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Review

A Review of the Occurrence of Alpha-Emitting Radionuclides in Wild Mushrooms

by
Dagmara Strumińska-Parulska
1,* and
Jerzy Falandysz
2,3,†
1
Toxicology and Radiation Protection Laboratory, Faculty of Chemistry, University of Gdańsk, 80-308 Gdańsk, Poland
2
Environmental Chemistry & Ecotoxicology Laboratory, Faculty of Chemistry, University of Gdańsk, 80-308 Gdańsk, Poland
3
Environmental and Computational Chemistry Group, School of Pharmaceutical Sciences, Zaragocilla Campus, University of Cartagena, Cartagena 130015, Colombia
*
Author to whom correspondence should be addressed.
†
Jerzy Falandysz is visiting professor at affiliation 3.
Int. J. Environ. Res. Public Health 2020, 17(21), 8220; https://doi.org/10.3390/ijerph17218220
Submission received: 22 September 2020 / Revised: 1 November 2020 / Accepted: 3 November 2020 / Published: 6 November 2020
(This article belongs to the Special Issue Environment–Macromycetes (Fungi)–Edible Fungi)
Versions Notes

Abstract

:
Alpha-emitting radioisotopes are the most toxic among all radionuclides. In particular, medium to long-lived isotopes of the heavier metals are of the greatest concern to human health and radiological safety. This review focuses on the most common alpha-emitting radionuclides of natural and anthropogenic origin in wild mushrooms from around the world. Mushrooms bio-accumulate a range of mineral ionic constituents and radioactive elements to different extents, and are therefore considered as suitable bio-indicators of environmental pollution. The available literature indicates that the natural radionuclide 210Po is accumulated at the highest levels (up to 22 kBq/kg dry weight (dw) in wild mushrooms from Finland), while among synthetic nuclides, the highest levels of up to 53.8 Bq/kg dw of 239+240Pu were reported in Ukrainian mushrooms. The capacity to retain the activity of individual nuclides varies between mushrooms, which is of particular interest for edible species that are consumed either locally or, in some cases, also traded on an international scale. The effective radiation dose from the ingestion of this food can reportedly range from 0.033 µSv/kg dw to 26.8 mSv/kg and varies depending on the country. Following pollution events, such consumption may expose consumers to highly radiotoxic decay particles produced by alpha emitters.

1. Introduction

Mushrooms are a highly biodiverse group of organisms, a part of the traditional gastronomic heritage of the world, and also an important source of nutrients for small and large wildlife [1]. Some mushrooms are seen as having healing properties and, above all, many, when well-prepared, have a delicious taste [2]. Mushrooms typically grow in forests and fields, but almost all ecosystems will support their growth in the proper substrate medium [3]. These fruiting bodies of fungi are relatively rich in minerals and trace metals (including radionuclides) on a dry weight (dw) basis [4,5,6].
Although the phenomenon of radioactivity was discovered over 100 years ago, the special significance recorded in the pages of radiochemistry and nuclear chemistry history was realized from the 1940s to the 1960s [7,8,9]. The development and use of nuclear energy and the testing of nuclear weapons have in the past created a flux of released artificial radiation emitters that have been deposited in various environmental and food compartments, undergone biogeochemical cycles, and thus necessitate the need for control and surveillance measures [9,10,11,12]. In particular, nuclear weapons testing has led to massive contamination of nuclear test sites [13], and atmospheric detonations (1945–1980) and major accidents at nuclear power plants (i.e., Chernobyl in 1986 and Fukushima in 2011) have resulted in a substantial spread of radioactive isotopes all over the world. To some extent, emissions can also arise from current human activities such as mining, coal burning, and oil and gas exploration [14,15,16,17,18,19,20]. A range of edible mushrooms, including species foraged from the wild, are efficient bio-accumulators of various radioactive contaminants [21,22,23,24,25,26].
Most of the studies on radioactivity in edible mushrooms reported so far have been dedicated to the activity concentration of less hazardous gamma emitters (electromagnetic radiation), such as the artificial nuclides 134/137Cs, and the natural nuclide, 40K [3,23,27,28,29,30,31,32]. From a radio-toxicological point of view, the nuclides of the greatest importance are medium- and long-lived alpha-radioactive isotopes. Alpha decay (α-decay) is a form of decay where an atomic nucleus produces an alpha particle and changes into a different atomic nucleus. An alpha particle equals the 4He nucleus, containing two protons and two neutrons. Alpha particles have energy from 2 (147Sm) to 8.8 MeV (212Po), with a median of 5 MeV and a velocity of about 15,000 km/s. Because of their rather large mass and low speed, alpha particles interact with other atoms. The high mass and charge of alpha particles, in relation to other forms of nuclear radiation, give them greater ionizing power, but the penetration depth is much smaller [30]. Every significant alpha emitter present in the environment belongs to Group A (highly toxic radioisotopes) [33]. Thus, the ingestion of an alpha emitter and the resulting exposure to the internal organs of humans or animals could be of high concern when the source is contaminated food or feed [34,35]. At present, 210Po is judged as one of the most hazardous radionuclides. It is 10,000 times more toxic than hydrogen cyanide, and alongside the botulinum toxin, it is one of the most toxic substances ever known [36]. The use of 210Po as a poison to kill Alexander Litvinenko in 2006 increased interest in the radio-toxicological properties of this radioisotope as well as its occurrence in the environment and bioaccumulation in food products [37].
The analysis of alpha-emitting nuclides in mushrooms, foods and other biological materials is very laborious, highly time-consuming, and expensive, because of the complicated analytical procedures that are required for low or ultralow physical occurrence and the required sensitivity of detection, selectivity and accuracy of analytical equipment [38]. In consequence, the amount of information available on the occurrence of alpha emitters in environmental matrices including mushrooms is much lower in comparison to other radionuclides and especially, as mentioned, the gamma emitters.
The aim of this review is to present an overview on the occurrence and bio-concentration of alpha radioactivity in mushrooms worldwide along with consideration of the health aspects for human consumers.

2. Alpha Emitters in Mushrooms

Analytical data on the occurrence of the alpha emitters (210Po, 222Rn, 226Ra, 228Th, 230Th, 232Th, 234U, 235U, 236U, 238U, 238Pu, 239Pu, 240Pu, 241Am) in mushrooms were collected from the available literature (49 papers and reports) and are systematically presented in Table 1 and Table 2. In a few cases, the collected literature data on the radioactivity concentration were converted (using a consensus value of 10% dry matter relative to fresh mushrooms) with the aim of normalization, comparability and presentation of the results based on a dry weight (dw). Unlike certain other nutritional elements, alpha-emitting radionuclides are not essential for fungi, but they are absorbed by the mycelium, bio-accumulated in the fruiting bodies (mushrooms) and cycled in the food webs which extend to animals and humans. The risk from low-level radiation is still unknown and is based on the linear hypothesis which has been in operation that demonstrated that the relationships between hazard and radiation dose at high levels of exposure also apply to low levels [33,39]. Baeza et al. analyzed 239+240Pu, 234,238U, 228,230,232Th, and 226Ra bioaccumulation and distribution in a series of cultures of the species Pleurotus eryngii under controlled laboratory conditions. During the growth period, 226Ra was located in the gills of the cap, while 239+240Pu, 234,238U, and 228,230,232Th were observed mostly in the remaining part of the cap [40]. However, there are no studies on inter-species differences in alpha-emitters accumulation in cultivated mushrooms under controlled conditions.

