Blanka Maňkovská
Forest Research Institute
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Featured researches published by Blanka Maňkovská.
Environmental Pollution | 2010
Harry Harmens; D.A. Norris; Eiliv Steinnes; Eero Kubin; Juha Piispanen; Renate Alber; Yuliya Aleksiayenak; Oleg Blum; Munevver Coskun; Maria Dam; L. De Temmerman; J.A. Fernández; Marina Frolova; M. V. Frontasyeva; L. González-Miqueo; Krystyna Grodzińska; Zvonka Jeran; Szymon Korzekwa; M. Krmar; Kestutis Kvietkus; Sébastien Leblond; Siiri Liiv; Sigurður H. Magnússon; Blanka Maňkovská; Roland Pesch; Åke Rühling; J.M. Santamaría; Winfried Schröder; Zdravko Špirić; Ivan Suchara
In recent decades, mosses have been used successfully as biomonitors of atmospheric deposition of heavy metals. Since 1990, the European moss survey has been repeated at five-yearly intervals. Although spatial patterns were metal-specific, in 2005 the lowest concentrations of metals in mosses were generally found in Scandinavia, the Baltic States and northern parts of the UK; the highest concentrations were generally found in Belgium and south-eastern Europe. The recent decline in emission and subsequent deposition of heavy metals across Europe has resulted in a decrease in the heavy metal concentration in mosses for the majority of metals. Since 1990, the concentration in mosses has declined the most for arsenic, cadmium, iron, lead and vanadium (52-72%), followed by copper, nickel and zinc (20-30%), with no significant reduction being observed for mercury (12% since 1995) and chromium (2%). However, temporal trends were country-specific with sometimes increases being found.
Environmental Pollution | 2011
Harry Harmens; D.A. Norris; David Cooper; Gina Mills; Eiliv Steinnes; Eero Kubin; Lotti Thöni; J.R. Aboal; Renate Alber; A. Carballeira; Munevver Coskun; L. De Temmerman; Marina Frolova; L. González-Miqueo; Zvonka Jeran; Sébastien Leblond; Siiri Liiv; Blanka Maňkovská; Roland Pesch; Jarmo Poikolainen; Åke Rühling; J.M. Santamaría; P. Simonèiè; Winfried Schröder; Ivan Suchara; Lilyana Yurukova; Harald G. Zechmeister
In 2005/6, nearly 3000 moss samples from (semi-)natural location across 16 European countries were collected for nitrogen analysis. The lowest total nitrogen concentrations in mosses (<0.8%) were observed in northern Finland and northern UK. The highest concentrations (≥ 1.6%) were found in parts of Belgium, France, Germany, Slovakia, Slovenia and Bulgaria. The asymptotic relationship between the nitrogen concentrations in mosses and EMEP modelled nitrogen deposition (averaged per 50 km × 50 km grid) across Europe showed less scatter when there were at least five moss sampling sites per grid. Factors potentially contributing to the scatter are discussed. In Switzerland, a strong (r(2) = 0.91) linear relationship was found between the total nitrogen concentration in mosses and measured site-specific bulk nitrogen deposition rates. The total nitrogen concentrations in mosses complement deposition measurements, helping to identify areas in Europe at risk from high nitrogen deposition at a high spatial resolution.
Environmental Pollution | 2012
Harry Harmens; Ilia Ilyin; Gina Mills; J.R. Aboal; Renate Alber; Oleg Blum; Munevver Coskun; L. De Temmerman; J.A. Fernández; Rui Figueira; M. V. Frontasyeva; Barbara Godzik; Natalia Goltsova; Zvonka Jeran; Szymon Korzekwa; Eero Kubin; Kestutis Kvietkus; Sébastien Leblond; Siiri Liiv; Sigurður H. Magnússon; Blanka Maňkovská; Olgerts Nikodemus; Roland Pesch; Jarmo Poikolainen; Dragan Radnović; Åke Rühling; J.M. Santamaría; Winfried Schröder; Zdravko Špirić; Trajče Stafilov
Previous analyses at the European scale have shown that cadmium and lead concentrations in mosses are primarily determined by the total deposition of these metals. Further analyses in the current study show that Spearman rank correlations between the concentration in mosses and the deposition modelled by the European Monitoring and Evaluation Programme (EMEP) are country and metal-specific. Significant positive correlations were found for about two thirds or more of the participating countries in 1990, 1995, 2000 and 2005 (except for Cd in 1990). Correlations were often not significant and sometimes negative in countries where mosses were only sampled in a relatively small number of EMEP grids. Correlations frequently improved when only data for EMEP grids with at least three moss sampling sites per grid were included. It was concluded that spatial patterns and temporal trends agree reasonably well between lead and cadmium concentrations in mosses and modelled atmospheric deposition.
