Radionuclide biosorption by the aquatic plants of Pistia stratiotes
The activity of leaves and roots of Pistia stratiotes from the Seversky Donets river has been measured. The visible activity of ¹³¹I in roots of plant is found. The content estimate of ¹³¹I in water of Seversky Donets river before extraction of samples of a hydrophyte gives value exceeding 1 Bk/l. T...
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| Опубліковано в: : | Вопросы атомной науки и техники |
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| Дата: | 2014 |
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Національний науковий центр «Харківський фізико-технічний інститут» НАН України
2014
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| Назва журналу: | Digital Library of Periodicals of National Academy of Sciences of Ukraine |
| Цитувати: | Radionuclide biosorption by the aquatic plants of Pistia stratiotes / N.P. Dikiy, A.N. Dovbnya, Yu.V. Lyashko, D.V. Medvedev, E.P. Medvedeva, M.A. Botova, N.P. Khlapova, I.D. Fedorets // Вопросы атомной науки и техники. — 2014. — № 5. — С. 50-53. — Бібліогр.: 14 назв. — англ. |
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Digital Library of Periodicals of National Academy of Sciences of Ukraine| _version_ | 1860257569316012032 |
|---|---|
| author | Dikiy, N.P. Dovbnya, A.N. Lyashko, Yu.V. Medvedev, D.V. Medvedeva, E.P. Botova, M.A. Khlapova, N.P. Fedorets, I.D. |
| author_facet | Dikiy, N.P. Dovbnya, A.N. Lyashko, Yu.V. Medvedev, D.V. Medvedeva, E.P. Botova, M.A. Khlapova, N.P. Fedorets, I.D. |
| citation_txt | Radionuclide biosorption by the aquatic plants of Pistia stratiotes / N.P. Dikiy, A.N. Dovbnya, Yu.V. Lyashko, D.V. Medvedev, E.P. Medvedeva, M.A. Botova, N.P. Khlapova, I.D. Fedorets // Вопросы атомной науки и техники. — 2014. — № 5. — С. 50-53. — Бібліогр.: 14 назв. — англ. |
| collection | DSpace DC |
| container_title | Вопросы атомной науки и техники |
| description | The activity of leaves and roots of Pistia stratiotes from the Seversky Donets river has been measured. The visible activity of ¹³¹I in roots of plant is found. The content estimate of ¹³¹I in water of Seversky Donets river before extraction of samples of a hydrophyte gives value exceeding 1 Bk/l. The detection of activity of ¹³¹I in roots of Pistia stratiotes can be used for its monitoring in the biosphere. The photoactivation analysis has been used for measuring of element content in leaves and roots of Pistia stratiotes. Accumulation in roots versus leaves of Pistia stratiotes Mn, Co, Ni, Mo, I, Pb and also isotopes ²²⁸Ac, ²¹⁴Pb and ²¹⁴Bi was detected.
Была измерена активность листьев и корней Pistia stratiotes из Северского Донца. Зарегистрирована заметная активность ¹³¹I в корнях растения. Оценка содержания ¹³¹I в воде Северского Донца перед извлечением образцов гидрофита дает значение, превышающее 1 Бк/л. Метод детектирования активности ¹³¹I в корнях Pistia stratiotes может быть использован для мониторинга его в биосфере. Фотоактивационный анализ был использован для измерения содержания элементов в листьях и корнях Pistia stratiotes из Северского Донца. Обнаружено накопление в корнях относительно накопления в листьях Pistia stratiotes Mn, Co, Ni, Mo, I, Pb, а также изотопов ²²⁸Ac, ²¹⁴Bi и ²¹⁴Pb .