2.1. Naturally Occurring Radioisotopes in Mushrooms

Natural radiation includes permanent low-level cosmic radiation and the radiation arising from the decay of naturally occurring radionuclides, namely the primordial radioactive elements in the crust of the Earth and their radioactive decay products (natural radioactive decay chains). Thus, human exposure to radiation has always been an unavoidable effect of the ubiquitous distribution of natural radioactivity [41]. Cosmogenic radionuclides (i.e., 3H, 14C) are produced constantly by a bombardment of stable nuclides by cosmic rays, principally in the atmosphere. The origin of the primordial natural radionuclides of the Earth (i.e., 40K, 87Rb, 235U, 238U, 232Th) is connected to the phenomenon of nucleosynthesis in stars, and their half-lives are longer or comparable with the age of the Earth. The secondary natural radioactive elements found in the environment are directly joined to the very long half-lives of the parents of these chains: the uranium (parent nuclide 238U), thorium (parent nuclide 232Th), and actinium (parent nuclide 235U) decay chains [42].
Technologically enhanced naturally occurring radioactive materials (TENORM) consist of materials including, usually, industrial wastes or by-products enriched with radioactive elements found in the environment, such as uranium (U), thorium (Th), and potassium (K) and any of their decay products, such as radium (Ra) and radon (Rn), polonium (Po) and radiolead (Pb) [14,43,44,45,46]. The presence of nuclides in mushrooms and plant-based foods depends on the geological structure of the lithosphere, the agronomic condition of arable soils, and the climate [47,48]. In general, higher activity concentrations of radionuclides have been measured in Ramsar (Iran), Kerala and Madras (India), Yangjiang (China), Pakistan, Brazil and Sudan, in high natural radioactivity background areas or impacted by TENORM [15,47,49,50,51,52,53].
Activity concentrations of naturally occurring radionuclides accumulated in mushrooms worldwide vary over a wide range—about eight orders of magnitude (Table 1). The highest activity concentration among all the mushrooms studied so far has been reported for polonium 210Po (T1/2 = 138.4 days) that appears at the end of the decay chain of uranium 238U and is an interesting natural element to investigate due to its radioecology (high bioconcentration factor) and one of the highest radiotoxic characteristics [48,54]. 210Po enters the biosphere through various routes of terrestrial and marine radio-ecological pathways. The major source of contamination of flora and fauna with 210Po basically comes from contaminated soil or through aerosol-associated fallout from the atmosphere [48,55,56]. 210Po is more easily accumulated by mushrooms and has higher bioconcentration factors when compared to other alpha emitters [57]. The increase in polonium concentration in mushrooms may also be related to the chemical similarities with sulfur or selenium elements [58]. Polonium is an element from the oxygen family, together with sulfur, selenium and tellurium—so called chalcogen elements. The susceptibility of fungi to higher accumulation of 210Po than other alpha emitters could be explained in part by the type and quantity of sulfur (S) ligands that they produce, but this has not been studied so far. Mushrooms differ in their contents of sulfur, which is a major chemical element in mushrooms as well as the main element in ligands for, e.g., Hg or Se. The type and quantity of sulfur ligands associated with 210Po that bio-accumulate in mushrooms is a species-specific feature that is dependent on environmental conditions related to the soil bedrock background composition as well as anthropogenic pollution, as in the case of several other metallic elements [54].
The highest activity concentrations of 210Po have been reported in mushrooms from Scandinavia [23,59,60] and in mushrooms growing close to a uranium mine in Germany [61], while the lowest levels are seen in collections from Poland and New Zealand [57,62,63,64,65,66] (Table 1). The authors Guillén and Baeza (2014) noted that the pattern distribution of 210Po seemed to be species-dependent [67], but a comparison of inter-genus data shows that the most important aspects are local conditions, e.g., natural radioactivity, atmospheric fallout, geological conditions, etc. [20,23,57,59,61,63].
Radium, 226Ra (T1/2 = 1600 years), along with 210Po, belongs to the natural series of 238U [48]. The highest 226Ra activity concentrations have been reported in mushrooms collected in the vicinity of uranium mines or places with a higher natural uranium background [61,68,69]. The variation of 226Ra occurrence in mushrooms is substantially lower in the areas not affected by higher 210Po and 226Ra backgrounds [61,70,71,72,73,74,75,76,77,78,79] (Table 1).
The uptake of thorium (228Th T1/2 = 1.91 years; 230Th T1/2 = 7.54 × 104 years; 232Th T1/2 = 1.4 × 1010 years) by mushrooms, as well as uranium (238U T1/2 = 4.47 × 109 years; 235U T1/2 = 7.04 × 108 years; 234U T1/2 = 2.45 × 105 years) [80,81] is lower than that of 210Po and 226Ra (Table 1), and this can be related to low bio-concentration factors for Th and U, regardless of their abundance in soil [4,5,82]. However, significant differences between uranium and thorium activity concentrations have been reported. In the case of thorium, the highest activity concentrations of 228Th and 232Th have been noticed in Brazil, with the lowest in Poland [73,76,78,83,84,85,86,87,88,89,90,91]. In the case of uranium, the highest activity concentrations of the alpha emitters 234U, 235U and 238U have been reported in mushrooms from Germany, Turkey, Finland, and Slovakia [60,61,86,88,90], with the lowest being in Poland, Serbia, Bosnia and Herzegovina as well as China (Yunnan) and New Zealand [58,62,70,71,78,83,84,89,91,92,93,94,95]. If the uranium activity is compared to its daughter nuclide, 226Ra, the maximum radium activity concentration is always higher than the activity of the parent (238U). This might suggest that they are not in equilibrium in mushrooms. The increase in radium activity concentration might be due to the chemical similarities with calcium, in much the same way as polonium is physically and chemically an analog of the chalcogen elements (group 16 of the periodic table) [58,67,96]. However, the reported data have shown that mushrooms may bioaccumulate 234U and 238U more effectively than 230Th and 232Th, while both elements (U and Th) were bio-excluded (bioaccumulation factor values in the range from 0.005 to 0.19) [86,89,91].

2.2. Anthropogenic (Artificial, Man-Made) Radioisotopes in Mushrooms

Anthropogenic radioactive contamination of the environment became a reality on 16 July 1945, when the first fission weapon was tested near the town of Alamogordo (New Mexico, USA). Nuclear weapon testing and accidents in civil installations have led to massive artificial (man-made) radioactive pollution that has been spread all over the world. Since 1945, at least eight nations have detonated 2047 nuclear devices, with between 423 and 520 being carried out in the atmosphere [19]. The production of plutonium and other transuranic isotopes has been estimated at 0.33 PBq of 238Pu, 7.8 PBq of 239Pu, 5.2 PBq of 240Pu, 170 PBq of 241Pu, 0.00037 PBq of 241Am, and 0.00026 PBq of 244Cm. In Europe, the nuclear accident at the Chernobyl Nuclear Power Plant caused the biggest radiation pollution event in the history of nuclear energy [101,102]. The incident released 20 kg of plutonium (0.025 PBq of 238Pu, 0.055 PBq of 239,240Pu, 5 PBq of 241Pu), 0.006 PBq of 241Am, and 0.006 PBq of 243,244Cm [9,103,104,105]. The most recent nuclear accident, namely at the Fukushima Daiichi nuclear power plant (NPP) was estimated to be 15 times smaller than that at Chernobyl [102]. It has released about 2.4–19 GBq of 238Pu, 0.41–3.2 GBq of 239Pu, 0.51–3.2 GBq of 240Pu and 9.8–100 GBq of 242Cm [106]. Since 2015, the atmospheric releases from the Fukushima Daiichi NPP have continued, but at very low levels which were not of radiological concern [106]. Thus, the medium- and long-lived radioactive isotopes and especially the alpha-isotopes (such as 238Pu, 239Pu, 240Pu, 241Am, 243,244Cm, 237Np) are of the greatest importance from the point of view of human health and functioning of ecosystems, as they are radioactive and toxic metals, and hazardous environmental pollutants [54,107].
Also activity concentrations of artificial radionuclides accumulated in mushrooms worldwide vary over a wide range (Table 2), but their reported range of contamination of mushrooms is smaller when compared to natural radioisotopes (Table 1 and Table 2). Nevertheless, the presence of man-made nuclides in mushrooms and plant-based foods depends on local radioactive pollution conditions (nuclear test sites, facilities, accidents and distance from these sites) and is influenced by global atmospheric fallout [9,12,108,109]. Due to analytical difficulties, very few studies have dealt with anthropogenic alpha emitters released into the environment, and have instead focused on the most common radioactive elements, namely plutonium and americium, as well as uranium 236U [83,84,85,86,92,108,110,111,112,113,114,115,116,117,118].
There is only one article on 236U (T1/2 = 2.34 × 107 years) activity concentration in mushrooms [92], which is an activation product of 235U or a decay product of 240Pu. Its presence has been reported due to work on depleted uranium dispersion and pollution in the environment of the Balkan region as a result of the Balkan (Kosovo) War in 1999. The 236U activity concentrations in mushrooms determined by Jia et al. 2004 [92] ranged from 0.014 to 0.038 Bq/kg dw (Table 2). Among the four major plutonium isotopes, three are alpha emitters: 238Pu (T1/2 = 87.7 years), the fissile and the most important isotope, 239Pu (T1/2 = 24,110 years), as well as 240Pu, which is produced via neutron capture of 239Pu (T1/2 = 6564 years) [107]. Plutonium is not effectively accumulated by mushrooms and shows a similar distribution in fruiting bodies to that of thorium and uranium (stem > cap > gills) [40]. Baeza et al. studied 239+240Pu accumulation in the saprophytic fungus Pleurotus eryngii cultivated under laboratory conditions and its occurrence in wild-growing mycorrhizal mushroom species (Tricholoma equestre), and concluded that its distribution seemed to be species-dependent, but were not able to confirm whether saprophytic fungi presented a lower content of this radionuclide than mycorrhizal fungi, as was observed in the case of 137Cs [40,115]. The highest activity concentrations of Pu isotopes have been determined in mushrooms collected at sites in the Ukraine that were associated with indirect contamination from the Chernobyl incident fallout in 1986 [83,108,112]. Mushrooms of various species foraged elsewhere in Europe were affected by both sources—namely, the global atmospheric fallout from earlier weapons testing and the incident at Chernobyl [84,85,86,110,111,112,113,114,116,117,118] (Table 2).
The element americium may originate from global atmospheric fallout connected to nuclear weapon testing or as a decay product of its parent nuclide, 241Pu, which was identified in Chernobyl fallout [103]. So far, its presence has been measured and reported only in mushrooms sampled in European countries such as Finland, Slovakia, Spain and the UK, and the activity concentrations were the lowest of all the alpha emitters, i.e., in the range from 0.003 to 1.01 Bq/kg dw [86,113,114,115,116,117,118] (Table 2).
Radioactive elements, especially alpha emitters, are not essential metals for biota. Due to their occurrence in the environment, they are bio-accumulated along with essential micronutrients as well as toxic elements. When compared to the essential trace elements, the activity concentrations of the alpha-emitting radionuclides in wild-growing mushrooms from unpolluted areas in this study were much lower (e.g., alpha emitters of U, Th, Ra, Rn) or lower (e.g., alpha emitters of Po, Pu, Am, or 236U) [5,91,119,120]. In some species, such as Amanita citrina, Laccaria sp., Tricholoma populinum, Strobilomyces strobilaceus, Russula exalbicans, Leccinum aurantiacum, Hebeloma sinapizans, and Cantharellus cibarius, the amounts of uranium and thorium were higher than stable lead (Pb) or silver (Ag) [4]. As mentioned, the occurrence of natural alpha-nuclides in mushrooms is related to the geochemistry of soil bedrock, agronomic activities and climate and the presence of man-made nuclides in mushrooms depends on local radioactive pollution (nuclear test sites, facilities or accidents as well as the distance from the accident sites) as well as the impact of global atmospheric fallout. If the location in which mushrooms are collected is contaminated with radioactive substances (e.g., Chernobyl or Fukushima area, nuclear test sites), the number of alpha emitters (especially transuranic, as 235U, 236U, 238U, 239Pu, 240Pu) might be higher than stable toxic trace metals, e.g., lead (Pb), mercury, (Hg) [13,47,83,113,121,122,123].

