Characteristics of Aflatoxin B1 Degradation by Stenotrophomonas acidaminiphila and It’s Combination with Black Soldier Fly Larvae

Simple Summary Aflatoxin B1 (AFB1), one of the most hazardous mycotoxins commonly present in food and feed, causes great loss in livestock farming and severe safety risks to human health. In this paper, benefiting from using a sterile black soldier fly larvae (BSFL) system, we found that the ability of BSFL to degrade AFB1 was greatly reduced in the absence of gut microbiota, which indicated the important role of gut microbiota in AFB1 degradation. Furthermore, twenty-five AFB1-degrading bacteria were isolated from BSFL gut, and S. acidaminiphila A2 achieved the highest AFB1 degradation, by 94%. When S. acidaminiphila A2 was re-inoculated to BSFL, the detrimental effect of AFB1 on the growth performance of BSFL was alleviated, and complete AFB1 degradation in peanut meal was obtained. The present study may provide a strategy to degrade AFB1 in feedstuff through bioconversion with BSFL in combination with gut-originated AFB1-degrading bacteria, while providing a sustainable insect protein and fat source to animals. Abstract Aflatoxin B1 (AFB1) is a common mycotoxin contaminant in cereals that causes severe economic losses and serious risks to the health of humans and animals. In this paper, we investigated the characteristics of AFB1 degradation by black soldier fly larvae (BSFL) combined with commensal intestinal microorganisms. Germ-free BSFL and non-sterile BSFL were reared on peanut meal spiked with AFB1 for 10 days. The result showed that germ-free BSFL and non-sterile BSFL could achieve 31.71% and 88.72% AFB1 degradation, respectively, which indicated the important role of larvae gut microbiota in AFB1 degradation. Furthermore, twenty-five AFB1-degrading bacteria were isolated from BSFL gut, and S. acidaminiphila A2 achieved the highest AFB1 degradation, by 94%. When S. acidaminiphila A2 was re-inoculated to BSFL, the detrimental effect of AFB1 on the growth performance of BSFL was alleviated, and complete AFB1 degradation in peanut meal was obtained. In conclusion, the present study may provide a strategy to degrade AFB1 in feedstuff through bioconversion with BSFL in combination with gut-originated AFB1-degrading bacteria, while providing a sustainable insect protein and fat source to animals.


Introduction
Aflatoxins (AFs) are a group of toxic secondary metabolites produced by the Aspergillus species, notably Aspergillus flavus and Aspergillus parasiticus, that frequently contaminate Life 2023, 13, 234 3 of 13 medium was autoclaved at 121 • C for 15 min. The solid medium was added to 15 g L −1 agar based on the liquid medium.

Germ-Free Intestinal BSFL Model Construction
Germ-free BSFL was constructed as described in our previous study [22]. Fresh BSFL eggs provided by the BSFL Culturing Center of Henan Agricultural University were placed in a sterile centrifuge tube containing 1 mL of 2.7% NaClO solution and 1 mL of Sporgon (Beijing Mingyangkehua Bio-Technology, Beijing, China) and were shaken gently to disperse the eggs thoroughly. The disinfectant was decanted and the eggs were rinsed with sterile water three times. Disinfected eggs were inoculated into the brain heart infusion (BHI) medium and were incubated at 37 • C for 24 h. The culture was subsequently spread on the LB agar plates to verify the disinfection effect.

Degradation of AFB 1 in Peanut Meal by BSFL
Germ-free BSFL and non-sterile BSFL were reared on autoclaved wheat bran at 30 • C with 70% moisture content until 3rd instar larvae. Subsequently, twenty BSFL were inoculated into 9.0 g autoclaved peanut meal containing 100 ng g −1 AFB 1 . The BSFL were continuously reared for 10 days at 30 • C with 70% relative humidity. Three layers of gauze were added to the outside the incubator to maintain humidity and prevent larvae from creeping out. The AFB 1 -contaminated peanut meal without BSFL treatment was also put in the same condition to serve as the control. The BSFL and frass were separated by manual sieving with a 3 mm mesh and were dried at 75 • C for subsequent AFB 1 content analysis. The frass refers to the feces of the larvae and the residual substances of the feed. The AFB 1 content of all the samples was determined with high-performance liquid chromatography (HPLC) as described in Section 2.8. The AFB 1 degradation rate was calculated as: DR = (M1 − M2)/M1 × 100%, where M1 was the total AFB 1 content in the peanut meal, and M2 was the total AFB 1 content in the frass.