Environmental Pollution | 2015
Harry Harmens; David Norris; Katrina Sharps; Gina Mills; Renate Alber; Yuliya Aleksiayenak; Oleg Blum; S.-M. Cucu-Man; Maria Dam; L. De Temmerman; Antoaneta Ene; J.A. Fernández; Javier Martínez-Abaigar; M. V. Frontasyeva; Barbara Godzik; Zvonka Jeran; Pranvera Lazo; Sébastien Leblond; Siiri Liiv; Sigurður H. Magnússon; Blanka Maňkovská; G. Pihl Karlsson; Juha Piispanen; Jarmo Poikolainen; J.M. Santamaría; Mitja Skudnik; Zdravko Špirić; Trajče Stafilov; Eiliv Steinnes; Claudia Stihi
In recent decades, naturally growing mosses have been used successfully as biomonitors of atmospheric deposition of heavy metals and nitrogen. Since 1990, the European moss survey has been repeated at five-yearly intervals. In 2010, the lowest concentrations of metals and nitrogen in mosses were generally found in northern Europe, whereas the highest concentrations were observed in (south-)eastern Europe for metals and the central belt for nitrogen. Averaged across Europe, since 1990, the median concentration in mosses has declined the most for lead (77%), followed by vanadium (55%), cadmium (51%), chromium (43%), zinc (34%), nickel (33%), iron (27%), arsenic (21%, since 1995), mercury (14%, since 1995) and copper (11%). Between 2005 and 2010, the decline ranged from 6% for copper to 36% for lead; for nitrogen the decline was 5%. Despite the Europe-wide decline, no changes or increases have been observed between 2005 and 2010 in some (regions of) countries.
Journal of Geochemical Exploration | 1997
Kamil Vrana; Stanislav Rapant; Dušan Bodiš; Karol Marsina; Blanka Maňkovská; Ján Čurlík; Peter Šefčík; Jozef Daniel; Ladislav Lučivjanský; Jaroslav Lexa; Silvester Pramuka
Abstract The Geochemical Atlas of Slovak Republic (49,036 km 2 ) at a scale of 1 : 1,000,000 was compiled during 1991–1995 together with maps of associated geochemical and ecological features at a scale of 1 :200,000. Investigations were aimed at the evaluation of concentrations and distributions of Al, As, Ba, Be, Ca, Ce, Co, Cd, Cs, Cr, Cu, Fe, Ga, Hg, K, La, Li, Mg, Mn, Mo, Na, Ni, P, Pb, Rb, Sb, Se, Sn, Sr, Th, U, V, W, Y, Zn, Zr in groundwater (16,359 samples), stream sediments (24,422 samples), rocks (3839 samples), soils (9892 samples from 4946 profiles; A and C horizons of each profile were sampled) and forest biomass (the foliage of the forest tree species from 3063 plots was sampled). In groundwater field measurements of temperature, pH, conductivity, dissolved O 2 , acidity, alkalinity were done. The evaluation was oriented to the natural radioactivity of the Slovak territory as follows: rocks (K, U, Th, U tot and dose rate, 15,573 reference spectrometric points), radon risk and water (U nat , 226 Ra, 222 Rn; 5271 samples). The main objective of the Geochemical Atlas was to construct single-component maps showing concentrations of chemical elements, compounds and measured parameters in the researched media of Slovakia at a scale of 1 : 1,000.000 and to create interactive databases of chemical composition and/or measured parameters of groundwater, biomass, rocks, soils, stream sediments and natural radioactivity, for the entire territory of the Slovak Republic. The single-component maps are not constructed in the part ‘Rocks’, where all the main rocks types of Slovakia are presented in the ‘Map of lithogeochemical rock types of Slovakia at a scale of 1: 500,000’. The edition of six atlases has been planned. In 1997 the first three atlases will appear (Groundwater, Biomass, Natural Radioactivity). Publishing of last three atlases (Rocks, Soils, Stream Sediments) is planned for 1998. Since the analytical works on stream sediments were finished during 1997, it was not possible to present here the results of that part of the Geochemical Atlas.
