日本地球惑星科学連合2019年大会

講演情報

[E] 口頭発表

セッション記号 A (大気水圏科学) » A-HW 水文・陸水・地下水学・水環境

[A-HW22] 流域の物質輸送と栄養塩循環-源流域から沿岸海域まで-

2019年5月30日(木) 10:45 〜 12:15 201B (2F)

コンビーナ:小林 政広(国立研究開発法人森林研究・整備機構 森林総合研究所)、吉川 省子(農業・食品産業技術総合研究機構 農業環境変動研究センター)、安元 純(琉球大学 農学部 地域農業工学科)、Adina Paytan(University of California Santa Cruz)、座長:安元 純(琉球大学 農学部 地域農業工学科)

12:00 〜 12:15

[AHW22-17] セレンガ河における元素動態への懸濁粒子の役割

★招待講演

*川東 正幸1Orgilbold Myangan2Bolormaa Oyuntsetseg2 (1.首都大学東京、2.モンゴル国立大学)

キーワード:バイカル湖、懸濁粒子沈降、支流分岐

Lake Baikal is one of the cleanest lake in the world. However, there are many sources of pollution such as mining, industry and agriculture in the river basin of the main tributary, Selenga River which is flowing into Lake Baikal. Lake Baikal actually face to severe pollution affected by anthropogenic activities in the watershed. Natural cleaning mechanism can still be functioning to prevent pollutants flow into the Baikal. Since suspended solids (SS) in the Selenga River can play a role as carriers of heavy metals and organic pollutants, their dynamics should be addressed to know the mechanism.

Water and sediment samples were collected in the Russian territory from the Mongolian border to the shore of the Baikal including the Selenga Delta. SS samples were further recovered using a glass fiber filter from the water samples. Surface sediments and SS samples were digested with the mixture of nitric acid and perchloric acid for determination of elements using Inductively Coupled Plasma Atomic Emission Spectrometry (ICP-AES).

Elemental concentrations were changeable depending on SS concentration along the tributary. Changes in SS concentration can be controlled by flow rate of the tributary. The significant relationship were observed between SS and sesquioxides mainly consisting of Fe and Al. Both of Mn and Cr were also common constituents of the SS oxides despite of their low concentration in SS. In contrast, Zn and Cu have no correlation with SS, indicating that they are specifically accumulated onto SS surface at a point where the two elements were released. The concentration of SS gradually decreased accompanied by decrease in heavy metals in SS in the delta region. On the contrary, those elements in the surface sediments increased to downstream in the delta region. Deposition process of SS in the delta can be occurred due to decrease in flow rate by channel bifurcation of tributaries, back water effect from Lake Baikal and SS trapping by vegetation in the delta. The delta has a potential to trap SS, resulting that water quality in the Lake Baikal has been protected of water quality in Lake Baikal.