Biodegradation of Aflatoxin B1 in the Baijiu Brewing Process by Bacillus cereus

Aflatoxin is a potent mycotoxin and a common source of grain contamination that leads to great economic losses and health problems. Although distilled baijiu cannot be contaminated by aflatoxin, its presence in the brewing process affects the physiological activities of micro-organisms and reduces product quality. Bacillus cereus XSWW9 capable of degrading aflatoxin B1 (AFB1) was isolated from daqu using coumarin as the sole carbon source. XSWW9 degraded 86.7% of 1 mg/L AFB1 after incubation at 37 °C for 72 h and tolerated up to 1 mg/L AFB1 with no inhibitory effects. Enzymes in the cell-free supernatant of XSSW9 played a significant role in AFB1 degradation. The AFB1-degradation activity was sensitive to protease K and SDS treatment, which indicated that extracellular proteins were responsible for the degradation of AFB1. In order to investigate the AFB1-degradation ability of XSSW9 during the baijiu brewing process, AFB1 and XSWW9 were added to grain fermentation (FG-T) and normal grain fermentation without AFB1, while normal grain fermentation without AFB1 and XSWW9 was used as a control (FG-C). At the end of the fermentation, 99% AFB1 was degraded in the residue of fermented grains. The differences of microbial communities in the fermented grains showed that there were no significant differences between FG-T and FG-C in the relative abundance of dominant genera. The analysis of volatile compounds of their distillation showed that the contents of skeleton flavor components was similar between FG-T and FG-C. These results offer a basis for the development of effective strategies to reduce the effect of AFB1 on the brewing process and ensure that the production of baijiu is stable.


Introduction
Mycotoxins are secondary metabolites produced by some fungi that grow on cereals and cereal products. Most mycotoxins have carcinogenic, teratogenic, and mutagenic effects, among which aflatoxin is the most damaging [1]. In addition to their effects on human health, mycotoxins affect the microbial community structure and the metabolic functions of micro-organisms. Aflatoxin is classified as a class I carcinogen by the Cancer Research Institute of the World Health Organization (WHO). It is a highly toxic substance which can damage the liver of humans or livestock and potentially lead to liver cancer and even death in severe cases [2]. More than 20 types of aflatoxins and derivatives have been isolated to date, among which AFB 1 is the most toxic and carcinogenic [3]. Under favorable growth conditions, mycotoxigenic fungi can lead to contamination during grain production, storage, processing, and distribution [4]. Sorghum is often damaged by rain in the field and severely infected with grain mold, including aspergillus infection and aflatoxin production. Mycotoxin contamination and grain mold of sorghum are considered the most important threats to grain quality and production across the world [4]. In addition, corn is affected by Previously, there were few reports on the use of micro-organisms to degrade mycotoxins in baijiu brewing materials or control the mycotoxins produced by daqu microorganisms. In this study, we explored the effects of using AFB 1 -degrading strains in the baijiu brewing process. We isolated bacteria capable of degrading AFB 1 from daqu and evaluated the ability of the isolates to degrade AFB 1 . The microbial community dynamics and metabolic profile in the baijiu brew were analyzed. Overall, this study represents the first step in understanding the metabolism and function of AFB 1 -degrading strains in brewing liquor, and it may help improve the quality of baijiu.

Isolation of Microbial Strains for AFB 1 Degradation
A strain with a stable and remarkable performance of AFB 1 degradation was screened by subculturing it six times in a primary liquid medium with coumarin as the sole carbon source. This strain, named XSWW9, could degrade more than 85% of 1 mg/L AFB 1 after 2 d of cultivation in a fermentation medium under static conditions at 37 • C.
We cloned and analyzed the complete 16S rRNA gene of strain XSWW9. Phylogenetic analysis indicated that XSSW9 was a strain of Bacillus cereus. The 16S rRNA gene of XSSW9 was 99.24% similar to that of Bacillus cereus strain ATCC 14579 ( Figure 1a). The colonies appeared pale yellow to yellow on potato dextrose agar and other nutritive media ( Figure 1b). XSWW9 was able to hydrolyze aesculin, but not starch. The optimum pH was 6.0-8.0, and the strain could grow at 20-50 • C with an optimum growth temperature range of 30-37 • C.
Next, XSSW9 was cultured with 1 mg/L AFB 1 , and the biomass of the strain and AFB 1 degradation were investigated. After 36 h of rapid growth, the biomass of XSSW9 reached a peak and stabilized, and after 48 h, the biomass gradually dropped. It was suggested that the metabolism of the strain was extremely active in the 24-48 h window. The period of AFB 1 degradation coincided with this time interval. The concentration of AFB 1 dropped quickly as microbial growth increased at the beginning of the lag phase, and more than 85% of AFB 1 was degraded within 72 h (Figure 1c).

