1. Introduction
Dried and fresh chili peppers (
Capsicum annuum L.) hold significant prominence within the culinary, agricultural, and medicinal sectors in China, where they contribute not only to dietary diversity but also to national economic development. Their production and utilization enhance local cuisine while supporting extensive agricultural activities and food-processing industries [
1,
2]. As the world’s largest producer of fresh chili peppers, China has established a robust agricultural infrastructure for cultivating this crop, achieving an annual yield of over 18 million tons [
2]. Moreover, chili pepper cultivation plays a vital role in rural revitalization initiatives, providing farmers with profitable opportunities and strengthening regional economies [
1]. The distinction between dried and fresh chili peppers further reflects their cultural and culinary significance across China. Fresh peppers are integral to traditional dishes such as hot pots, where their characteristic flavor profiles and varying pungency levels contribute to gastronomic richness [
3]. Their spiciness results primarily from capsaicinoids, especially capsaicin and dihydrocapsaicin, which impart both pungency and notable medicinal properties [
4,
5].
The cultivation of chili peppers across China mirrors the country’s diverse agro-ecological landscape and showcases the remarkable adaptability of this crop under evolving climatic conditions [
2]. Distinct climatic zones enable the production of region-specific pepper varieties, such as those from Sichuan and Yunnan, which are deeply embedded in local cuisines and cultural identity [
6]. These geographical and climatic differences shape plant physiology, flavor development, and resilience to environmental stressors, while also influencing disease prevalence and pathogen behavior. Environmental factors, including elevated humidity, high temperatures, and substantial rainfall, play crucial roles in determining the incidence of fungal pathogens and the accumulation of associated mycotoxins [
7,
8]. Chili peppers grown in high-humidity regions are particularly susceptible to fungal invasion, highlighting the influence of climate-driven ecological pressures on contamination risk [
9].
Within this broader agricultural context, chili pepper is recognized as a commercially important crop that is highly vulnerable to fungal colonization and subsequent mycotoxin production. Fungal infections can occur throughout the entire production chain—from field growth and harvest to drying, processing, and storage—making chili peppers susceptible at multiple critical points [
10,
11]. Improper postharvest handling practices, such as insufficient drying or extended storage under humid conditions, further exacerbate the risk of fungal proliferation and toxin accumulation [
12]. Processed chili products, such as crushed or powdered red pepper, are even more susceptible to contamination than whole fruits, particularly under suboptimal storage conditions with elevated moisture levels [
13,
14,
15].
Mycotoxins, harmful secondary metabolites produced primarily by filamentous fungi, represent a major global food-safety challenge due to their presence in a wide range of agricultural commodities. These toxins pose severe risks to human and animal health and contribute to significant economic losses worldwide [
16,
17,
18,
19,
20,
21]. The principal toxigenic genera associated with food contamination include
Aspergillus,
Fusarium, and
Penicillium, alongside lesser contributors such as
Alternaria and
Cladosporium, all of which synthesize diverse toxins under favorable environmental conditions [
22,
23,
24,
25]. Although more than 300 mycotoxins have been identified, only a subset, including aflatoxins, trichothecenes, zearalenone, fumonisins, ochratoxins, and patulin, are considered highly hazardous due to their potent toxicity and frequent occurrence in food systems [
18,
26]. The health risks posed by these toxins are severe and well-documented. Aflatoxin B
1 (AFB
1) is a potent hepatocarcinogen, classified by the International Agency for Research on Cancer as a Group 1 human carcinogen, with its frequent occurrence in spices representing a major global food safety burden [
27]. Ochratoxin A (OTA), commonly detected in dried commodities, is a nephrotoxin and a possible human carcinogen (IARC Group 2B), with chronic exposure linked to kidney disease in humans [
28]. Furthermore, co-exposure to AFB
1 and fumonisin B
1 (FB
1) has been shown to induce synergistic hepatotoxic and carcinogenic effects in animal models, suggesting that co-contamination may pose a significantly greater risk to human health than exposure to either toxin alone [
29,
30]. These contaminants readily enter the food chain either directly through mold-infected crops or indirectly via animal-derived products containing toxin residues or metabolites [
31,
32,
33]. Major foodborne mycotoxin classes include trichothecenes—such as deoxynivalenol (DON) and T-2 toxins; aflatoxins (AFB
1, AFB
2, AFG
1, and AFG
2); ochratoxins (OTA and OTB); zearalenone (ZEN); fumonisins (FB
1, FB
2, and FB
3); patulin (PAT); and citrinin (CIT). More recently, emerging mycotoxins, including Alternaria toxins (AOH, AME, TeA, TEN, and ALT), enniatins (ENNA, ENNA1, ENNB, and ENNB1), and beauvericin (BEA), have gained attention due to their rising prevalence and uncertain toxicological profiles [
34].
