. Expansion of bacteriophages IS linked to aggravated intestinal inflammation and colitis. Cell Host Microbe. 2019;25:285–99. https://0-doi-org.brum.beds.ac.uk/10.1016/j.chom.2019.01.008. (Elsevier Ltd).

    Article  PubMed  PubMed Central  CAS  Google Scholar 

  41. Isani G, Falcioni ML, Barucca G, Sekar D, Andreani G, Carpenè E, et al. Comparative toxicity of CuO nanoparticles and CuSO4 in rainbow trout. Ecotoxicol Environ Saf. 2013;97:40–6. https://0-doi-org.brum.beds.ac.uk/10.1016/j.ecoenv.2013.07.001. (Elsevier).

    Article  PubMed  CAS  Google Scholar 

  42. Wang T, Long X, Liu Z, Cheng Y, Yan S. Effect of copper nanoparticles and copper sulphate on oxidation stress, cell apoptosis and immune responses in the intestines ofjuvenile Epinephelus coioides. Fish Shellfish Immunol. 2015;44:674–82. https://0-doi-org.brum.beds.ac.uk/10.1016/j.fsi.2015.03.030. (Elsevier Ltd).

    Article  PubMed  CAS  Google Scholar 

  43. Eleftherianos I, Revenis C. Role and importance of phenoloxidase in insect hemostasis. J Innate Immun. 2011;3:28–33.

    Article  PubMed  CAS  Google Scholar 

  44. Marieshwari BN, Bhuvaragavan S, Sruthi K, Mullainadhan P, Janarthanan S. Insect phenoloxidase and its diverse roles: melanogenesis and beyond. J Comp Physiol B. 2023;193(1):1–23.

  45. Zhang Q, Wang S, Zhang X, Zhang R, Zhang Z. Negative Impact of Pseudomonas aeruginosa Y12 on Its Host Musca domestica. Front Microbiol. 2021;12:691158.

  46. Deng Ye, Jiang Yi-Huei, Yang Yunfeng, He Zhili, Luo Feng, Zhou Jizhong. Molecular ecological network analyses. BMC Bioinformatics. 2012;13:113.

    Article  PubMed  PubMed Central  Google Scholar 

  47. Zhou J, Deng Y, Luo F, He Z, Tu Q, Zhi X. Functional molecular ecological networks. mBio. 2010;1(4):e00169–10.

  48. Dini-Andreote F, De Cássia PE, Silva M, Triadó-Margarit X, Casamayor EO, Van Elsas JD, Salles JF. Dynamics of bacterial community succession in a salt marsh chronosequence: Evidences for temporal niche partitioning. ISME J. 2014;8:1989–2001.

    Article  PubMed  PubMed Central  CAS  Google Scholar 

  49. Wang S, Zhang K, Zhang Q, Li Y, Yin Y, Liu W, et al. Pseudomonas aeruginosa Y12 play positive roles regulating larval gut communities when housefly encountered copper stress. Ecotoxicol Environ Saf. 2023;258:114978.

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Acknowledgements

The authors are grateful to Liu Chao for his kind help with the sequencing and graphing.

Funding

This work was supported by the National Natural Science Foundation of China [grant numbers 81572028, 81871686].

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YYS: Methodology, Investigation, Writing—original draft. WSM: Investigation, Writing—review and editing. ZKX, LY, LWJ, ZQ, ZXY, KXX, AS: Writing—review and editing. ZZ, ZRL: Conceptualization, Supervision, Funding acquisition, Writing— review and editing.

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Yin, Y., Wang, S., Zhang, K. et al. Klebsiella pneumoniae in the intestines of Musca domestica larvae can assist the host in antagonizing the poisoning of the heavy metal copper. BMC Microbiol 23, 383 (2023). https://0-doi-org.brum.beds.ac.uk/10.1186/s12866-023-03082-7

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