2013
DOI: 10.1016/j.soilbio.2013.03.015
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Spatial variability of soil fungal and bacterial abundance: Consequences for carbon turnover along a transition from a forested to clear-cut site

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Cited by 38 publications
(29 citation statements)
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“…This finding agrees with previous studies showing that DOC is the primary energy source for microorganisms and affects their activity in the soil [25,27]. Churchland et al [17] also reported that even in disturbed sites, DOC was the main source of C that influenced the composition of the microbial community and soil respiration rates up to ten meters from a forested to clear-cut site. Another study found that the addition of N changed the amount and biodegradability of soil DOC through stimulating microbial metabolic activity and preferentially utilizing organic acids based on Biolog analyses [51].…”
Section: Discussionsupporting
confidence: 92%
“…This finding agrees with previous studies showing that DOC is the primary energy source for microorganisms and affects their activity in the soil [25,27]. Churchland et al [17] also reported that even in disturbed sites, DOC was the main source of C that influenced the composition of the microbial community and soil respiration rates up to ten meters from a forested to clear-cut site. Another study found that the addition of N changed the amount and biodegradability of soil DOC through stimulating microbial metabolic activity and preferentially utilizing organic acids based on Biolog analyses [51].…”
Section: Discussionsupporting
confidence: 92%
“…This suggests that in treatments with a reduction in SOC quality (i.e., a lower relative abundance of high-quality C), less C was mineralized without any change in the quality of the C used. This result is consistent with results from previous assessments, which have found similar d 13 C in respired CO 2 in spite of d 13 C differences in substrates respired (Fernandez et al 2003, Churchland et al 2013, and undistinguishable d 13 C in CO 2 produced from different DIRT treatments in short term assessments of fresh soil (Crow et al 2006). Thus we see evidence for a selective microbial use of high-quality components of the SOC, with a resulting respiration dominated by the abundance of high-quality C remaining, as suggested by the stable d 13 C (Fig.…”
Section: Soc Use By Fungal and Bacterial Decomposerssupporting
confidence: 92%
“…Thus, after a cycle of microbial use, the C released back to the soil environment as a result of microbial turnover has become enriched in d 13 C (Abraham et al 1998, Cifuentes andSalata 2001). Since microbial derived C is of lower quality compared to plant-derived C (Å gren et al 1996, Schiff et al 1997, Cotrufo et al 2013, the gradual enrichment in d 13 C signal in SOC that develops with each microbial use cycle coincides with a gradual reduction in SOC quality (Churchland et al 2013). Although it is theoretically possible that this relationship can be offset by changes in the composition of compounds that make up the SOC (e.g., an enrichment of lignin) due to compound specific differences in d 13 C signals, the pattern has been found to be robust within and between soils and to overshadow compound specific differences (Sollins et al 2009, Gunina andKuzyakov 2014).…”
Section: Introductionmentioning
confidence: 99%
“…The differences in the d 13 C derived from the weighted mean of all PLFA attributed to the groups (e.g. bacteria, Gram negative bacteria, Gram positive bacteria, fungi) is also provided in each case from the data provided in this study and Churchland et al (2013). References for this Kramer and Gleixner (2006) 6.4…”
Section: Discussionmentioning
confidence: 99%
“…C3/C4 crop change experiments; Kramer and Gleixner 2006; or free-air in situ CO 2 enrichment (FACE) experiments; Billings and Ziegler 2008;Streit et al 2014). Consequently, few studies have investigated the natural variations of d 13 C PLFA to assess potential variation in microbial d 13 C (Baum et al 2009;Cusack et al 2011;Churchland et al 2013). …”
Section: Introductionmentioning
confidence: 99%