Productivities of microbial decomposers during early stages of decomposition of leaves of a freshwater sedge

SUMMARY 1. We examined standing-senescing, standing-dead and recently fallen leaf blades of Carex walteriana in fens of the Okefenokee Swamp to determine the nature of the microbial decomposers in the early stages of decomposition, measuring both standing crops and productivities ([3H]leucineprotein method for bacteria, [14C]acetateergosterol for fungi). 2. Fungal standing crops (ergosterol) became detectable at the mid-senescence stage (leaves about half yellow-brown) and rose to 14–31 mg living-fungal C g−1 organic mass of the decaying system; bacterial standing crops (direct microscopy) were ± 0.2 mgC g−1 until the fallen-leaf stage, when they rose to as high as 0.9 mgC g−1. 3. Potential microbial specific growth rates were similar between fungi and bacteria, at about 0.03–0.06 day−1, but potential production of fungal mass was 115–512 μgC g−1 organic mass day−1, compared with 0–22 μgC g−1 day−1 for bacteria. Rates of fungal production were about 6-fold lower on average than previously found for a saltmarsh grass, perhaps because much lower phosphorus concentratiofis in the freshwater fen limit fungal activity. 4. There was little change in lignocellulose (LC) percentage of decaying leaves, although net loss of organic mass at the fallen, broken stage was estimated to be 59%, suggesting that LC was lost at rates proportional to those for total organics during decay. Monomers of fungal-wall polymers (glucosamine and mannose) accumulated 2- to 4-fold during leaf decay. This may indicate that an increase found for proximate (acid-detergent) lignin could be at least partially due to accumulation of refractory fungal-wall material, including melanin. 5. A common sequence in decaying aquatic grasses is suggested: principally fungal alteration of LC during standing decay, followed by a trend toward bacterial decomposition of the LC after leaves fall and break into particles.

[1]  S. Y. Newell,et al.  Sexual productivity and spring intramarsh distribution of a key salt-marsh microbial secondary producer , 1995 .

[2]  S. Y. Newell Total and Free Ergosterol in Mycelia of Saltmarsh Ascomycetes with Access to Whole Leaves or Aqueous Extracts of Leaves , 1994, Applied and environmental microbiology.

[3]  D. Buxton,et al.  A Comparison of the Insoluble Residues Produced by the Klason Lignin and Acid Detergent Lignin Procedures , 1994 .

[4]  R. Hodson,et al.  Support of bacterioplankton production by dissolved humic substances from three marine environments , 1994 .

[5]  A. Sethuraman,et al.  Microbial Delignification with White Rot Fungi Improves Forage Digestibility , 1993, Applied and environmental microbiology.

[6]  S. Y. Newell Decomposition of shoots of a salt-marsh grass: methodology and dynamics of microbial assemblages , 1993 .

[7]  C. Hopkinson A comparison of ecosystem dynamics in freshwater wetlands , 1992 .

[8]  Jos T. A. Verhoeven,et al.  Carex litter decomposition and nutrient release in mires with different water chemistry , 1992 .

[9]  S. Y. Newell,et al.  Early diagenesis of lignin-associated phenolics in the salt marsh grass Spartina alterniflora , 1992 .

[10]  J. Harvey,et al.  Ammonium and phosphate dynamics in a Virginia salt marsh , 1992 .

[11]  R. Hatfield,et al.  Effect of white rot basidiomycetes on chemical composition and in vitro digestibility of oat straw and alfalfa stems. , 1992, Journal of animal science.

[12]  S. Y. Newell,et al.  Contribution to lignocellulose degradation and DOC formation from a salt marsh macrophyte by the ascomycete Phaeosphaeria spartinicola , 1992 .

[13]  M. Moran,et al.  Carbohydrate Signatures of Aquatic Macrophytes and Their Dissolved Degradation Products as Determined by a Sensitive High-Performance Ion Chromatography Method , 1991, Applied and environmental microbiology.

[14]  S. Y. Newell,et al.  Toward A Method For Measuring Instantaneous Fungal Growth Rates In Field Samples , 1991 .

[15]  H. Hoppe Microbial Extracellular Enzyme Activity: A New Key Parameter in Aquatic Ecology , 1991 .

[16]  M. Moran,et al.  Bacterial production on humic and nonhumic components of dissolved organic carbon , 1990 .

[17]  A. Ward,et al.  A mathematical model for the growth of mycelial fungi in submerged culture , 1990, Biotechnology and bioengineering.

[18]  S. Findlay,et al.  Comparison of detritus dynamics in two tidal freshwater wetlands , 1990 .

[19]  Sy. Lee Net aerial primary productivity, litter production and decomposition of the reef Phragmites communis in a nature reserve in Hong Kong: management implications , 1990 .

[20]  W. Bryant,et al.  Juncus roemerianus production and decomposition along gradients of salinity and hydroperiod , 1990 .

[21]  J. Miller,et al.  Decomposition and microbial dynamics for standing, naturally positioned leaves of the salt-marsh grass Spartina alterniflora , 1989 .

[22]  M. Moran,et al.  Bacterial secondary production on vascular plant detritus: relationships to detritus composition and degradation rate , 1989, Applied and environmental microbiology.

[23]  J. Lay,et al.  Carbon conversion efficiency for bacterial growth on lignocellulose: Implications for detritus‐based food webs , 1988 .

[24]  T. Clark,et al.  Consumption of substrate components by the cultivated mishroom lentinus edodes during growth and fruiting on softwood and hardwood-based media , 1988 .

[25]  H. Greening,et al.  Changes in macrophyte community structure following drought in the okefenokee swamp, Georgia, U.S.A. , 1987 .

[26]  S. Y. Newell,et al.  Calculation of cell production of coastal marine bacteria based on measured incorporation of [3H]thymidine1,2 , 1987 .

[27]  Curtis J. Richardson,et al.  Processes controlling movement, storage and export of phosphorus in a fen peatland , 1986 .

[28]  Jackson R. Webster,et al.  VASCULAR PLANT BREAKDOWN IN FRESHWATER ECOSYSTEMS , 1986 .

[29]  R. Hodson,et al.  Incorporation versus biosynthesis of leucine: implications for measuring rates of protein synthesis and biomass production by bacteria in marine systems , 1986 .

[30]  S. Y. Newell,et al.  Trophic interactions between heterotrophic Protozoa and bacterioplankton in estuarine water analyzed with selective metabolic inhibitors , 1986 .

[31]  M. Moran,et al.  Biogeochemical Cycling of Lignocellulosic Carbon in Marine and Freshwater Ecosystems: Relative Contributions of Procaryotes and Eucaryotes , 1986 .

[32]  Mary Ann Moran,et al.  Effects of pH and plant source on lignocellulose biodegradation rates in two wetland ecosystems, the Okefenokee Swamp and a Georgia salt marsh1,2,3 , 1985 .

[33]  D. Lewis,et al.  Relationship of fungal chemical markers to normal and benodanil-affected growth and development of Puccinia hordei in leaves of barley , 1985 .

[34]  G. Bratbak,et al.  Bacterial dry matter content and biomass estimations , 1984, Applied and environmental microbiology.

[35]  D. Lamport,et al.  A microapparatus for liquid hydrogen fluoride solvolysis: sugar and amino sugar composition of Erysiphe graminis and Triticum aestivum cell walls. , 1983, Analytical biochemistry.

[36]  G. E. Lang,et al.  A Critique of the Analytical Methods Used in Examining Decomposition Data Obtained From Litter Bags , 1982 .

[37]  J. Hedges,et al.  Characterization of lignin by gas capillary chromatography of cupric oxide oxidation products , 1982 .