» Articles » PMID: 29492595

Links Between Heathland Fungal Biomass Mineralization, Melanization, and Hydrophobicity

Overview
Journal Microb Ecol
Date 2018 Mar 2
PMID 29492595
Citations 3
Authors
Affiliations
Soon will be listed here.
Abstract

Comprehending the decomposition process is crucial for our understanding of the mechanisms of carbon (C) sequestration in soils. The decomposition of plant biomass has been extensively studied. It revealed that extrinsic biomass properties that restrict its access to decomposers influence decomposition more than intrinsic ones that are only related to its chemical structure. Fungal biomass has been much less investigated, even though it contributes to a large extent to soil organic matter, and is characterized by specific biochemical properties. In this study, we investigated the extent to which decomposition of heathland fungal biomass was affected by its hydrophobicity (extrinsic property) and melanin content (intrinsic property). We hypothesized that, as for plant biomass, hydrophobicity would have a greater impact on decomposition than melanin content. Mineralization was determined as the mineralization of soil organic carbon (SOC) into CO by headspace GC/MS after inoculation by a heathland soil microbial community. Results show that decomposition was not affected by hydrophobicity, but was negatively correlated with melanin content. We argue that it may indicate that either melanin content is both an intrinsic and extrinsic property, or that some soil decomposers evolved the ability to use surfactants to access to hydrophobic biomass. In the latter case, biomass hydrophobicity should not be considered as a crucial extrinsic factor. We also explored the ecology of decomposition, melanin content, and hydrophobicity, among heathland soil fungal guilds. Ascomycete black yeasts had the highest melanin content, and hyaline Basidiomycete yeasts the lowest. Hydrophobicity was an all-or-nothing trait, with most isolates being hydrophobic.

Citing Articles

Fungal Strain Influences Thermal Conductivity, Hydrophobicity, Color Homogeneity, and Mold Contamination of Mycelial Composites.

Verhelst J, Vandersanden S, Nouwen O, Rineau F Materials (Basel). 2025; 17(24.

PMID: 39769650 PMC: 11727980. DOI: 10.3390/ma17246050.


Food Web Uncertainties Influence Predictions of Climate Change Effects on Soil Carbon Sequestration in Heathlands.

Reyns W, Rineau F, Spaak J, Franken O, Berg M, van der Plas F Microb Ecol. 2019; 79(3):686-693.

PMID: 31654107 DOI: 10.1007/s00248-019-01444-1.


Fungal Succession During the Decomposition of Ectomycorrhizal Fine Roots.

Gray L, Kernaghan G Microb Ecol. 2019; 79(2):271-284.

PMID: 31392355 DOI: 10.1007/s00248-019-01418-3.


The continuing relevance of "older" mycorrhiza literature: insights from the work of John Laker Harley (1911-1990).

Koide R, Fernandez C Mycorrhiza. 2018; 28(7):577-586.

PMID: 30014212 DOI: 10.1007/s00572-018-0854-8.

References
1.
Chau H, Si B, Goh Y, Vujanovic V . A novel method for identifying hydrophobicity on fungal surfaces. Mycol Res. 2009; 113(Pt 10):1046-52. DOI: 10.1016/j.mycres.2009.06.007. View

2.
Lal R . Soil carbon sequestration impacts on global climate change and food security. Science. 2004; 304(5677):1623-7. DOI: 10.1126/science.1097396. View

3.
Schmidt M, Torn M, Abiven S, Dittmar T, Guggenberger G, Janssens I . Persistence of soil organic matter as an ecosystem property. Nature. 2011; 478(7367):49-56. DOI: 10.1038/nature10386. View

4.
Ron E, Rosenberg E . Natural roles of biosurfactants. Environ Microbiol. 2001; 3(4):229-36. DOI: 10.1046/j.1462-2920.2001.00190.x. View

5.
Clemmensen K, Finlay R, Dahlberg A, Stenlid J, Wardle D, Lindahl B . Carbon sequestration is related to mycorrhizal fungal community shifts during long-term succession in boreal forests. New Phytol. 2014; 205(4):1525-1536. DOI: 10.1111/nph.13208. View