Electronic Journal of Polish Agricultural Universities (EJPAU) founded by all Polish Agriculture Universities presents original papers and review articles relevant to all aspects of agricultural sciences. It is target for persons working both in science and industry,regulatory agencies or teaching in agricultural sector. Covered by IFIS Publishing (Food Science and Technology Abstracts), ELSEVIER Science - Food Science and Technology Program, CAS USA (Chemical Abstracts), CABI Publishing UK and ALPSP (Association of Learned and Professional Society Publisher - full membership). Presented in the Master List of Thomson ISI.
2003
Volume 6
Issue 2
Topic:
Horticulture
ELECTRONIC
JOURNAL OF
POLISH
AGRICULTURAL
UNIVERSITIES
Matraszek R. 2003. CHANGES OF ROOT PHYSIOLOGICAL INDICES DEPENDING ON Ni AND Ca CONTENT IN THE SUBSTRATE, EJPAU 6(2), #05.
Available Online: http://www.ejpau.media.pl/volume6/issue2/horticulture/art-05.html

CHANGES OF ROOT PHYSIOLOGICAL INDICES DEPENDING ON NI AND CA CONTENT IN THE SUBSTRATE

Renata Matraszek

 

ABSTRACT

The effects of nickel on changes of roots physiological indices of zucchini cv. ‘Soraya’ and maize cv. ‘Złota Karłowa’ grown in the medium with various Ca contents were investigated using pot experiment. An attempt was made to explain this problem based on the following parameters: root volume, root adsorptive surface (total and active) and active surface of 1 cm3. Additionally, Ni and Ca contents were determined in roots. Three levels of nickel: 10, 40 or 60 mg Niˇkg-1 (NiSO4ˇ7H2O) and two levels of calcium: 250 or 400 mg Caˇkg-1 (CaCO3) in the substrate were used in the study. Plants grown without nickel at lower and higher calcium level in the nutrient medium were used as control. It was found that the value of root physiological indices of the studied plant species grown in the medium containing 250 mg Caˇkg-1 diminished with the increase of Ni the substrate. Increasing amount of nickel in the su

Key words: nickel, calcium, zucchini, maize, root physiological indicators.

INTRODUCTION

Soil and water contaminated with metals pose a major environmental and human health problem that is still in need of an effective, economical and affordable technological solution. Plant-based remediation techniques are showing increasing promise for use in contaminated soils. The use of plants to clean soil and water contaminated with toxic metals (phytoremediation) is the most rapidly developing, environmentally friendly and cost effective technology [5, 6, 7, 8, 23, 25, 34].

One of the most environmentally important metallic pollutants is nickel. It is an element specifically adsorbed by soil colloids. In the soil solid phase it occurs in an exchangeable form bound with sesquioxides and organic matter as well as with crystal lattice of minerals [9]. Though nickel solubility in soils increases with acidity, its great mobility is observed even under the neutral or alkaline conditions [14]. Mobile forms of nickel are readily available for plants and ions taken up by plants are mainly accumulated in roots [12, 13, 15, 16, 29]. It is known that heavy metals in soils can be immobilised by increasing pH of solution or by providing additional high-quality matrix surfaces. Increase in pH of the growing medium as well as the use of specific binding agents decrease the plant-available fractions of heavy metals and allows us to cultivate plants in spite of pollutant presence in soil [27].

Interaction between nickel and other cations consists mainly in co-operation in the uptake process and exclusion of trace elements from their physiological functions. In general optimal supply of plants with nutrients including Ca restricts phytotoxic activity of nickel [18, 19, 31]. The aim of the studies was to determine the influence of nickel on physiological activity of zucchini and maize roots, at optimal and high calcium level in the substrate, as based on: root volume, total adsorptive surface, active adsorptive surface, active surface of 1 cm3. Moreover Ca and Ni contents in roots of both plant species were measured.