Adaptability of B. cereus XSSW9 to the Temperatures Found in Baijiu Fermentation Pits
During the fermentation of baijiu, the grains are fermented in fermentation pits at temperatures ranging from 20 to 50 • C. Since the survival status of micro-organisms is greatly affected by temperature, we investigated whether B. cereus XSSW9 can survive normally in this environment and degrade toxins. A batch test of AFB 1 degradation by XSWW9 fermentation broth with an initial AFB 1 concentration of 1 mg/L was carried out at 20-50 • C ( Figure 2). The optimal temperature for the growth of XSWW9 was 37 • C. Accordingly, XSWW9 presented the highest AFB 1 degradation ratio at 37 • C as the removal of AFB 1 by either adsorption or biodegradation is dependent on the biomass. In addition, the biomass and degradation rate of AFB 1 were lower when the strain was grown at 50 • C. It is possible that the high temperature inhibited the growth of the strain; thus, the degradation rate of AFB 1 was also significantly lower. The biomass of the strain and the degradation rate of AFB 1 increased alongside increasing temperatures between 20 and 37 • C. In this range, increased temperatures may have promoted the bioavailability of organic compounds, which thereby facilitated the biodegradation process [39]. Overall, this strain has a high growth and AFB 1 degradation rate at temperatures found in baijiu fermentation pits.
We cloned and analyzed the complete 16S rRNA gene of strain XSWW9. Phylogenetic analysis indicated that XSSW9 was a strain of Bacillus cereus. The 16S rRNA gene of XSSW9 was 99.24% similar to that of Bacillus cereus strain ATCC 14579 (Figure 1a). The colonies appeared pale yellow to yellow on potato dextrose agar and other nutritive media ( Figure 1b). XSWW9 was able to hydrolyze aesculin, but not starch. The optimum pH was 6.0-8.0, and the strain could grow at 20-50 °C with an optimum growth temperature range of 30-37 °C.   Next, XSSW9 was cultured with 1 mg/L AFB1, and the biomass of the strain and AFB1 degradation were investigated. After 36 h of rapid growth, the biomass of XSSW9 reached a peak and stabilized, and after 48 h, the biomass gradually dropped. It was suggested that the metabolism of the strain was extremely active in the 24-48 h window. The period of AFB1 degradation coincided with this time interval. The concentration of AFB1 dropped quickly as microbial growth increased at the beginning of the lag phase, and more than 85% of AFB1 was degraded within 72 h (Figure 1c).

