doi:10.1016/S0378-1127(03)00146-4
Copyright © 2003 Elsevier Science B.V. All rights reserved.
Carbon stock estimates for sugi and hinoki forests in Japan
Miki Fukuda
,
, a, Toshiro Ieharaa and Mitsuo Matsumotob
a Resources Analysis Laboratory, Forestry and Forest Products Research Institute, Matsunosato 1, Tsukuba, Ibaraki 305-8687, Japan
b Policy and Systems Analysis Laboratory, Forestry and Forest Products Research Institute, Matsunosato 1, Tsukuba, Ibaraki 305-8687, Japan
Received 18 July 2002;
revised 29 August 2002;
accepted 10 March 2003. ;
Available online 21 May 2003.
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Abstract
Forest inventory data are widely used for broad-scale quantification of forest carbon budgets. Such data usually represent forest wood volume (m3 ha−1), which needs to be converted to biomass carbon value (Mg C ha−1) for carbon stock estimates. Our main objective is to estimate the carbon stock for all sugi (Cryptomeria japonica D. Don) and hinoki (Chamaecyparis obtusa Endl.) plantations in Japan on the basis of age-class-based forestry statistics. To achieve this purpose, we estimated regional wood volume accumulation and biomass allocation over time for sugi and hinoki forests to calculate and map the carbon stock in all sugi and hinoki plantations in Japan on the basis of forestry statistics. Hinoki forests showed smaller accumulation of volume than sugi forests from ca. 25 years old to maturity; the accumulation of wood volume per hectare at 80 years old was <600 m3 ha−1 for hinoki and >600 m3 ha−1 for sugi. Patterns of biomass allocation to forest components varied by forest type; the proportion of branch biomass in 0–20-year-old hinoki forests is 5–10% larger than that of sugi; the proportion of stem biomass in the same age range is 5–10% smaller than that of sugi; the ratio of roots was approximately constant as its average value, 20.4% for sugi and 22.7% for hinoki. The ratios of total biomass to bole biomass (i.e., expansion factor (EF), Mg total biomass Mg−1 bole biomass) decreased with increasing age, and became nearly constant after 30 years old for sugi and hinoki. The mean EFs were the same for the two forest types, with a value of 1.72 Mg Mg−1. Our results suggest that sugi and hinoki plantations in Japan, respectively, store 346.4×106 and 139.2×106 Mg of carbon, with an area-weighted mean of 76.81 and 58.01 Mg C ha−1. High amounts of carbon stock in both sugi and hinoki are located in the southwestern part of Japan.
Author Keywords: Carbon stock; Biomass allocation; Conversion factor; Sugi (Cryptomeria japonica D. Don) plantations; Hinoki (Chamaecyparis obtusa Endl.) plantations
Fig. 1. (a) Pattern of accumulation of volume per hectare over time in sugi forests predicted by equations (1) Tohoku-P, (4) N-Akita, (13) north Japan, (14) middle Japan, and (15) Kyushu from the values in Table 3. (b) Pattern of accumulation of volume per hectare over time in hinoki forests predicted by equations (21) north middle Japan and (22) Kyushu from the values in Table 3.
Fig. 2. (a) Biomass allocation as a function of age for sugi. The scattered points were the ratio of roots to total biomass, the ratio of roots and bole to total, and the ratio of roots, bole, and branches to total, of individual stand data. Solid lines stand for the ratio of roots to total as its average value, 20.4%, and Mitscherlich curves as final equations were chosen to express the proportion of roots and bole, and the proportion of roots, bole and branches (see text and
Table 4). (b) Biomass allocation as a function of age for hinoki. The scattered points were the ratio of roots to total biomass, the ratio of roots and bole to total, and the ratio of roots, bole, and branches to total, of individual stand data. Solid lines stand for the ratio of roots to total as its average value, 22.7%, and Mitscherlich curves as final equations were chosen to express the proportion of roots and bole, and the proportion of roots, bole and branches (see text and
Table 4).
Fig. 3. EF (Mg total biomass Mg
−1 bole biomass) of individual stand data and EF calculated by biomass allocation models as a function of age for sugi and hinoki forests. The scattered points show the EFs of individual stand data and the EFs calculated from Mitscherlich formula in
Table 4.
Fig. 4. BEF (Mg total biomass m
−3 bole volume) of individual stand data for sugi and hinoki forests. The scattered points show the BEFs of individual stand data.
Fig. 5. (a) Map of carbon stock (above- and belowground, Mg C) in 1990 for sugi forests in Japan. Solid lines stand for the borders between prefectures. (b) Map of carbon stock (above- and belowground, Mg C) in 1990 for hinoki forests in Japan. Solid lines stand for the borders between prefectures.
Table 1. Data sets and their contributing regionsa

Table 2. Basic density of sugi and hinoki

Table 3. Regression coefficients for the Mitscherlich formula relating the accumulation of wood volume (m3 ha−1) to stand age for sugi and hinoki forest typesa

Table 4. Average values of the ratio of roots to total biomass (%) and regression coefficients for equations relating allocation fraction (AF, %) to age for sugi and hinoki forestsa

Table 5. Conversion factors by region and forest type drawn from the literaturea

Table 6. Conversion factors for sugi and hinoki forestsa

Table 7. Calculated carbon stocks for sugi and hinoki forests in Japan for 1990–1995
