Title

Alimov, A. F. (2007): Theory of Ecosystem Functioning: Application to Estuarine Ecology. Abstracts of the Symposium ECSA42 ‘‘Estuarine Ecosystems: Structure, Function and Management”, 16–22 September 2007. Svetlogorsk, Russia, 8–9 pp. (In Russian).

Anjum, N. A, Ahmad, I., Figueira, E., Duarte, A. C. and Pereira, E. (2013): Phenological development stages variation versus mercury tolerance, accumulation, and allocation in salt marsh macrophytes Triglochin maritima and Scirpus maritimus prevalent in Ria de Aveiro coastal lagoon (Portugal). Environmental Science and Pollution Research, 20: 3910-3922.

Aquino, R. S., Grativol, C. and Mourão, P. A. S. (2011): Rising from the Sea: Correlations between sulfated polysaccharides and salinity in plants. PLoS ONE, 6(4): e18862. https://doi. org/10.1371/journal.pone.0018862

Batalov, A. A., Giniyatullin, R. Kh. and Kagarmanov, I. R. (1991): Salicaceae - their participation in the formation of vegetation cover in technogenic landscapes of the Southern Urals. In: Proceedings of the conference «Flora and vegetation of Siberia and the Far East» dedicated to memory of L. M. Cherepnin. Krasnoyarsk, 73–74 pp. (In Russian).

Boestfleisch, C., Papenbrock, J. (2017): Changes in secondary metabolites in the halophytic putative crop species Crithmum maritimum L., Triglochin maritima L. and Halimione portulacoides (L.) Aellen as reaction to mild salinity. PLoS ONE, 12(4): e0176303. https://doi. org/10.1371/journal.pone.0176303

Bowes, G. G., Bowes, S. K., Rao, G. M. and Estavillo, J. B. (2002): Reiskind C₄ mechanisms in aquatic angiosperms: comparisons with terrestrial C₄ systems. Functional Plant Biology, 29: 379-392.

Breslina, I. P. (1980): Seaside meadows of the Kandalaksha Bay of the White Sea. In: Biological and floristic studies in connection with the protection of nature in the Arctic. Apatity, 132–143 pp. (In Russian).

Clifford, S. C, Arndt, S. K, Corlett, J. E, Joshi, S., Sankhla, N., Popp, M. and Jones, H. G. (1998): The role of solute accumulation, osmotic adjustment, and changes in cell wall elasticity in drought tolerance in Ziziphus mauritiana (Lamk.). Journal of Experimental Botany, 49: 967-977.

Davey, M. P., Bryant, D. N., Cummins, I., Gates, P., Ashenden, T. W., Baxter, R. and Edwards, R. (2004): Effects of elevated CO₂ on the vasculature and phenolic secondary metabolism of Plantago maritima. Phytochemistry, 65: 2197-2204.

Davis, A. J., Dale, N. M. and Ferreira, F. J. (2003): Pearl millet as an alternative feed ingredient in broiler diets. Journal of Applied Poultry Research, 12(2): 137-144.

Galibina, N. A., Terebova, E. N. (2008): Characterization of cell wall properties in needles from scotch pine trees of various vigor. Russian Journal of Plant Physiology, 55(3): 419-425.

Gamaley, U. V. (2004): Transport system of vascular plants. SPb, 424 p. (In Russian).

Gorshkova, T. A. (2007): The plant cell wall as a dynamic system. Moscow, 429 p. (In Russian).

Gulyaeva, E. N., Morozova, K. V., Markovskaya, E. F., Nikolaeva, N. N. and Zapevalova, D. S. (2016): Anatomical and morphological features of leaves of dominant species on the Barents Sea coast. Proceedings of PetrSU, 155: 13-19. (In Russian).

Hall, J. L. (2002): Cellular mechanisms for heavy metal detoxification and tolerance. Journal of Experimental Botany, 53: 1-11.

Han, R.-M., Lefèvre I., Albacete, A., Pérez-Alfocea, F., Barba-Espín, G., Díaz-Vivancos, P., Quinet, M., Ruan, C.-J., Hernández, J.A., Cantero-Navarro, E. and Lutts, S. (2013): Antioxidant enzyme activities and hormonal status in response to Cd stress in the wetland halophyte Kosteletzkya virginica under saline conditions. Physiologia Plantarum, 147: 352-368.

Han, R.-M., Lefèvre, I., Ruan, C.-J., Qin, P. and Lutts, S. (2012): NaCl differently interferes with Cd and Zn toxicities in the wetland halophyte species Kosteletzkya virginica (L.) Presl. Plant Growth Regulation, 68: 97-109.

Iiyama, K., Lam, T. and Stone, B. (1994): Covalent cross-links in the cell wall. Plant Physiology, 104: 315-320.

Ilyin, G.V., Usygina, I. S. and Kasatkina, N. E. (2015): Geoecological state of seas in the environment in the Russian Arctic under the present technogenic stresses. Bulletin of the Kola Science Center of the Russian Academy of Sciences, 21: 82-93. (In Russian).

Joly, R. J, Zaerr, J. B. (1987): Alteration of cell-wall water content and elasticity in Douglas-Fir during periods of water deficit. Plant Physiology, 83: 418-422.

Kausch, H. (1990): Biological processes in the estuarine environment. In: W. Michaelis (eds): Estuarine water quality management. Coastal and estuarine studies (Formerly lecture notes on coastal and estuarine studies), vol. 36. Springer, Berlin, Heidelberg. https://doi.org/10.1007/ 978-3-642-75413-5_52

Kosobryukhov, A. A., Markovskaya, E. F. (2016): Halophyte adaptation to the gradient of conditions at the intertidal zone of the White Sea Cost (with Triglochin maritima L. as an example). Global Media Journal, 14(27): 37-45.