Adaptability of B. cereus XSSW9 to the Temperatures Found in Baijiu Fermentation Pits
During the fermentation of baijiu, the grains are fermented in fermentation pits at temperatures ranging from 20 to 50 °C. Since the survival status of micro-organisms is greatly affected by temperature, we investigated whether B. cereus XSSW9 can survive normally in this environment and degrade toxins. A batch test of AFB1 degradation by XSWW9 fermentation broth with an initial AFB1 concentration of 1 mg/L was carried out at 20-50 °C ( Figure 2). The optimal temperature for the growth of XSWW9 was 37 °C. Accordingly, XSWW9 presented the highest AFB1 degradation ratio at 37 °C as the removal of AFB1 by either adsorption or biodegradation is dependent on the biomass. In addition, the biomass and degradation rate of AFB1 were lower when the strain was grown at 50 °C. It is possible that the high temperature inhibited the growth of the strain; thus, the degradation rate of AFB1 was also significantly lower. The biomass of the strain and the degradation rate of AFB1 increased alongside increasing temperatures between 20 and 37 °C. In this range, increased temperatures may have promoted the bioavailability of organic compounds, which thereby facilitated the biodegradation process [39]. Overall, this strain has a high growth and AFB1 degradation rate at temperatures found in baijiu fermentation pits.  AFB 1 degradation due to cell-free supernatant, cell supernatant, and cell extracts of XSSW9 cultured in fermentation medium without AFB 1 for 48 h was investigated by conducting an additional incubation of these fractions with 1 mg/L AFB 1 in the dark at 37 • C for 72 h ( Figure 3). AFB 1 was shown to be stable after 72 h of incubation in pbs at 37 • C. A significant reduction (p < 0.0001; 87.04% AFB 1 degradation) was observed when AFB 1 was treated with the cell-free supernatant of XSWW9. In contrast, the bacterial cells and cell extracts showed relatively low AFB 1 degradation ratios (20.4% and 41.4%, respectively). These results suggested that a secreted factor played a major role in AFB 1 degradation. treated with the cell-free supernatant of XSWW9. In contrast, the bacterial cells and ce extracts showed relatively low AFB1 degradation ratios (20.4% and 41.4%, respectively These results suggested that a secreted factor played a major role in AFB1 degradation.
Next, protease K treatment was performed to investigate whether the degradation AFB1 is enzymatic. The AFB1 degradation ratio of the cell-free supernatant decreased 59.8% after treatment with protease K, and it decreased to 12.9% after treatment with pr tease K combined with SDS. Similarly, the AFB1 degradation ratio of the cell extracts d creased to 27.3% after treatment with protease K, and it decreased to 11.8% after treatme with protease K combined with SDS. These results indicated that enzymes or other pr teins might play important roles in the degradation of AFB1 by the strain XSWW9 [40 Similar findings were reported by Sangare et al. [41] and Yu et al. [42].
The mechanisms of the microbial detoxification of mycotoxins have been classifie previously based on binding or degradation [43]. Currently, the most common mech nism applied to remove mycotoxins on an industrial scale is adsorption. However, a sorbed toxins can potentially be released during prolonged incubation periods [44,45]. strain XSWW9, the proteins secreted by the cells played a major role in AFB1 degradatio Therefore, XSWW9 may have greater application potential than available strains.  The strain XSWW9 was cultured in a fermentation medium without AFB 1 at 37 • C for 48 h. The cell-free supernatant, cell supernatant, and cell extracts were collected and cultured at 37 • C for 48 h to test their ability to degrade AFB 1 and the effect of protease K treatment. The data represent the means and standard deviations for triplicate independent experiments. Next, protease K treatment was performed to investigate whether the degradation of AFB 1 is enzymatic. The AFB 1 degradation ratio of the cell-free supernatant decreased to 59.8% after treatment with protease K, and it decreased to 12.9% after treatment with protease K combined with SDS. Similarly, the AFB 1 degradation ratio of the cell extracts decreased to 27.3% after treatment with protease K, and it decreased to 11.8% after treatment with protease K combined with SDS. These results indicated that enzymes or other proteins might play important roles in the degradation of AFB 1 by the strain XSWW9 [40]. Similar findings were reported by Sangare et al. [41] and Yu et al. [42].
The mechanisms of the microbial detoxification of mycotoxins have been classified previously based on binding or degradation [43]. Currently, the most common mechanism applied to remove mycotoxins on an industrial scale is adsorption. However, adsorbed toxins can potentially be released during prolonged incubation periods [44,45]. In strain XSWW9, the proteins secreted by the cells played a major role in AFB 1 degradation. Therefore, XSWW9 may have greater application potential than available strains.

The Effect of Temperature and pH on AFB 1 Degradation by the Cell-Free Supernatant of B. cereus XSSW9
The degradation rate of AFB 1 increased as the incubation temperature increased from 20 • C to 37 • C. However, when the incubation temperature reached 50 • C, the degradation rate of AFB 1 showed a significant decrease (Figure 4a). These results are consistent with the hypothesis that the factor responsible for mycotoxin degradation in the supernatant of strain XSWW9 is a protein.

The Effect of Temperature and pH on AFB1 Degradation by the Cell-Free Supernatant of B. cereus XSSW9
The degradation rate of AFB1 increased as the incubation temperature increased from 20 °C to 37 °C. However, when the incubation temperature reached 50 °C, the degradation rate of AFB1 showed a significant decrease (Figure 4a). These results are consistent with the hypothesis that the factor responsible for mycotoxin degradation in the supernatant of strain XSWW9 is a protein.  The time profile of AFB1 degradation due to the cell-free supernatant was also recorded. Most of the degradation occurred within 48 h, and the degradation rate decreased as the AFB1 concentration fell (Figure 4c).

