Some mineral constituents of Parasol Mushroom (Macrolepiota procera).

This article reports background concentrations of Ag, Ba, Cd, Co, Cr, Cs, Cu, Ga, Hg, Mn, Mo, Pb, Rb, Sb, Sr, Se, Tl, V and Zn in caps and stalks of M. procera collected from four spatially distant sites across Poland. The elements were determined using inductively coupled plasma-mass spectrometry (ICP-MS), hydride generation atomic absorption spectrometry (HG-AAS) or a cold vapor atomic absorption spectrometry (CV-AAS). Copper, zinc, rubidium, selenium, chromium and cobalt were the most abundant amongst elements determined in this mushroom. Some elements (Cu, Zn, Rb, Se, Pb, Hg, Cd, Mo) occurred at greater concentrations in the caps than stalks of M. procera and some (Ag, Ba, Sr, V, Tl) dominated in the stalks, while for some other this proportion was similar or varied (Mn, Cr, Co, Ga, Sb, Cs) depending on the sampling site. For elements such as copper, zinc, rubidium as well as selenium some spatial similarity in distribution and/or concentration values both in caps and stalks was noted. Cadmium and lead content in caps of M. procera was usually below the European Union tolerance limit value of 2.0 and 3.0 microg/g dw set for cultivated mushrooms, respectively. These two toxic metals have been found in elevated concentration in M. procera from unpolluted stands outside of Poland as reported by some authors, which implies the possibility of relatively high background levels in this species.

Content and bioconcentration of mercury in mushrooms from northern Poland.

Mercury (Hg) was quantified using cold vapour-atomic absorption spectrometry (CV-AAS) in the fruiting bodies of nine edible and five inedible mushrooms and in underlying soil substrate samples. In total, 404 samples comprising caps and stalks and 202 samples of soil substrate (0-10 cm layer) were collected in 1996 from Trójmiejski Landscape Park, northern Poland. Mean Hg concentrations in the soil substrate for different species varied between 10 +/- 3 and 780 +/- 500 ng x g(-1) dry wt (range 2.3-1700). Among edible mushroom species, Horse Mushroom (Agaricus arvensis), Brown Birch Scaber Stalk (Leccinum scabrum), Parasol Mushroom (Macrolepiota procera), King Bolete (Boletus edulis) and Yellow-cracking Bolete (Xerocomus subtomentosus) contained elevated concentrations of Hg ranging from 1600 +/- 930 to 6800 +/- 4000 ng x g(-1) dry wt in the caps. Concentrations of Hg in the stalks were 2.6 +/- 1.1 to 1.7 +/- 1.0 times lower than those in the caps. Some mushroom species investigated had high Hg levels when compared with specimens collected from the background reference sites elsewhere (located far away from the big cities) in northern Poland. Bioconcentration factors of Hg in the caps of Horse Mushroom, Parasol Mushroom and Brown Birch Scaber Stalk were between 150 +/- 58 and 230 +/- 150 ng x g(-1) dry wt, respectively, and for inedible Pestle-shaged Puffball (Claviata excipulformis) was 960 +/- 300 ng x g(-1) dry wt. Linear regression coefficients between Hg in caps and in stalks and Hg soil concentrations showed a positive relationship for A. arvensis and Horse mushroom (p < 0.05) and a negative correlation for the caps of Death Caps (Amanita phalloides) and Woolly Milk Cap (Lactarius torminosus) (p < 0.05), while for other species no clear trend was found.

Total mercury in mushrooms and underlying soil substrate from the Borecka Forest, Northeastern Poland.