3. Risk Assessment

Humans are exposed to radiation from two types of sources: external, which includes radionuclides in the Earth and cosmic radiation, and internal radiation from radionuclides incorporated in the body. In this study, the key pathways of radionuclide intake are inhalation, and ingestion of food and water [124]. In the International System of Units (SI), the unit of ionizing radiation dose and a measurement of the biological health effect of ionizing radiation on the human body is the Sievert (Sv). If the dose is received over a very short duration, the LD50/60 is estimated at 4–5 Sv [125], so SI prefixes are frequently used: i.e., the millisievert (mSv) and microsievert (μSv). The assessment of the potential risk to human health connected to all ionizing radiation sources is phrased as the sum of all evaluated effective doses (E) from all sources (internal and external) and is mostly given in mSv per year. For exposure to the general public, the ICRP recommends that the limit should be expressed as an effective dose of 1 mSv annually [125]. An impact of the total annual effective dose on an adult from any food consumption may be presented as a dose from the mass of the food consumed (Sv/kg dw) and calculated as the function of the product of the radioisotope conversion coefficient (Sv/Bq) and its activity concentration (Bq/kg dw) in the foodstuff:
E = A × dc;
where:
  • A—activity concentration (Bq/kg dw),
  • dc—dose coefficient (conversion factor) (Sv/Bq), defined as the dose received from the unit of radioactivity intake; the ICRP conversion coefficients recommended for the ingestion of alpha emitters presented in the review in the case of adult members of the public, range from 4.5 × 10−8 Sv/Bq for 238U to 1.2 × 10−6 Sv/Bq for 210Po, with an average value of 10−7 Sv/Bq (exact values are shown in Table 1 and Table 2) [97].
The potential health hazard risk due to the consumption of mushrooms is presented in Table 1 and Table 2. These radioelements are toxic to humans, both chemically (connected to their toxic heavy metals properties; some with characteristics that are similar to the alkaline earth metal ions) and radiologically (connected to their nuclear disintegration), under certain conditions, and their toxicity varies depending on the chemical and physical forms, amounts ingested and route of exposure. If the exposure involves multiple active radioisotopes, the chemical and radiological toxicity can be additive or may potentiate in some instances [126,127,128]. However, the dose calculations for human radiological protection are very conservative and consider worst-case scenarios [29,97]. 210Po is one of the most important radionuclides to which humans are exposed [129]. 210Po, together with gaseous radon (220Rn, 222Rn), 226Ra, 210Pb, and 40K, are natural radioactive materials that deliver the highest dose to living organisms [43]. The associated radiation produces the same primary basic physicochemical effects of excitation and ionization within the biological material and differs only in the spatial distribution and intensity of these effects. At low levels of radiation, the clinical symptoms might not be observed (radiolysis and small genetic reactions: mutations, cells necrosis or apoptosis; changes in the blood, etc.) or might occur after a number of years as stochastic effects (i.e., leukemia). At much higher levels (more than 1 Sv), there are many observed (determined) symptoms depending on the magnitude of the dose: nausea and vomiting, headache, fatigue, fever, low number of white blood cells, bleeding, anemia, etc. [33,130].
Of the reported activity concentrations for mushrooms worldwide, the highest effective doses have been calculated for 210Po as a result of its high concentrations and the high value of its conversion coefficient. Thus, 210Po occurrence would be the main source of alpha radiation for mushroom consumers (0.28–26,400 µSv/kg dw) (Table 1). It is followed by 226Ra, which, at high concentrations, results in high effective doses for consumers (0.006–196 µSv/kg dw) (Table 1). The values of the annual radiation dose from thorium and uranium alpha emitters decay ingested through mushroom consumption may be much lower because these radionuclides are accumulated to a much lower extent. Although thorium radioisotopes are characterized by higher values of the conversion coefficient, the doses from their decay are comparable to uranium, because thorium is weakly accumulated (Table 1). The doses from anthropogenic alpha emitters have been significantly lower, even when mushrooms have been collected from potentially polluted areas (e.g., Ukraine) (Table 2).
The total effective dose that might be received from the reported content of naturally occurring alpha-emitters has been estimated to be in the range of 0.007 µSv/kg dw–26.7 mSv/kg dw depending on the country (Table 1). Anthropogenic radionuclides might give an effective dose from 0.026 µSv/kg dw to 44.4 µSv/kg dw (Table 2). Thus, the total effective dose from all reported sources might in be the range of 0.033 µSv/kg dw to 26.8 mSv/kg dw. As mentioned before, the recommended yearly adult dose limit is 1 mSv for the general public [97]. Depending on the origin of the wild mushroom, some specimens may be highly enriched with alpha-emitting radionuclides and the resulting effective dose may be significantly higher than permitted values. In unpolluted areas, the main source of radiation would be naturally occurring radionuclides, especially 210Po and 226Ra.

4. Conclusions

The main pathways of radionuclide exposure are ingestion of food and water and inhalation. Among food products, wild mushrooms are a possible source of radionuclides as they accumulate radioactive elements in much the same way as other metals, and various species have different retention capacities for individual radionuclides. The radioactive analogs of essential elements are effectively accumulated, i.e., 210Po and 226Ra, while other heavy radioelements (especially artificial radionuclides) are not heavily accumulated. Thus, naturally occurring radionuclides are the most abundantly occurring of all the bio-accumulated alpha emitters. Local geological conditions and potential radioactive pollution are the most important factors influencing the bioaccumulation level. Thus, depending on the origin of the mushrooms, some might be highly enriched with alpha-emitting radionuclides, and the effective dose might be significantly higher than suggested values (i.e., IAEA, ICRP). In unpolluted areas, the main source of radiation would be naturally occurring radionuclides, especially 210Po and 226Ra.

Author Contributions

The authors contributed equally to this work. All authors have read and agreed to the published version of the manuscript.

Funding

The authors would like to thank the Ministry of Sciences and Higher Education for the financial support of this work under the grant: DS/531-T030-D773-20.

Conflicts of Interest

The authors declare that they have no conflict of interest.