Degradation of AFB1 by the Cell-Free Supernatant of XSSW9 during Grain Fermentation
To verify AFB1's removal ability in actual production, external AFB1 was added to the zaopei without measurable mycotoxin content to a final concentration of 20 μg/kg, and the normal baijiu production fermenter was set as a blank control. In order to assess the representative degradation rate of AFB1 in the grains, three different height grains were  The time profile of AFB 1 degradation due to the cell-free supernatant was also recorded. Most of the degradation occurred within 48 h, and the degradation rate decreased as the AFB 1 concentration fell (Figure 4c).

Degradation of AFB 1 by the Cell-Free Supernatant of XSSW9 during Grain Fermentation
To verify AFB 1 's removal ability in actual production, external AFB 1 was added to the zaopei without measurable mycotoxin content to a final concentration of 20 µg/kg, and the normal baijiu production fermenter was set as a blank control. In order to assess the representative degradation rate of AFB 1 in the grains, three different height grains were selected from the top, middle, and lower layers. Table 1 shows the content of residual AFB 1 . The AFB 1 degradation rate was close to 100% after 28 days of fermentation in the fermenter, which was significantly higher than in the cell-free supernatant, which was 87.04%. We consider two reasons for this finding. First, the actual AFB 1 content during fermentation (20 µg/kg) was much lower than that of the cell-free supernatant (1 mg/kg). Moreover, it is likely that the nutrients in the actual production were richer, so cell activity was maintained longer and reached a higher total biomass. At the same time, the upper limit of AFB 1 degradation in actual production and the controllable degree of actual system contamination needs to be further explored. Note: It can be concluded that AFB 1 has been completely degraded in the sample when the content of AFB 1 in the sample is less than 0.1 µg/kg.

Dynamics of Microbial AFB 1 Degradation during Grain Fermentation
Dynamics within the grain microbial consortium during AFB 1 degradation were determined using 16S rRNA sequencing. AFB1 and XSWW9 were added to the grain fermentation (FG-T), while normal grain fermentation without AFB1 and XSWW9 was used as control (FG-C). Fermented grains with 20 µg/kg AFB 1 were tested at four timepoints-0 d (initial fermented grains), 7 d (rapid warming period of wine lees), 14 d (lees stabilization stage), and 28 d (pre-wine making). After quality filtering and assignment, a total of 74,933, 40,129, 31,902, and 35,589 OTUs were generated at each timepoint. Similarly, the data for the control group included 81,557, 36,832, 39,406, and 31,799 OTUs. Figure 5 shows the microbial consortium composition and the eleven most abundant bacterial phyla in the different fermented grains based on the OTU assignments. In the fermentation process of baijiu, the primary micro-organisms are bacteria and actinomycetes, and bacteria play a major role in aroma production. Most of the Bacillus species have high proteinase activity and are functional bacteria in the Maillard reaction in baijiu. Weissella and Acinetobacter are functional bacteria that metabolize ethanol and catalyze ester production during fermentation. In addition, most strains of Weissella can  The initial control grain samples (0 d) presented the major genera Weissella (59.48%), Acinetobacter (12.15%), Enterobacter (145%), and Lactococcus (8.21%). Other classes comprising more than 0.10% included Kosakonia (0.34%), Cronobacter (4.15%), Leuconostoc (0.26%), Lactobacillus (2.90%), and Enterococcus (2.88%) (Figure 5a). At the same time, the initial grain samples (0 d) contained the major genera Weissella (58.81%), Acinetobacter (4.41%), Enterobacter (14.99%), and Lactococcus (7.34%). Five other classes comprised more than 0.10%, including Kosakonia (0.41%), Cronobacter (4.10%), Leuconostoc (0.89%), Lactobacillus (1.86%), and Enterococcus (2.86%) (Figure 5b). There was no significant difference between the two major strains and their percentages. The principal component analysis (PCA) of microbial fractions in the fermentation process showed that FG-C and FG-T could be divided into four main components, and there were significant differences in the microbial fractions of the same fermentations at different times, while the differences in the microbial fractions of FG-C and FG-T at the same period were not significant (Figure 5c).
In both the control and experimental groups, Weissella was predominant during the first seven days of fermentation, but after 14 days of fermentation, the content of Weissella decreased significantly, while the content of Acinetobacter increased rapidly and gradually became the dominant strain in solid-state fermentation. It is worth noting that the richness and diversity of prokaryotes in the zaopei did not change significantly when fortified bacterial liquid was added. This observation is also consistent with the observation that the aroma compounds of the baijiu produced by the two fermentations were not significantly different ( Figure 6). These results indicated that the traditional fermentation process is largely unaffected when the added strains are derived from the daqu.
In the fermentation process of baijiu, the primary micro-organisms are bacteria and actinomycetes, and bacteria play a major role in aroma production. Most of the Bacillus species have high proteinase activity and are functional bacteria in the Maillard reaction in baijiu. Weissella and Acinetobacter are functional bacteria that metabolize ethanol and catalyze ester production during fermentation. In addition, most strains of Weissella can grow on methanol as the only carbon source, which is helpful to reduce the methanol content in baijiu.