Була вимiряна активнiсть листя i корення Pistia stratiotes iз Сiверського Донця. Зареєстрована помiтна активнiсть ¹³¹I у коренях рослини. Оцiнка вмiсту ¹³¹I у водi Сiверського Донця перед витяганням зразкiв гiдрофiта дає значення, яке перевищує 1 Бк/л. Метод детектування активностi ¹³¹I у коренях Pistia stratiotes може бути використаний для монiторiнгу його в бiосферi. Фотоактивацiйний аналiз був використаний для вимiрювання вмiсту елементiв у листках i кореннях Pistia stratiotes iз Сiверського Донця. Виявлено накопичення в коренях вiдносно накопичення в листях Pistia stratiotes Mn, Co, Ni, Mo, I, Pb, а також iзотопiв ²²⁸Ac, ²¹⁴Bi і ²¹⁴Pb.
|
| first_indexed | 2025-12-07T18:51:10Z |
| format | Article |
| fulltext |
RADIONUCLIDE BIOSORPTION BY THE AQUATIC
PLANTS OF PISTIA STRATIOTES
N.P.Dikiy1∗, A.N.Dovbnya1, Yu.V.Lyashko1, D.V.Medvedev1,
E.P.Medvedeva1, M.A.Botova1, N.P.Khlapova2, I.D.Fedorets2
1National Science Center ”Kharkov Institute of Physics and Technology”, 61108, Kharkov, Ukraine
2V.N. Karazin Kharkov National University, 61077, Kharkov, Ukraine
(Received June 31, 2014)
The activity of leaves and roots of Pistia stratiotes from the Seversky Donets river has been measured. The visible
activity of 131I in roots of plant is found. The content estimate of 131I in water of Seversky Donets river before
extraction of samples of a hydrophyte gives value exceeding 1 Bk/l. The detection of activity of 131I in roots
of Pistia stratiotes can be used for its monitoring in the biosphere. The photoactivation analysis has been used
for measuring of element content in leaves and roots of Pistia stratiotes. Accumulation in roots versus leaves of
Pistia stratiotes Mn, Co, Ni, Mo, I, Pb and also isotopes 228Ac, 214Pb and 214Bi was detected.
PACS: 89.60.-k
1. INTRODUCTION
Water contamination by radio nuclides, heavy
metals and industrial pollutants is a very important
problem in the world. Last years the phytotechnolo-
gies are used for contamination removal by plants.
The principal mechanism for contamination uptake
is sorption by roots [1]. The main mechanism in-
volved in biosorption is ion exchange between mono-
valent metals as counter ions present in macrophytes
biomass and heavy metal ion and protons taken up
from water [2]. A review of literature shows that
metals can be removed by inexpensive biological ma-
terials as algae, fungi and bacteria [3, 4].
In 2011 Pistia stratiotes has appeared in the waste
canal of thermal power station-2 which takes places
on the Seversky Donets river near the settlement Es-
har of the Kharkov region. The significant amounts of
Pistia stratiotes have been discovered in the Seversky
Donets river in 2013 year (Fig.1). The water temper-
ature in Seversky Donets river was 25.1◦C in July
2013. The temperature in the waste canal of thermal
power station-2 (0.5 km below the water discharge)
was 30.2◦C. Water plant of Pistia stratiotes is a plant
of warm water aquariums and botanic gardens from
tropical fields from Africa. The facts of the occur-
rence of this water plant in Europe are registered [5].
Most likely, this plant is brought in reservoirs from
decorative ponds and aquariums. The tropical water
plant has appeared in natural reservoirs of medial lat-
itudes for refining of city sewage, waste of factories,
enterprises of the textile industry. This water plant
is used also in a combination to other water plants
for sewage treatment of pig-breeding complexes.
The given water plant is a plant-introdutsent (im-
migrant). This plant grows and multiplies rapidly
and also intensively absorbs almost all biogenic ele-
ments and their compounds from water. Efficacy of
compound cleaning is ∼95%. The cleared water is
used for watering of agricultural crops.
Fig.1. Surface of the Seversky Dontets covered by
Pistia stratiotes
Last years it is observed dilating of a geographic
range of diffusion and acceleration invasion processes
of Pistia stratiotes. It is promoted processes of warm-
ing of a climate observed in last year’s, and also
the thermal contamination of water objects. The
Pistia stratiotes can hibernate if water does not freeze
[6] in the winter.