References

  1. Falandysz, J.; Treu, R. Fungi and environmental pollution. J. Environ. Sci. Health B 2017, 52, 147. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  2. de Oliveira, A.P.; Naozuka, J. Preliminary results on the feasibility of producing selenium-enriched pink (Pleurotus djamor) and white (Pleurotus ostreatus) oyster mushrooms: Bioaccumulation, bioaccessibility, and Se-proteins distribution. Microchem. J. 2019, 145, 1143–1150. [Google Scholar] [CrossRef]
  3. Kalač, P. Radioactivity of European Wild Growing Edible Mushrooms; Nova Science Publ.: Hauppauge, NY, USA, 2012. [Google Scholar]
  4. Borovička, J.; Kubrová, J.; Rohovec, J.; Řanda, Z.; Dunn, C.E. Uranium, thorium and rare earth elements in macrofungi: What are the genuine concentrations? Biometals 2011, 24, 837–845. [Google Scholar] [CrossRef]
  5. Falandysz, J.; Borovička, J. Macro and trace mineral constituents and radionuclides in mushrooms: Health benefits and risks. Appl. Microbiol. Biotechnol. 2013, 97, 477–501. [Google Scholar] [CrossRef] [Green Version]
  6. Jaworska, G.; Pogoń, K.; Skrzypczak, A.; Bernaś, E. Composition and antioxidant properties of wild mushrooms Boletus edulis and Xerocomus badius prepared for consumption. J. Food Sci. Technol. 2015, 52, 7944–7953. [Google Scholar] [CrossRef] [Green Version]
  7. Becquerel, H. Sur les radiations invisibles émises par les sels d’uranium. Acad. Sci. Paris 1896, 122, 689–694. [Google Scholar]
  8. Curie, P.; Curie, M. Sur une substance nouvelle radio-active contenue dans la pechblende. C. R. l’Acad. Sci. Paris 1898, 127, 175–178. [Google Scholar]
  9. Aarkrog, A. Source of Terms and Inventories of Anthropogenic Radionuclides; Environmental Science and Technology Department/Ecology Section; Riso National Laboratory: Roskilde, Denmark, 1991. [Google Scholar]
  10. Jaworowski, Z. Natural and man-made radionuclides in the global atmosphere. IAEA Bull. 1982, 24, 35–39. Available online: https://www.iaea.org/sites/default/files/24205683539.pdf (accessed on 12 August 2020).
  11. Skwarzec, B.; Strumińska, D.; Boryło, A. Bioaccumulation and distribution of plutonium in fish from Gdansk Bay. J. Environ. Radioact. 2001, 55, 167–178. [Google Scholar] [CrossRef]
  12. Ikäheimonen, T.K.; Ilus, E.; Klemola, S.; Dahlgaard, H.; Ryan, T.; Eriksson, M. Plutonium and americium in the sediments off the Thule air base, Greenland. J. Radioanal. Nucl. Chem. 2002, 252, 339–344. [Google Scholar] [CrossRef]
  13. Taira, Y.; Hayashida, N.; Brahmanandhan, G.M.; Nagayama, Y.; Yamashita, S.; Takahashi, J.; Gutevitc, A.; Kazlovsky, A.; Urazalin, M.; Takamura, N. Current concentration of artificial radionuclides and estimated radiation doses from 137Cs around the Chernobyl nuclear power plant, the Semipalatinsk nuclear testing site, and in Nagasaki. J. Radiat. Res. 2011, 52, 88–95. [Google Scholar] [CrossRef] [Green Version]
  14. Heaton, B.; Lambley, J. TENORM in the oil, gas and mineral mining industry. Appl. Radiat. Isot. 1995, 46, 577–581. [Google Scholar] [CrossRef]
  15. Paschoa, A.S.; Godoy, J.M. The areas of high natural radioactivity and TENORM wastes. Int. Congr. Ser. 2002, 1225, 3–8. [Google Scholar] [CrossRef]
  16. Saueia, C.H.; Mazzilli, B.P.; Favaro, D.I.T. Natural radioactivity in phosphate rock, phosphogypsum and phosphate fertilizers in Brazil. J. Radioanal. Nucl. Chem. 2005, 264, 445–448. [Google Scholar] [CrossRef]
  17. Saueia, C.H.; Mazzilli, B.P. Distribution of natural radionuclides in the production and use of phosphate fertilizers in Brazil. J. Environ. Radioact. 2006, 89, 229–239. [Google Scholar] [CrossRef] [PubMed]
  18. Szerbin, P.; Juhász, L.; Csige, I.; Várhegyi, A.; Vincze, J.; Szabó, T.; Maringer, F.-J. Tenorm’s around coal fired power plant tailings ponds in Hungary. Int. Congr. Ser. 2005, 1276, 365–366. [Google Scholar] [CrossRef]
  19. UNSCEAR—United Nations Scientific Committee on the Effects of Atomic Radiation. UNSCEAR 2000 Report, Report to the general assembly Vol. I ANNEX C Exposures to the Public from Man-Made Sources of Radiation. 2000. Available online: http://www.unscear.org/docs/reports/annexc.pdf (accessed on 12 August 2020).
  20. Strumińska-Parulska, D.; Olszewski, G. Is ecological food also radioecological?—210Po and 210Pb studies. Chemosphere 2018, 191, 190–195. [Google Scholar] [CrossRef]
  21. Cocchi, L.; Kluza, K.; Zalewska, T.; Apanel, A.; Falandysz, J. Radioactive caesium (134Cs and 137Cs) in mushrooms of the genus Boletus from the Reggio Emilia in Italy and Pomerania in Poland. Isot. Environ. Health Stud. 2017, 53, 620–627. [Google Scholar] [CrossRef]
  22. Falandysz, J.; Zhang, J.; Zalewska, T. Radioactive artificial 137Cs and natural 40K activity in 21 edible mushrooms of the genus Boletus species from SW China. Environ. Sci. Pollut. Res. 2017, 24, 8189–8199. [Google Scholar] [CrossRef] [Green Version]
  23. Gwynn, J.P.; Nalbandyan, A.; Rudolfsen, G. 210Po, 210Pb, 40K and 137Cs in edible wild berries and mushrooms and ingestion doses to man from high consumption rates of these wild foods. J. Environ. Radioact. 2013, 116, 34–41. [Google Scholar] [CrossRef]
  24. Saniewski, M.; Zalewska, T.; Krasińska, G.; Szylke, N.; Wang, Y.; Falandysz, J. 90Sr in King Bolete Boletus edulis and certain other mushrooms consumed in Europe and China. Sci. Total Environ. 2016, 543, 287–294. [Google Scholar] [CrossRef]
  25. Strumińska-Parulska, D.I.; Skwarzec, B.; Pawlukowska, M. Plutonium fractionation in southern Baltic Sea sediments. Isot. Environ. Health Stud. 2013, 48, 526–542. [Google Scholar] [CrossRef]
  26. Steinhauser, G.; Brandl, A.; Johnson, T.E. Comparison of the Chernobyl and Fukushima nuclear accidents: A review of the environmental impacts. Sci. Total Environ. 2014, 470–471, 800–817. [Google Scholar] [CrossRef] [PubMed]
  27. Rantavaara, A. Radioactivity of Vegetables and Mushrooms in Finland after the Chernobyl Accident in 1986; STUK-A59; Finnish Centre for Radiation and Nuclear Safety: Helsinki, Finland, 1987; Available online: https://inis.iaea.org/collection/NCLCollectionStore/_Public/19/001/19001484.pdf (accessed on 12 August 2020).
  28. Kalač, P. A review of edible mushroom radioactivity. Food Chem. 2001, 75, 29–35. [Google Scholar] [CrossRef]
  29. Kalač, P. Mineral Composition and Radioactivity of Edible Mushrooms; Academic Press: Oxford, UK, 2019. [Google Scholar]
  30. L’Annunziata, M.F. Radioactivity; Elsevier Science: Amsterdam, The Netherlands, 2007. [Google Scholar] [CrossRef]
  31. Daillant, O.; Boilley, D.; Josset, M.; Hettwig, B.; Fischer, H.W. Evolution of radiocaesium contamination in mushrooms and influence of treatment after collection. J. Radioanal. Nucl. Chem. 2013, 297, 437–441. [Google Scholar] [CrossRef]
  32. Falandysz, J.; Saniewski, M.; Zhang, J.; Zalewska, T.; Liu, H.-G.; Kluza, K. Artificial 137Cs and natural 40K in mushrooms from the subalpine region of the Minya Konka summit and Yunnan Province in China. Environ. Sci. Pollut. Res. 2018, 25, 615–627. [Google Scholar] [CrossRef] [Green Version]
  33. IAEA—International Atomic Energy Agency. Basic Toxicity Classification of Radionuclides; Technical Reports Series No. 15; IAEA: Vienna, Austria, 1963. [Google Scholar]
  34. Donaldson, L.; Department of Health. Information to Health Professionals Regarding the Radioactive Material ‘Polonium-210′ Resulting from a Radiological Incident Occurring in November 2006; National Health Service Central Alerting System: London, UK, 2006. [Google Scholar]
  35. Strumińska-Parulska, D.I. Determination of 210Po in calcium supplements and the possible related dose assessment to the consumers. J. Environ. Radioact. 2015, 150, 121–125. [Google Scholar] [CrossRef]
  36. Ansoborlo, E. Poisonous polonium. Nat. Chem. 2014, 6, 454. [Google Scholar] [CrossRef] [Green Version]
  37. Olszewski, G.; Szymańska, M.; Westa, M.; Moniakowska, A.; Block, K.; Strumińska-Parulska, D. On the extraction efficiency of highly radiotoxic 210Po in Polish herbal teas and possible related dose assessment. Microchem. J. 2019, 144, 431–435. [Google Scholar] [CrossRef]
  38. Lehto, J.; Hou, X. Chemistry and Analysis of Radionuclides: Laboratory Techniques and Methodology; Wiley-VCH Verlag: Weinheim, Germany, 2011. [Google Scholar]
  39. Ojovan, M.I.; Lee, W.E.; Kalmykov, S.N. An Introduction to Nuclear Waste Immobilisation; Elsevier: Amsterdam, The Netherlands, 2019. [Google Scholar] [CrossRef]
  40. Baeza, A.; Guillén, F.J.; Salas, A.; Manjon, J.L. Distribution of radionuclides in different parts of a mushroom: Influence of the degree of maturity. Sci. Total Environ. 2006, 359, 255–266. [Google Scholar] [CrossRef] [PubMed]
  41. Linsalata, P. Uranium and thorium decay series radionuclides in human and animal foodchains—A review. J. Environ. Qual. 1994, 23, 633–642. [Google Scholar] [CrossRef]
  42. Fowler, W.A. Nuclear Astrophysics; American Philosophical Society: Philadelphia, PA, USA, 1967. [Google Scholar]
  43. Bem, H. Radioaktywność w Środowisku Naturalnym; Polska Akademia Nauk. Oddział w Łodzi: Łódź, Poland, 2005. [Google Scholar]
  44. Amin, M.; Khandaker, M.U.; Shyen, A.K.S.; Mahat, R.H.; Nor, R.M.; Bradley, D.A. Radionuclide emissions from a coal-fired power plant. Appl. Radiat. Isot. 2013, 80, 109–116. [Google Scholar] [CrossRef]
