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Dr. of Biology Bukharina I.L.
Udmurt State University, Russia
Contents and dynamics of the main
elements of mineral nutrition of shoots of plants in urban environment
The
chemical composition of plant leaves is formed by both the direct and indirect
influence of atmospheric pollution through the soil. The concentration of
nutrients in assimilation organs is often used as a parameter to assess the
industrial pollution in monitoring the state of plants. The industrial
pollution causes the change in the element composition of the structural parts
of plants, thus there is a lack or excess of certain elements, in other words,
the ratio between different elements changes (Vinokurova, 2003; Sukhareva,
Lukina, 2004; Bukharina and others, 2007; Darral, 1989; Innes, 1995).
Due to
the number of studies it was found that high content of nitrogen in the leaves
may be related to the ability of plants under stress conditions to increase the
content of free amino acids as well as to absorb gaseous nitrogen pollutants
such as nitrogen oxides and ammonia from the air and involve them in the
metabolism (Barber, 1988; Vasfilov, 2003; Innes, 1995). The excess of nitrogen
is toxic to plants because it causes inhibition of photosynthesis through the
suppression of the synthesis of chlorophyll. There is a perception that the
ratio of N:P:K is a homeostatic functional status of the plant organism.
The
purpose of our research is to reveal the influence of urban environment on the
exchange of the basic elements of mineral nutrition in plants.
The studies were conducted in Izhevsk. Izhevsk is a
large industrial center of the Urals region with well-developed industry,
transportation network and social infrastructure.
Species
of woody plants which account for about 70% of green area of the city were the
objects of the study. The studied plants had good or satisfactory life and
middle-generative ontogenetic state. The studied
species grew along highways and sanitary-protective zones (SPZ) of industrial
enterprises that are the main polluters of the city such as “Avtozavod”,
“Bummash”, “Izhstal”. The suburban area and the territory of the largest city
park were selected as a conventional control zones (CCZ).
The soils in the conventional control zones have low
levels of pollution. The level of soil pollution along highways and in
sanitary-protective zones of industrial enterprises is assessed as moderately
dangerous, and in the area of enterprises “Izhstal” and “Avtozavod” as
extremely dangerous.
Twice during the vegetation period we determined the
content of major mineral nutrients (nitrogen, potassium and phosphorus) in the
stem part and in the leaves of one year old shoots of woody plants (Guidelines
…, 1982). To interpret the obtained
results we used the program “Statistica 5.5”.
The analysis revealed
that the content of the basic elements of mineral nutrition depends on the
peculiarities of species, place of growth conditions and period of plant
vegetation as well as the interaction of these factors. In June and September the leaves of Betula pendula Roth, Salix
caprea L., Tilia cordata Mill. and Sorbus aucuparia L.
growing in different types of plantations do not have significant differences in
a given indicator (Table 1) except for Betula
pendula and Salix caprea in plantations growing along highways, and Tilia cordata Mill in plantations of
sanitary-protective zones. During the first period of observation the leaves of Rosa majalis Herrm. growing in the CCZ
are provided with nitrogen better in comparison with other types of
plantations, during the second period - on the contrary. The stem part of one
year old shoot of Betula pendula and Salix caprea growing in conditions of
intensive industrial pollution has the higher indices of nitrogen content in
June and in September than the indices of conventional control zones.
The reaction of introduced species is somewhat
different. In June the leaf blades of Acer negundo L., Populus balsamifera L. and Malus
baccata (L.) Borkh in the plantations along highways and SPZ of industrial
enterprises contain nitrogen in quantities exceeding conventional control zone
and during the leaf fall - on the contrary. Both the beginning and the end of the
vegetation period of Caragana arborescens
Lam. are characterized by the accumulation of nitrogen in the leaves of plants
growing along the highways, and in September - in industrial zones too. In June
the stem of the shoots of introduced woody plants growing in the highway
plantations has more nitrogen content than those growing in the conventional
control zones, while Caragana arborescens
growing in the SPZ of industrial enterprises and highway plantations in the
period of leave fall has more nitrogen in shoots.