Screening and Identification of AFB 1 -Degrading Bacteria from BSFL Gut
Larvae from AFB 1 -contaminated peanut meal were surfaced cleaned with 75% alcohol and sterile 1% NaCIO solution, and sterile water. The intestines were dissected and washed. One gram of intestine sample was added to 10 mL of peptone water (0.1% w/v), mixed well by vortex and agitated for 30 min. The sample was diluted from 10 −1 to 10 −7 with sterile distilled water, and 100 µL of each dilution was spread on LB agar medium containing 1 µg mL −1 AFB 1 at 37 • C for 48 h. Single colonies were streaked on the same medium in different petri dishes to purify each isolate. Subsequently, the bacterial isolates were cultured in 50 mL of LB medium at 37 • C for 24 h and then tested for AFB 1 degradation capacity. An aliquot of 990 µL of bacterial culture was mixed with 10 µL of 10 µg mL −1 AFB 1 standard stock solution, and incubated at 37 • C for 48 h. In the control group, the bacterial culture was replaced with a sterile LB medium. The residual AFB 1 was extracted and quantified with high-performance liquid chromatography (HPLC). The AFB 1 degradation rate was calculated using the following equation: DR = (1 − C T /C C ) × 100%, where DR was the degradation rate and CT and CC were the AFB 1 concentration of experimental treatments and the control group, respectively.
Taxonomic characterization of the screened AFB 1 -degrading bacteria was performed by sequence analysis of the 16S rRNA gene. The genomic DNA was extracted using a Rapid Bacteria Genomic DNA Isolation Kit (Sangon Biotech, Shanghai, China). The 16S rRNA gene was amplified with universal primer 27F (5 -AGAGTTTGATCCTGGCTCAG-3 ) and 1492R (5 -TACGACTTAACCCCAATCGC-3 ). The obtained sequence was analyzed using a BLAST search in the NCBI database (http://blast.ncbi.nlm.nih.gov/blast, accessed on 3 March 2020), and was aligned using the Clustal W program. The phylogenetic tree was constructed by MEGA 7.0 according to the neighbor-joining algorithms with 1000 bootstrapping.

Characterization of the AFB 1 Degradation Ability of Stenotrophomonas acidaminiphila Strain A2
To determine the functional detoxification component, we analyzed the effects of the culture supernatant, cell pellets and cell fragments of the strain A2 on the AFB 1 removal ability. The bacterial culture was centrifuged at 12,000× g for 10 min. The culture supernatant and cell pellets were separated and then the supernatant was filtered with a 0.22 µm filter before use. The pellets were washed twice in PBS and then given an equal volume of PBS. A portion of cell suspension was sonicated on ice for 1 min and centrifuged at 12,000× g for 15 min at 4 • C to obtain cell fragments. The bacterial culture, culture supernatant, cell pellets and cell fragments were individually incubated with AFB 1 at 37 • C for 24 h. The sterile LB medium with AFB 1 was incubated for the same duration of time as a control. The experiment was conducted in triplicate. The effects of incubation time, pH, temperature, metal ions and AFB 1 content on AFB 1 removal by the strain A2 culture supernatant were further evaluated. The bacterial culture supernatant was incubated with AFB 1 for 8, 12, 16, 20, 24, 28, 32 and 36 h. The effect of pH on AFB 1 degradation was studied by adjusting the pH of bacterial culture supernatant to 5.0, 6.0, 7.0, 8.0 and 9.0 with 1 M HCI or 1 M NaOH and then incubating the samples at 37 • C for 24 h. The effect of temperature on AFB 1 degradation was studied by incubating the bacterial culture supernatant with AFB 1 at 20, 30, 40, 50, 60, 70, 80, 90 and 100 • C for 24 h. The effect of metal ions on AFB 1 degradation was explored by adding Na + , Cu 2+ , Mn 2+ , Mg 2+ , Ca 2+ , Zn 2+ and Fe 3+ to the bacterial culture supernatant at the final concentration of 1 mM, which was then incubated with AFB 1 at 37 • C for 24 h. Moreover, the AFB 1 degradation capacity of the bacterial culture supernatant was investigated at different initial AFB 1 concentrations (100, 200, 300, 400 and 500 ng mL −1 ).