  45. Hilal, M.A.; Attallah, M.F.; Mohamed, G.Y.; Fayez-Hassan, M. Evaluation of radiation hazard potential of TENORM waste from oil and natural gas production. J. Environ. Radioact. 2014, 136, 121–126. [Google Scholar] [CrossRef]
  46. AlNabhani, K.; Khan, F.; Yang, M. Management of TENORMs produced during oil and gas operation. J. Loss Prev. Proc. Ind. 2017, 47, 161–168. [Google Scholar] [CrossRef]
  47. IAEA—International Atomic Energy Agency. High levels of natural radiation. In Proceedings of the International Conference, Ramsar, Iran, 3–7 November 1990. [Google Scholar]
  48. Persson, B.R.R.; Holm, E. Polonium-210 and lead-210 in the terrestrial environment: A historical review. J. Environ. Radioact. 2011, 102, 420–429. [Google Scholar] [CrossRef]
  49. El Mrabet, R.; Abril, J.M.; Delgado, A.; Garcia-Tenorio, R.; Manjón, G.; Periáñez, R. Evaluation of the radioactive impact of the phosphogypsum wastes used as amendment in agriculture soils. Radioprotection 2005, 40 (Suppl. 1), S335–S341. [Google Scholar] [CrossRef]
  50. Giri, S.; Jha, V.N.; Singh, G.; Tripathi, R.M. Estimation of annual effective dose due to ingestion of natural radionuclides in foodstuffs and water at a proposed uranium mining site in India. Int. J. Radiat. Biol. 2013, 89, 1071–1078. [Google Scholar] [CrossRef]
  51. Arunachalam, K.D.; Baskaran, K.V.; Rao, D.D.; Sathyapriya, R.; Annamalai, S.K.; Kuruva, J.K.; Hari, S. Ingestion of Polonium (210Po) via dietary sources in high background radiation areas of south India. Int. J. Radiat. Biol. 2014, 90, 867–875. [Google Scholar] [CrossRef]
  52. Persson, B.R.R. 210Po and 210Pb in the terrestrial environment. Curr. Adv. Environ. Sci. (CAES) 2014, 2, 22–37. [Google Scholar]
  53. Tchuente, S.; Kwato, N. Natural radiation exposure to the public in the oil-bearing Bakassi Peninsula, Cameroon. Radioprotection 2015, 50, 35–41. [Google Scholar] [CrossRef]
  54. Heiserman, D.L. Księga Pierwiastków Chemicznych; Prószyński i S-ka: Warszawa, Poland, 1997. [Google Scholar]
  55. Henricsson, F.; Persson, B.R.R. Polonium-210 in the Bio-Sphere: Bio-Kinetics and Biological Effects; Nova Science Publishers, Inc.: New York, NY, USA, 2012. [Google Scholar]
  56. Carvalho, F.; Fernandes, S.; Fesenko, S.; Holm, E.; Howard, B.; Martin, P.; Phaneuf, M.; Porcelli, D.; Pröhl, G.; Twining, J. The Environmental Behaviour of Polonium; Technical Reports Series no. 484; IAEA: Vienna, Austria, 2017. [Google Scholar]
  57. Szymańska, K.; Strumińska-Parulska, D. Atmospheric fallout impact on 210Po and 210Pb content in wild growing mushrooms. Environ. Sci. Pollut. Res. 2020, 27, 20800–20806. [Google Scholar] [CrossRef] [Green Version]
  58. Strumińska-Parulska, D.; Olszewski, G.; Moniakowska, A.; Zhang, J.; Falandysz, J. Bolete mushroom Boletus bainiugan from Yunnan as a reflection of the geographical distribution of 210Po, 210Pb and uranium (234U, 235U, 238U) radionuclides, their intake rates and effective exposure doses. Chemosphere 2020, 253, 126585. [Google Scholar] [CrossRef]
  59. Vaaramaa, K.; Solatie, D.; Aro, L. Distribution of 210Pb and 210Po concentrations in wild berries and mushrooms in boreal forest ecosystems. Sci. Total Environ. 2009, 408, 84–91. [Google Scholar] [CrossRef]
  60. Turtiainen, T.; Brunfeldt, M.; Rasilainen, T.; Skipperud, L.; Valle, L.; Mrdakovic Popic, J.; Roos, P.; Sundell-Bergman, S.; Rosén, K. Doses from Natural Radioactivity in Wild Mushrooms and Berries to the Nordic population, Interim Report from the NKS-B BERMUDA Activity; NKS-273; Nordisk Kernesikkerhedsforskning: Roskilde, Denmark, 2013; ISBN 978-87-7893-346-1. [Google Scholar]
  61. Wichterey, K.; Sawallisch, S. Naturally occurring radionuclides in mushrooms from uranium mining regions in Germany. Radioprotection 2002, 37, 353–358. [Google Scholar] [CrossRef]
  62. Pearson, A.J.; Gaw, S.; Hermanspahn, N.; Glover, C.N. Natural and anthropogenic radionuclide activity concentrations in the New Zealand diet. J. Environ. Radioact. 2016, 151, 601–608. [Google Scholar] [CrossRef] [Green Version]
  63. Strumińska-Parulska, D.I.; Szymańska, K.; Krasińska, G.; Skwarzec, B.; Falandysz, J. Determination of 210Po and 210Pb in red-capped scaber (Leccinum aurantiacum): Bioconcentration and possible related dose assessment. Environ. Sci. Pollut. Res. 2016, 23, 22606–22613. [Google Scholar] [CrossRef]
  64. Strumińska-Parulska, D.I.; Olszewski, G.; Falandysz, J. 210Po and 210Pb bioaccumulation and possible related dose assessment in parasol mushroom (Macrolepiota procera). Environ. Sci. Pollut. Res. 2017, 24, 26858–26864. [Google Scholar] [CrossRef] [Green Version]
  65. Szymańska, K.; Falandysz, J.; Skwarzec, B.; Strumińska-Parulska, D. 210Po and 210Pb in forest mushrooms of genus Leccinum and topsoil from northern Poland and its contribution to the radiation dose. Chemosphere 2018, 213, 133–140. [Google Scholar] [CrossRef]
  66. Szymańska, K.; Strumińska-Parulska, D.; Falandysz, J. Isotopes of 210Po and 210Pb in Hazel bolete (Leccinellum pseudoscabrum)—Bioconcentration, distribution and related dose assessment. Environ. Sci. Pollut. Res. 2019, 26, 18904–18912. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  67. Guillén, J.; Baeza, A. Radioactivity in mushrooms: A health hazard? Food Chem. 2014, 154, 14–25. [Google Scholar] [CrossRef] [PubMed]
  68. Al-Azmi, D.; Saad, H.R.; Farhan, A.R. Comparative study of desert truffles from Kuwait and other countries in the middle east for radionuclide concentration. Biol. Trace Elem. Res. 1999, 71, 309–315. [Google Scholar] [CrossRef]
  69. Changizi, V.; Angaji, M.; Reza Zare, M.; Abbasnejad, K. Evaluation of 226Ra, 232Th, 137Cs and 40K “Agaricus bisporus” activity in cultivated edible mushroom formed in Tehran Province—Iran. Iranian J. Med. Phys. 2012, 9, 239–244. [Google Scholar] [CrossRef]
  70. Eckl, P.; Hofmann, W.; Türk, R. Uptake of natural and man-made radionuclides by lichens and mushrooms. Radiat. Environ. Biophys. 1986, 25, 43–54. [Google Scholar] [CrossRef]
  71. Kirchner, G.; Daillant, O. Accumulation of 210Pb, 226Ra and radioactive cesium by fungi. Sci. Total Environ. 1998, 222, 63–70. [Google Scholar] [CrossRef]
  72. Baeza, A.; Guillén, J.; Bernedo, J.M. Soil-fungi transfer coefficients: Importance of the location of mycelium in soil and of the differential availability of radionuclides in soil fractions. J. Environ. Radioact. 2005, 81, 89–106. [Google Scholar] [CrossRef] [PubMed]
  73. Turhan, Ş.; Köse, A.; Varinlioğlu, A. Radioactivity levels in some wild edible mushroom species in Turkey. Isot. Environ. Health Stud. 2007, 43, 249–256. [Google Scholar] [CrossRef]
  74. de Castro, L.P.; Maihara, V.A.; Silva, P.S.C.; Figueira, R.C.L. Artificial and natural radioactivity in edible mushrooms from Sao Paulo, Brazil. J. Environ. Radioact. 2012, 113, 150–154. [Google Scholar] [CrossRef]
  75. Rakić, M.; Karaman, M.; Forkapić, S.; Hansman, J.; Kebert, M.; Bikit, K.; Mrdja, D. Radionuclides in some edible and medicinal macrofungal species from Tara Mountain, Serbia. Environ. Sci. Pollut. Res. 2014, 21, 11283–11292. [Google Scholar] [CrossRef]
  76. Faweya, E.B.; Ayeni, M.J.; Kayode, J. Accumulation of natural radionuclides by some edible wild mushrooms in Ekiti State, Southwestern, Nigeria. World J. Nucl. Sci. Tech. 2015, 5, 107–110. [Google Scholar] [CrossRef] [Green Version]
  77. Kioupi, V.; Florou, H.; Kapsanaki-Gotsi, E.; Gonou-Zagou, Z. Bioaccumulation of the artificial Cs-137 and the natural radionuclides Th-234, Ra-226, and K-40 in the fruit bodies of Basidiomycetes in Greece. Environ. Sci. Pollut. Res. 2016, 23, 613–624. [Google Scholar] [CrossRef]
  78. Pelgunov, A.N.; Pelgunova, L.A. Radionuclide accumulation in mushrooms over the territory of Pleshcheyevo Lake National Park. Biol. Bull. 2016, 43, 1389–1392. [Google Scholar] [CrossRef]
  79. Tuo, F.; Zhang, J.; Li, W.; Yao, S.; Zhou, Q.; Li, Z. Radionuclides in mushrooms and soil-to-mushroom transfer factors in certain areas of China. J. Environ. Radioact. 2017, 180, 59–64. [Google Scholar] [CrossRef] [PubMed]
  80. Browne, E.; Firestone, R.B. Table of Radioactive Isotopes; Wiley: New York, NY, USA, 1986. [Google Scholar]
  81. Lenarczyk, K. Możliwości Wykorzystania Toru w Energetyce. Politechnika Warszawska. 2004. Available online: http://www-host-1.ee.pw.edu.pl/sep/nowa/download/torWenergetyce.pdf (accessed on 12 August 2020).
  82. Gadd, G. Geomycology: Biogeochemical transformations of rocks, minerals, metals and radionuclides by fungi, bioweathering and bioremediation. Mycol. Res. 2007, 111, 3–49. [Google Scholar] [CrossRef]
  83. Mietelski, J.W.; Baeza, A.S.; Guillén, J.; Buzinny, M.; Tsigankovc, N.; Gaca, P.; Jasińska, M.; Tomankiewicz, E. Plutonium and other alpha emitters in mushrooms from Poland, Spain and Ukraine. Appl. Radiat. Isot. 2002, 56, 717–729. [Google Scholar] [CrossRef]
  84. Baeza, A.; Guillén, J.; Mietelski, J.W. Uptake of alpha and beta emitters by mushrooms collected and cultured in Spain. J. Radioanal. Nucl. Chem. 2004, 261, 375–380. [Google Scholar] [CrossRef]
  85. Baeza, A.; Guillén, J. Influence of the soil bioavailability of radionuclides on the transfer of uranium and thorium to mushrooms. Appl. Radiat. Isot. 2006, 64, 1020–1026. [Google Scholar] [CrossRef]
  86. Galanda, D. Stanovenie Aktinoidov Metódami Spektrometrie Alfa. Ph.D. Thesis, Faculty of Natural Sciences of Comenius University, Bratislava, Czech, 2011. [Google Scholar]