Environmental Pollution | 2001
Roman Longauer; Dušan Gömöry; Ladislav Paule; David F. Karnosky; Blanka Maňkovská; Gerhard Müller-Starck; Kevin E. Percy; Robert C. Szaro
The effects of industrial pollution on allelic and genotypic structures of Norway spruce. European silver fir and European beech were investigated by means of isozyme analysis. In a mixed Norway spruce-silver fir forest stand in an area heavily polluted by sulphur dioxide and heavy metals in the region of Spis (eastern Slovakia), pairs of neighbouring damaged and apparently healthy trees were selected in two replicates (44 and 69 pairs in a heavily and moderately damaged stand, respectively). Pairwise sampling of trees with contrasting vitality was applied to reduce potential effects of site heterogeneity on the vitality of sampled trees. No significant differences in allelic and genotypic frequencies were found between sets of healthy and declining trees. There were differences in the single-locus heterozygosities, but these were not consistent between the replicates. However, the set of damaged trees exhibited higher levels of genetic multiplicity and diversity, possibly due to the deleterious effect of rare alleles under the conditions of air pollution. Consequently. following the decline of pollutant-sensitive trees, the remaining stand will be depleted of a part of alleles with unknown adaptive value to future selection pressures.
Water Air and Soil Pollution | 1996
Blanka Maňkovská
The concentration of mercury has been determined in assimilation organs of forest trees from 10 main industrial regions of Slovakia, four mountain forests and one military area and compared with concentration of mercury from 1356 permanent monitoring plots of Slovakia. The mercury concentration ranges for 2 yr old needles of Picea abies Karst. were (in mg kg−1): 1.249–4.402 (Rudnany iron ore mines), 0.013–0.749 (nine other industrial regions), 0.021–0.737 (four mountain forests) and 0.053–0.538 (military area). The mercury content in the soil (0–5 cm) from a mercury smelting plant ranged from 9.9 to 130 mg kg−1, and the moss Pleurozium schreberi contained 3.8–9.1 mg kg−1. The values obtained were compared with the available literature data.
Water Air and Soil Pollution | 1997
Blanka Maňkovská
The foliage contents of Stotal and Ntotal were determined in 405 Permanent monitoring plots in four National Parks and sixteen Landscape Protection Areas and were compared with 1483 Permanent monitoring plots on Slovakia. The foliage content of S ranged from 0.72 to 6.77 g kg−1 in hardwoods and from 0.98 to 4.3 g kg−1 in softwoods. A critical increase was determined in one National Park and in four Landscape Protection Areas. The foliage content of N ranged from 9.7 to 48.7 g kg−1 in softwoods, and from 7.8 to 51.4 g kg−1 in hardwoods. An insufficient level of N was determined in one Landscape Protection Area and a critical increase in four Landscape Protection Areas. The sulphur to nitrogen ratio ranged from 0.08 to 0.176 in softwoods, and from 0.078 to 0.253 in hardwoods. The foliage surface on hitherto explored four National Parks and sixteen Landscape Protection Areas in network 4×4 km was covered by all categories of rigid fallout particles. Fly-ash from coal combustion were observed each of National Parks and Landscape Protection Areas by scanning electron microscopy. Mycelia and spore, mineral matters, sand and soil particles were present on all National Parks and Landscape Protection Areas. Particles derived from aluminium production were observed at three Landscape Protection Areas. Particles derived from cement production and from lime works were observed at two National Parks and six Landscape Protection Areas. Particles derived from ferrous metals industry were observed at each of National Parks and Landscape Protection Areas and particles typical for other technologies were present in three of National Parks and twelve Landscape Protection Areas.
Archive | 1997
Blanka Maňkovská
Concentrations of Al, Be, Ca, Cd, Co, Cr, Cu, Fe, Hg, K, Li, Mg, Mn, N, Na, Ni, Pb, Rb, S, Sr, V and Zn in the foliage of five species, three mosses and humus from 3063 plots are completed with their contents related to the limit values and composition of individual particles in stomata of leaves. In comparison 1991/94 for mosses reduced concentrations of Cd, Pb and Zn as well as increased concentrations of Cr, Cu, Fe and Ni were found.
Environmental Pollution | 2008
Winfried Schröder; Roland Pesch; Cordula Englert; Harry Harmens; Ivan Suchara; Harald G. Zechmeister; Lotti Thöni; Blanka Maňkovská; Zvonka Jeran; Krystyna Grodzińska; Renate Alber