MATERIALS AND METHODS

The experimental plants were: zucchini (Cucurbita pepo conv. giromontiina L.) ‘Soraya’ cv. and sugar maize (Zea mays var. saccharata Kcke) ‘Złota Karłowa’ cv. The studies were conducted in a green house with solid culture method in pots containing 3 kg of quartz sand as the medium. In order to eliminate any impurities and mineral components the sand was treated with muriatic acid then washed using distilled water and roasted. Total amounts of nutrients applied per each kilogram of the substrate were as follows: N – 270 mg (NH4NO3); P – 80 mg (KH2PO4); K – 270 mg (K2SO4 and KH2PO4); Mg – 100 mg (MgCl2); Fe – 10 mg (Fe2+ citrate) and 0.5 ml 1% of microelements solution (A-Z). Two calcium contents: 250 or 400 mg Caˇkg-1 were used in the experiment. All nutrients, except calcium, were introduced into the substrate as s aline water solutions in three doses. The first one was administered before seeds sowing and the other two at the stage of two and four specific leaves, respectively. Calcium was administered once during setting up the experiment, when the sand was mixed up with CaCO3; pH of the growing medium was adjusted to 5.8. Moreover 3 doses of nickel: 10; 40 or 60 mg Niˇkg-1 were additionally set. The metal was added through a solution of NiSO4ˇ7H2O on the following day after the others nutrients application. Plants grown without nickel at lower and higher calcium level in the nutrient medium were used as control. The experiment consisted of 8 treatments: three levels of nickel, two levels of calcium and two controls. Six replications with two plants in each were used and the whole experiment was repeated three times. At harvest (eleven weeks of vegetation) root volume as well as physiological indices of root (total adsorptive surface, adsorptive active surface and active sur face of 1 cm3) were determined using Sabinin and Kolosov method [2]. After mineralization of the dry material nickel content was determined using the AAS method on Philips PU 9100X apparatus [20]. Calcium content was determined by manganometric method [3]. The analyses were made in three replications and the obtained results were statistically evaluated, using Duncan’s multiple range test at the significance level a = 0.05.

RESULTS AND DISCUSSION

Physiological properties of zucchini and maize roots depended of nickel and calcium levels in the growing medium (figs. 1-4). Nickel in the amount of 10 mg Ni·kg-1 caused distinct changes in root physiological indices of studied plant species growing at the lower level of Ca (250 mg Caˇkg-1). Statistically significant decrease in root volume, total and active adsorptive surface as well as active surface of 1 cm3 zucchini and maize roots have been found. Only the decrease in maize root volume and active surface of 1 cm3 zucchini roots was not statistically significant. Root volume, total and active adsorptive surface as well as active surface of 1cm3 zucchini roots dropped by: 41, 28, 71 and 51% respectively, while maize roots – 22, 49, 45 and 42% (figs. 1-3). Nickel levels 40 and 60 mg Ni·kg-1 resulted in fur ther significant decrease of root physiological indicators of both studied plant species. Root volume of zucchini and maize grown at the substrate containing 40 mg Niˇkg-1 came down by 84 and 52%, respectively, whereas in the medium contaminated with the 60 mg Niˇkg-1 root volume of studied plant species dropped by 93 and 71% (figs. 1-3). The reduction in volume and length of roots and as a result decrease of adsorptive activity indices due to the increased nickel doses in the growing medium as shown by Gabrielli et. al. [11] may be caused by mitoses inhibition in root apical meristem and by the restriction of elongation of cell walls following mitotic divisions. The decrease in total root surface may be also caused by restriction of carbohydrate translocation from the shoots to roots (data not given). The decrease in total and active adsorptive surface of zucchini roots was equal 62 and 50% (40 mg Niˇkg-1) and 86 and 90% (60  mg Niˇkg-1), whereas for maize – 81 and 81% (40 mg Niˇkg-1) and 87 and 88% (60 mg Niˇkg-1) (figures 2a, 2b). As reported by Szymańska and Molas [30] toxic influence of nickel on the roots is expressed by reduction of elongation, geotropic reaction disturbance as well as with the presence of unequal swellings – outgrowths in the root basal layer which results in the changes of root adsorptive properties. Reduction of root adsorptive capacity can result from the presence of nickel in cell walls and hairs zone as well as from simultaneous inhibition of membrane permeability e.g. for calcium ions [30]. Our results (fig. 5) confirmed studies of other authors [1, 10] showing that the increasing amounts of nickel in the substrate caused successive significant increase Ni content in roots of both studied plant species being always higher in zucchini roots. Calcium content in zucchini roots grown in the envir onment contaminated with Ni increased whereas in the case of the maize the opposite relationship was found (fig. 4). It is probably related to different tolerance of two studied plant species to nickel. Maize is more tolerant species as compared with a susceptible zucchini. Calcium is a well known component of signal transduction pathways. It can active and regulate many processes in eucaryotic cells. Small intracellular changes of Ca concentration can regulate such processes as elongation and division of cells, the metabolism, transport and secretion [4, 17, 28]. In the last decade a pivotal role of cytosolic free Ca2+ ions, acting as the secondary messenger, in transduction of various hormonal and environmental signaals to the responsive elements of cellular metabolism has been well established in plant cells [4, 21, 22, 24, 26, 31, 32, 33].