Strong development of Pistia stratiotes can cause
of shadowing of the water areas of the river. In such
conditions the vegetation in the water will die off and
the hydrochemical state of the river, first of all an
∗Corresponding author E-mail address: ndikiy@kipt.kharkov.ua
50 ISSN 1562-6016. PROBLEMS OF ATOMIC SCIENCE AND TECHNOLOGY, 2014, N5 (93).
Series: Nuclear Physics Investigations (63), p.50-53.
oxygen regimen to worsen. It can cause local (or
mass) destruction of fish and other hydrobionts that
will lead to the further deterioration of river water.
The Pistia stratiotes is object of intensive study
because of a series of unique its properties. The Pistia
stratiotes produce a big amounts of Ca oxalate crys-
tals in specialized cells called crystal idioblasts [7]. It
has been determined that Ca2+ channels play a key
role in Ca oxalate crystal formation in this plants.
Table 1. Concentration of radioactive isotopes in
the coals of Donetsk basin used on the Zmievsky
state district power station, Bq/kg [8, 9]
Coal type 226Ra 232Th 40K
Anthracite culm 17 ≤5 226
sludge 30.3 17.3 305
Ordinary coal 39.2 52.6 684
Donetsk coal [8] 18.5...107
Donetsk coal [9] 22.2...51.8
By thermal power station operation the greatest
contribution to environmental contamination bring
such radio nuclides, as 210Pb (∼25%), 232Th (∼30%),
228Th (∼20%), 238U (∼10%), 40K (∼2%), 226Ra
(∼2%), 228Ra (∼1.0%). Concentration of natural ra-
dio nuclides in the coals used on the Zmievsky state
district power station is presented in Table 1.
Table 2. Atmospheric isotopes release from NPP in
Ukraine (the data of project INPRO ENV), Bq/y
isotope Bq/year isotope Bq/year
1H 1.50·1011 89Sr 1.10·106
47Ar 1.70·1010 90Sr 1.50·105
51Cr 2.60·106 95Zr 5.30·105
54Mn 1.30·106 95Nb 4.60·105
59Fe 5.50·105 110mAg 4.50·105
58Co 8.50·105 133Xe 6.10·1012
60Co 2.30·106 135Xe 1.10·1012
85Kr 5.10·1011 131I 4.80·107
85mKr 4.60·1011 134Cs 7.10·105
87Kr 8.40·1010 137Cs 1.50·106
88Kr 1.90·1011
Nuclear power plants (NPP) also cause releasing
of radioactive isotopes into the atmosphere (Table 2).
Thereupon some isotopes represent danger at incor-
poration into a human body. Owing to the high rate
of metabolic processes in children the 131I is espe-
cially dangerous. The transport of 131I through the
grass → cow → milk → man food chain is caused pri-
marily by the interception efficiency of typical pasture
vegetation for the radionuclide, the unique secretion
of iodine into milk by the cow, and the rapidity with
which milk is processed and reaches the consumer.
The aim of the present study is to investigate the
mechanism of the simultaneous removal of metals de-
rived from industrial activities from dead freshwater
macrophytes and the creation of a method of moni-
toring of 131I in biosphere by means of detection of
its activity in roots of Pistia stratiotes.
2. MATERIALS AND METHODS
Samples of Pistia stratiotes from the Seversky
Donets river were investigated. Samples Pistia
stratiotes were taken in October, 2013. Investigation
of radionuclide activity in dry native samples (roots,
leaf) of Pistia stratiotes was conducted using Ge(Li)-
detector with energy resolution of 3.2 keV at the en-
ergy of 1333 keV. Time of activity measurements of
samples weighing up to 0.5 kg was 6...12 hours. Nat-
ural isotopes – 40K, 235,238U, 232Th families, cosmic
– 7Be, and anthropogenesis - 137Cs and 131I were de-
tected in native samples. The errors of measurements
were from 3 to 25%. Activation of samples has been
conducted with use brake radiation of the linear ac-
celerator electrons NSC KIPT with electron energy
23 MeV and a current 500 µA. Activation of samples
was carried out on air, the temperature of samples in
the course of activation did not exceed 40◦C. Trace
elements Zn, Ni, Ca, I, Mn, Rb, Zr, Na and oth-
ers were determined. The limit of detection elements
for photoactivation analysis was 10−4...10−7wt. The
ashing of samples was spent at temperature 700◦C.