Summarizing the results of the analysis received in
both periods of observation we found out that the shoots of most species
studied as in the sanitary-protective zones of industrial enterprises and in
the highway plantations had significantly higher percentage of nitrogen content
in comparison with the conventional control zone.
In our opinion, one reason for the high nitrogen
content may be the absorption of nitrogen-containing pollutants from the air by
leaves. The nitrogen oxides content analysis of air shows the maximum
concentration and the highest indices of annual average concentration in the
areas of research. The analysis of mineral forms of nitrogen in soils permissible
for plants revealed their low content. The correlation between nitrogen content
in the leaves with the concentration of nitric oxide in the air (correlation
coefficient is r = 0.15, significance level is P = 0.049, n = 168) was
calculated.
It should be emphasized that Caragana arborescen revealed a high correlation dependence of these
indices (r = 0.98, Ð = 3.5×10-8). Of course, this type of plant
should be the most widely used in landscaping areas of the city with high
concentrations of nitrogen compounds in the air. The analysis of the relationship between total nitrogen in shoots
and permissive forms of nitrogen for plants in soils showed weak. Of particular note Caragana arborescens for which the
greatest correlation coefficient between the content of total nitrogen in
leaves and nitrate in the soil was set (r = 0.78, Ð < 0.05).
The analysis of the potassium content in the one year
old structural parts of shoots showed the increase in the content of this
element in the leaves of Betula pendula and Salix caprea growing in the highway plantations in June in
comparison with those growing in the conventional control zones (Table 2). The
increasing concentration of potassium in leaf blades of Tilia cordata, Sorbus
aucuparia and Rosa majalis, growing
in the plantations of SPZ of industrial plants and highway plantations is
observed during the leaf fall period.
In the same
types of plantations in stem part of the shoot of Betula pendula, Tilia cordata and Sorbus aucuparia in both periods of observation the potassium
content was higher than in the CCZ. In
Caragana arborescens in both types of
plantings for special purposes, in September, while Malus baccata in both periods of observations the potassium content
in shoots increased in comparison with those growing in the conventional
control zones.
Summarizing the data, we can say that with the
increasing degree of industrial pollution the potassium in the leaves of most
studied species increases significantly, which may be related to changes in
water exchange in plants under water deficit. The phosphorus content in leaves
of introduced species in both periods of observation in the plantations of
industrial zones and in highway plantations is lower than in the conventional
control zones (Table 3). It was not possible to allot the distinct patterns of
change in the phosphorus content in the leaf apparatus of native species. We
received the similar test results on the content of this element in the stem
parts of the shoot. At the same time in the conditions of intensive industrial pollution the stems of Salix caprea, Sorbus aucuparia and Malus
baccata have higher phosphorus content.
Thus, in the conditions of industrial environment the increase in nitrogen and
potassium contents in the structural parts of plants is accompanied by a
decrease in phosphorus concentration, i.e. there is an imbalance in the content
of major mineral elements of plant nutrition in a man-made environment.
Literature:
1.
Barber, S. A. Bioavailability
of nutrients in the soil. Mechanistic approach. M: Agropromizdat, 1988. 376 pp.
2. Bukharina, I. L.,
Povarnitsina, T. M., Vedernikov, K. E.
Ecological and biological characteristics of woody plants in the urban
environment: a monograph. Izhevsk: Izhevsk State Agricultural Academy, 2007. 216 pp.
3. Vasfilov S.P. Possible ways of negative influence of acid gases on plants // General
Biology Magazine, 2003. T. 64. Pp. 146-159.
4.
Vinokurova, R. I.
Regularities of the accumulation and distribution of chemical elements in the
phytomass of spruce-fir plantation zone of mixed forests of the Middle Volga
region: Abstract of Biology PhD dissertation. Yoshkar-Ola, 2003. 273 pp.
5.
Guidelines
for feed analysis /Ed. L.M. Derzhavin. M.: Kolos, 1982. 74 pp.
6.
Sukhareva, T.A., Lukin, N.V. Chemical composition and morphometric characteristics
of the Siberian spruce needles in the Kola Peninsula in the degradation of
forest succession // Forestry. 2004. ¹ 2. Pp. 36-43.
7. Darral N.M.
The effect of air pollutants on physiological processes in plants // Plant.