The Influence of Stenotrophomonas acidaminiphila Strain A2 on the Growth Performance and AFB 1 Degradation Capacity of BSFL
Non-sterile BSFL were first reared on wheat bran until the 3rd instar larvae, and they were then divided into three groups. For the control group, twenty non-sterile BSFL and 9.0 g of autoclaved peanut meal were added. For the AFB 1 group, twenty non-sterile BSFL were inoculated into 9.0 g of autoclaved peanut meal containing 100 ng g −1 AFB 1 . For the AFB 1 +A2 group, twenty non-sterile BSFL and 1 mL of Stenotrophomonas acidaminiphila strain A2 culture suspension (OD600 = 1.0) were added to 9.0 g of autoclaved peanut meal containing 100 ng g −1 AFB 1 . Moreover, 1 mL of Stenotrophomonas acidaminiphila strain A2 culture suspension (OD600 = 1.0) was inoculated into 9.0 g of autoclaved peanut meal containing 100 ng g −1 AFB 1 without BSFL. The experiments were performed for 10 days in an incubator at 37 • C with 70% relative humidity. The survival rate, feed consumption rate and feed conversion rate of BSFL were determined as follows. The survival rate of BSFL (%) = (N1/N2) × 100%, where N1 and N2 were the BSFL survival numbers before and after rearing, respectively. Feed consumption rate of BSFL (%) = (W1 -W2)/W1 × 100%, where W1 was the weight of dry matter of peanut meal, and W2 was the weight of dry matter of frass. Feed conversion rate of BSFL (%) = (W3 − W4)/W1 × 100%, where W1 was the weight of dry matter of peanut meal, and W3 and W4 were the dry weight of BSFL before and after rearing, respectively. The AFB 1 degradation rate was determined as described in Section 2.3.
Dried BSFL samples were ground into homogenous powder for the measurement of nutritional compositions. The crude protein content was measured using hte Kjeldahl method based on GB 5009.5-2016 [23]; crude fat content was determined by Soxhlet Extraction based on GB 5009.6-2016 [24]; crude ash content was determined using the burning weighing method based on GB 5009.4-2016 [25]. The amino acid contents of BSFL were determined by liquid chromatography (LC) based on the method described by GB 5009.124-2016 [26]. 2.7. Quantification of AFB 1 by HPLC AFB 1 quantification was carried out by a high-performance liquid chromatography (HPLC) coupled with a fluorescence detector (Shimadzu, Tokyo, Japan). Detection conditions were: excitation at 360 nm and emission at 440 nm. A Diamonsil ® C18 reverse phase column (5 µm, 4.6 × 150 mm) was used for separation with the mobile phase consisting of water: methanol (45:55, v/v) at a flow rate of 1 mL min −1 . The sample injection volume was 10 µL. The AFB 1 standard samples were prepared in methanol with the concentration gradients (0, 6.25, 12.5, 25, 50, 75 and 100 ng mL −1 ) to establish the standard curve for AFB 1 concentration calculation.

Statistical Analysis
All experiments were performed with three replications. Student's t-test was used to determine the statistical significance of AFB 1 degradation rate between GF-BSFL and NS-BSFL groups. A one-way analysis of variance (ANOVA) with Tukey's multiple comparison test was performed to compare survival rate, feed consumption rate, body length, average dry weight and feed conversion rate among CON, AFB 1 and AFB 1 +A2 groups. The difference was regarded as statistically significant when p < 0.05.