3. RESULTS AND DISCUSSION
In Fig.2 the γ-spectrum of the initial sample of the
leaf of Pistia stratiotes is presented. In γ-spectrum
of investigating sample the various elements are ob-
served (226Ra, 7Be, 214Pb, 208Tl, 137Cs, 40K and oth-
ers) (Table 3). Special interest causes 7Be (T1/2=53
days). 7Be is generated by cosmic rays in the up-
per troposphere and stratosphere, and is a tracer of
downward aerosol transport.
400 800 1200 1600
101
102
103
214Bi 609 keV
228Ac 969 keV
co
un
ts
channel
40K 1461 keV
214Bi
1764 keV
228Ac 911 keV
511 keV
7Be 478 keV
131I 364 keV
Fig.2. Energy spectrum of own radioactivity of leaf
of Pistia stratiotes
It is especially necessary to note detection 131I.
It arrives into the water of the river in the course of
deposition of aerosols of the working NPP. The high
coefficient of accumulation Pistia stratiotes iodine al-
lows to register isotope 131I (see Table 3). Consid-
erable quantity of iodine collects by roots of Pistia
stratiotes. Therefore the possibility of determination
of 131I by means of activity of Pistia stratiotes allows
to carry out radioiodine monitoring in an environ-
ment.
In Fig.3 the gamma spectrum of the irradiated
sample of root of Pistia stratiotes is given. A consid-
erable quantity of elements (Table 4) were registered.
51
Table 3. The activity of root and leaf of Pistia
stratiotes and activity ratio of root vs leaf (dry wt.)
root, Bq/kg leaf, Bq/kg root vs leaf
40K 604 2573 0.23
131I 2032 153 13.3
7Be 138 287 0.48
226Ra 119 23.9 4.98
228Ac 81.3 7.65 10.62
214Pb 41.8 2.7 15.50
214Bi 38.1 3.61 10.55
208Tl 10.6 4.41 2.41
212Pb 9.56 2.15 4.45
137Cs 1.3 0.90 1.14
400 800 1200 1600 2000
101
102
103
104
105
126I 666 keV
co
un
ts
channel
22Na 1275 keV
47Ca 1297 keV
57Ni 1377 keV
54Mn 835 keV
89Zr 909 keV
511 keV
126I 389 keV
47Sc 159 keV
Fig.3. Energy spectrum of root of Pistia stratiotes
after an irradiation on the electronic accelerator
The content of elements in the leaves and roots of
Pistia stratiotes from Seversky Donets has the singu-
larities. The Seversky Donets river is not pure. We
will note in Pistia stratiotes high enough concentra-
tions of essential elements of Ca and K. The content
of elements in roots of Pistia stratiotes is big due to
accumulation of conventionally essential elements of
Mn, Co, Ni, Mo and I. Also high value of accumula-
tion by roots of Pistia stratiotes toxic elements of Pb,
U and As.
The iodine content in roots of Pistia stratiotes
from the Seversky Doners river is ∼10−4 g/g. As-
suming that the coefficient of accumulation of iodine
by roots of Pistia stratiotes is ∼1000 it is possible
to estimate the iodine content in the water: ∼10−7
g/g [10]. In turn, it is possible to estimate the con-
tent of 129I and 131I. For Europe the attitude 129I/I is
∼10−6 [11]. Hence, the 129I and 131I contents in wa-
ter the Seversky Doners river were ∼10−13 g/g and
∼2 Bk/l, accordingly. The estimate of the content
of 137Cs in water is ∼10−3 Bq/l that coincides with
mean values in Ukraine [12]. The estimate of value of
the ratio of 137Cs/Cs is ∼10−8. The ratio 137Cs/Cs
for leaves of Pistia stratiotes is 27.8 Bq/mg. For ex-
ample, of the most polluted wood in Finland (Kul-
laa, 18.2 kBq/m2) the ratio 137Cs/Cs is 5100 Bq/mg
[13]. The difference between the ratios of 137Cs/Cs is
partly attributable to the different deposition levels
of 137Cs. A positive correlation between the total de-
position of 137Cs and the 137Cs/Cs ratio was observed
for the different sites. However, different concentra-
tions of stable Cs in soil and rivers (e.g. vegetation,
geology, soil type) also affect the 137Cs/Cs ratio.