Analysis of Volatile Aroma Compounds during AFB 1 Degradation in Grain Fermentation
The aroma compounds in liquor distillated from different fermentations were identified to assess the influence of zaopei bioaugmentation on the volatile profiles of fresh liquor. In the experimental group, 164 volatile compounds were detected, including 58 esters, 23 alcohols, 8 acids, 20 aldehydes, 11 ketones, 3 furans, 5 phenols, and 37 other compounds. Similarly, a total of 169 volatile substances were detected in the blank control, including 60 esters, 23 alcohols, 8 acids, 21 aldehydes, 11 ketones, 3 furans, 6 phenols, and 37 other compounds (Figure 6a,b). The alcohol meter measured 50.7% vol for the experimental group and 51.4% vol for the control group. This also corresponds to the content of ethanol in the GC-MS profiles of both groups.
The flavor characteristics of baijiu are mainly determined by esters, alcohols, aldehydes, ketones, and other volatile compounds. Therefore, we analyzed major volatile compounds in the two groups of baijiu, including ethyl acetate, butyrate, butyl acetate, isobutanol, isoamyl acetate, n-butanol, isoamyl alcohol, ethyl n-hexanoate, ethyl lactate, ethyl caprylate, 1-octen-3-ol, isoamyl lactate, ethyl caprate, phenylacetaldehyde, diethyl succinate, phenethyl acetate, phenethyl alcohol, and ethyl 9-oxononanoate (Figure 6c). Overall, no significant differences in flavor compounds were observed in the two groups of baijiu. As shown in Figure 6, in the experimental group, the largest family of volatile flavors was esters, followed by acids, alcohols, and a small number of ketones, aromatics, and aldehydes. Likewise, the control liquor presented high contents of these six flavor groups. These results indicated that the difference in the content of the main volatile compounds between the two types of baijiu was very small and almost negligible. We can therefore conclude that the addition of the cell-free supernatant of the experimental strain during the baijiu solid-state fermentation process resulted in the degradation of AFB 1 in the grains of baijiu. As shown in Figure 6, in the experimental group, the largest family of vo flavors was esters, followed by acids, alcohols, and a small number of ketones, arom and aldehydes. Likewise, the control liquor presented high contents of these six f groups. These results indicated that the difference in the content of the main volatile pounds between the two types of baijiu was very small and almost negligible. W therefore conclude that the addition of the cell-free supernatant of the experimental s during the baijiu solid-state fermentation process resulted in the degradation of AF the grains without affecting the flavor and taste of the baijiu. This conclusion is also i with our expectations.

Conclusions
We screened a strain of Bacillus cereus with a stable degradation ability of AFB1 strong aromatic daqu, and the strain showed very high tolerance to high concentra of AFB1. The strain was blended with normal zaopei for bioaugmentation, and the

Conclusions
We screened a strain of Bacillus cereus with a stable degradation ability of AFB 1 from strong aromatic daqu, and the strain showed very high tolerance to high concentrations of AFB 1 . The strain was blended with normal zaopei for bioaugmentation, and the solid-state fermentation process was analyzed using GC-MS. We found that the strain could efficiently degrade AFB 1 without affecting the microbial community of zaopei or the aroma profile of baijiu. Thus, the bioaugmentation of zaopei can further improve the safety factor during the fermentation of the grains without affecting the quality of baijiu. In conclusion, we provide a new approach for the degradation of AFB 1 potentially present in baijiu zaopei. The role of this strain in other foods and feeds needs to be further investigated.