Kosova, K., Vítamvas, P., Urban, M. O., Prašil, I. T. and Renaut, J. (2018): Plant abiotic stress proteomics: the major factors determining alterations in cellular proteome. Frontiers in Plant Science, 9: 122. doi: 10.3389/fpls.2018.00122

Krzesłowska, M. (2011): The cell wall in plant cell response to trace metals: Polysaccharide remodeling and its role in defense strategy. Acta Physiologiae Plantarum, 33: 35-51.

Kulbat, K. (2016): The role of phenolic compounds in plant resistance. Biotechnology and Food Science, 80(2): 97-108.

Laghlimi, M., Baghdad, B., El Hadi, H. and Bouabdli, A. (2015): Phytoremediation mechanisms of heavy metal contaminated soils: A review. Open Journal of Ecology, 5: 375-388.

Lavid, N., Schwartz, A., Yar Den, O. and Tel-Or, E. (2001): The involvement of polyphenols and peroxidase acitivities in heavy metal accumulation by epidermal glands of water lily (Nymphaeceaea). Planta, 212(3): 323-331.

Liu, H. Y., Liao, B. H. and Lu, S. Q. (2004): Toxicity of surfactant, acid rain and Cd²⁺ combined pollution to the nucleus of Vicia faba root tip cells. Chinese Journal of Applied Ecology, 15: 493-496.

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Maberly, S. C., Madsen, T. V. (2002): Freshwater angiosperm carbon concentrating mechanisms: processes and patterns. Functional Plant Biology, 29: 393-405.

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[1] Order of Ministry of Agriculture of the Russian Federation of Decemder 13. 2016. №. 552. (2016). On the approval of water quality standards for water bodies of fishery value, including the standards of maximum permissible concentrations of harmful substances in the waters of water bodies of fishery value. (In Russian).

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Title:	*Cell wall functional activity and metal accumulation of halophytic plant species Plantago maritima* and Triglochin maritima on the White Sea littoral zone (NW Russia)**
Authors Name:	Elena N. Terebova, Evgenya F. Markovskaya, Vera I. Androsova, Maria A. Pavlova, Natalia V. Oreshnikova
Journal:	Czech Polar Reports
Issue:	10
Volume:	2
Page Range:	169-188
No. of Pages:	20
Year:	2020
DOI:	10.5817/CPR2020-2-14
Publishers:	muniPress Masaryk University Brno
ISSN:	1805-0689 (Print), 1805-0697 (On-line)
Language:	English
Subject:
Abstract:	The presented study supplements the knowledge on ion-exchange capacity, swelling capacity (elasticity) of the plant cell wall, and the accumulation of heavy metals in halophytic species Plantago maritima and Triglochin maritima in the tidal zone of the White Sea western coast. The littoral soils of the coastal territories are sandy or rocky-sandy, medium and slightly saline with poor content of organic substances, Mn, Zn, Ni, and Pb. Studied soils are considered as uncontaminated by heavy metals because they contain background amounts of Fe and Cu. Sea water is significantly polluted by Fe (3.8 MPC) and Ni (55 MPC), has poor content of Zn and Cu and background level of Pb and Mn. The coastal dominant plant species P. maritima and T. maritima were characterized by intensive metals accumulation which was reflected in the coefficient of biological absorption (CBA) of metal by a whole plant. For P. maritima the following metal accumulation series was obtained: Cu (3.29)> Zn (2.81)> Ni (1.57)> Pb (1.30)> Mn (1.21)> Fe (0.97), and for T. maritima: Ni (3.80)> Fe (2.08)> Cu (1.91)> Zn (1.84)> Pb (1.51)> Mn (1.31). Roots accumulated 50–70% of Ni, Cu, Zn, Pb and Mn of the total metal content in the plant while leaves and stems contained 30–50%. Fe was allocated mainly in the roots (80%). The ion-exchange capacity of the plant cell wall for P. maritima and T. maritima was established as follows correspondingly: 3570–3700 and 2710–3070 μmol g^-1 dry cell weight per leaf; 2310–2350 and 1160–1250 μmol g^-1 dry cell weight per root.
Keywords:	plant cell wall, ion exchange capacity, swelling coefficient, heavy metals, coefficient of biological absorption, halophytes, estuary
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(1991): Salicaceae - their participation in the formation of vegetation cover in technogenic landscapes of the Southern Urals. In: Proceedings of the conference «Flora and vegetation of Siberia and the Far East» dedicated to memory of L. M. Cherepnin. Krasnoyarsk, 73–74 pp. (In Russian). Boestfleisch, C., Papenbrock, J. (2017): Changes in secondary metabolites in the halophytic putative crop species Crithmum maritimum L., Triglochin maritima L. and Halimione portulacoides (L.) Aellen as reaction to mild salinity. PLoS ONE, 12(4): e0176303. https://doi. org/10.1371/journal.pone.0176303 Bowes, G. G., Bowes, S. K., Rao, G. M. and Estavillo, J. B. (2002): Reiskind C₄ mechanisms in aquatic angiosperms: comparisons with terrestrial C₄ systems. Functional Plant Biology, 29: 379-392. Breslina, I. P. (1980): Seaside meadows of the Kandalaksha Bay of the White Sea. In: Biological and floristic studies in connection with the protection of nature in the Arctic. Apatity, 132–143 pp. (In Russian). 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