Table 4. The elements content in root and leaf of
Pistia stratiotes and ratio of elements content in
root versus leaf (dry weight)
root, g/g leaf, g/g ratio root/leaf
Na 1.78·10−2 5.38·10−3 3.32
K 1.99·10−2 8.49·10−2 0.23
Ca 1.75·10−2 2.0·10−2 0.87
Ti 6.01·10−4 1.62·10−4 3.71
Cr 4.32·10−6 5.65·10−5 7.65
Mn 2.03·10−2 7.26·10−4 27.90
Co 2.62·10−5 1.03·10−6 25.44
Ni 9.79·10−5 5.65·10−6 17.32
Zn 7.46·10−4 1.19·10−4 6.27
As 4.95·10−6 7.2·10−7 7.05
Br 6.33·10−6
Rb 1.63·10−5 1.77·10−5 0.92
Sr 4.25·10−4 5.87·10−4 0.72
Y 3.38·10−6 4.96·10−6 6.81
Zr 1.19·10−5 4.79·10−6 2.48
Nb 2.2·10−6 1.37·10−6 1.60
Mo 9.93·10−6 6.26·10−7 15.86
I 1.55·10−4 1.11·10−5 14.02
Cs 3.25·10−8
Ce 3.94·10−6 1.67·10−6 2.37
Pb 1.28·10−4 5.13·10−6 24.96
U 3.74·10−6 5.27·10−7 7.10
Table 5. The ratio of elements content of ash vs
leaf and root (dry weight) of Pistia stratiotes
elem. ash vs
leaf
ash vs
root
elem. ash vs
leaf
ash vs
root
Na 4.2 3.02 Br 3.4 nd
Ca 4.06 3.39 Rb 4.19 2.68
Ti 4.48 2.87 Sr 4.11 2.68
Cr 4.0 3.08 Zr 3.73 3.78
Mn 4.15 3.08 Nb 2.21 2.24
Ni 3.75 3.16 Mo 4.26 2.48
Zn 4.51 3.31 I 3.87 1.73
As 4.6 2.69 Ce 3.05 3.03
Pb 3.10 2.61 U 4.05 3.65
In Table 5 the ratio of element content in ashes
versus initial Pistia stratiotes (dry weight) are given.
These ratios for leaves were ∼4 and ∼3 for roots.
Considerable calcium quantity is caused the for-
mation of compounds of type of KAlSi3O8, SiO2,
Fe2O3 and others which cause the formation of small
amounts of flying compounds [14]. That in turn is
the positive factor at use of Pistia stratiotes as an
absorption material for heavy metals, Sr, As and I.
4. CONCLUSIONS
1. The 131I activity of one of dangerous radioiso-
topes from NPP has been registered in roots of Pistia
stratiotes by γ-spectrometry.
2. Accumulation of Mn, Co, Ni, Mo, I, Pb and
isotopes 228Ac, 214Pb and 214Bi has been detected in
52
roots and leaves of Pistia stratiotes (their ratios were
counted).
3. Photoactivation analysis possesses advantages
at the determination of sorption of radioisotopes by
plants.
4. The developed methods allow carrying out ra-
dioisotopes monitoring in the biosphere.
References
1. H.Denny, D.Wilkins. Zinc tolerance in Betula
spp.II. Microanalyticalstudies of zinc uptake into
root tissues // New Phyt. 1987, v. 106, p. 525-534.
2. P.Miretzky, A. Saralegui, A.F.Cirelli. Simultane-
ous heavy metal removal mechanism by dead ma-
crophytes // Chemosphere 2006, v. 62 p. 247-254.