Chemicals and Culture Media
AFB 1 was purchased from Macklin (Shanghai Macklin Biochemical Technology Co., Shanghai, China).
NB medium was measured in g/L and contained 10 peptones, 3 beef extract powders, and 5 NaCl. The pH was adjusted to 7.4.
Fermentation medium was measured in g/L and contained 10 peptones, 3 beef extract powders, 8.5 NaCl, 1 KH 2 PO 4 , and 1 glucose. The pH was adjusted to 7.0.

Preparation of Daqu Micro-Organism Suspensions
Daqu from a traditional production facility was used as the microbial source. Five grams of daqu material were taken and transferred into 100 mL of sterile water, homogenized with glass beads, shaken for 2 h at 37 • C, and dispersed well to obtain a suspension.

Enrichment and Isolation of Degrading Micro-Organism
Coumarin was used as the sole carbon source to enrich the microbes which can degrade AFB 1 , according to a previously described method [46]. The daqu micro-organism suspensions were seeded into 100 mL of NB medium at 10% inoculum in 250 mL flasks and incubated under static conditions at 37 • C for 3 d. For the first transfer, the culture was transferred into 150 mL of enrichment medium (with a final concentration of coumarin 1.0 g/L) at 10% inoculum in a 250 mL flask at 37 • C and 160 rpm for 3 d. The transfer was conducted repeatedly with gradually increasing concentrations of coumarin for the enrichment cultivation.
After the last enrichment, the culture was serially diluted, 100 µL of diluted solution was spread on an isolation agar medium each time, and then it was cultured at 37 • C for 5 d. The selected colonies were picked repeatedly from the isolation agar plates until apparent purity was reached.

Culture of Micro-Organisms
The selected strain from the isolation agar plates was grown in a fermentation medium at 37 • C for 24 h with shaking at 160 rpm to obtain the fermentation broth.

Degradation Test of AFB 1 by B. cereus XSSW9
A sample comprising of 800 µL of fermentation (including alternatively cell-free supernatant, washed cells, and cell extract) was combined with 200 µL of AFB 1 methanol solution (5 mg/L) in a 5 mL EP tube, followed by incubation at 37 • C and 160 rpm for 72 h in the dark. Finally, the residual AFB 1 concentration was determined.

Detection of AFB 1 Concentration
AFB 1 was extracted from the degradation test sample with an equal volume chloroform three times and evaporated under nitrogen gas. The samples were dissolved in a methanolwater solution (1:1, v/v) and filtered. Then, the concentration of AFB 1 was analyzed using HPLC-FLD on a Shimadzu lc-40 Series instrument (Shimadzu, Nanjing, China) equipped with a fluorescence detector. The chromatographic column was a Venusil MP C18 (5.0 µm, 250 mm × 4.6 mm, 5 µm), and it was kept at 40 • C. The mobile phase was methanol:H 2 O (1:1, v/v) with a flow rate of 1.0 mL/min, and the injection volume was 10 µL. The excitation and detection wavelength were set to 360 and 440 nm, respectively. The degradation ratio was calculated according to the following formula: degradation ratio = (1 − AFB 1 peak area following treatment/AFB 1 peak area in initial sample) × 100%.

Identification of the AFB 1 Degrading Strain
The selected potential strain was identified using 16S rDNA sequence analysis. The 16S rDNA was amplified by PCR using the universal primers 27F (5 -AGAGTTTGATCCTGGCT CAG-3 ) and 1492R (5 -TACGGCTACCTTGTTACGACTT-3 ). The sequencing was conducted by Shanghai Majorbio Bio-pharm Technology Co., Ltd. (Shanghai, China). Then, the sequence was compared with known sequences in the GenBank database using the Basic Local Alignment Search Tool (BLAST) program (http://blast.ncbi.nlm.nih.gov, accessed on 27 November 2021). After multiple sequence alignments were performed using CLUSTAL_X 2.1, a phylogenetic tree was constructed using MEGA 11.0.10.