Comparison of AFB 1 Degradation Ability of Germ-Free BSFL and Non-Sterile BSFL
The AFB 1 was not detected in the body of germ-free BSFL and non-sterile BSFL, which suggested that BSFL rapidly excreted or catabolized AFB 1 after ingestion. As shown in Table 1, the frass weight, AFB 1 concentration in frass and total residual AFB 1 content in frass in non-sterile BSFL treatment were significantly lower than those in the germ-free BSFL treatment. The AFB 1 degradation rate reached 31.71% and 88.72%, respectively, after treatment of germ-free BSFL and non-sterile BSFL.

Screening and Identification of AFB 1 -Degrading Bacteria from BSFL Gut
Individual isolates tested for AFB 1 degradation from the larval gut would provide direct evidence for AFB 1 degradation by gut microbiota. Two hundred and sixty eight bacteria were isolated from BSFL gut, and twenty-five of them displayed AFB 1 -degrading ability with a degradation percentage ranging from 28% to 94% ( Figure 1A). The colony of the strain A2, which displayed the highest AFB 1 degradation rate, was faint yellow with non-smooth edges on LB agar ( Figure 1B). Phylogenetic analysis indicated that the strain A2 belonged to the genus Stenotrophomonas in the phylogenetic clade of Stenotrophomonas acidaminiphila ( Figure 1C). The 16S rRNA gene of the strain A2 was 99.36% similar to that of S. acidaminiphila CB19. The taxonomic identification of ten other bacterial strains capable of degrading more than 60% of AFB 1 is shown in Table S1. acidaminiphila ( Figure 1C). The 16S rRNA gene of the strain A2 was 99.36% similar to that of S. acidaminiphila CB19. The taxonomic identification of ten other bacterial strains capable of degrading more than 60% of AFB1 is shown in Table S1.

Characterization of the AFB1 Degradation Ability of S. acidaminiphila Strain A2
In order to confirm the components for the degradation of AFB1 by strain A2, the bacterial culture, cell-free culture supernatant, cell pellets and cell fragments were individually tested for their AFB1-degrading abilities. The cell-free culture supernatant, cell pellets and cell fragments displayed quite different degradation activities. The cell-free culture supernatant achieved 86% AFB1 degradation, while the cell pellets and cell fragments could only degrade AFB1 by less than 20% (Figure 2A). Thus, the major active components of the strain A2 for AFB1 degradation were in the cell-free culture supernatant. The proteinase K treatment could destroy the active components in culture supernatant, and resulted in a decrease of the AFB1 degradation rate to 44%. The AFB1 degradation by the strain A2 cell-free culture supernatant was time-dependent. As shown in Figure 2B, the AFB1 degradation rate was only 43% at 8 h, and increased gradually with the increase of incubation time up to 24 h. The degradation of AFB1 was sensitive to the pH value. The cell-free culture supernatant could effectively degrade AFB1 at neutral and alkaline pH, achieving 77% to 92% AFB1 degradation at pH 7.0 to 9.0 ( Figure 2C). However, the percentage of AFB1 degradation decreased to less than 40% at pH 5.0 and 6.0. The effect of temperature on AFB1 degradation by the strain A2 cell-free culture supernatant is shown in Figure 2D. The AFB1 degradation rate ascended rapidly from 50% to 88% as the temperature rose from 20 to 40 °C, and then increased slightly to almost 100% at 70 °C. The further increase of incubation temperature led to a rapid decrease of AFB1 degradation rate. The effects of metal ions showed that the presence of Zn 2+ resulted in the reduction of AFB1 degradation rate from 86% to 65%, while Na + , Cu 2+ , Mn 2+ , Mg 2+ , Ca 2+ and Fe 3+ showed little effect on AFB1 degradation ( Figure 2E). Another important factor that can affect the AFB1 degradation rate is the substrate concentration. The result presented in Figure 2F shows that the cell-free culture supernatant was able to degrade more than 78% of AFB1 at an initial concentration of 100 to 500 ng mL −1 .

