- •It is recommended for publishing as a study aid by the Editorial Board of Tomsk Polytechnic University
- •Соntents
- •Introduction
- •1. History of knowledge development about biosphere chemical composition and scale of its transformations
- •Global emission of chemical elements (thous.T/year) (according to V.V. Yermakov, 2003)
- •2. Key approachers to classification of chemical elements
- •Fig. 1 Classification of elements in human organism in terms of abundance and use (Underwood e., 1962)
- •Vital elements in composition of organisms (according to а. Lenindger)
- •Content of some elements in plants, animal and human organisms, mg/kg
- •Concentration of cations in marine water and organisms liquids of some mammals and birds, mg/kg (Bgatov а.V., 1999, with recalculations of Ignatova т.N., 2009)
- •Biogenetic classification of elements
- •3. Factors and processes element composition formation of living matter
- •4. Regional aspects of biogeochemistry
- •4.1. Conditions of the Natural Environment Components According to Ecological-Geochemical Monitoring and Population Health Data (Tomsk Region)
- •Geochemical specific characteristics in districts of Tomsk region to maximum element concentration in pathologically changed thyroid glands (relative to regional monitoring)
- •Different diseases of separate thyroid gland pathology types in districts of Tomsk region per 1000 persons (during 5 years)
- •4.2. Element composition of human organs and tissues
- •Contemporary estimation of the environmental pathology (wt. %) and trace elements (mg/kg) in a human body (From Ulf Lindh, 2005 with changes)
- •Comparative estimation of element analysis results obtained by inaa method with published data of domestic and international standards
- •4.3. Biogeochemistry of uranium and thorium
- •Thorium content in the plants of the Large Vasyugan marsh, mg/kg (dm) (“Geochemistry…”, 2002)
- •4.4. Rare earth element in human organs and tissues
- •4.5. Element content in children hair samples
- •Comparative analysis of evaluation level of the chemical element concentration in human hair (mg/kg, dry weight)
- •Comparative data of children hair composition (mg/kg, dry weight) from different regions of Russia, Belorussia and Kazakhstan
- •Geochemical specification of population hair in Tomsk oblast and other regions (n – number of samples)
- •Conclusion
- •References
- •Geochemistry of living organisms
- •Published in author’s version
- •Printed in the tpu Publishing House in full accordance with the quality of the given make up page
Comparative analysis of evaluation level of the chemical element concentration in human hair (mg/kg, dry weight)
Element |
Average element content |
||||
Tomsk oblast Mean ±Std Err (N=538) |
1 |
2 |
3 |
4 |
|
Na |
603 ± 25 |
650 |
12,9 ± 0,75 |
147 |
165 |
Ca |
2626 ± 99 |
3200 |
678 ± 161 |
750 |
770 |
Sc |
0,05 ± 0,004 |
n \ d |
0,0098 ±0,0015 |
0,0014 |
0,0079 |
Cr |
4,7 ± 0,4 |
3,8 |
1,09 ±0,1 |
0,167 |
0,558 |
Fe |
522 ± 49 |
4300 |
87 ± 20,5 |
9,6 |
33,77 |
Co |
0,26 ± 0,02 |
0,00295 |
0,13 ± 0,014 |
0,013 |
0,0762 |
Zn |
182 ± 3,5 |
260 |
n \ d |
142 |
n \ d |
As |
0,7 ± 0,03* |
2,0 |
n \ d |
0,085 |
0,158 |
Se |
0,87 ± 0,15 |
n \ d |
0,5 ± 0,7 |
0,830 |
n \ d |
Br |
12,6 ± 1,7 |
12,5 |
2,37 ± 0,016 |
37 |
6,82 |
Rb |
1,9 ± 0,4* |
23,5 |
1,97 ± 0,02 |
0,093 |
0,445 |
Sr |
14,3 ± 0,7* |
0,05 |
n \ d |
1,20 |
n \ d |
Ag |
0,47 ± 0,6 |
3,45 |
0,18 ± 0,007 |
0,231 |
0,164 |
Sb |
0,12 ± 0,07 |
6,5 |
0,1 ± 0,014 |
0,022 |
0,134 |
Cs |
0,08 ± 0,004* |
n \ d |
n \ d |
0,00067 |
0,708 |
Ba |
15,4 ± 0,67* |
5,0 |
n \ d |
0,640 |
4,901 |
La |
0,27 ± 0,01 |
n \ d |
0,085 ± 0,02 |
0,035 |
0,043 |
Ce |
0,4 ± 0,03 |
n \ d |
0,18 ± 0,002 |
0,039 |
0,057 |