A significant challenge In modern mycotoxin research is the widespread co-occurrence of multiple toxins within the same commodity. Multi-mycotoxin contamination is now recognized as a critical food-safety issue because such toxins frequently coexist, may display additive or synergistic effects, and often withstand degradation during conventional food processing [
35]. This is a particularly high risk in spices such as chilies. Market monitoring data indicates a high susceptibility potential, as
Capsicum-containing products are frequently among the most contaminated species worldwide, especially in hot climates [
36]. Critically, contamination is often multifaceted. A significant number of co-contaminated products are also reported in studies specifically conducted on chili-based or chili-containing products. For example, studies on fresh sweet peppers and resulting products showed that many samples were contaminated with several toxigenic fungi (
Aspergillus,
Fusarium, and
Alternaria) and their associated mycotoxins, such as aflatoxins and ochratoxin A [
37]. Such widespread co-occurrence makes routine exposure combinatorial and creates complexities in risk assessment.
Their co-occurrence has been documented in cereals, medicinal plants, chili-based products, and animal feed, leading to cumulative health risks for both humans and livestock [
35,
38]. Therefore, understanding interactions among co-occurring mycotoxins and accurately assessing their combined toxicity is essential for effective risk evaluation and public health protection [
39,
40,
41]. Owing to suboptimal drying and storage, dried chilies and spices are high-risk commodities. A targeted monitoring study in Myanmar found that 56.1% of dried chili samples exceeded the EU limit for aflatoxins, and ochratoxin A was detected in 91% of the samples [
42]. In Italian sweet pepper, there was multiplex mycotoxin contamination, with 100% of the samples containing between 2 and 16 mycotoxins, including OTA (51% occurrence) and aflatoxins (31% occurrence), highlighting serious problems in drying and processing [
37]. Dried chili peppers are among the most vulnerable to multi-mycotoxin contamination. Market surveys based on scientific research demonstrate widespread co-occurrence of aflatoxins, ochratoxin A, and sterigmatocystin, with a large proportion of samples exceeding the EU maximum limits for aflatoxin B
1 (5 µg/kg) and total aflatoxins (10 µg/kg), especially in processed products such as powder and flakes [
43].
To address the limited understanding of how fungal diversity and mycotoxin contamination interact across chili pepper products, this study undertakes a comprehensive assessment of toxigenic fungi associated with fresh and dried chili peppers in Guangzhou. By integrating morphological characterization, multilocus molecular identification, and LC–MS/MS–based toxin profiling, the research aims to characterize species-specific toxigenic potential, elucidate patterns of co-contamination among multiple mycotoxins, and compare contamination risks between fresh and dried peppers. The study aims to assess substrate-dependent production of fumonisin B1 by selected Fusarium species on PDA and citrinin production by Penicillium on CYA and YES media, thereby providing further insight into the influence of growth conditions on toxin biosynthesis and contributing to a more nuanced understanding of potential food-safety risks. This study represents the first comprehensive integration of multilocus phylogeny and quantitative multi-mycotoxin assessment for retail chili peppers in southern China.