Characterization of the AFB 1 Degradation Ability of S. acidaminiphila Strain A2
In order to confirm the components for the degradation of AFB 1 by strain A2, the bacterial culture, cell-free culture supernatant, cell pellets and cell fragments were individually tested for their AFB 1 -degrading abilities. The cell-free culture supernatant, cell pellets and cell fragments displayed quite different degradation activities. The cell-free culture supernatant achieved 86% AFB 1 degradation, while the cell pellets and cell fragments could only degrade AFB 1 by less than 20% (Figure 2A). Thus, the major active components of the strain A2 for AFB 1 degradation were in the cell-free culture supernatant. The proteinase K treatment could destroy the active components in culture supernatant, and resulted in a decrease of the AFB 1 degradation rate to 44%. The AFB 1 degradation by the strain A2 cell-free culture supernatant was time-dependent. As shown in Figure 2B, the AFB 1 degradation rate was only 43% at 8 h, and increased gradually with the increase of incubation time up to 24 h. The degradation of AFB 1 was sensitive to the pH value. The cell-free culture supernatant could effectively degrade AFB 1 at neutral and alkaline pH, achieving 77% to 92% AFB 1 degradation at pH 7.0 to 9.0 ( Figure 2C). However, the percentage of AFB 1 degradation decreased to less than 40% at pH 5.0 and 6.0. The effect of temperature on AFB 1 degradation by the strain A2 cell-free culture supernatant is shown in Figure 2D. The AFB 1 degradation rate ascended rapidly from 50% to 88% as the temperature rose from 20 to 40 • C, and then increased slightly to almost 100% at 70 • C. The further increase of incubation temperature led to a rapid decrease of AFB 1 degradation rate. The effects of metal ions showed that the presence of Zn 2+ resulted in the reduction of AFB 1 degradation rate from 86% to 65%, while Na + , Cu 2+ , Mn 2+ , Mg 2+ , Ca 2+ and Fe 3+ showed little effect on AFB 1 degradation ( Figure 2E). Another important factor that can affect the AFB 1 degradation rate is the substrate concentration. The result presented in Figure 2F shows that the cell-free culture supernatant was able to degrade more than 78% of AFB 1 at an initial concentration of 100 to 500 ng mL −1 .

Effect of Stenotrophomonas acidaminiphila Strain A2 on the Growth Performance of BSFL
It is shown in Figure 3A that feeding the peanut meal without AFB1 resulted in a BSFL survival rate of 93%, indicating that the applied rearing condition was suitable to support its growth and development. However, the survival rate of BSFL reduced to 64% under exposure to AFB1 in the same condition. After the inoculation of S. acidaminiphila A2 into the AFB1-contaminated peanut meal, the survival rate of BSFL increased up to 86%. As presented in Figure 3B-E, the feed consumption rate, body length, average dry weight and feed conversion rate of BSFL were significantly reduced in the AFB1 group in comparison with the CON group, but no remarkable differences were observed between the AFB1+A2 group and the CON group. Thus, S. acidaminiphila A2 could effectively alleviate the toxicity of AFB1 to BSFL. In addition, the nutritional compositions of BSFL were determined ( Table 2). The exposure to AFB1 did not significantly influence crude ash and crude protein content, but resulted in an increase of crude fat in the body of BSFL. The addition of S. acidaminiphila A2 in AFB1-contaminated peanut meal slightly decreased the crude protein content in harvested BSFL. A total of seventeen free amino acids, including eight essential amino acids, were found in BSFL. There were no significant differences in thirteen individual free amino acids among the three groups. The Proline and Alanine content in BSFL harvested in the AFB1 and AFB1+A2 groups were lowered in comparison with the CON group. The Serine and Cystine content in BSFL harvested in the AFB1 group were significantly reduced after the addition of S. acidaminiphila A2.