  87. Rosa, M.M.L.; Maihara, V.A.; Taddei, M.H.T.; Silva, M.A.; Ferreira, M.T. Determination of 228Th, 232Th, and 228Ra in wild mushroom from a naturally high radioactive region in Brazil. In Proceedings of the 2011 International Nuclear Atlantic Conference—INAC 2011, Belo Horizonte, MG, Brazil, 24–28 October 2011. [Google Scholar]
  88. Akça, S.; Sögüt, O.; Küçükönder, E.; Karatepe, S.; Dogru, M. Radioactivity levels in some mushroom species and consequent doses. Asian J. Chem. 2014, 26, 879–882. [Google Scholar] [CrossRef]
  89. Mohammed, R.S.; Ahmed, R.S.; Abdaljalil, R.O. Uranium, thorium, potassium, and cesium radionuclides concentrations in desert truffles from the governorate of Samawah in southern Iraq. J. Food Prot. 2018, 81, 1540–1548. [Google Scholar] [CrossRef]
  90. Türkekul, I.; Yeşilkanat, C.M.; Ciriş, A.; Kölemen, U.; Çevik, U. Interpolated mapping and investigation of environmental radioactivity levels in soils and mushrooms in the Middle Black Sea Region of Turkey. Isot. Environ. Health Stud. 2018, 54, 262–273. [Google Scholar] [CrossRef]
  91. Szymańska, K.; Strumińska-Parulska, D.; Falandysz, J. Uranium (234U, 238U) and thorium (230Th, 232Th) in mushrooms of genus Leccinum and Leccinellum and the potential effective ionizing radiation dose assessment for human. Chemosphere 2020, 250, 126242. [Google Scholar] [CrossRef]
  92. Jia, G.; Belli, M.; Sansone, U.; Rosamilia, S.; Gaudino, S. Concentration, distribution and characteristics of depleted uranium (DU) in the Kosovo ecosystem: A comparison with the uranium behavior in the environment uncontaminated by DU. J. Radioanal. Nucl. Chem. 2004, 260, 481–494. [Google Scholar] [CrossRef]
  93. Jia, G.; Belli, M.; Sansone, U.; Rosamilia, S.; Gaudino, S. Concentration and characteristics of depleted uranium in water, air and biological samples collected in Serbia and Montenegro. Appl. Radiat. Isot. 2005, 63, 381–399. [Google Scholar] [CrossRef]
  94. Jia, G.; Belli, M.; Sansone, U.; Rosamilia, S.; Gaudino, S. Concentration and characteristics of depleted uranium in biological and water samples collected in Bosnia and Herzegovina. J. Environ. Radioact. 2006, 89, 172–187. [Google Scholar] [CrossRef] [PubMed]
  95. Žunić, Z.S.; Mietelski, J.W.; Błażej, S.; Gaca, P.; Tomankiewicz, E.; Ujić, P.; Čeliković, I.; Čuknić, O.; Demajo, M. Traces of DU in samples of environmental bio-monitors (non-flowering plants, fungi) and soil from target sites of the Western Balkan region. J. Environ. Radioact. 2008, 99, 1324–1328. [Google Scholar] [CrossRef] [PubMed]
  96. Falandysz, J.; Saba, M.; Strumińska-Parulska, D. 137Caesium, 40K and total K in Boletus edulis at different maturity stages: Effect of braising and estimated radiation dose intake. Chemopshere 2020. submitted. [Google Scholar]
  97. ICRP—International Commission on Radiological Protection. The 2007 Recommendations of the International Commission on Radiological Protection; ICRP Publ. 103. Ann. ICRP 37 (2-4); The International Commission on Radiological Protection: Ottawa, ON, Canada, 2007. [Google Scholar]
  98. Strumińska-Parulska, D.; Moniakowska, A.; Wang, Y.; Zhang, J.; Falandysz, J. Radiotoxic 210Po and 210Pb occurrence, variability, their intake rates and effective exposure doses in sclerotia of medicinal Wolfiporia cocos from polymetallic soils in Yunnan, China. Environ. Geochem. Health 2020. submitted. [Google Scholar]
  99. Strumińska-Parulska, D.; Falandysz, J.; Wang, Y. Radiotoxic 210Po and 210Pb in uncooked and cooked Boletaceae mushrooms from Yunnan (China) including intake rates and effective exposure doses. J. Environ. Radioact. 2020, 217, 106236. [Google Scholar] [CrossRef]
  100. Skwarzec, B.; Jakusik, A. 210Po bioaccumulation by mushrooms from Poland. J. Environ. Monit. 2003, 5, 791–794. [Google Scholar] [CrossRef]
  101. Strumińska-Parulska, D.I.; Skwarzec, B.; Fabisiak, J. Plutonium bioaccumulation in seabirds. J. Environ. Radioact. 2011, 102, 1105–1111. [Google Scholar] [CrossRef]
  102. Imanaka, T.; Hayashi, G.; Endo, S. Comparison of the accident process, radioactivity release and ground contamination between Chernobyl and Fukushima-1. J. Radiat. Res. 2015, 56 (Suppl. 1), 56–61. [Google Scholar] [CrossRef] [Green Version]
  103. Strumińska-Parulska, D.I.; Skwarzec, B. Plutonium isotopes 238Pu, 239+240Pu, 241Pu and 240Pu/239Pu atomic ratios in the southern Baltic Sea ecosystem. Oceanologia 2010, 52, 499–512. [Google Scholar] [CrossRef] [Green Version]
  104. Skwarzec, B.; Jahnz-Bielawska, A.; Strumińska-Parulska, D.I. The inflow of 238Pu and 239+240Pu from the Vistula River catchment area to the Baltic Sea. J. Environ. Radioact. 2011, 102, 728–734. [Google Scholar] [CrossRef]
  105. Strumińska-Parulska, D.I.; Skwarzec, B.; Tuszkowska, A. The inflow of 238Pu and 239+240Pu from the Odra and Pomeranian rivers catchments area to the Baltic Sea. J. Environ. Radioact. 2012, 113, 63–70. [Google Scholar] [CrossRef] [PubMed]
  106. IAEA—International Atomic Energy Agency. The Fukushima Daiichi Accident—Technical Volume 4/5, Radiological Consequences; IAEA: Vienna, Austria, 2015. [Google Scholar]
  107. Strumińska-Parulska, D.I. A study on determination of potentially hazardous plutonium isotopes in environmental samples. J. Environ. Sci. Health Part C 2013, 31, 145–169. [Google Scholar] [CrossRef]
  108. Yamamoto, M.; Shiraishi, K.; Los, I.P.; Kamarikov, I.Y.; Buzinny, M.G. Alpha-emitting radionuclide contents in food samples as related to the Chernobyl accident. J. Radioanal. Nucl. Chem. Lett. 1995, 201, 459–468. [Google Scholar] [CrossRef]
  109. Kershaw, P.J.; Kins, L.S.; McCubbin, D.; Aldridge, J.N. Plutonium: The legacy of Sellafield. Radioact. Environ. 2001, 1, 305–328. [Google Scholar] [CrossRef]
  110. Mietelski, J.W.; LaRosa, J.; Ghods, A. 90Sr and 239+240Pu, 238Pu, 241Am in some samples of mushrooms and forest soil from Poland. J. Radioanal. Nucl. Chem. 1993, 170, 243–258. [Google Scholar] [CrossRef]
  111. Mietelski, J.W.; Jasińska, M.; Kubica, B.; Kozak, K.; Macharski, P. Radioactive contamination of Polish mushrooms. Sci. Total Environ. 1994, 157, 217–226. [Google Scholar] [CrossRef]
  112. Hoshi, M.; Yamamoto, M.; Kawamura, H.; Shinohara, K.; Shibata, Y.; Kozlenko, M.T.; Takatsuji, T.; Yamashita, S.; Namba, H.; Yokoyama, N.; et al. Fallout radioactivity in soil and food samples in the Ukraine: Measurements of iodine, plutonium, cesium, and strontium isotopes. Health Phys. 1994, 67, 187–191. [Google Scholar] [CrossRef]
  113. Fulker, M.J.; Jackson, D.; Leonard, D.R.P.; McKay, K.; John, C. Dose due to man-made radionuclides in terrestrial wild foods near Sellafield. J. Radiol. Prot. 1998, 18, 3–13. [Google Scholar] [CrossRef]
  114. Outola, I. Effect of industrial pollution on the distribution of Pu and Am in soil and on soil-to-plant transfer of Pu and Am in a pine forest in SW Finland. J. Radioanal. Nucl. Chem. 2003, 257, 267–274. [Google Scholar] [CrossRef]
  115. Baeza, A.; Guillén, J.; Mietelski, J.W.; Gaca, P. Soil-to-fungi transfer of 90Sr, 239+240Pu, and 241Am. Radiochim. Acta 2006, 94, 75–80. [Google Scholar] [CrossRef]
  116. Lehto, J.; Vaaramaa, K.; Leskinen, A. 137Cs, 239,240Pu and 241Am in boreal forest soil and their transfer into wild mushrooms and berries. J. Environ. Radioact. 2013, 116, 124–132. [Google Scholar] [CrossRef]
  117. RIFE-21—Radioactivity in Food and the Environment, 2015; Report of the Centre for Environment, Fisheries and Aquaculture Science; Environment Agency, Food Standards Agency, Food Standards Scotland, Natural Resources Wales, Northern Ireland Environment Agency and the Scottish Environment Protection Agency: Preston, UK, 2016.
  118. RIFE-24—Radioactivity in Food and the Environment, 2018; Report of the Centre for Environment, Fisheries and Aquaculture Science; Environment Agency, Food Standards Agency, Food Standards Scotland, Natural Resources Wales, Northern Ireland Environment Agency and the Scottish Environment Protection Agency: Preston, UK, 2019.
  119. Johanson, K.J.; Nikolova, I.; Taylor, A.F.S.; Vinichuk, M.M. Uptake of Elements by Fungi in the Forsmark Area. SKB-TR-04-26; 2004. Available online: https://www.osti.gov/etdeweb/servlets/purl/20599333 (accessed on 12 August 2020).
  120. Mirończuk-Chodakowska, I.; Socha, K.; Zujko, M.E.; Terlikowska, K.M.; Borawska, M.H.; Witkowska, A.M. Copper, manganese, selenium and zinc in wild-growing edible mushrooms from the eastern territory of “Green Lungs of Poland”: Nutritional and toxicological implications. Int. J. Environ. Res. Public Health 2019, 16, 3614. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  121. Afarideh, H.; Payrovan, H. Determination of trace elements including uranium of water in Ramsar area. INIS-MF-13747 1993, 25, 415. [Google Scholar]
  122. Basha, A.M.; Yasovardhan, N.; Satyanarayana, S.V.; Reddy, G.V.S.; Kumar, A.V. Trace metals in vegetables and fruits cultivated around the surroundings of Tummalapalle uranium mining site, Andhra Pradesh, India. Toxic. Rep. 2014, 1, 505–512. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  123. Samuel-Nakamura, C.; Robbins, W.A.; Hodge, F.S. Uranium and associated heavy metals in Ovis aries in a mining impacted area in Northwestern New Mexico. Int. J. Environ. Res. Public Health 2017, 14, 848. [Google Scholar] [CrossRef]