4. Discussion
The present study provides one of the most detailed assessments to date of fungal diversity and multi-mycotoxin contamination in both fresh and dried chili peppers produced and marketed in Guangzhou, southern China. It should be emphasized that the fungal isolation, in vitro mycotoxin production assays, and quantification of mycotoxins in chili samples were conducted as independent studies. Thus, no causative linkage between strain and sample was assumed, nor was a molecular or quantitative relation between certain fungal isolates and the content of one or several mycotoxins in the corresponding chili samples demonstrated. Consequently, the inferences drawn are associations, not causality. The results demonstrate that chili peppers function as highly conducive substrates for a wide array of toxigenic fungi, particularly species of
Fusarium and
Penicillium. While
F. concentricum,
F. fujikuroi,
F. sulawesiense,
F. commune, and
F. verticillioides have been previously documented on chili peppers [
7,
102,
103,
104], this study reports seven species for the first time globally on this host:
F. annulatum,
F. compactum,
F. pernambucanum,
F. ramsdenii,
F. tardichlamydosporum,
P. citrinum, and
P. steckii. This expanded diversity, including
F. annulatum,
F. commune,
F. compactum,
F. concententricum,
F. fujikuroi,
F. pernambucanum,
F. ramsdenii,
F. sulawesiense,
F. tardichlamydosporum,
F. verticillioides,
P. citrinum, and
P. steckii, underscores the high diversity of fungal communities colonizing chili peppers in this region. These observations align with global evidence that
Capsicum fruits, like many horticultural commodities, are predisposed to colonization by multiple pathogenic and spoilage fungi along the farm-to-market continuum [
23,
105,
106]. We selected 23 strains for targeted mycotoxin production tests based on their taxonomic relevance (species with known FB
1 or CIT potential) and on their frequency of isolation (the most common from symptomatic samples). This targeted approach introduces selection bias that may overestimate the prevalence of toxigenic strains, but it efficiently assesses the toxigenic capacity of the species most relevant to observed contamination patterns. In addition, toxigenic potential varied across species and culture conditions, with certain
Fusarium isolates capable of producing FB
1 on PDA. In contrast,
Penicillium species, especially
P. citrinum and
P. steckii, exhibited clear citrinin production on both CYA and YES media, indicating that the type of substrate plays an important role in regulating mycotoxin biosynthesis and, consequently, potential food safety risks. It is important to emphasize that while in vitro toxicity, particularly FB
1 production by
Fusarium species and CIT by
Penicillium species on PDA, YES, and CYA aligns with mycotoxin profiles in chili samples, this establishes biological plausibility, not causality. Linking specific isolates to contamination would require targeted molecular approaches (e.g., qPCR of biosynthetic genes), which we acknowledge as a future research direction.
A major finding from this study is the high frequency of multi-mycotoxin contamination, in which DON, AFB
1, OTA, FB
1, ZEN, and citrinin were detected simultaneously in both fresh and dried peppers. Such co-contamination implies a diverse fungal microbiome and no single-species attack. Also, in sweet peppers, paprika, and other spices, the occurrence of overlapping toxins has been reported in earlier work, produced simultaneously by toxigenic
Fusarium and
Penicillium species, and both toxins could be found together in a food [
106,
107]. This emphasizes the need for analysis using multi-toxin screening systems, since single-mycotoxin risk assessment underestimates the combined and synergistic risks inherent in mixed toxicity [
35]. Toxic interactions among mycotoxins are not well understood at low chronic doses present in the daily diet [
108].
The dominance of
Fusarium species in fresh chili pepper samples corresponds with their ecology as highly aggressive plant pathogens that can invade crop tissues at different stages of crop development.
Fusarium infections on
Capsicum plants are reported to cause severe symptoms and wilting, leaf yellowing, and fruit rot with vascular discoloration, resulting in a serious reduction of yield as well as marketable fruit [
109,
110]. Especially worrisome are species such as
F. verticillioides and
F. fujikuroi, which are known to produce fumonisins and other mycotoxins associated with cancer, immunotoxicity, and gastrointestinal toxicity [
111,
112,
113]. The universal detection of DON in all isolates from both fresh and dried peppers further emphasizes the metabolic flexibility of trichothecene-producing
Fusarium species, which are known to synthesize these toxins early during host colonization [
114]. Earlier research in China revealed significant
Fusarium contamination in sweet peppers [
7], supporting the trends observed here, given the agronomic and ecological similarities between sweet and chili pepper cultivars. A unique challenge posed by
Fusarium species is their ability to produce multiple mycotoxins simultaneously, often within the same substrate. This study contributes to the growing evidence that
Fusarium can co-produce an array of compounds—including fumonisins, trichothecenes, moniliformin, beauvericin, zearalenone, and [
115,
116]—leading to complex contamination patterns that complicate detection and risk management. Even at trace levels, these toxins can exert significant toxic effects, and their concurrent presence is increasingly recognized as a major limitation to traditional mycotoxin control strategies [
117,
118].