Fig. 1. Volume of zucchini and maize roots depending on various Ni and Ca contents in the substrate; For each of two plant species means in columns marked with the same letter are not significantly different at P = 0.05

Fig. 2a. Adsorptive surface of zucchini roots depending on various Ni and Ca contents in the substrate; For each of two plant species means in columns marked with the same letter are not significantly different at P = 0.05

Fig. 2b. Adsorptive surface of maize roots depending on various Ni and Ca contents in the substrate; For each of two plant species means in columns marked with the same letter are not significantly different at P = 0.05

Fig. 3. 1 cm3 active surface of zucchini and maize roots depending on various Ni and Ca contents in the substrate; For each of two plant species means in columns marked with the same letter are not significantly different at P = 0.05

Fig. 4. Calcium concentration in zucchini and maize roots depending on various Ni and Ca contents in the substrate; For each of two plant species means in columns marked with the same letter are not significantly different at P = 0.05

Fig. 5. Nickel concentration in zucchini and maize roots depending on various Ni and Ca contents in the substrate; For each of two plant species means in columns marked with the same letter are not significantly different at P = 0.05

In control at higher calcium level (0 mg Niˇkg-1; 400 mg Ca·kg-1) noticeable decrease of total adsorptive surface of maize roots (by 18%) not causing its distinct changes in zucchini roots has been reported (fig. 2a, b). At the same time high calcium level caused a significant increase of Ca content in zucchini roots and a significant decrease in its concentration in maize roots (fig. 4). This different reaction of roots in two studied plants species may result from larger demand for calcium ions in the case of zucchini than maize or from smaller sensitivity of zucchini roots to Ca excess in the substrate. Calcium excess is not very toxic for plants and even large Ca concentration affects its increase in root tissues insignificantly. Calcium in apoplast is in equilibrium with Ca ions in soil solution.

The effect of higher calcium level on root activity indexes in nickel contaminated plants was different depending on nickel dose and plant species. High calcium level (400 mg Caˇkg-1 of the substrate) independent of nickel level (10-60 mg Niˇkg-1 of the substrate) did not have a significant effect on root physiological indices in maize but caused a significant increase of zucchini root volume (figs. 1-3). Depending on nickel dose (10, 40 or 60 mg Niˇkg-1) zucchini roots volume increased by 20, 109 and 387%, respectively. At he same time significant (by 65%) increase of active adsorptive surface of zucchini roots was found but only at the lowest studied nickel content in the substrate i.e. 10 mg Niˇkg-1 (figs. 1-3). The higher calcium level in the growing medium (400 mg Caˇkg-1) led to lower content of nickel in the roots of both studied plant species but only at the highest Ni dose in the medium (60 mg Niˇkg-1) and the reaction was greater in the case of maize. Thus under these conditions a significant drop of nickel content in maize roots by 39% and zucchini roots by 22% was obtained (fig. 5). The higher calcium level in the growing medium (400 mg Caˇkg-1) resulted in significant decrease of calcium content in maize roots but only under the highest nickel level (60 mgˇkg-1) (fig. 4).