Effect of Stenotrophomonas acidaminiphila Strain A2 on the Growth Performance of BSFL
It is shown in Figure 3A that feeding the peanut meal without AFB 1 resulted in a BSFL survival rate of 93%, indicating that the applied rearing condition was suitable to support its growth and development. However, the survival rate of BSFL reduced to 64% under exposure to AFB 1 in the same condition. After the inoculation of S. acidaminiphila A2 into the AFB 1 -contaminated peanut meal, the survival rate of BSFL increased up to 86%. As presented in Figure 3B-E, the feed consumption rate, body length, average dry weight and feed conversion rate of BSFL were significantly reduced in the AFB 1 group in comparison with the CON group, but no remarkable differences were observed between the AFB 1 +A2 group and the CON group. Thus, S. acidaminiphila A2 could effectively alleviate the toxicity of AFB 1 to BSFL. In addition, the nutritional compositions of BSFL were determined ( Table 2). The exposure to AFB 1 did not significantly influence crude ash and crude protein content, but resulted in an increase of crude fat in the body of BSFL. The addition of S. acidaminiphila A2 in AFB 1 -contaminated peanut meal slightly decreased the crude protein content in harvested BSFL. A total of seventeen free amino acids, including eight essential amino acids, were found in BSFL. There were no significant differences in thirteen individual free amino acids among the three groups. The Proline and Alanine content in BSFL harvested in the AFB 1 and AFB 1 +A2 groups were lowered in comparison with the CON group. The Serine and Cystine content in BSFL harvested in the AFB 1 group were significantly reduced after the addition of S. acidaminiphila A2.

Degradation of AFB 1 by BSFL Combined with Stenotrophomonas acidaminiphila Strain A2
The AFB 1 synergistic degradation between BSFL and commensal S. acidaminiphila A2 was explored. As shown in Figure 4, S. acidaminiphila A2 could degrade 41% AFB 1 in peanut meal after 10 days, while complete AFB 1 degradation was achieved by BSFL in combination with S. acidaminiphila A2.

Degradation of AFB1 by BSFL Combined with Stenotrophomonas aci
The AFB1 synergistic degradation between BSFL and commens was explored. As shown in Figure 4, S. acidaminiphila A2 could deg nut meal after 10 days, while complete AFB1 degradation was achi bination with S. acidaminiphila A2.

Discussion
Among numerous saprophagous insects, BSFL have become a date for bioconversion. They can effectively convert various organ mal manure, food waste and agricultural residues, to obtain high-q rich in protein and fat [16]. Previous research has shown that BSF mycotoxins (aflatoxins B1/B2/G2, deoxynivalenol, ochratoxin A, z pesticides (chlorpyrifos, chlorpyrifos-methyl, pirimiphos-methyl) tion in the larvae harvested [27]. Moreover, Meijer et al. [28] found enzymes and cytoplasmic reductases were involved in the metabol in BSFL, which could transform AFB1 into aflatoxicol and aflatox using a sterile BSFL system, we found that the ability of BSFL to deg reduced in the absence of microbiota, which indicated the importan the degradation. Indeed, insect gut microbiota can be considered an fluidity or malleability. The larval intestinal microbiota is a crucial c nutrient metabolic process [22] and helps the host to tolerate heav grade antibiotics [30,31]. Lou et el. [30] identified two bacterial strai GLD-1 and Ochrobactrum intermedium GLD-2-capable of degrad BSFL gut. Yang et al. [31] found that ciprofloxacin degradation by with intestinal microorganisms, and five strains that degrade cipr fied including Klebsiella pneumoniae BSFLG-CIP1, Trichosporon as otrichum sp. BSFLG-CIP3, Pichia kudriavzevii BSFLG-CIP4 and Pro