Cell and Environment. 1989. V. 12. Pp. 1-30.
8. Innes J.L. Influence of air pollution on the foliar
nutrition of conifers in Great Britain // Environ. Pollut. 1995. V. 88. Pp.
183-192.
Table 1 – The nitrogen content in the shoots of woody
plants growing in the city areas of different functional purpose, % of absolutely dry mass (Izhevsk)
Plant species |
Vegetation period
|
Places of plantations |
|||||
CCZ * |
SPZ of industrial
enterprises ** |
Highway plantings |
|||||
Leaves |
Stems |
Leaves |
Stems |
Leaves |
Stems |
||
Betula pendula Roth. |
June |
2.51 |
1.29 |
2.72 |
1.73 |
3.07 |
1.69 |
September |
0.68 |
0.77 |
0.63 |
2.82 |
0.61 |
2.62 |
|
Acer negundo
L. |
June |
2.41 |
2.13 |
3.32 |
2.23 |
4.24 |
2.45 |
September |
2.41 |
0.94 |
1.33 |
1.24 |
1.30 |
1.77 |
|
Populus balsamifera L |
June |
1.87 |
2.27 |
2.92 |
1.54 |
2.96 |
2.92 |
September |
1.87 |
1.71 |
1.47 |
1.39 |
0.94 |
1.37 |
|
Tilia cordata Mill. |
June |
3.05 |
1.63 |
3.20 |
1.58 |
3.19 |
2.13 |
September |
0.91 |
2.50 |
1.50 |
2.29 |
0.67 |
1.19 |
|
Salix caprea
L. |
June |
2.57 |
1.36 |
2.69 |
1.97 |
3.20 |
1.92 |
September |
1.07 |
1.47 |
0.96 |
1.76 |
1.34 |
1.90 |
|
Sorbus aucuparia
L. |
June |
1.95 |
1.22 |
1.83 |
2.10 |
1.72 |
1.93 |
September |
0.99 |
0.38 |
0.90 |
2.04 |
0.71 |
1.52 |
|
Malus baccata (L.) Borkh |
June |
2.03 |
1.79 |
2.49 |
1.79 |
2.56 |
2.30 |
September |
1.00 |
0.75 |
1.13 |
1.49 |
1.09 |
0.60 |
|
Rosa majalis Herrm. |
June |
4.14 |
1.31 |
2.30 |
1.15 |
2.48 |
1.70 |
September |
0.79 |
2.02 |
1.81 |
1.42 |
1.15 |
1.62 |
|
Caragana arborescens Lam. |
June |
3.19 |
3.66 |
2.48 |
3.16 |
3.35 |
3.35 |
September |
0.01 |
0.01 |
2.00 |
1.78 |
3.05 |
2.36 |
Notes. *CCZ – conditional control zone; **SPZ – sanitary-protective zones
of industrial enterprises. LSD05
for leaves = 0.4; for stems = 0.2.