A suitable Ca content in the nickel contaminated environment determines its biological activity which is shown in formation of root physiological indicators. However this mechanism of Ca reduction to nickel activity is differentiated depending on the plant species. Summing up it can be stated that the reaction of zucchini and maize roots to increasing nickel concentration in the substrate with two calcium levels in the plant nutritive medium may result from various tolerance both studied species to nickel but also from larger demand for calcium ions in the case of zucchini than maize from smaller sensitivity of zucchini roots to Ca excess in the substrate. Additional amounts of calcium ions in the substrate did not neutralize toxic effects of nickel on maize roots as in the case of zucchini roots in spite of higher nickel content in zucchini roots than in maize roots.

CONCLUSIONS

  1. The value of root physiological indices (volume, total and active adsorptive surface, active surface of 1 cm3) of zucchini and maize grown in the medium containing 250 mg Caˇkg-1 diminished with the increase of Ni the substrate (10-60 mg Niˇkg-1)

  2. Increasing amount of nickel in the substrate (10-60 mgˇkg-1) caused a successive significant increase of Ni content in roots of both studied plant species however higher Ni concentration was found in zucchini roots than in maize.

  3. Calcium content in zucchini roots grown in the environment contaminated with Ni (10-60 mgˇkg-1) increased whereas in the case of the maize the opposite relationship was found.

  4. The effect of higher calcium level on root activity indexes in nickel contaminated plants was different depending on nickel dose and plant species.

  5. High calcium level (400 mg Caˇkg-1 of the substrate) independent of nickel level (10-60 mg Niˇkg-1 of the substrate) did not have a significant effect on root physiological indices in maize but caused a significant increase of zucchini root volume. At he same time significant increase of active adsorptive surface of zucchini roots was found but only at the lowest studied nickel content in the substrate i.e. 10 mg Niˇkg-1.

  6. The higher calcium level in the growing medium (400 mg Caˇkg-1) led to lower content of nickel in the roots of both studied plant species but only at the highest Ni dose in the medium (60 mg Niˇkg-1) and the reaction was greater in the case of maize.

  7. The higher calcium level in the growing medium (400 mg Caˇkg-1) resulted in significant decrease of calcium content in maize roots but only in the presence of highest Ni level (60 mgˇkg-1 of the substrate).

REFERENCES

  1. Baccouch S., Chaoui A., El Ferjani E., 1998. Nickel toxicity: Effect on growth and metabolism of maize. J. Plant Nutr. 21, 3, 577-588.

  2. Basławska S. S., Trubieckowa O. M., 1964. Praktikum po fizjołogii rastenij [Practice in plant physiology]. Moskwa, 198-205 [in Russian].

  3. Blaim K., Szynal J., 1968. Influence of (2-chloroethyl)-trimethyl-ammonium chloride (CCC) on the content and distribution of calcium in wheat stalks during growth. Bull. Acad. Pol. Sci. ser. Biol. 16, 63-65.

  4. Bush D. S., 1995. Calcium regulation in plant cells and its role in signalling. Annu. Rev. Plant. Mol. Biol. 46, 95-122.

  5. Chaney R. L., Malik M., Li Y. M., Brown S. L., Brewer E. P., Angle J. S., Baker A. J. M., 1997. Phytoremediation of soil metals. Current opinion in Biotechnology. 8, 279-284.