Discussion
Among numerous saprophagous insects, BSFL have become a strikingly good candidate for bioconversion. They can effectively convert various organic wastes, such as animal manure, food waste and agricultural residues, to obtain high-quality insect biomass rich in protein and fat [16]. Previous research has shown that BSFL can biodegrade six mycotoxins (aflatoxins B1/B2/G2, deoxynivalenol, ochratoxin A, zearalenone) and three pesticides (chlorpyrifos, chlorpyrifos-methyl, pirimiphos-methyl) with no bioaccumulation in the larvae harvested [27]. Moreover, Meijer et al. [28] found that cytochrome P450 enzymes and cytoplasmic reductases were involved in the metabolic conversion of AFB 1 in BSFL, which could transform AFB 1 into aflatoxicol and aflatoxin P 1 . Benefiting from using a sterile BSFL system, we found that the ability of BSFL to degrade AFB 1 was greatly reduced in the absence of microbiota, which indicated the important role of microbiota in the degradation. Indeed, insect gut microbiota can be considered an additional organ with fluidity or malleability. The larval intestinal microbiota is a crucial contributor to the BSFL nutrient metabolic process [22] and helps the host to tolerate heavy metals [29] and degrade antibiotics [30,31]. Lou et al. [30] identified two bacterial strains-Alcaligenes faecalis GLD-1 and Ochrobactrum intermedium GLD-2-capable of degrading lincomycin from BSFL gut. Yang et al. [31] found that ciprofloxacin degradation by BSFL was associated with intestinal microorganisms, and five strains that degrade ciprofloxacin were identified including Klebsiella pneumoniae BSFLG-CIP1, Trichosporon asahii BSFLG-CIP2, Geotrichum sp. BSFLG-CIP3, Pichia kudriavzevii BSFLG-CIP4 and Proteus mirabilis BSFLG-CIP5. In the current study, twenty-five AFB 1 -degrading bacteria were isolated from the intestine of BSFL reared on AFB 1 -contaminated peanut meal. Among them, Stenotrophomonas acidaminiphila strain A2 displayed the highest AFB 1 degradation rate of 94%. Similarly, Guan et al. [32] previously obtained a Stenotrophomonas Maltophilia from tapir feces, which could reduce AFB 1 by 82.5% in the liquid medium at 37 • C for 72 h. Cai et al. [33] reported that Stenotrophomonas sp. CW117 isolated from soils was able to degrade more than 90% of AFB 1 at the initial concentration of 40 to 4000 µg L −1 within 24 h.
The active components responsible for AFB 1 degradation were located in the culture supernatant of S. acidaminiphila A2. This is in agreement with the report of Cai et al. [33], who studied the AFB 1 degradation mechanism by Stenotrophomonas sp. CW117 and revealed that extracellular enzymes and non-protein components were responsible for the degradation activity. In a previous study of Zhao et al. [34], a 32 kDa extracellular enzyme with AFB 1 degradation capacity was purified from Myxococcus fulvus. Guo et al. [35] reported that the spore CotA laccase from Bacillus licheniformis could catalyze the C3-hydroxylation of AFB 1 , resulting in the formation of non-toxic transformation products aflatoxin Q 1 and epi-aflatoxin Q 1 . Further study was needed to elucidate the enzymatic mechanisms for AFB 1 degradation in S. acidaminiphila A2. The degradation of AFB 1 by S. acidaminiphila A2 depends on factors such as incubation time, pH, temperature, metal ions and substrate concentration. The AFB 1 degradation by the culture supernatant of S. acidaminiphila A2 was a relatively rapid and continuous process, with 67% AFB 1 degraded in the first 12 h and 87% degraded after 24 h. Similar results were obtained elsewhere. Cai et al. [33] reported a 52% reduction of AFB 1 within 6 h by a cell-free supernatant of Stenotrophomonas sp. CW117. Microbacterium proteolyticum B204 isolated from bovine feces could eliminate about 80% of AFB 1 after a 12 h treatment [36]. The culture supernatant of S. acidaminiphila A2 could effectively degrade AFB 1 under neutral and alkaline pH conditions, but gradually lost its AFB 1 degradation capacity at acidic pH. The effect of pH on AFB 1 degradation by a culture supernatant of S. maltophilia 35-3 showed a similar trend [32]. Moreover, the highest AFB 1 degradation was achieved at pH 7 and 8 by