  124. NRC—National Research Council. Evaluation of Guidelines for Exposures to Technologically Enhanced Naturally Occurring Radioactive Materials; The National Academies Press: Washington, DC, USA, 1999. [Google Scholar] [CrossRef]
  125. ICRP—International Commission on Radiological Protection. Compendium of Dose Coefficients Based on ICRP Publication 60; ICRP Publ. 119, Ann. ICRP 41 (Suppl); The International Commission on Radiological Protection: Ottawa, ON, Canada, 2012. [Google Scholar]
  126. ATSDR—Agency for Toxic Substances and Disease Registry. Toxicological Profile for Thorium; Agency for Toxic Substances and Disease Registry (US): Atlanta, GA, USA, 1990. [Google Scholar]
  127. Prokeš, J.; Šromová, S.; Jojková, K.; Štambergová, A.; Vulterin, K.; Leifertová, I.; Lisá, M.; Roosová, M. Hormetic effect of low doses of uranium in rats. Sci. Total Environ. 1991, 101, 161. [Google Scholar] [CrossRef]
  128. Keith, S.; Faroon, O.; Roney, N.; Scinicariello, F.; Wilbur, S.; Ingerman, L.; Llados, F.; Plewak, D.; Wohlers, D.; Diamond, G. Toxicological Profile for Uranium, Toxicological Profile for Uranium; Agency for Toxic Substances and Disease Registry (US): Atlanta, GA, USA, 2013. [Google Scholar]
  129. Carvalho, F. 210Po and 210Pb intake by the Portuguese population: The contribution of seafood in the dietary intake of 210Po and 210Pb. Health Phys. 1995, 69, 469–480. [Google Scholar] [CrossRef]
  130. ICRP—International Commission on Radiological Protection. The Evaluation of Risks from Radiation, ICRP Publication 8; The International Commission on Radiological Protection: Belfast, Ireland, 1965. [Google Scholar]
Table
Table 1. The activity concentration ranges of naturally occurring alpha-emitting radioisotopes in wild-growing mushrooms (the Latin names of the species are cited as described by the authors—the current names of some species can be found on the Index Fungorum web site) collected from different countries as well as the effective dose from mushrooms consumption presented as a proportion of total dietary consumption (µSv/kg dw) (* calculation based on the isotopic activity concentration and effective dose coefficients (Sv/Bq) for ingestion of radionuclides for adults [97]).
Table 1. The activity concentration ranges of naturally occurring alpha-emitting radioisotopes in wild-growing mushrooms (the Latin names of the species are cited as described by the authors—the current names of some species can be found on the Index Fungorum web site) collected from different countries as well as the effective dose from mushrooms consumption presented as a proportion of total dietary consumption (µSv/kg dw) (* calculation based on the isotopic activity concentration and effective dose coefficients (Sv/Bq) for ingestion of radionuclides for adults [97]).
Radionuclide
(Sv/Bq)		SpeciesActivity Concentration (Bq/kg dw)Effective Dose * (µSv/kg dw)CountryReferences
210Po
(1.2 × 10−6)		Baorangia bicolor, Boletus bainiugan, B. calopus, B. flammans, B. obsclereumbrinus, Butyriboletus roseoflavus, Rubroboletus sinicus, Rugiboletus extremiorientale, Wolfiporia cocos1.66–3081.99–370China[58,98,99]
Albatrellus ovinus, Cantharellus cibarius, Cortinarius armillatus, C. caperatus, Craterellus cornucopioides, C. tubaeformis, Hygrophorus camarophyllus, Lactarius rufus, L. scrobiculatus, L. utilis, L. torminosus, Leccinum variicolor, L. versipelle, L. vulpinum, Rozites caperatus, Russula aeruginea, R. decolorans, R. paludosa, R. parazurea, R. xerampelina, R. vinosa, Suillus luteus6–22,0007.2–26,400Finland[59,60]
Agaricus sp., Boletus sp., Leccinum sp., Lepiota sp., Lycoperda sp., Suillus sp., Xerocomus sp.1.0–6401.2–768Germany[61]
Not specified<9<10.8New Zealand[62]
Leccinum scabrum, L. versipelle, Russula paludosa, R. decolorans4.7–1985.64–238Norway[23]
Amanita muscaria, A. rubescens, A. phalloides, Agaricus silvicolae-similis, Boletus edulis, Cantharellus cibarius, Hydnum repandum, Imleria badia, Lactarius torminosus, Leccinum scabrum, L. versipelle, L. aurantiacum, L. aurantiacum var. quercinum, L. vulpinum, L. aurantiacum var. duriusculum, Leccinellum pseudoscabrum, Lycoperdon excipuliforme, Macrolepiota procera, Marasmius oreades, Russula cyanoxantha, R. nobilis, R. solaris, Scleroderma citrinum, Strobilomyces strobilaceus, Tylopilus felleus, Suillus bovinus, S. luteus, Xerocomus badius, X. subtomentosus0.23–170.28–20.4Poland[57,63,64,65,66,100]
222RnBoletus edulis, Leccinum aurantiacum, L. scabrum, Paxillus involutus16–36-Russia[78]
226Ra
(2.8 × 10−7)		Amanita fulva, Armillaria mellea, Boletus edulis, Cantharellus cibarius, Flammulina velutipes, Gomphus clavatus, Hydnum repandum, Leccinum scabrum, Macrolepiota procera, Paxillus involutus, Rozites caperata, Russula cyanoxantha, R. emetica, Suillus variegatus, Xerocomus badius22–486.16–13.4Austria[70]
Agaricus campestris, A. blazei, Agaricus sp., Lentinula edodes, Pleurotus eryngii, P. ostreatus, P. ostreatoroseus7.3–662.04–18.5Brazil[74]
Agaricus blazei, Armillaria solidipes, Boletus aereus, B. brunneissimus, B. edulis, Boletus sp., Cantharellus cibarius, Cyclocybe parasitica, Flammulina velutipes, Gomphus floccosus, Hygrophorus russula, Hypsizygus ulmarius, Lactarius hatsudake, L. volemus, Lentinula edodes, Leucocalocybe mongolica, Macrolepiota albuminosa, Neoboletus obscureumbrinus, Pleurotus djamor, Termitomyces albuminosus, Tylopilus balloui, T. felleus0.05–3.650.014–1.02China[79]
Terfezia sp.419117Egypt[68]
Not specified29.3–61.68.20–17.3France[71]
Agaricus sp., Boletus sp., Leccinum sp., Lepiota sp., Lycoperdon sp., Suillus sp., Xerocomus sp.0.3–5120.084–143Germany[61]
Agaricus campestris, A. xanthodermus, Armillaria mellea, Boletus sp., Bovista plumbea, Chroogomphus rutilus, Clavariadelphus truncates, Clitocybe nebularis, Clitocybe sp., Cortinarius sp., Entoloma sp., Hydnellum concrescens, Hydnum rufescens, Hygrocybe acutoconica, Inocybe sp., Lactarius salmonicolor, Lepista flaccida, L. nuda, Lycoperdon perlatum, Macrolepiota mastoidea, Marasmius oreades, Melanoleuca cognata, Mycena seynii, Ramaria formosa, R. obtusissima, Russula delica, Sarcodon martioflavus, Suillus collinitus, Vascellum pratense0.3–1.00.084–0.28Greece[77]
Terfezia sp., and not specified edible mushrooms60–70016.8–196Iran[68,69]
Terfezia sp.439122Kuwait[68]
Pleurotus squarrosulus, Psathyrella atroumbonata, Pleurotus tuber-regium, Termitomyces striatus, T. robustus2.68–21.60.75–6.05Nigeria[76]
Boletus edulis, Leccinum aurantiacum, L. scabrum, Paxillus involutus29–788.12–21.8Russia[78]
Amanita muscaria, A. curtipes, Clitocybe sp., Gymnopilus penetrans, Hebeloma cylindrosporum, Lactarius deliciosus, Lycoperdon perlatum, Plerurotus eryngii, Rhizopogon roseolus, Russula cessans, R. toruosa, Tricholoma equestre, T. pessandatum, T. terreum0.021–620.006–17.4Spain[40,72]
Boletus sp., Brunneoporus malicola, Fomitopsis pinicola, Ganoderma applanatum, Hericium clathroides, Megacollybia platyphylla, Pluteus cervinus, Suillellus luridus4–141.12–3.92Serbia[75]
Terfezia sp.438122Tunisia[68]
Agaricus campestris, Agaricus porphyrocephalus, Boletus edulis, Craterellus cornucopioides, Cantharellus cibarius, Lepiota cristata, Lycogala epidendrum, Marasmius oreades, Morchella esculenta, Nectria cinnabarina, Stropharia coronilla4.4–5.21.23–1.46Turkey[73]
228Th
(7.2 × 10−8)		Not specified3.1–1270.22–9.14Brazil[87]
Armillaria mellea, Boletus reticulatus, Cantharellus cibarius, Grifola frondosa, Lactarius deliciosus, Leccinum sp., Suillus luteus0.34–31.80.025–2.29Slovakia[86]
Amanita muscaria, A. ponderosa, Hebeloma cylindrosporum, Lactarius deliciosus, Macrolepiota procera, Plerurotus eryngii, Rhizopogon roseolus, Russula cessans, Suillus bovinus, Terfezia arenaria, T. boudieri, Tricholoma equestre, T. terreum, Tricholoma sp.1.4–130.11–0.94Spain[40,84,85]
230Th
(2.1 × 10−7)		Leccinellum pseudoscabrum, Leccinum aurantiacum, L. aurantiacum var. duriusculum, L. aurantiacum var. quercinum, L. vulpinum0.04–2.130.001–0.16Poland[91]
Cantharellus cibarius, Grifola frondosa, Lactarius deliciosus, Leccinum sp., Suillus luteus0.05–3.750.004–0.27Slovakia[86]
Agaricus campestris, Amanita muscaria, A. ponderosa, Hebeloma cylindrosporum, Lactarius deliciosus, Macrolepiota procera, Omphalotus olearius, Plerurotus eryngii, Rhizopogon roseolus, Russula cessans, Suillus bovinus, Terfezia arenaria, T. boudieri, Tricholoma equestre, T. terreum, Tricholoma sp.0.053–6.90.004–0.50Spain[40,83,84,85]
232Th
(2.3 × 10−7)		Not specified0.6–1420.14–32.7Brazil[87]
Terfezia sp.1.76–3.710.41–0.85Iraq[89]
Pleurotus squarrosulus, Psathyrella atroumbonata, Pleurotus tuber-regium, Termitomyces striatus, T. robustus8.57–14.31.97–3.29Nigeria[76]
Leccinellum pseudoscabrum, Leccinum aurantiacum, L. aurantiacum var. duriusculum, L. aurantiacum var. quercinum, L. vulpinum0.02–0.630.005–0.15Poland[91]
Boletus edulis, Leccinum aurantiacum, L. scabrum, Paxillus involutus13–332.99–7.59Russia[78]
Armillaria mellea, Boletus reticulatus, Cantharellus cibarius, Grifola frondosa, Lactarius deliciosus, Leccinum sp., Suillus luteus0.04–4.590.009–1.06Slovakia[86]
Agaricus campestris, Amanita muscaria, A. ponderosa, Hebeloma cylindrosporum, Lactarius deliciosus, Macrolepiota procera, Omphalotus olearius, Plerurotus eryngii, Rhizopogon roseolus, Russula cessans, Suillus bovinus, Terfezia arenaria, T. boudieri, Tricholoma equestre, T. terreum, Tricholoma sp.0.061–10.70.014–2.46Spain[40,83,84,85]
