Falandysz Jerzy, Fernandes Alwyn R, Kilanowicz Anna, Eun Heesoo
Department of Toxicology, Faculty of Pharmacy, Medical University of Lodz, Poland.
School of Environmental Sciences, University of East Anglia, United Kingdom.
Rocz Panstw Zakl Hig. 2025 Jun 26;76(1):7-28. doi: 10.32394/rpzh/203700. Epub 2025 May 21.
The accelerating global use of lanthanides in modern consumer goods has introduced a new source of environmental pollution and potential health hazards. Evaluating risk for human exposure to these rare earth elements (REE) is hampered by limited occurrence data in foods, partly because reliable, sensitive and accurate determination is challenging. An objective of this work was to critically review lanthanide occurrence in fruiting bodies (mushrooms) of edible wild terrestrial (epigeic) and subterranean (hypogeic) macrofungi and their soil substrates, while also assessing the reported data for analytical quality. Given the paucity of information, all available literature on lanthanides in wild mushrooms was considered. Key requirements for credible REE determination in fungal biomass include avoiding cross contamination from substrates, exclusion of spectral/non-spectral interferences through robust purification and selective, sensitive measurement procedures, inclusion of the full range of lanthanides and strict quality control. In general, both high and lower resolution ICP-MS techniques were evidentially able to provide more reliable outcomes if these requirements were followed. A second objective was to propose a rational approach to assess data reliability by combining the above methodological attributes with the characteristics of lanthanide occurrence in mushrooms: (i) adherence to Oddo-Harkins order, visualised as a descending sawtooth pattern - a result of unfractionated uptake and accumulation of lanthanides from soils and other substrates (ii) typical individual concentration ratios (e.g., La/Sm, Ce/Nd, Ce/Sm) that indicate reliable determination, (iii) bio-exclusion of lanthanides by wild fungi (bioconcentration factors < 1). Data from studies that met these requirements confirmed typically low concentrations (0.07 μg kg-1 of Lu in to 940 μg kg-1 of Ce in ) with patterns corresponding to Oddo-Harkins order across reported fungal types, maintaining the unfractionated REE substrate patterns. However, given the upward trend in REE usage, the continued monitoring of macrofungi is prudent.
镧系元素在现代消费品中的全球使用加速,带来了新的环境污染源和潜在健康危害。评估人类接触这些稀土元素(REE)的风险受到食品中相关存在数据有限的阻碍,部分原因是可靠、灵敏且准确的测定具有挑战性。这项工作的一个目标是严格审查镧系元素在可食用野生陆生(表生)和地下(内生)大型真菌子实体(蘑菇)及其土壤基质中的存在情况,同时评估所报告数据的分析质量。鉴于信息匮乏,考虑了所有关于野生蘑菇中镧系元素的现有文献。在真菌生物质中进行可靠的REE测定的关键要求包括避免来自基质的交叉污染,通过强大的纯化以及选择性、灵敏的测量程序排除光谱/非光谱干扰,涵盖所有镧系元素范围以及严格的质量控制。一般来说,如果遵循这些要求,高分辨率和低分辨率的电感耦合等离子体质谱技术显然都能够提供更可靠的结果。第二个目标是提出一种合理的方法,通过将上述方法学属性与蘑菇中镧系元素存在的特征相结合来评估数据可靠性:(i)遵循奥多 - 哈金斯顺序,表现为下降的锯齿状模式——这是从土壤和其他基质中未分馏吸收和积累镧系元素的结果;(ii)典型的个体浓度比(例如,La/Sm、Ce/Nd、Ce/Sm)表明测定可靠;(iii)野生真菌对镧系元素的生物排除(生物富集因子<1)。符合这些要求的研究数据证实,所报道的真菌类型中浓度通常较低(从钇的0.07μg/kg到铈的940μg/kg),且模式与奥多 - 哈金斯顺序相对应,保持了未分馏的REE基质模式。然而,鉴于REE使用量的上升趋势,对大型真菌进行持续监测是明智的。