There is a small mire consisting mainly of a bog and a pond system, of about 0.3ha in area, in the Hakkoda Botanical Laboratory of Tohoku University located near Sukayu Spa at about 900m a. s. l. in the Hakkoda Mountains, Northeastern Japan (Fig. 1). To conserve the bog environment, the laboratory attempted to maintain the water table at a constant level by dredging a drainage channel from the pond every summer. As a result, bare ground occurred at the eastern part of the pond. That operation was stopped in the late 1970s, and the bare ground has been gradually submerged by shallow water. Consequently, a type of hydrarch succession has progressed there. The process of invasion and establishment of
Sphagnum recurvum var.
brevifolium community in this hydrarch succession was examined for five years, from 1990 to 1994.
In the first stage, probably it commencing around 1980 when the bare ground dried up during the summer season,
Juncus yokoscensis appeared. This was followed by invasion of
Drepanocladus fluitans. Except during the summer drought, the habitat was continuously submerged in this stage. During these stages, the litter originating from these plants was thinly deposited on the bare ground. Around 1987,
Sph. recurvum invaded the site and grew annually at a certain rate until 1991. It was thought that this process was as follows: many small pieces of
Sph. recurvum shoots were torn off at the margin of the original bog (Fig. 3) and floated to the pond. These small pieces of shoots caught on the layer of litter and grew into the present shoots in situ. Judging from the growth rate of shoots examined for five years, it is assumed that the first invasion of pieces of shoots occurred in 1987. The growth of shoots decreased in 1992, and the lower part of these shoots became fibrous and separated from the upper part. This indicates that formation of sphagna peat began five years after the first invasion (Fig. 6)
To clarify the hydrological conditions supporting the invasion and formation of
Sph. recurvum community, water levels of the pond were measured for two years, 1993 and 1994. The lowest water level, recorded on August 10 during the extraordinarily dry summer of 1994, was 10cm lower than the highest level. Under that condition, although the habitat of Sph. recurvum was exposed, the plants did not wither. The usual downward displacement of water level from the highest level in summer season was 6cm, and even under such conditions, most of the habitat was covered with less than 1cm of shallow water (Fig. 4 and Fig. 7). The most desirable environment for establishment of
Sph. recurvum community on bare ground was a shallow pool with a water depth of less than 4cm (Fig. 4).
Based on the results of observations and measurements of the invasion process of
Sph. recurvum mentioned above, the following questions are briefly discussed.
Some sphagna bogs have been destroyed by the trampling of hikers, and great efforts has been made to reestablish the injured bog vegetation. The results obtained here indicates that self-recovery is possible if a shallow water pool is artificially or naturally induced at destroyed sites. At such sites, the initial invaders, such as
Juncus yokoscensis and some mosses, appear immediately and this stage progresses to the sphagna stage after a short duration.
Peat cores from many mires are frequently intercalated by layers of volcanic ash. Boundaries between peat and volcanic ash layers are mostly very sharp. This indicates that mire vegetation recovers immediately on a bare volcanic ash surface. Such vegetational recovery in the past is supported by the successional process of
Sph. recurvum community examined here.
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