陸水学雑誌
Online ISSN : 1882-4897
Print ISSN : 0021-5104
ISSN-L : 0021-5104
CHEMICAL STUDIES ON CARBON CYCLE IN LAKE SUWA BY DETERMINING PH AND TOTAL CARBON DIOXIDE
Tadashiro KOYAMAOsamu SATOTakao TOMINOKatsuji MATSUNAGAHideo KURASAWA
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ジャーナル フリー

1972 年 33 巻 4 号 p. 61-70

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Carbon cycle in Lake Suwa (maximum depth : 6.7 m;area : 14.5 km2) which is a highly polluted and eutrophic lake in Nagano Prefecture, Japan, was studied by determining pH and total carbon dioxide as follows :
(1) Total carbon dioxide (Total CO2) of the lake water was determined by KOYAMA's method. The same water sample was aerated in order to be equilibrated with air. Total CO2 of the aerated water sample was determined as an original total carbon dioxide (Orig. CO2).
In the stably stratified lake waters, the difference (ΔCO2) between Orig. CO2 and Total CO2 corresponds to the net fixation of CO2 (N. Fix. CO2) in a case of positive value and the net formation of CO2 (N. Form. CO2) in a case of negative value.
In the case of Lake Suwa, however, it should be suitable to call the former as the preserved amount of net fixation of CO2 (P. A. N. Fix. CO2) and the latter as the preserved amount of net formation of CO2 (P. A. N. Form. CO2), because the lake water layers are easily mixed and some of the dissolved CO2 may be exchanged for the atmospheric CO2 through all seasons.
From a vertical distribution of ΔCO2, P. A. N. Fix. CO2 or P. A. N. Form. CO2 in a water column was calculated on the basis of (g C/m2).
(2) Relation curves between pH and Total CO2 of the lake water were constructed from pH and Total CO2 values obtained from the water samples collected in different months.
(3) Greater part of the numerous data of Total CO2 values used in this study were estimated from a large number of vertical distributions of pH values obtained at different times in different days while comparing with the relation curves between pH and Total CO2.
(4) Average P. A. N. Fix. CO2 (A. P. A. N. Fix. CO2) and average P. A. N. Form. CO2 (A. P. A. N. Form. CO2) in a whole day were estimated from the values of P. A. N. Fix. CO2 and P. A. N. Form. CO2 in a water column, which were estimated at different times in the day.
(5) Numerous data of these A. P. A. N. Fix. CO2 or A. P. A. N. Form. CO2 in the water column were estimated on different days in different months.
(6) A histogram of A. P. A. N. Fix. CO2 and A. P. A. N. Form. CO2 was then constructed against months.
(7) This histogram shows the following facts : (a) A. P. A. N. Fix. CO2 ranged between 3.8 and 6.6 g C/m2 from April through August. (b) A. P. A. N. Form. CO2 ranged between -8.2 and -12.9 g C/m2 from September through December. (c) On the assumption that the average exchangeability of CO2 between air and lake water in a month is similar to those of the adjacent months, the difference between A. P. A. N. Fix. CO2 or A. P. A. N. Form. CO2 of a month and that of an adjacent month corresponds to the average net fixation rate of CO2 during the two months in a case of positive value and to the average net formation rate of CO2 in a case of negative value. (d) The average net fixation rate of CO2 and the average net formation rate of CO2 correspond to the average net production rate and the average net decomposition rate of organic matter respectively.
(8) The maximum net production rate which was found between March and April amounted up to 4.5 g C/m2. day and the maximum net decomposition rate which was found between August and September amounted up to-13.5 g C/m2. day.

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© The Japanese Society of Limnology
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