Penicillium species, in contrast, were more abundant in dried chili peppers—consistent with their ability to thrive under low-water-activity storage conditions.
P. citrinum, the dominant species identified, is a well-established producer of citrinin, a nephrotoxin implicated in renal impairment and oxidative damage [
119,
120]. Improper drying of chili peppers creates microenvironments with elevated humidity, facilitating
Penicillium colonization and citrinin production [
121]. This pattern is consistent with surveys in India, Korea, and Europe, where Penicillium was consistently identified as a major colonizer of stored peppers and paprika products [
106,
122,
123]. The higher contamination levels in dried peppers reinforce the importance of controlled drying and storage, especially in regions where sun-drying remains a primary postharvest method.
Multiple recent studies consistently indicate that multi-mycotoxin contamination and co-occurrence are widespread across food and feed commodities, and advances in analytical technologies have considerably improved the detection of these complex toxin mixtures. Mohammedi-Ameur et al. [
124] reported the simultaneous presence of major mycotoxins—including aflatoxins (AFs), OTA, DON, and fumonisins (FBs)—alongside emerging mycotoxins in large-scale commodity surveys, indicating that single-toxin surveillance substantially underestimates real exposure. Similarly, Annunziata et al. [
125] observed that a high proportion of feed samples contained two or more regulated mycotoxins, with frequent co-occurrence of DON + FBs and AFB
1 + FB
1 in the same samples. Expanding this global perspective, Gruber-Dorninger et al. [
126] documented that more than 90% of aquaculture feeds and plant-based feed ingredients were contaminated with at least one mycotoxin and that co-contamination involving multiple toxin classes was highly prevalent. Region-specific cereal surveys by Penagos-Tabares et al. [
127] highlighted concerning non-compliance rates for aflatoxins and fumonisins in maize harvests from 2021 to 2024, with pronounced effects of climate variability and contamination patterns across harvest years. In support of these findings, pan-regional analyses by Freitag et al. [
128] showed that annual weather fluctuations considerably influence multi-mycotoxin occurrence profiles, with drought years showing particularly high co-occurrence of aflatoxins and fumonisins, thereby complicating risk prediction models. Concurrently, method development studies by El-Khatib et al. [
41] and Giannioti et al. [
129] have expanded LC–MS/MS multi-analyte platforms to detect dozens of regulated and emerging mycotoxins, demonstrating that complex mixtures of regulated, masked, and emerging toxins are routinely present in single samples. The toxicological relevance of these mixtures has been reinforced by experimental studies, with Ochieng et al. [
130] reporting that combined exposure to AFB
1 and FB
1 produces more severe adverse health effects in animal models than exposure to toxins alone and that mitigation strategies targeting only one toxin often leave other contaminants unaddressed. Furthermore, regional monitoring and exposure assessment studies by Sabillón et al. [
131] and Nešić et al. [
40] have quantified human and animal co-exposures and emphasized the analytical and regulatory challenges posed by masked and emerging mycotoxins.
Comparable contamination patterns have been widely reported in dried fruits, which frequently harbor multiple mycotoxins at significant concentrations. In Turkish dried figs, Heperkan et al. [
132] identified the co-occurrence of OTA (0.1–15.3 ng/g), fumonisin B
1 (FB
1) (0.05–3.65 µg/g), and aflatoxins (0.1–763.2 ng/g) within the same samples. A subsequent LC–MS/MS investigation by Sulyok et al. [
133] revealed extremely high levels of OTA (up to 11,400 µg/kg), tenuazonic acid (TeA) (18–299,000 µg/kg), and FB
1 (13–1430 µg/kg) in individual Turkish fig samples. In China, Wei et al. [
134] analyzed 220 dried fruit samples—including raisins, dried apricots, dates, and wolfberries—and reported frequent occurrence of
Alternaria toxins such as TeA, tentoxin (TEN), and mycophenolic acid (MPA), with 31.4% of samples containing two to four toxins simultaneously. In Egyptian dried dates, Abdallah et al. [
135] detected OTA levels as high as 6070 µg/kg alongside FB
2 (16.2 µg/kg) and AFB
1 (14.4 µg/kg) in the same samples. Similarly, Galván-Romero et al. (2022) [
136] observed the co-detection of AFB
1 (up to 75 µg/kg) and OTA (up to 50 µg/kg) at different stages of the dried fig value chain in Spain. A comprehensive review by Gilbert and Senyuva [
137] further confirmed that dried figs frequently contain multiple mycotoxins simultaneously, including AFB
1, AFB
2, AFG
1, AFG
2, OTA, fumonisin B
2, and kojic acid, with contamination levels varying widely depending on geographical origin and processing methods.