Table 2 – The
potassium content in the shoots of woody plants growing in the city areas of
different functional purpose, % of
absolutely dry mass (Izhevsk)
Plant species |
Vegetation period
|
Places of plantations |
|||||
CCZ* |
SPZ of industrial
enterprises** |
Highway plantings |
|||||
Leaves |
Stems |
Leaves |
Stems |
Leaves |
Stems |
||
Betula pendula Roth. |
June |
1.27 |
0.37 |
1.27 |
0.41 |
3.07 |
0.47 |
September |
0.56 |
0.25 |
1.57 |
0.37 |
1.24 |
0.38 |
|
Acer negundo
L. |
June |
1.81 |
0.83 |
2.42 |
0.75 |
1.90 |
0.83 |
September |
3.79 |
0.89 |
1.95 |
0.54 |
2.16 |
0.79 |
|
Populus balsamifera L |
June |
2.22 |
0.91 |
1.97 |
0.89 |
2.40 |
0.74 |
September |
1.56 |
0.63 |
2.72 |
0.61 |
1.51 |
0.77 |
|
Tilia cordata Mill. |
June |
2.34 |
0.50 |
1.77 |
0.66 |
2.08 |
0.66 |
September |
0.97 |
0.51 |
2.41 |
0.64 |
2.84 |
0.58 |
|
Salix caprea
L. |
June |
1.35 |
0.46 |
1.85 |
0.59 |
2.58 |
0.80 |
September |
1.37 |
0.82 |
1.42 |
0.62 |
2.93 |
0.77 |
|
Sorbus aucuparia
L. |
June |
1.79 |
0.42 |
1.38 |
0.57 |
0.92 |
0.57 |
September |
0.70 |
0.36 |
1.23 |
0.48 |
1.70 |
0.51 |
|
Malus baccata (L.) Borkh |
June |
2.17 |
0.55 |
1.96 |
0.80 |
1.85 |
0.92 |
September |
0.97 |
0.30 |
2.26 |
0.42 |
2.63 |
0.62 |
|
Rosa majalis Herrm. |
June |
2.03 |
0.57 |
1.28 |
0.86 |
1.23 |
0.75 |
September |
0.93 |
0.52 |
1.11 |
0.49 |
1.17 |
0.42 |
|
Caragana arborescens Lam. |
June |
2.18 |
8.41 |
1.58 |
4.86 |
2.82 |
0.86 |
September |
0.79 |
0.33 |
1.19 |
0.69 |
1.70 |
0.73 |
Notes. *CCZ – conventional
control zone; **SPZ – sanitary-protective zones of industrial enterprises. LSD05
for leaves = 0.10; for stems = 0.20.
Table
3 – The phosphorus content in the
shoots of woody plants growing in the city areas of different functional
purpose, % of absolutely dry mass
(Izhevsk)
Plant species |
Vegetation period
|
Places of plantations |
||||||
CCZ* |
SPZ of industrial
enterprises** |
Highway plantings |
||||||
Leaves |
Stems |
Leaves |
Stems |
Leaves |
Stems |
|||
Betula pendula Roth. |
June |
0.65 |
0.18 |
0.53 |
0.41 |
0.88 |
0.34 |
|
September |
0.37 |
0.14 |
0.70 |
0.32 |
0.22 |
0.28 |
||
Acer negundo
L. |
June |
1.03 |
0.55 |
0.75 |
0.56 |
0.89 |
0.50 |
|
September |
0.38 |
0.79 |
0.32 |
0.31 |
0.28 |
0.39 |
||
Populus balsamifera L |
June |
0.70 |
0.56 |
0.49 |
0.48 |
0.50 |
0.53 |
|
September |
0.38 |
0.80 |
0.72 |
0.35 |
0.18 |
0.39 |
||
Tilia cordata Mill. |
June |
0.59 |
0.42 |
0.82 |
0.49 |
0.92 |
0.52 |
|
September |
0.33 |
0.36 |
0.45 |
0.67 |
0.11 |
0.36 |
||
Salix caprea
L. |
June |
0.50 |
0.47 |
0.60 |
0.48 |
0.56 |
0.55 |
|
September |
0.46 |
0.10 |
0.23 |
0.28 |
0.48 |
0.59 |
||
Sorbus aucuparia
L. |
June |
0.81 |
0.23 |
0.61 |
0.37 |
1.42 |
0.28 |
|
September |
0.45 |
0.21 |
0.67 |
0.63 |
0.72 |
0.47 |
||
Malus baccata (L.) Borkh |
June |
1.07 |
0.43 |
0.67 |
0.28 |
0.74 |
0.52 |
|
September |
0.50 |
0.22 |
0.83 |
0.39 |
0.43 |
0.37 |
||
Rosa majalis Herrm. |
June |
1.46 |
0.33 |
0.86 |
0.37 |
0.57 |
0.32 |
|
September |
0.79 |
0.76 |
0.40 |
0.80 |
0.19 |
0.46 |
||
Caragana arborescens Lam. |
June |
0.50 |
0.77 |
0.34 |
0.75 |
0.59 |
0.45 |
|
September |
0.25 |
1.34 |
0.14 |
0.36 |
0.25 |
0.79 |
||
Notes. *CCZ – conventional control zone; **SPZ – sanitary-protective zones of industrial enterprises. LSD05 for leaves = 0.10; for stems = 0.10.