3. Y.Ho, J. Porter, G.McKay. Equilibrium
isotherm studies for sorption of divalent metal
ions onto peat: Cu, Ni and Pb single component
systems // Water Air Soil Pollut. 2002, v. 141,
p. 1-33.
4. P.Kaewarn. Biosorption Cu (II) form aqueous so-
lution by pre-treatrd biomass of marine algae //
Chemosphere 2002, v. 47, p. 1081-1085.
5. V.V. Soloveva. Floristic finds and unusual occur-
rences bioecologists of hydrophytes in ponds of
Samara // Phytodiversity of the Eastern Europe
2006, N.2, p. 174-180 (in Russian).
6. A.V. Shcherbakov, S.P.Mayorov. Water adven-
tive plants of the Moscow region // Bull. Udmurt
univ., Biol. Sci. Earth. 2013, iss. 2, p. 57-61.
7. G.M.Volk, L.J.Goss, V.R. Franceschi. Calcium
Channels are Involved in Calcium Oxalate Crys-
tal Formation in Specialized Cells of Pistia stra-
tiotes // Annals Botany. 2004, v. 93, p. 741-753.
8. V.A.Knizhnikov, R.M.Barhudarov. Relative es-
timate of radiative danger to the population from
outliers in atmosphere of thermal and atomic sta-
tions // AE 1977, v. 43, p. 191-196 (in Russian).
9. L.A. Ilin, V.A.Knizhnikov, N.K. Shandala, et al.
Oncologic ”price” of thermal and atomic energy,
Moscow: ”Medicine”, 2001, 240 p. (in Russian).
10. Q. Lu, Z.L.He, D.A.Graetz et al. Uptake and dis-
tribution ofmetals bywater lettuce (P. stratiotes)
//Environ. Sci. Pollut. Res. 2011, v.18, p.978-986.
11. J.E.Moran. Sources of I and 129I in rivers // Wa-
ter Resources Research. 2002, v. 38, N.8, p. 1149.
12. G.D.Kovalenko. Radioecology Ukraine, Kharkov:
”PH INGEK”, 2008, 264 p. (in Russian).
13. S.Yoshida, Y.Muramatsu, M. Steiner, et al. Re-
lationship between radiocesium and stable ce-
sium in plants and mushrooms collected from for-
est ecosystems with different contamination lev-
els // IRPA-10, 2000, p. 11-244.
14. M.K.Misra, K.W.Ragland, A.J. Baker. Wood
ash composion as a function of furnace tem-
perature // Biomass Bioenergy, 1993, v. 4, N.2,
p. 103-116.
ÁÈÎÑÎÐÁÖÈßÐÀÄÈÎÍÓÊËÈÄÎÂÂÎÄÍÛÌÈÐÀÑÒÅÍÈßÌÈPISTIASTRATIOTES
Í.Ï.Äèêèé, A.Í.Äîâáíÿ, Þ.Â.Ëÿøêî, Ä.Â.Ìåäâåäåâ, Å.Ï.Ìåäâåäåâà, Ì.À.Áîòîâà,
Í.Ï.Õëàïîâà, È.Ä.Ôåäîðåö
Áûëà èçìåðåíà àêòèâíîñòü ëèñòüåâ è êîðíåé Pistia stratiotes èç Ñåâåðñêîãî Äîíöà. Çàðåãèñòðèðîâàíà
çàìåòíàÿ àêòèâíîñòü 131I â êîðíÿõ ðàñòåíèÿ. Îöåíêà ñîäåðæàíèÿ 131I â âîäå Ñåâåðñêîãî Äîíöà ïå-
ðåä èçâëå÷åíèåì îáðàçöîâ ãèäðîôèòà äàåò çíà÷åíèå, ïðåâûøàþùåå 1 Áê/ë. Ìåòîä äåòåêòèðîâàíèÿ
àêòèâíîñòè 131I â êîðíÿõ Pistia stratiotes ìîæåò áûòü èñïîëüçîâàí äëÿ ìîíèòîðèíãà åãî â áèîñôåðå.