DON was detected in both fresh and dried peppers; however, higher levels were found in dried samples, possibly reflecting its stability and the early onset of its biosynthesis during initial tissue invasion. The robustness of DON under varying environmental conditions has been reported previously and is linked to the physiology of trichothecene-producing
Fusarium species [
111,
114]. The detection of fumonisin B
1 and zearalenone in fresh samples suggests that toxin accumulation may begin in the field and continue postharvest if environmental conditions remain favorable. Similar observations were made in sweet peppers from China, where preharvest
Fusarium infections were identified as the main source of mycotoxin contamination [
7].
Citrinin production by
Penicillium in this study was considerably influenced by the culture medium, with both
P. citrinum and
P. steckii producing higher levels of citrinin on YES than on CYA, suggesting that nutrient composition plays a critical role in regulating secondary metabolite biosynthesis. These findings are consistent with earlier reports indicating that citrinin production varies widely among
Penicillium species and depends on growth conditions, with Bragulat et al. [
138] reporting citrinin production in
P. expansum,
P. citrinum, and
P. verrucosum on both CYA and YES. In contrast, no production was detected in numerous
Aspergillus species. The strong toxigenic capacity of
P. citrinum has also been highlighted through rapid screening methods, including coconut cream agar, which confirmed its reliability as a citrinin producer [
139]. The higher citrinin yields observed on YES in the present study may be largely attributed to the high sucrose content of this medium, which provides an easily metabolizable carbon source that enhances fungal growth and stimulates the polyketide biosynthetic pathway responsible for citrinin formation. This observation is further supported by Davis et al. [
140], who documented maximum citrinin production on sucrose- and yeast extract–rich media. In contrast, comparatively lower production has been reported on potato-based media for several fungi [
141]. Overall, these findings indicate that carbon source availability, particularly sucrose, influences citrinin biosynthesis and may contribute to the risk of toxin accumulation under nutrient-rich conditions.
The results of the present study showed that PDA supported only low-level FB
1 production by the tested
Fusarium species, with
Fusarium verticillioides being the most potent producer. In contrast,
F. annulatum showed much lower levels, and other species produced only trace or non-detectable amounts, suggesting that PDA is not a highly favorable substrate for strong FB
1 biosynthesis. This observation is consistent with previous findings that culture medium composition considerably influences mycotoxin production, as shown for citrinin, where Mohamed et al. [
139] reported efficient detection on Coconut Cream Agar after 4–5 days of incubation, demonstrating the importance of substrate specificity for toxin expression, while Davis et al. [
140] recorded very high citrinin yields (up to 1.75 g/L) on a sucrose–yeast extract medium, indicating that rich carbon–nitrogen sources greatly enhance toxin synthesis. In contrast, Gu et al. [
141] reported that potato dextrose medium yielded the lowest citrinin production among several tested media for
Monascus anka. However, measurable toxin levels were still detected, which closely parallels the present findings, where PDA supported only limited FB
1 production by
Fusarium spp. Thereby, these findings suggest that PDA is suitable for screening and comparative evaluation of toxigenic potential. Still, it does not promote high mycotoxin yields, and substrate optimization is essential for maximizing toxin production in laboratory studies.