M. proteolyticum B204 [36]. Regarding the effect of temperature, we found that high temperature did not inhibit the AFB 1 degradation by a culture supernatant of S. acidaminiphila A2. Indeed, the degradation rate increased with the increase of temperature from 20 • C to 70 • C. Samuel et al. [37] also reported that the percentage of AFB 1 degradation by culture supernatant of Pseudomonas aeruginosa N17-1 was elevated from 45% at 20 • C to 90% at 65 • C. The culture supernatant of Trichoderma reesei CGMCC3.5218 could achieve more than 90% AFB 1 degradation at a temperature range from 45 • C to 90 • C [38]. These results imply that the enzymes or proteins involved in the AFB 1 degradation are thermostable. Various metal ions were examined for their effects on the AFB 1 degradation, and it was shown that the presence of Zn 2+ led to a decrease of AFB 1 degradation rate by a culture supernatant of S. acidaminiphila A2. The inhibitory effect of Zn 2+ was commonly observed on AFB 1 -degrading strains including Stenotrophomonas sp. CW117 [33], P. aeruginosa N17-1 [37] and T. reesei CGMCC3.5218 [38].
The growth performance of BSFL in AFB 1 -contaminated peanut meal was investigated. The exposure to AFB 1 resulted in a decrease of the survival rate and dry weight of BSFL as well as a reduction of feed consumption rate and feed conversion rate. However, Bosh et al. [20] previously found that BSFL displayed a high tolerance to AFB 1 , and their survival rate and body weight were not influenced when fed with poultry feed spiked with 0.5 mg kg −1 AFB 1 . BSFL are considered a promising alternative protein and fat source for use in animal feed. Interestingly, we found that the presence of AFB 1 in peanut meal could increase crude fat content by 2% but did not influence crude protein content in BSFL. In a recent study by Zhao et al. [39], yellow mealworms reared on AFB 1 -containing bran could provide the same quality of available larval protein and fat as those fed on bran without AFB 1 . The effect of AFB 1 on fat metabolism in the two different insects is worth further study. The presence of S. acidaminiphila A2 could alleviate the detrimental effect of AFB 1 on the growth performance of BSFL. Functional bacteria isolated from the BSFL gut have been found to benefit the growth of BSFL. Pei et al. [22] reported that Bacillus velezensis EEAM 10B could improve the protein synthesis process and digestive enzyme activities in BSFL, thus elevating the substance uptake and protein conversion ability of BSFL. When the intestinal ciprofloxacin-degrading isolates were re-inoculated to the sterile BSFL system, the larvae survival rate and weight were significantly increased in comparison with the sterile BSFL system [31]. Moreover, the addition of ciprofloxacin-degrading isolates could enhance the ciprofloxacin degradation efficiency of the sterile BSFL system. In our study, the AFB 1 in peanut meal could be completely degraded by BSFL in combination with S. acidaminiphila A2. The metabolic pathways of AFB 1 in BSFL and S. acidaminiphila A2 should be further investigated and clarified in depth. A toxicological test of the AFB 1 degradation product is also necessary.

Conclusions
The present study indicated that AFB 1 in peanut meal could be degraded by 31.71% and 88.72%, respectively, by germ-free BSFL and non-sterile BSFL for 10 days. Twenty-five AFB 1 -degrading bacteria were isolated from BSFL gut, and S. acidaminiphila A2 achieved the highest AFB 1 degradation, by 94%. The exposure to AFB 1 had an adverse effect on the growth performance of BSFL, resulting in a decrease of larvae survival rate and body weight. The supplementation of S. acidaminiphila A2 to BSFL could achieve complete AFB 1 degradation in peanut meal and alleviate the negative effect of AFB 1 on the growth performance of BSFL. Thus, it is promising to degrade AFB 1 in contaminated feedstuff by BSFL in combination with commensal AFB 1 -degrading microorganisms.
Supplementary Materials: The following supporting information can be downloaded at: https: //www.mdpi.com/article/10.3390/life13010234/s1, Table S1: Identification of strains capable of degrading more than 60% of AFB 1 by 16S rRNA gene analysis.