Preparation of Cell-Free Supernatant, Cell Supernatant, and Cell Extracts of B. cereus XSSW9
After activation in a sterilized fermentation medium, the strain was transplanted into 100 mL of fresh fermentation medium in a 250 mL flask and incubated under dynamic conditions at 37 • C and 160 rpm for 48 h. After centrifugation at 12,000 g for 10 min, the 20 mL cell-free supernatant and cells were collected.
The cells were washed twice and re-suspended in an equal volume of 50 mM Phosphate buffered saline (PBS) (PH6.4) to prepare the cell supernatant.
The cells were disintegrated using an ultrasonic cell disintegrator (Nanjing Xian'ou Instrument Manufacturing Co., Nanjing, China). After centrifugation at 12,000 g for 10 min at 4 • C, the supernatant was filtered using 0.22 µm syringe filters (Tianjin Keyilon Experimental Equipment Co., Tianjin, China) to produce the cell extracts.
The effect of the protease treatment was determined by exposing the cell-free supernatant and cell extract to 1 g/L protease K (Shanghai Aladdin Biochemical Technology Co., Ltd, Shanghai, China). for 1 h at 37 • C or 1 g/L protease K plus 1% SDS for 6 h at 37 • C [47]. To determine the effect of temperature, the reaction mixture was incubated in the dark at 20, 25, 28, 30, and 37 • C for 72 h.
In the pH tests, initial pH values of the reaction mixture were adjusted to 4.0, 5.0, 6.0, 7.0, 8.0, 9.0, 10.0, and 11.0 with relevant sodium phosphate buffers. The filtrated fermentation medium was adjusted to different pH values and used as a control.

Grain Fermentation (Baijiu Brewing)
A sample comprising 10 kg of sorghum was broken into 4-8 petals, and a weighed sample of 8 kg was suspended in hot water above 85 • C, which corresponded to a moisture content of 58-62%. After 24 h of wetting, the grain was treated with retort steam for 0-60 min, after which 30 vol % of 80-90 • C hot water was added, spread, and left to cool to 25 • C. Then, 10% of daqu, 200 µg of AFB 1 , and 20 mL of cell-free supernatant of XSWW9 were added, mixed well, placed into a fermentation barrel, sealed with film, and fermented for 28 days. The grain fermentation with the added AFB 1 and XSWW9 was used to test the AFB 1 -degrading ability of XSSW9 during the liquor brewing process, and the samples were named FG-T. The normal grain fermentation without AFB 1 and XSWW9 was used as a control named FG-C. After 28 days, the grains were distilled in three fractions, and the middle fraction of high-quality baijiu was used for analysis.

Determination of Volatile Compounds
Headspace solid-phase microextraction gas chromatography-mass spectrometry (HS-SPME-GC-MS) was used to determine the volatile compounds [40]. Samples comprising of 200 µL of the liquor were placed into a 10 mL headspace vial with 3 mL of saturated NaCl, 10 µL of internal standard (2-octanol, 0.0822 g/L, Sigma-Aldrich, St. Louis, MO, USA), and a magnetic rotor. They were then placed in a constant temperature water bath with a magnetic stirrer for mixing at 60 • C for 50 min. At the same time, a 50/30 µm DVB/CAR/PDMS fiber (Supelco, Bellefonte, PA, USA) was used to extract the volatile compounds for 45 min at 60 • C. Then, the vial was placed in a thermostatic block stirrer to equilibrate for 10 min at 50 • C and subsequently extracted for 45 min with stirring at 500 rpm. After extraction, the SPME fiber was withdrawn into the needle and immediately inserted into the injection port of the Thermo Fisher Scientific GC-MS(GC/MS-QP2020., Shimadzu Corporation, Kyoto, Japan) system, which was coupled with a trace TR-WAX fused silica capillary column (30 m × 0.25 mm i.d; 0.25 µm film thickness; the inlet temperature was 250 • C; there was no splitting; the column temperature profile was 40 • C and was maintained for 5 min; then, it was ramped up to 230 • C at 5 • C/min and maintained for 5 min; a high purity helium was the carrier gas at a flow rate of 1 mL/min; the connection port temperature was 250 • C; the ionization mode was EI; the electron energy was 70 eV; the ion source temperature was 230 • C; and the scan range was 40-450 amu). The mass spectra of the sample analytes were compared with the standard spectra. The data were processed using Xcalibur™ software (Thermo Fisher Scientific, Waltham, MA, USA). The component content was calculated using the peak area normalization method, and the final compound mass concentration was expressed as the mean ± standard deviation.

Statistical Analysis
All assays were conducted in triplicate unless otherwise specified. Data are presented as the means ± the standard deviations (SD). A Student's t-test was used to perform the statistical analysis. Statistical significance was accepted at a p value < 0.05.