Environmental conditions appear to be important factors associated with fungal colonization and mycotoxin biosynthesis in chili peppers, with high ambient humidity, elevated temperatures, and inconsistent drying practices likely enhancing fungal proliferation and toxin accumulation [
110,
142]. Traditional sun-drying, which is widely practiced in rural production systems, may inadvertently increase mycotoxin risks when peppers are exposed for prolonged periods under fluctuating moisture conditions [
106,
143]. Our findings show that dried peppers contained higher levels of AFB
1, OTA, FB
1, ZEN, and citrinin than fresh peppers. Aflatoxin B
1 and ochratoxin A, which are primarily produced by species of
Aspergillus and
Penicillium, are known to be synthesized optimally under fluctuating humidity conditions during drying and storage, providing a plausible explanation for their greater occurrence in dried samples [
16,
144]. In addition to fungal presence, factors such as the drying environment, plant physiology, and substrate composition may influence mycotoxin biosynthesis [
19,
145,
146], and high humidity during drying can further facilitate both fungal growth and secondary metabolite production. These observations highlight the importance of controlled dehydration systems, in which temperature and relative humidity can be tightly regulated to inhibit microbial proliferation, and reinforce the concept that each stage of processing—fresh handling, drying, and storage—imposes distinct but interconnected risk factors that must be addressed through stage-specific mitigation strategies [
147].
Chili peppers represent a clear example of how agricultural production, fungal ecology, and food-safety risks converge, as indicated by the present study, which revealed a complex fungal community dominated by toxigenic
Fusarium and
Penicillium species in both fresh and dried peppers marketed in Guangzhou, China. The widespread detection of multiple mycotoxins indicates that chili peppers are highly susceptible to contamination throughout the production and marketing chain. The frequent co-occurrence of multiple mycotoxins, in some cases exceeding international safety limits, indicates potential public health concerns and suggests additive or synergistic toxic effects. These findings emphasize the critical role of postharvest handling, particularly efficient drying and proper storage, in lowering fungal activity and suppressing toxin accumulation. Moreover, the detection of emerging and previously underreported
Fusarium species suggests that shifting environmental and market conditions may be reshaping fungal populations on chili peppers, reinforcing the need for continuous surveillance and integrated management approaches. Although this study focused on
Fusarium and
Penicillium.
Aspergillus species the main producers of AFB
1 and OTA, were likely present in the samples but were not successfully identified due to methodological limitations or unfavorable isolation conditions. They were recorded collectively under other genera’ (11% of isolates). Numerous studies have documented toxigenic
Aspergillus in chili peppers worldwide [
8,
10,
42,
148], and their presence during drying and storage explains the detection of these toxins.
This section compares the mycotoxin concentrations and prevalence observed in fresh and dried chili peppers from the present study with data reported in other relevant literature (
Table 14). A prominent finding in our study was that dried chili samples had 2- to 10-fold higher levels of toxins than fresh ones. Our results offer a broader spectrum of contamination than previously described: DON, AFB
1, OTA, and FB
1 were detected at 100% in dried samples; however, previous reports have reported different patterns of contamination.
Venkatachalapathi et al. [
148], who conducted the first preharvest study in India found 48% of fresh red chili samples contaminated with AFs (AFB
1: 0.4–20 µg/kg) and observed differences among various agro-ecological zones. Su et al. [
149] observed a 100% AFs contamination rate in dried red chili pepper, but the levels were many times lower (≤7.19 µg/kg). San Phyo et al. [
42] have also reported AFs (97%) and OTA (91%) in dried chili from Myanmar, with values ranging from 0.25 to 72.8 µg/kg for AFs and between 1.7−139 µg/kg for OTA as levels of contamination; out of them, the percentage (56.1%) exceeds the EU limits on maximum levels for aflatoxins. Akintola et al. [
150] detected AFB
1 in 100% of dried chili products (pods, flakes and powder) from Oman at levels up to 19.4 ppb with 34% of powder samples above the threshold value of 10 ppb. Chen et al. [
152] found OTA in dried red chilies from China at levels of up to 54.12 µg/kg (peel) and 36.67 µg/kg (seed), with 22.5–34.7% exceeding the EU limit of 20 µg/kg. The amount of AFB
1 (ND–39. 12 µg/kg), OTA (ND–39. 79 µg/kg), and ZEN (ND–11. 16 µg/kg). In red pepper imported from Turkey, a number of the samples exceeded the limits established by the Turkish Food Codex. Lasram et al. [
154] detected AFB
1 in 90% and AOT in 80% of red chili powder samples from Tunisia (AFB
1: 0.1 ranging from to 27.1 µg/kg; OTA: ranged from 0.5 to 35.2 µg/kg). Iqbal et al. [
155] also reported AFB
1 (up to 11.7 µg/kg) and OTA (30.4 µg/kg) in red chili sauce from Pakistan, with 44.8% samples exceeding EU limits for AFB
1 and 23% of the samples surpassing EU levels for OTA. Pickova et al. [
9] analyzed paprika samples from the Czech Republic, 35% of which contained OTA, and AFs were detected in 10%, all being below EU maximum limits.