  6. Chen Y. X., Lin Q., Luo Y. M., He Y. F., Zhen, Yu Y. L., Tian G. M., Wong M. H., 2003. The role of citric acid on the phytoremediation of heavy metal contaminated soil. Chemosphere 50, 807-811.

  7. Chen H. M., Zheng C. R., Tu C., Shen Z. G., 2000. Chemical methods and phytoremediation of soil contaminated with heavy metals. Chemosphere 41, 229-234.

  8. Cunningham S. D., Berti W. R., Huang J. W., 1995. Phytoremediation of contaminated soils. Trends in Biotechnology 13, 393-397.

  9. Dudka S., Piotrowska M., Chłopecka A., 1993. Formy chromu i niklu w glebach. [w:] Chrom, nikiel i glin w środowisku [Chromium and nickel forms in soils. [In:] Chromium, nickel and aluminium in the environment]. Zesz. Nauk. PAN. 5, 15-22 [in Polish].

  10. Ewais E. A., 1997. Effect of cadmium, nickel and lead on growth, chlorophyll content and proteins of weeds. Biol. Plant. 39, 3, 403-410.

  11. Gabrielli R., Pandolfini T., Vergnano O., Palandri M. R., 1990. Comparison of two species with different nickel tolerances strategies. Plant Soil. 122, 271-277.

  12. Gorlach E., 1994. Roślina jako czynnik zmniejszający negatywne skutki skażenia gleb metalami ciężkimi [Plant as the factor reducing negative results of soil pollution with heavy metals]. Biul. Regionalny ZDR AR w Krakowie. 305, 163-172 [in Polish].

  13. Gorlach E., Gambuś F., 1989. Wpływ interakcji pomiędzy metalami ciężkimi (Cd, Cu, Ni, Pb i Zn) w glebie na ich pobieranie przez życicę wielokwiatową (Lolium multiflorum) [The influence of interactions between heavy metals (Cd, Cu, Ni and Pb) in soil on their uptake by italian ryegrass (Lolium multiflorum)]. Acta Agr. et Silv. ser. Agr. 28, 61-72 [in Polish].

  14. Kabata-Pendias A., Pendias H., 1999. Biogeochemia pierwiastków śladowych [Biogeochemistry of trace elements]. PWN Warszawa, 340 [in Polish].

  15. Kabata-Pendias A., Piotrowska M., Witek T., 1993. Ocena jakości i możliwości rolniczego użytkowania gleb zanieczyszczonych metalami ciężkimi [Estimation of physicochemical properties and possibility of agricultural management of soils polluted with heavy metals].IUNG Puławy, 5, 53, 5-14 [in Polish].

  16. Klobušický K., Kopeć M., 1997. Cadmium and nickel contents in soil, roots and herbage of semi-natural grassland situated on different altitudes in regions of Slovakia. Zesz. Probl. Post. Nauk Roln. 448b, 125-129.

  17. Marschner H., 1995 Mineral nutrition of higher plants. Academic Press, New York.

  18. Matraszek R., 2000. Fizjologiczno-morfologiczna reakcja na nikiel wybranych gatunków roślin [Physiological and morphological reaction of selected plants species on nickel]. Rozprawa doktorska. AR Lublin, 328 [in Polish].

  19. Matraszek R., Wawron M., 1999. Fitotoksyczne oddziaływanie niklu na w zależności od stężenia jonów Ca i Fe w podłożu [Nickel phytotoxicity in relation to Ca and Fe concentration in the medium]. Materiały VII Ogólnopolskiego Zjazdu Naukowego Hodowców Roślin Ogrodniczych pt.: "Hodowla Roślin Ogrodniczych u progu XXI wieku”. AR Lublin, 4-5 luty, 545-549 [in Polish].

  20. Ostrowska A., Gawliński S., Szczubiałka Z., 1991. Metody analizy i oceny właściwości gleb i roślin [Methods useful in analysis and estimation of soils and plants properties]. Katalog IOŚ. Warszawa, 334 [in Polish].