Total mercury concentrations were determined by cold-vapor atomic absorption spectroscopy in 240 composite samples of the caps, 240 of the stalks, and 16 of the whole fruiting bodies of 13 species of wild mushrooms and in 256 samples of underlying soil substrate collected from the Borecka Forest and the adjacent area in 1998. The area of the study is a background site with no known local sources of mercury emission. The mercury concentrations of the fruiting bodies varied largely (range between 14 and 14,000 ng/g dry weight) depending on the site and mushroom species investigated, but were less varied in soil samples (between 5 and 86 ng/g dry weight). The fruiting bodies of king bolete (Boletus edulis) showed greatest content of mercury. King bolete and yellow-cracking bolete (Xerocomus subtomentosus) collected from the Borecka Forest both contained in the caps around threefold greater concentrations of mercury than were noted for the same species collected from the surrounding area with 9,900 +/- 2,700 and 3,600 +/- 1,400, and 480 +/- 190 and 160 +/- 70 ng/g dry weight, respectively. Apart from the king bolete, relatively elevated concentrations of mercury were quantified also in a whole fruiting bodies of common puffball (Lycoperdon perlatum) with 3,400 +/- 1,300 ng/g as well as in the caps and stalks of common scaber stalk (Leccinum scabrum) with 1,200 +/- 740 and 1,100 +/- 380 ng/g dry weight. In other species investigated, the mercury concentrations were below 1,000 ng/g dry weight, and the smallest values were noted for crab-scended brittle gills (Russula xerampelina) with 60 +/- 20 in the caps and 40 +/- 20 ng/g dry weight in the stalks. For the species such as larch bolete, bay bolete (Xerocomus badius), yellow-cracking bolete, king bolete, common scaber stalk, fly agaric (Amanita muscaria), crab-scented brittle gills, honey mushroom (Amariella mellea) and safron milk cap (Lactarius deliciosus) a positive correlation (0.01 < p < 0.05) between the mercury content and size (diameter) of the caps was found, and in some cases also between mercury content of the stalks and size (height) of the fruiting body. The bioconcentration factor (BCF) values of total mercury were greatest for king bolete, i.e., 250 +/- 65 in the caps and 140 +/- 47 in the stalks, while for the other species investigated were between 200 +/- 91 and 1.8 +/- 0.5 in the caps, and 94 +/- 57 and 1.7 +/- 0.4 in the stalks. Nevertheless, despite great values of BCF of mercury indicated for some species and also a positive correlation between mercury content of the caps/stalks and underlying soil substrate, subsequent coefficients of determination were usually below 40%, and only for bay bolete (stalk), yellow-cracking bolete (cap), common scaber stalk (cap), hard bolete (Leccinum griseum) (cap, stalk), crab-scented gills (stalk), and honey mushroom (cap) were up to 68, 82, 42, 82, 51, 74, and 45%, respectively. The values of the cap/stalk Hg quotient were greatest for larch bolete (Suillus flavus) collected from the Borecka Forest (4.4 +/- 1.3) and for honey mushroom (2.7 +/- 0.9) from the adjacent area.

Chlorinated cyclodiene pesticide residues in blue mussel, crab, and fish in the Gulf of Gdansk, Baltic Sea.

Chlordane components (CHLs) and their metabolites (heptachlor, cis-heptachlor epoxide, U82, MC4, trans-chlordane, MC5, cis-chlordane, MC7, oxychlordane, MC6- and trans- and cis-nonachlor) and aldrin, dieldrin, endrin, isodrin, endosulfan 1, endosulfan 2, and mirex were quantified in the soft tissues of blue mussel, a whole crab, and whole fishes collected from the spatially different sites in the Gulf of Gdansk. Six to twelve chlordane compounds and metabolites and dieldrin were detected in all organisms examined while aldrin, endrin, isodrin, endosulfans 1 and 2, and mirex were not found above the detection limit of the method. The lipid weight based concentrations in Baltic biota were relatively small and ranged from 12 to 150 and 7.6-77 ng/g, while between 0.16 and 6.8 and 0.10-6.6 ng/g in fresh tissue, respectively. The profile (%) of chlordane compounds was very similar between various fish species with trans-nonachlor (28 +/- 17), cis-chlordane (23 +/- 18), oxychlordane (13 +/- 7), and heptachlor epoxide (11 +/- 5) as major constituents and was totally different in crab with oxychlordane as the most dominating (>65%) compound. Blue mussel, lamprey, and three-spined stickleback exhibited a smallest ability to metabolize CHLs, and such fishes as cod, lesser sand-eel, sand-eel, pikeperch, perch, round goby, flounder, and herring showed a slightly better ability, while crab was able to effectively metabolize most of CHL compounds except trans-nonachlor. A value of the quotient of the trans-nonachlor to cis-chlordane concentrations (N/C quotient) was 1.0 in blue mussel, 3.1 in crab, and between 0.9 and 1.8 in fish. Both the small concentrations of CHLs in all organisms and the values of N/C quotients close to 1 imply on a long-range aerial transport through movement of the air masses from the remote regions of the northern hemisphere as a main source of this pesticide in the Gulf of Gdansk. The interdependences between the CHL profiles for various fish species and between different sampling sites were examined using the principal component analysis (PCA) method. Applying the PCA model the first four significant components explained 90% (43% + 23% + 15% + 8%) of the total variance in the data matrix.

ICP/MS and ICP/AES elemental analysis (38 elements) of edible wild mushrooms growing in Poland.

Thirty-eight elements, including toxic cadmium, lead, mercury, silver and thallium, were determined in 18 species of wild edible mushrooms collected from several sites in Pomorskie Voivodeship in northern Poland in 1994. Elements were determined by double focused high resolution inductively coupled plasma mass spectrometry (HR-ICP-MS) and inductively coupled plasma atomic emission spectroscopy (ICP-AES), after wet digestion of the dried samples with concentrated nitric acid in closed PTFE vessels using a microwave oven. K, P and Mg were present at levels of mg/g dry matter; Na, Zn, Ca, Fe, Cu, Mn, Rb, Ag, Cd, Hg, Pb, Cs, Sr, Al and Si were present at microg/g levels, while Tl, In, Bi, Th, U, Ce, Pr, Nd, Sm, Eu, Gd, Tb, Dy, Ho, Er, Tm, Yb, La, Lu and Ba were present at ng/g levels.