Importantly, the mean estimated DON concentration found in our study was highest (0.56 ± 0.51 µg/g; maximum 1.74 µg/g), and data on this mycotoxin in chili matrices have rarely been reported and analyzed in previous work, indicating a critical control point during the drying process.
In fresh analyzed samples, the contamination profile was significantly different: CIT predominated with the prevalence of 100% at a low level (0.019 ± 0.009 µg/g), whereas OTA was completely absent. In contrast to the studies by Lasram et al. [
154] and San Phyo et al. [
42], who observed OTA in 80–91% of dried chili products, indicating that OTA contamination occurs mainly during post-harvest processing and drying rather than at the field level.
Dry matrices were favorable for achieving good reproducibility (lower RSDs), and fresh samples exhibited issues, particularly when considering the strong matrix effect on CIT (ME = 88.3%) and low recovery of AFB
1 (43.29%), which suggest that analytical methods must be optimized according to matrix contamination for moist samples. Such matrix effects are very seldom reported in the literature, where most studies refer only to dried products (cf.
Table 11 and
Table 12). This is the first report on a systematic comparison of mycotoxin contamination between fresh and dried chili using validated analytical methods optimized for both matrices.
Levels of aflatoxin B
1 (AFB
1) in dried chili samples were as high as 180 µg/kg, which is 36-fold greater than the EU maximum tolerance level for
Capsicum spices (5 µg/kg). The concentrations of ochratoxin A (OTA) also reached 54 µg/kg, which was about 2.7-fold greater than the EU limit (20 µg/kg). These results depict an appreciable level of exceedance of regulatory limits for targeted mycotoxins in dried chili pepper [
42,
156]. Such high levels of AFB
1 and OTA may pose public health concerns and underscore the pressing need for enhanced post-harvest management techniques, storage conditions, and ongoing surveillance programs to meet international food safety guidelines.
Ultimately, our findings highlight the importance of stringent control over post-harvest processes to mitigate mycotoxin contamination in the final product. It is noteworthy that this approach entails several methodological limitations. The first limitation of the proposed approach is that fungal isolation, in vitro toxin production, and mycotoxin quantification were performed independently; hence, no direct strain-to-sample linkage was established. Some Fusarium and Penicillium isolates exhibited toxigenic potential in culture media; however, this observation does not prove that they were responsible for contamination of the original samples. Future work is crucial to adopt qPCR or ddPCR targeting biosynthetic genes (e.g., fum1 and pksCT) to correlate fungal biomass with toxin concentrations in the sample. The second limitation is that isotopically labeled internal standards were not utilized in LC-MS/MS quantification due to budget constraints. Stable isotope dilution assays remain the widespread gold standard for offsetting matrix effects, even though matrix-matched calibration has been fully validated in accordance with SANTE/EC and AOAC guidelines. This constraint was evident in fresh original samples (as received), where higher matrix effects (88.3% for CIT and 43.29% for AFB1) were observed. As such, future work also needs to include isotope-labeled internal standards for enhanced accuracy in complex matrices. The third limitation stems from a lack of monitoring of environmental parameters (e.g., temperature, relative humidity, and water activity) during drying and storage. These climatic factors influence fungal proliferation and toxin biosynthesis, and their lack of monitoring limits the predictive power of modeling. Real-time environmental and climate monitoring aspects must be integrated into prospective studies. We anticipate that addressing these limitations will reinforce risk assessment and post-harvest mitigation strategies.