Ôîòîàêòèâàöèîííûé àíàëèç áûë èñïîëüçîâàí äëÿ èçìåðåíèÿ ñîäåðæàíèÿ ýëåìåíòîâ â ëèñòüÿõ è êîð-
íÿõ Pistia stratiotes èç Ñåâåðñêîãî Äîíöà. Îáíàðóæåíî íàêîïëåíèå â êîðíÿõ îòíîñèòåëüíî íàêîïëåíèÿ
â ëèñòüÿõ Pistia stratiotes Mn, Co, Ni, Mo, I, Pb, à òàêæå èçîòîïîâ 228Ac, 214Bi è 214Pb.
ÁIÎÑÎÐÁÖIß ÐÀÄIÎÍÓÊËIÄIÂ ÂÎÄÍÈÌÈ ÐÎÑËÈÍÀÌÈ PISTIASTRATIOTES
Ì.Ï.Äèêèé, A.Ì.Äîâáíÿ, Þ.Â.Ëÿøêî, Ä.Â.Ìåäâåä¹â, Î.Ï.Ìåäâåä¹âà, Ì.Î.Áîòîâà,
Í.Ï.Õëàïîâà, I.Ä.Ôåäîðåöü
Áóëà âèìiðÿíà àêòèâíiñòü ëèñòÿ i êîðåííÿ Pistia stratiotes iç Ñiâåðñüêîãî Äîíöÿ. Çàðå¹ñòðîâàíà ïîìiòíà
àêòèâíiñòü 131I ó êîðåíÿõ ðîñëèíè. Îöiíêà âìiñòó 131I ó âîäi Ñiâåðñüêîãî Äîíöÿ ïåðåä âèòÿãàííÿì
çðàçêiâ ãiäðîôiòà ä๠çíà÷åííÿ, ÿêå ïåðåâèùó¹ 1 Áê/ë. Ìåòîä äåòåêòóâàííÿ àêòèâíîñòi 131I ó êîðåíÿõ
Pistia stratiotes ìîæå áóòè âèêîðèñòàíèé äëÿ ìîíiòîðiíãó éîãî â áiîñôåði. Ôîòîàêòèâàöiéíèé àíàëiç áóâ
âèêîðèñòàíèé äëÿ âèìiðþâàííÿ âìiñòó åëåìåíòiâ ó ëèñòêàõ i êîðåííÿõ Pistia stratiotes iç Ñiâåðñüêîãî
Äîíöÿ. Âèÿâëåíî íàêîïè÷åííÿ â êîðåíÿõ âiäíîñíî íàêîïè÷åííÿ â ëèñòÿõ Pistia stratiotes Mn, Co, Ni,
Mo, I, Pb, à òàêîæ içîòîïiâ 228Ac, 214Bi i 214Pb.