  21. Pandey S., Tiwari S. B., Upadhyaya K. C. Sopory S. K., 2000. Calcium signalling: linking environmental signals to cellular functions. Critical Revievs in Plant Sciences. 19, 291-318.

  22. Plieth C., 2001. Plant calcium signalling and monitoring: pros and cons and recent experimental approaches. Protoplasma 218, 1-23.

  23. Raskin I., Smith R. D., Salt D. E., 1997. Phytoremediation of metals: using plants to remove pollutants from the environment. Current Opinion in Biotechnology 8, 221-226.

  24. Rengel Z., Zhang W. H., 2003. Role of dynamics of intracellular calcium in aluminium toxicity syndrome. New Phytologists (0), - doi: 10.1046/j.1469-8137.2003.00821.x.

  25. Robinson B. H., Brooks R. R., Clothier B. E., 1999. Soil amendments affecting nickel and cobalt uptake by Bekherya coddii: potential use for phytomining and phytoremediation. Annals of Botany 84, 689-694.

  26. Sanders D., Pelloux J., Brownlee C., Harper J. F., 2002. Calcium at the crossroads of signalling. Plant Cell. 14, 10-417.

  27. Stumm W., Morgan J. J., 1996. Aquatic Chemistry. 3rd ed. Willey, New York.

  28. Skórzyńska-Polit E., Tukendorf A., Selstam E., Baszyński T., 1998. Calcium modifies Cd effect on runner bean plants. Environmental and Experimental Botany 40, 275-286.

  29. Szymańska M., Matraszek R., Świąder A., 1997. Zaburzenia procesów w korzeniu pod wpływem niklu na przykładzie Sinapis alba L. [The disturbances of root processes in the presence of nickel on the example of Sinapis alba L.]. Materiały II Ogólnopolskiej Konferencji pt.: "Zastosowanie kultur in vitro w fizjologii roślin”. Kraków 21-23 listopada 1996, 227-232 [in Polish].

  30. Szymańska M., Molas J., 1994. Toksyczny wpływ niklu na wczesne fazy rozwojowe ogórka (Cucumis sativus L.) w warunkach in vitro [The toxic influence of nickel on early stages of Cucumis sativus L. development in vitro conditions]. Materiały I Ogólnopolskiej Konferencji pt.:, "Zastosowanie kultur in vitro w fizjologii roślin”. Kraków, 15-17 grudzień, 343-351 [in Polish].

  31. Świąder A., Matraszek R., 1996. Wczesne fazy rozwojowe soi w zależności od zawartości niklu i wapnia w podłożu [Early stages of soybean development in dependently on nickel and calcium contents in the medium]. Materiały Ogólnopolskiej Konferencji Naukowej pt.:, "Strączkowe rośliny białkowe II. Soja.". Lublin 28 listopada, 197-202 [in Polish].

  32. Trewavs A., 1999. Le calcium, c’est la vie: Calcium males waves. Plant Physiology 120, 1-6

  33. Webb A. A. R., McAinsh M. R., Taylor J. E., Hetherington A. M., 1996. Calcium ions as intracellular second messengers in higher plants. Advances in Botanical Research 22, 45-96.

  34. Wójcik M., 2000. Fitoremediacja – sposób oczyszczania środowiska [Phytoremediation – the way of environment cleaning]. Kosmos 49, 135-147 [in Polish].


Renata Matraszek
Department of Plant Physiology
Agricultural University in Lublin
15 Akademicka Street, 20-468 Lublin, Poland
tel. (+48 81) 445 68 79
e-mail: metal@agros.ar.lublin.pl

Responses to this article, comments are invited and should be submitted within three months of the publication of the article. If accepted for publication, they will be published in the chapter headed ‘Discussions’ in each series and hyperlinked to the article.


[BACK] [MAIN] [HOW TO SUBMIT] [SUBSCRIPTION] [ISSUES] [SEARCH]