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Role of Microorganisms in Carbon Cycling in Soils 141<br />

Table 1. Microbial C content (Cmic) of soils from different ecosystems. Microbial biomass<br />

was measured by the fumigation extraction or substrate-induced respiration method<br />

Ecosystem Horizon Cmic Reference<br />

(cm) (µg/g) Corg<br />

(%)<br />

Arable soils 0–20 70– 720a 1.0–3.8 Beck et al. (1997)<br />

0–15 420– 980 2.5–5.5 Franzlübbers et al. (2000)<br />

0– 5 250– 1080 3.0–6.0 Hu et al. (1997)<br />

Grassland Litter 9650 2.1 Ross et al. (1996)<br />

0–10 2670 2.9<br />

10–20 1120 1.9<br />

20–30 470 2.0<br />

F 25900a ND Johnson et al. (1998)<br />

0– 7 6600–15700a ND<br />

0–10 1120– 1510 ND Bardgett et al. (1999)<br />

Temperate forest 0–10 420– 1770a 0.9–2.6 Beck et al. (1997)<br />

0– 5 800– 1670 1.2–6.0 Hu et al. (1997)<br />

5–10 160– 430 ND<br />

5–10 370– 600 ND<br />

Litter 10830 2.3 Ross et al. (1996)<br />

FH 7670 2.0<br />

0–10 1670 2.1<br />

10–20 730 1.8<br />

20–30 260 1.0<br />

Subtropical forest 0–10 330– 1090 0.9–1.8 Maithani et al. (1996)<br />

10–20 200– 790 0.7–1.3<br />

Tropical forest 0–10 210– 490 2.1–3.4 Salamanca et al. (2002)<br />

Tropical forest 0–12 170– 860 0.5–1.1 Waldrop et al. (2000)<br />

Tropical forest 0–10 950– 1970 1.4–2.9 Cleveland et al. (2004)<br />

Tundra 0– 5 2990–13900 2.1–3.6 Weixin and Ross (1993)<br />

Alpine meadows 0–10 1000– 2750 1.7–2.8 Zeller et al. (2001)<br />

Boreal forest Litter 2500– 6000 ND Schimel et al. (1999)<br />

Semiarid 0–15 120– 330 3.2–4.8 Kanchikerimath<br />

and Singh (2001)<br />

Arid/Mediterranean 0–20 30– 700 0.8–8.0 García et al. (1994)<br />

ND, Not determined<br />

a Results based on the measurement of substrate-induced respiration<br />

In principle, soil organic carbon is derived from autotrophic organisms<br />

– higher plants and autotrophic microorganisms. Dead plant and microbial<br />

material are the most important energy sources for soil microorganisms.<br />

The organic debris is either mineralized, i.e., completely decomposed to<br />

CO2, or humified. The latter process leads to soil organic matter fractions<br />

of widely varying turnover half-lives, from several decades to thousands of<br />

years. Note that mineralization and humification are parallel processes. De-

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