53
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| id | nasplib_isofts_kiev_ua-123456789-80478 |
| institution | Digital Library of Periodicals of National Academy of Sciences of Ukraine |
| issn | 1562-6016 |
| language | English |
| last_indexed | 2025-12-07T18:51:10Z |
| publishDate | 2014 |
| publisher | Національний науковий центр «Харківський фізико-технічний інститут» НАН України |
| record_format | dspace |
| spelling | Dikiy, N.P. Dovbnya, A.N. Lyashko, Yu.V. Medvedev, D.V. Medvedeva, E.P. Botova, M.A. Khlapova, N.P. Fedorets, I.D. 2015-04-18T09:57:23Z 2015-04-18T09:57:23Z 2014 Radionuclide biosorption by the aquatic plants of Pistia stratiotes / N.P. Dikiy, A.N. Dovbnya, Yu.V. Lyashko, D.V. Medvedev, E.P. Medvedeva, M.A. Botova, N.P. Khlapova, I.D. Fedorets // Вопросы атомной науки и техники. — 2014. — № 5. — С. 50-53. — Бібліогр.: 14 назв. — англ. 1562-6016 PACS: 89.60.-k https://nasplib.isofts.kiev.ua/handle/123456789/80478 The activity of leaves and roots of Pistia stratiotes from the Seversky Donets river has been measured. The visible activity of ¹³¹I in roots of plant is found. The content estimate of ¹³¹I in water of Seversky Donets river before extraction of samples of a hydrophyte gives value exceeding 1 Bk/l. The detection of activity of ¹³¹I in roots of Pistia stratiotes can be used for its monitoring in the biosphere. The photoactivation analysis has been used for measuring of element content in leaves and roots of Pistia stratiotes. Accumulation in roots versus leaves of Pistia stratiotes Mn, Co, Ni, Mo, I, Pb and also isotopes ²²⁸Ac, ²¹⁴Pb and ²¹⁴Bi was detected. Была измерена активность листьев и корней Pistia stratiotes из Северского Донца. Зарегистрирована заметная активность ¹³¹I в корнях растения. Оценка содержания ¹³¹I в воде Северского Донца перед извлечением образцов гидрофита дает значение, превышающее 1 Бк/л. Метод детектирования активности ¹³¹I в корнях Pistia stratiotes может быть использован для мониторинга его в биосфере. Фотоактивационный анализ был использован для измерения содержания элементов в листьях и корнях Pistia stratiotes из Северского Донца. Обнаружено накопление в корнях относительно накопления в листьях Pistia stratiotes Mn, Co, Ni, Mo, I, Pb, а также изотопов ²²⁸Ac, ²¹⁴Bi и ²¹⁴Pb . Була вимiряна активнiсть листя i корення Pistia stratiotes iз Сiверського Донця. Зареєстрована помiтна активнiсть ¹³¹I у коренях рослини. Оцiнка вмiсту ¹³¹I у водi Сiверського Донця перед витяганням зразкiв гiдрофiта дає значення, яке перевищує 1 Бк/л. Метод детектування активностi ¹³¹I у коренях Pistia stratiotes може бути використаний для монiторiнгу його в бiосферi. Фотоактивацiйний аналiз був використаний для вимiрювання вмiсту елементiв у листках i кореннях Pistia stratiotes iз Сiверського Донця. Виявлено накопичення в коренях вiдносно накопичення в листях Pistia stratiotes Mn, Co, Ni, Mo, I, Pb, а також iзотопiв ²²⁸Ac, ²¹⁴Bi і ²¹⁴Pb. en Національний науковий центр «Харківський фізико-технічний інститут» НАН України Вопросы атомной науки и техники Ядерно-физические методы и обработка данных Radionuclide biosorption by the aquatic plants of Pistia stratiotes Биосорбция радионуклидов водными растениями Pistiastratiotes Бiосорбцiя радiонуклiдiв водними рослинами Pistiastratiotes Article published earlier |
| spellingShingle | Radionuclide biosorption by the aquatic plants of Pistia stratiotes Dikiy, N.P. Dovbnya, A.N. Lyashko, Yu.V. Medvedev, D.V. Medvedeva, E.P. Botova, M.A. Khlapova, N.P. Fedorets, I.D. Ядерно-физические методы и обработка данных |
| title | Radionuclide biosorption by the aquatic plants of Pistia stratiotes |
| title_alt | Биосорбция радионуклидов водными растениями Pistiastratiotes Бiосорбцiя радiонуклiдiв водними рослинами Pistiastratiotes |
| title_full | Radionuclide biosorption by the aquatic plants of Pistia stratiotes |
| title_fullStr | Radionuclide biosorption by the aquatic plants of Pistia stratiotes |
| title_full_unstemmed | Radionuclide biosorption by the aquatic plants of Pistia stratiotes |
| title_short | Radionuclide biosorption by the aquatic plants of Pistia stratiotes |
| title_sort | radionuclide biosorption by the aquatic plants of pistia stratiotes |
| topic | Ядерно-физические методы и обработка данных |
| topic_facet | Ядерно-физические методы и обработка данных |
| url | https://nasplib.isofts.kiev.ua/handle/123456789/80478 |
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