Sm |
0,1 ± 0,01 |
n \ d |
0,009 |
n \ d |
n \ d |
Eu |
0,02± 0,001* |
n \ d |
n \ d |
n \ d |
n \ d |
Tb |
0,01 ± 0,0004* |
n \ d |
n \ d |
n \ d |
n \ d |
Yb |
0,05 ± 0,01* |
n \ d |
n \ d |
n \ d |
n \ d |
Lu |
0,008± 0,0005* |
n \ d |
n \ d |
n \ d |
n \ d |
Hf |
0,06 ± 0,004 |
n \ d |
n \ d |
0,0054 |
n \ d |
Ta |
0,04 ± 0,001* |
n \ d |
n \ d |
0,0044 |
n \ d |
Au |
0,06 ± 0,01 |
0,08 |
0,02 |
0,030 |
0,0662 |
Hg |
3,25 ± 0,4 |
6,0 |
n \ d |
0,261 |
3,313 |
Th |
0,07 ± 0,01 |
n \ d |
n \ d |
0,0013 |
n \ d |
U |
0,17 ± 0,01 |
n \ d |
n \ d |
0,057 |
n \ d |
Notes: N – sample number; n\ d. – no data; * -average calculation based on samples, where 50% of the values are less than determination range; 1 - Man. Medico-biological data, 1977; 2 - Saet U. E. et al., 1990 – children living in non-black earth zone of Russia; 3 - Rodushkin I., Axelsson M.D., 2000. – adults living in north-east Sweden (N=114); 4 - Ward N.I. et. al., 1987. – adults and children from Sophia, Bulgaria (N=36).
There is a rather high U concentration in children hair samples from Irkutsk oblast and Pavlodar, Kazakhstan. The reason of which could be the natural peculiarities of these regions. Another important factor is the significantly low index ratio of Th to U in these regions (Th/U = 0.06), while in other regions it includes 0.4 – 0.5.
The regional hair differences in Tomsk oblast is reflected in its geochemical series (Table 4). In comparing the concentration coefficient, obtained in the normalization of average values, to indexes from reference data (Saet U. E. et al., 1990), it has been observed that there is a significant difference in obtained values for several elements which, in its turn, underlines the fact of various sources of this or that element.
The geochemical element spectrum in the hair of children from Tomsk oblast is rather diverse, and the concentration coefficient is more than 2 for practically the whole series. This fact proves the assumption that the hair element content in the population of Tomsk region is complex and predominantly includes specific technogenic features.
The geochemical series for Tomsk and Cheljabinsk oblasts are analogous (Table 4). Both series, i.e elements with coefficient more than 1, start with sodium and end in stibium. At the same time, there exist identical elements for both regions Na, Sm, La, Br, Co, Ca and Au, while the following elements are only characteristic of Tomsk oblast Fe, Sc, Cr, Ag, Ce, and where the series Sc is only found in Tomsk oblast. The same sources of an element explain such a common geochemical association of these two different regions.
The element spectrum within the geochemical series in the children hair from Irkutsk oblast mainly reflects natural component content. Based on comparative data of some authors (Saet U. E. et al., 1990), it should be noted that a high Fe content in hair is specific for Tomsk and Irkutsk oblasts, while selenium content only for Irkutsk oblast and Kazakhstan. High Ag concentration in investigated hair is a specific feature for Kazakhstan.
Tomsk oblast was conventionally divided into five zones in accordance to the extent of the technogenic environment transformations: (1) area with high extent of technogenic environment transformations; (2) regions with highly- developed petroleum production; (3) Tomsk region (the most intensive technogenic environment); (4) Seversk, where the Siberian Chemical Plant (SCP) is located; (5) populated areas located in the north-eastern direction from the Siberian Chemical Plant (zone of material transport by wind).
The element content in children hair in above-mentioned zones is shown in the following diagrams - Fig. 2 and Fig. 3.
Table 3.