Agaricus campestris, A. porphyrocephalus, Amanita rubescens, Boletus edulis, Bonomyces sinopicus, Cantharellus cibarius, Craterellus cornucopioides, C. lutescens, Hygrophoropsis aurantiaca, Hypholoma fasciculare, Hypholoma spp., Lepiota cristata, Lycogala epidendrum, Marasmius oreades, Morchella esculenta, Nectria cinnabarina, Paxillus involutus, Pleurotus cornucopiae, Pycnoporus cinnabarinus, Pycnoporus spp., Russula delica, Stropharia coronilla0.35–1820.081–41.9Turkey[73,88,90]
234U
(4.9 × 10−8)		Not specified0.260.013Bosnia and Herzegovina[56]
Boletus bainiugan0.19–0.890.009–0.044China[58]
Fomes fomentarius1.0–6.900.049–0.34Kosovo[92,95]
Not specified<5<0.24New Zealand[62]
Armillaria mellea, Boletus edulis, Lactifluus vellereus, Leccinellum pseudoscabrum, Leccinum aurantiacum, L. aurantiacum var. duriusculum, L. aurantiacum var. quercinum, L. vulpinum, Macrolepiota procera, Xerocomus badius0.014–0.430.001–0.021Poland[83,91]
Not specified0.48–0.800.023–0.039Serbia[93]
Armillaria mellea, Boletus reticulatus, Cantharellus cibarius, Grifola frondosa, Lactarius deliciosus, Leccinum sp., Suillus luteus0.46–86.30.022–4.23Slovakia[86]
Agaricus campestris, Amanita muscaria, A. ponderosa, Hebeloma cylindrosporum, Lactarius deliciosus, Macrolepiota procera, Omphalotus olearius, Pleurotus eryngii, Rhizopogon roseolus, Russula cessans, Suillus bovinus, Terfezia arenaria, Terfezia boudieri, Tricholoma equestre, T. terreum, Tricholoma sp.0.15–7.00.007–0.34Spain[40,83,84,85]
235U
(4.7 × 10−8)		Not specified0.020.009Bosnia and Herzegovina[94]
Boletus bainiugan0.003–0.0640.0001–0.003China[58]
Not specified1.56–5.610.073–0.27France[71]
Fomes fomentarius0.070–0.520.003–0.024Kosovo[92,95]
Armillaria mellea, Boletus edulis, Lactifluus vellereus, Macrolepiota procera, Xerocomus badius0.006–0.0100.0003–0.0005Poland[83]
Not specified0.02–0.030.009–0.01Serbia[93]
Agaricus campestris, Amanita muscaria, A. ponderosa, Hebeloma cylindrosporum, Lactarius deliciosus, Macrolepiota procera, Omphalotus olearius, Plerurotus eryngii, Rhizopogon roseolus, Russula cessans, Suillus bovinus, Terfezia arenaria, T. boudieri, Tricholoma equestre, T. terreum, Tricholoma sp.0.007–0.420.0003–0.019Spain[40,83,84]
238U
(4.5 × 10−8)		Amanita fulva, Armillaria mellea, Boletus edulis, Cantharellus cibarius, Flammulina velutipes, Gomphus clavatus, Hydnum repandum, Leccinum scabrum, Macrolepiota procera, Paxillus involutus, Rozites caperata, Russula cyanoxantha, R. emetica, Suillus variegatus, Xerocomus badius44–921.98–4.14Austria[70]
Not specified0.270.013Bosnia and Herzegovina[94]
Agaricus blazei, Armillaria solidipes, Boletus aereus, B. bainiugan, B. brunneissimus, B. edulis, Boletus sp., Cantharellus cibarius, Cyclocybe parasitica, Flammulina velutipes, Gomphus floccosus, Hygrophorus russula, Hypsizygus ulmarius, Lactarius hatsudake, L. volemus, Lentinula edodes, Leucocalocybe mongolica, Macrolepiota albuminosa, Neoboletus obscureumbrinus, Pleurotus djamor, Termitomyces albuminosus, Tylopilus balloui, T. felleus0.15–7.680.007–0.34China[58,79]
Cantharellus cibarius, C. tubaeformis, Craterellus cornucopioides, Lactarius rufus924.14Finland[60]
Boletus sp., Suillus sp., Xerocomus sp., Leccinum sp., Lepiota sp., Agaricus sp., Lycoperdon sp.0.1–2590.004–11.6Germany[61]
Terfezia sp.2.3–5.880.10–0.26Iraq[89]
Fomes fomentarius0.7–11.30.03–0.51Kosovo[92,95]
Not specified40.18New Zealand[62]
Armillaria mellea, Boletus edulis, Lactifluus vellereus, Leccinellum pseudoscabrum, Leccinum aurantiacum, L. aurantiacum var. duriusculum, L. aurantiacum var. quercinum, L. vulpinum, Macrolepiota procera, Xerocomus badius0.015–0.510.0007–0.023Poland[83,91]
Boletus edulis, Leccinum aurantiacum, L. scabrum, Paxillus involutus7.4–190.33–0.85Russia[78]
Not specified0.67–1.110.03–0.05Serbia[93]
Armillaria mellea, Boletus reticulatus, Cantharellus cibarius, Grifola frondosa, Lactarius deliciosus, Leccinum sp., Suillus luteus0.45–99.40.020–4.47Slovakia[86]
Agaricus campestris, Amanita muscaria, A. ponderosa, Hebeloma cylindrosporum, Lactarius deliciosus, Macrolepiota procera, Omphalotus olearius, Pleurotus eryngii, Rhizopogon roseolus, Russula cessans, Suillus bovinus, Terfezia arenaria, T. boudieri, Tricholoma equestre, T. terreum, Tricholoma sp.0.12–7.300.005–0.33Spain[40,83,84,85]
Amanita rubescens, Bonomyces sinopicus, Cantharellus cibarius, Craterellus lutescens, Hygrophoropsis aurantiaca, Hypholoma fasciculare, Hypholoma spp., Pycnoporus cinnabarinus, Pycnoporus spp., Paxillus involutus, Pleurotus cornucopiae, Russula delica1.03–1680.046–7.56Turkey[88,90]
Table
Table 2. The activity concentration ranges of anthropogenic alpha-emitting radioisotopes in wild-growing mushrooms (the Latin names of the species are cited as described by the authors—the current names of some species can be found on the Index Fungorum web site) collected from a different countries as well as the effective dose from mushrooms consumption presented as a proportion of total dietary consumption (µSv/kg dw) (* calculation based on the isotopic activity concentration and effective dose coefficients (Sv/Bq) for ingestion of radionuclides for adults [97]).
Table 2. The activity concentration ranges of anthropogenic alpha-emitting radioisotopes in wild-growing mushrooms (the Latin names of the species are cited as described by the authors—the current names of some species can be found on the Index Fungorum web site) collected from a different countries as well as the effective dose from mushrooms consumption presented as a proportion of total dietary consumption (µSv/kg dw) (* calculation based on the isotopic activity concentration and effective dose coefficients (Sv/Bq) for ingestion of radionuclides for adults [97]).
Radionuclide (Sv/Bq)SpeciesActivity Concentration (Bq/kg dw)Effective Dose *
(µSv/kg dw)		CountryReferences
236U
(4.7 × 10−8)		Not specified0.014–0.0380.0007–0.002Kosovo[92]
238Pu
(2.3 × 10−7)		Armillaria mellea, Boletus edulis, Lactifluus vellereus, Macrolepiota procera, Xerocomus badius0.0001–0.0310.00002–0.007Poland[83]
Armillaria mellea, Boletus reticulatus, Cantharellus cibarius, Grifola frondosa, Lactarius deliciosus, Leccinum sp., Suillus luteus0.02–0.780.005–0.18Slovakia[86]
Agaricus campestris, Amanita muscaria, A. ponderosa, Hebeloma cylindrosporum, Lactarius deliciosus, Macrolepiota procera, Omphalotus olearius, Rhizopogon roseolus, Russula cessans, Suillus bovinus, Terfezia arenaria, T. boudieri, Tricholoma terreum, Tricholoma sp.0.0008–0.0200.0002–0.005Spain[83,84]
Not specified0.024–0.090.005–0.027UK[117,118]
Boletus edulis, Cantharellus cibarius, Paxillus involutus, Suillus luteus, Xerocomus badius0.029–43.60.007–10.03Ukraine[83,108,112]
239Pu
(2.5 × 10−7)		Not specified0.10.025UK[113]
239+240Pu
(2.5 × 10−7)		Russula decolorans0.002–0.020.0005–0.005Finland[114,116]
Armillaria mellea, Boletus edulis, Lactifluus vellereus, Leccinum sp., Macrolepiota procera, Xerocomus badius0.001–0.090.0003–0.023Poland[110,111]
Armillaria mellea, Boletus reticulatus, Cantharellus cibarius, Grifola frondosa, Lactarius deliciosus, Leccinum sp., Suillus luteus0.07–3.160.017–0,79Slovakia[86]
Agaricus campestris, Amanita muscaria, A. ponderosa, Clitocybe sp., Hebeloma cylindrosporum, Lactarius deliciosus, Lycoperdon perlatum, Macrolepiota procera, Omphalotus olearius, Pleurotus eryngii, Rhizopogon roseolus, Russula cessans, Suillus bovinus, Terfezia arenaria, T. boudieri, Tricholoma equestre, T. terreum, Tricholoma sp.0.0066–0.2460.0016–0.061Spain[40,83,84,115]
Not specified0.16–1.00.04–0.25UK[117,118]
Boletus edulis, Cantharellus cibarius, Paxillus involutus, Suillus luteus, Xerocomus badius0.053–53.780.013–13.45Ukraine[83,108,112]
241Am
(2.0 × 10−7)		Russula decolorans0.003–0.010.0006–0.002Finland[114,116]
Armillaria mellea, Boletus reticulatus, Cantharellus cibarius, Grifola frondosa, Lactarius deliciosus, Leccinum sp., Suillus luteus0.02–1.010.004–0.20Slovakia[86]
Amanita muscaria, Clitocybe sp., Hebeloma cylindrosporum, Lactarius deliciosus, Lycoperdon perlatum, Rhizopogon roseolus0.0086–0.0670.0017–0.013Spain[115]
Not specified0.065–0.980.013–0.19UK[113,117,118]
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Strumińska-Parulska, D.; Falandysz, J. A Review of the Occurrence of Alpha-Emitting Radionuclides in Wild Mushrooms. Int. J. Environ. Res. Public Health 2020, 17, 8220. https://doi.org/10.3390/ijerph17218220

AMA Style

Strumińska-Parulska D, Falandysz J. A Review of the Occurrence of Alpha-Emitting Radionuclides in Wild Mushrooms. International Journal of Environmental Research and Public Health. 2020; 17(21):8220. https://doi.org/10.3390/ijerph17218220

Chicago/Turabian Style

Strumińska-Parulska, Dagmara, and Jerzy Falandysz. 2020. "A Review of the Occurrence of Alpha-Emitting Radionuclides in Wild Mushrooms" International Journal of Environmental Research and Public Health 17, no. 21: 8220. https://doi.org/10.3390/ijerph17218220

APA Style

Strumińska-Parulska, D., & Falandysz, J. (2020). A Review of the Occurrence of Alpha-Emitting Radionuclides in Wild Mushrooms. International Journal of Environmental Research and Public Health, 17(21), 8220. https://doi.org/10.3390/ijerph17218220

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