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, 4) ( 2 6 d r t c s d a d p r h « 60 Co) щ (137Cs, 60Co) 226Ra , 60Co This paper distribution of n radionuclides in that the distribu clay and clay g silty fractions. determined by t accumulation of distribution and potassium conta registered only iК юче ы
, Key wor hydromica, pH . . » [6], . . , -, . » : 40K
r focuses on the natural (226Ra, n the sediments ution of 137Cs i grain-size fractio
The accumula the pH geochem f 232Th occurs d accumulation o
tained in hydro in a few samples
ые :
,
rds: radionu H barrier, sedi
« , . . . . -» х (226
e impact of cer 232Th, 40 ) a of the Baltic Se is determined by ons, while radio ation of 226Ra mical barrier at s mainly in clay of 40K is predom omica minerals s. : , , uclide distrib iment fraction , , . . .
6Ra, 232Th, 40
137Cs
.
– .
.
rtain factors on and anthropoge ea. The results o y the content of ocaesium is mai a by bottom se
t the water-seaf yey fractions of minantly determ s. Significant
ution pattern ns, grain-size c
. . . . . . : 0 ) . , . 23 . .
n the contempo nic ( 137Cs, 60 of the study sug f hydromica of s inly accumulated ediments is ma floor boundary. f the sediment. mined by the rati 60Co activity
, .
ns, Baltic S composition. , . . . . . .
(226Ra, 232
.
.
- ч щ х ( / )
х х
226
Ra 232Th 40K 137Cs 60Co
N
A σ A σ A σ A σ A σ
52 31 75 34 805 303 560 458 5 11 411
48 22 56 16 963 152 163 32 — — 29
47 19 52 11 837 143 63 39 3 2 49
25 8 32 6 615 108 14 8 — — 28
: 1.
. 60 ,
. 2. —
, σ — , N — .
137
Cs, 232Th
226
Ra c : —
— . Э
137
Cs « » ,
. Th Ra, ,
. 226Ra 232Th
, ,
, ,
U(Ra) Th
[14; 15].
.
R-. , ,
,
(pH, Eh) , .
Ц З
( )
(69 ) ,
(
) , ( . 1).
, 1,
, .
, « »,
, 232Th. , « », —
, .
— 137Cs, , Eh.
— 226Ra pH. 40 ,
. ,
232
Th. Э
, ,
226Ra
232Th
40
137Cs
pH
Eh
1.25-1.0
1.0-0.5 0.5-0.25 0.25-0.1
0.1-0.05
0.05-0.01 0.01-0.005 0,005-0,001
<0.001
-1,0 -0,8 -0,6 -0,4 -0,2 0,0 0,2 0,4 0,6 0,8 1,0 1,2
Фактор 1
-0,8 -0,6 -0,4 -0,2 0,0 0,2 0,4 0,6 0,8
Фактор
2
. 1. ,
Ph, Eh, ,
:
, H — .
.
. Э ,
. . [2],
.
[11],
.
. . . . [5] , ,
, 97,5%, . ё
,
,
.
,
.
.
, 226Ra pH.
Э :
, (R=+0,36) pH
226Ra, . . .
, , ,
, [7; 11].
, ,
, [12].
: pH
7,24—8,07 pH=7,4,
.
(pH =7,6—8,5) pH=8,0. ,
— ,
.
.
,
137
Cs ,
0,1—0,01 .
. [6; 11],
, :
, , , . . .
, . . [17],
. [3] ,
.
110—130 [3], . . .
( . . 1),
,
.
- Eh ,
,
. , , . .
.
, ,
,
-137Cs . ,
. Э
, «
-» . 1986 . ,
, —
.
.
137Cs, ,
27—32% ,
. 1992 .,
[1, . 16]. ,
,
. 137Cs
.
40K 39K. [4; 13] ,
(K1—1,5Al4[Si7—6,5Al1—1,5O20](OH)4⋅nH2O).
(0,005—0,001 ) (< 0,001 ) [3].
, ,
, 40 , , ,
.
,
.
.
,
, -
( . 2).
,
. .
(198—220 ),
[3].
226 Ra 232Th
40 K 137Cs
1.25-1.0 1.0-0.5
0.5-0.25 0.25-0.1
0.1-0.05
0.05-0.01
0.01-0.00 0005-000<0.001 Ph
Eh
-1,0 -0,8 -0,6 -0,4 -0,2 0,0 0,2 0,4 0,6 0,8 1,0
ктор 1
-1,0 -0,8 -0,6 -0,4 -0,2 0,0 0,2 0,4 0,6 0,8
ктор
2
. 2. ,
Ph, Eh, ,
Eh pH . .
-, .
, , — ,
.
137
Cs, 232Th
226Ra c
: — —
. Э
-, 137Cs — “ ”
.
137Cs
, .
. 226Ra
— . 232Th
,
.
40K ,
. 60Co
,
. , 60Co
С и и е ы
1. . ., . ., . . .
1992 . . ., 1993.
2. . ., .Ю., Ш . .
. , 1982.
3. / . . . . . . , 1976.
4. .
1:500 000 / - , - ; . . . .
., 1991.
5. . ., . .
// . 1978. . 238, №1. . 225—228.
6. . ., . . . ., 1975.
7. . . . , 1998.
8. . ., . ., . .
- // CCCP. 1997. . 355, №3. . 365—
368.
9. . ., . . 137Cs
// . 1988.
№5. . 540—554.
10. . ., . ., .
. , 1994.
11. . . . ., 1968.
12. . . . ., 1989.
13. . .
-: . … . .- . . ., 2002.
14. . ., . ., . .
// : .
. . ., 1987. . 47—55.
15. . . . ., 1974.
16. . ., . ., . . .
1988—1989 . ., 1994. 17. Ф . . . . 2. ., 1993.
О х
, - , ,
- .
E-mail: Andrey_Grigiryev@vsegei.ru
, - ,
, ,
.
E-mail: vladimirovs2001@mail.ru.
About authors
Dr. Andrey Grigoryev, Senior Research Fellow, All-Russian Geological Research Institute. E-mail: Andrey_Grigiryev@vsegei.ru
Dr. Maxim Vladimirov, deputy head of a department, Ministry of the Russian Federation for Civil Defence, Emergencies and Elimination of Consequences of Natural Disasters.