2016
DOI: 10.1007/s12665-016-5960-3
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Comparisons of lipid molecular and carbon isotopic compositions in two particle-size fractions from surface peat and their implications for lipid preservation

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Cited by 11 publications
(5 citation statements)
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“…Preferential postdepositional degradation of fresher and more labile nonmineral-associated OM in river sediments could also explain the lower TOC values and lower TOC and LCFA D 14 C values (older ages) of river sediments. However, since LCFA d 13 C values show no indication for enrichment due to degradation (Li et al, 2017;Wang et al, 2016), suggesting a similar origin for LCFAs in SPM and river sediments, we suspect that preferential transport and deposition of mineral-associated LCFAs is the most likely explanation. The lower ACL values for SPM than river sediments are the only indication of additional sources of n-C 24 -FAs to SPM, whereas brGDGT proxy values (BIT, #rings tetra ) are very comparable.…”
Section: Comparison Of Spm To River Sedimentsmentioning
confidence: 91%
“…Preferential postdepositional degradation of fresher and more labile nonmineral-associated OM in river sediments could also explain the lower TOC values and lower TOC and LCFA D 14 C values (older ages) of river sediments. However, since LCFA d 13 C values show no indication for enrichment due to degradation (Li et al, 2017;Wang et al, 2016), suggesting a similar origin for LCFAs in SPM and river sediments, we suspect that preferential transport and deposition of mineral-associated LCFAs is the most likely explanation. The lower ACL values for SPM than river sediments are the only indication of additional sources of n-C 24 -FAs to SPM, whereas brGDGT proxy values (BIT, #rings tetra ) are very comparable.…”
Section: Comparison Of Spm To River Sedimentsmentioning
confidence: 91%
“…Previous 13 C incubation studies have proven that warming can substantially alter the stability of SOM. , Hence, this suggests that long-chain n -alkyl molecules in soils may undergo specific indirect isotopic modification during accelerated microbial biodegradation associated with induced climate change (i.e., changes in the degradation of biomass inputs) . In fact, microbial degradation of long-chain n -alkanes is not a rare phenomenon in natural settings due to heterotrophic reworking during degradation. , …”
Section: Resultsmentioning
confidence: 99%
“…77 In fact, microbial degradation of long-chain n-alkanes is not a rare phenomenon in natural settings due to heterotrophic reworking during degradation. 78,79 Comparison between δ 13 C of long-chain n-alkanes (C 27 , C 29 , and C 31 ) from biomass debris (Figure S1) and those identified from SOM was not significantly different under the two habitats or the climatic treatments. This supports the idea that the isotopic composition of the n-alkanes can be attributed to the contributions of biomass from each habitat.…”
Section: Isotopic Composition (δmentioning
confidence: 99%
“…After cultivation, the CPI AF≥20 values of sand fractions in all TP soils depths showed a higher degree of degradation compared to corresponding fractions in NS (Figure 4), while the carbon content of TP sand fractions showed an increasing trend compared to that of NS (Figure 5). Generally, the coarser fractions contained inputs of fresher OM [38]. Although a continuous input of fresh biomass is expected during cultivation, intensive agricultural activities (plowing and fertilizing) may have promoted the degradation of SOM after exposure to oxygen, especially in the presence of reactive Fe [6,39].…”
Section: The Degradation Of Mineral-protected Lipidsmentioning
confidence: 99%