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Approximately 1,000 species of mushrooms are estimated to be poisonous worldwide (1). As many as 480 poisonous mushroom species have been reported in China (2). However, foraging, trading, and consuming wild mushrooms is a tradition in China. Poisonous and edible mushrooms with highly similar morphologies often grow in the same wild habitats, increasing the risk of accidental ingestion. Following a suspected poisoning, collecting and effectively detecting and identifying residual mushroom specimens or human biological samples (blood, urine, vomit, gastric lavage, etc.) during epidemiological investigations is crucial for diagnosis and treatment.
Between 2012 and 2023, the “Public Health Emergency Reporting and Management Information System” of the China CDC documented 653 mushroom poisoning incidents, including 3,229 poisoning cases and 710 deaths, which accounted for 21.87% (653/2,986) of reported foodborne poisoning incidents, 4.33% (3,229/74,586) of the poisonings, and 54.20% (710/1,310) of foodborne poisoning deaths. The fatality rate was 21.99% (710/3,229). From 2012 to 2020, the fatality rate showed minor fluctuations, peaked in 2020, and decreased significantly after 2022. Among all incidents, 551 (84.38%) lacked laboratory evidence of mushroom species identification, with causation determined through epidemiological investigation and clinical manifestations of poisoning. Detection and identification of poisonous mushrooms were conducted in 102 incidents (15.62%); however, 10 of these lacked test and identification results in their final reports, leaving 92 incidents (14.08% of total cases) with complete toxicological test or identification results.
Between 2012 and 2023, detection and identification results of poisonous mushroom incidents were available for all years except 2014. The number of mushroom poisoning incidents with detection and identification results was lowest in 2013 with only 1 incident, and highest in 2017, accounting for 22.83% (21/92) (Figure 1). A total of 13 provincial-level administrative divisions (PLADs) participated in detection and identification, with the top 5 PLADs by number of detection incidents being Hunan, Yunnan, Guangdong, Sichuan, and Guizhou, reporting 25 (27.17%), 22 (23.91%), 17 (18.48%), 9 (9.78%), and 6 (6.52%) incidents, respectively. Additionally, Guangxi and Fujian PLADs each reported 3 incidents with detection and identification results; Zhejiang PLAD reported 2; and Chongqing, Shandong, Hubei, Hebei, and Hainan PLADs reported 1 for each.
Figure 1.The years and PLADs distribution of detection and identification for mushroom poisoning reported incidents in China, 2012–2023.
Abbreviation: PLAD=provincial-level administrative division.The departments involved in the detection and identification of mushroom poisoning incidents were CDCs, universities, multi-department collaborations (including public security and agriculture), scientific research institutes, and hospitals, with composition ratios of 63.04%, 16.30%, 9.78%, 6.52%, and 4.35%, respectively. The detection methods included morphological identification, molecular biology detection, toxin detection, acute toxicity tests on animals, and combinations of these methods. Morphological identification, including that of high-definition photographs, was the most common (3), accounting for 60.87% of mushroom poisoning incidents with detection and identification results. This was followed by molecular biology detection and toxin detection, accounting for 13.04% and 11.96%, respectively (Table 1).
Detection methods Number of incidents Proportion (%) Morphological identification 31 33.70 Morphological identification of mushroom’s photograph 25 27.17 Molecular biology detection 12 13.04 Toxin detection 11 11.96 Morphological identification and toxin detection 4 4.35 Morphological identification and molecular biology detection 3 3.26 Toxin detection and molecular biology detection 2 2.17 Acute toxicity tests on animals 2 2.17 Morphological identification of mushroom’s photograph and toxin detection 1 1.09 Morphological identification of mushroom’s photograph and acute toxicity tests on animals 1 1.09 Total 92 100.00 Table 1. Distribution of toxicant detection methods with identification results from 2012 to 2023.
The distribution of detection and identification methods varied among the top 5 PLADs. In Hunan, 22 (88.00%), 2 (8.00%), and 1 (4.00%) incidents were identified by morphological identification, methods with two detection types, and acute toxicity tests on animals, respectively. In Yunnan, the numbers of incidents identified by morphological identification, toxin detection, molecular biology detection, and methods with two detection types were 8 (36.36%), 6 (27.27%), 4 (18.18%), and 4 (18.18%), respectively. In Guangdong, the numbers identified by morphological identification, methods with two detection types, and toxin detection were 10 (58.82%), 4 (23.53%), and 3 (17.65%), respectively. In Sichuan, the numbers identified by morphological identification and molecular biology tests were 5 (55.56%) and 4 (44.44%), respectively. In Guizhou, the numbers identified by morphological identification, molecular biology detection, and methods with two detection types were 3 (50.00%), 2 (33.33%), and 1 (16.67%), respectively.
Among the 92 mushroom poisoning incidents that reported toxicological detection and identification results (4–5), the most frequent incidents and poisonings involved acute liver failure, rhabdomyolysis, gastroenteritis, psycho-neurological disorders, and acute renal failure. Acute liver failure caused the most deaths, accounting for 55.17% (64/116) of all clinical types of mushroom poisoning. Twenty-five species were involved in the 92 mushroom poisoning incidents. Amanita exitialis and Russula subnigricans were responsible for the most incidents, both of which accounted for 17.39% (16/92) of all species. Amanita exitialis is the most prevalent type of mushroom with acute liver failure. The number of poisonings and the deaths attributed to A.exitialis accounted for 13.32% (55/413) and 16.38% (19/116) of all identified mushroom poisonings, respectively. Amanita fuliginea caused the largest number of deaths, accounting for 18.10%(21/116) (Table 2).
Clinical classifications Mushroom (or toxin) species Number of incidents Number of patients Deaths Fatality (%) Acute liver failure 41 162 64 39.51 Amanita exitialis 16 55 19 34.55 Amanita fuliginea 13 50 21 42.00 Amanita rimosa 4 13 6 46.15 Anmanita fuligineoides 2 18 8 44.44 Amanita sp. 2 5 3 60.00 Anmanita subpallidorosea 1 8 4 50.00 Galerina autumnalis 1 6 1 16.67 Galerina sp. 1 4 1 25.00 Galerina sulciceps 1 3 1 33.33 Rhabdomyolysis 16 52 20 38.46 Russula subnigricans 16 52 20 38.46 Gastroenteritis 9 44 4 9.09 Chlorophyllum molybdites 3 9 1 11.11 Russula japonica 2 17 0 0.00 Scleroderma 1 9 2 22.22 Chlorophyllum globosum 1 5 0 0.00 Russula laurocerasi 1 2 1 50.00 Scleroderma cepa 1 2 0 0.00 Psycho-neurological disorder 7 33 4 12.12 Amanita subglobosa 3 17 2 11.76 Amanita subfrostiana 1 7 1 14.29 Amanita parvipantherina 1 3 1 33.33 Amanita sychnopyramis 1 3 0 0.00 Gymnopilus dilepis 1 3 0 0.00 Acute renal failure 2 25 4 16.00 Amanita pseudoporphyria 2 25 4 16.00 Psycho-neurological disorder
and acute renal failure1 2 1 50.00 Amanita oberwinklerana and
Psathyrella candolleana1 2 1 50.00 Mixed class 3 21 3 14.29 More than 2 clinical types 3 21 3 14.29 Amatoxins 11 67 12 17.91 Unclassified 2 7 4 57.14 Unknown species that
causes animal death2 7 4 57.14 Total 92 413 116 28.09 Table 2. Distribution of species in poisonous mushroom incidents with poison detection and identification results from 2012 to 2023.
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