Role of discrete landscape units in controlling catchment dissolved organic carbon dynamics

[1] The spatial sources and delivery mechanisms of dissolved organic carbon (DOC) to streams are poorly understood. We examined the relationship between storm DOC dynamics, catchment landscape units, and catchment scale to elucidate controls on DOC export dynamics at the Maimai watersheds, a group of highly responsive, steep, wet catchments located on the west coast of the South Island of New Zealand. Specifically, we address the controls on the characteristic hysteresis in DOC export dynamics (i.e., DOC concentrations higher on the rising than falling limb of the discharge hydrograph) previously ascribed to a flushing mechanism. We found that during the storm event, the proportion of riparian runoff was larger on the rising than falling limb of the hydrograph, while the proportion of hillslope runoff was smaller on the rising than falling limb of the hydrograph. The delayed response of hillslope runoff resulted in a disconnection between hillslope and riparian areas early in the event and higher DOC concentrations on the rising limb than the falling limb of the event hydrograph. Later in the event, hillslope and riparian areas became connected once the hillslope soil moisture deficits were satisfied. We suggest that the relative timing of riparian and hillslope source contributions and the connections and disconnections of dominant runoff contributing areas are the first-order catchment controls on stream DOC concentrations and mass export.

[1]  Jeffrey J. McDonnell,et al.  A rationale for old water discharge through macropores in a steep, humid catchment. , 1990 .

[2]  R. Davies‐Colley,et al.  Absorption of light by yellow substance in freshwater lakes , 1987 .

[3]  Brian L. McGlynn,et al.  A review of the evolving perceptual model of hillslope flowpaths at the Maimai catchments, New Zealand , 2002 .

[4]  M. P. Mosley,et al.  Subsurface flow velocities through selected forest soils, South Island, New Zealand , 1982 .

[5]  M. Mosley Streamflow generation in a forested watershed, New Zealand , 1979 .

[6]  G. Hornberger,et al.  Modelling transport of dissolved silica in a forested headwater catchment: the effect of hydrological and chemical time scales on hysteresis in the concentration–discharge relationship , 2001 .

[7]  W. McDowell,et al.  Origin, Composition, and Flux of Dissolved Organic Carbon in the Hubbard Brook Valley , 1988 .

[8]  A. Pearce,et al.  Hydrology and related changes after harvesting native forest catchments and establishing pinus radiata plantations. Part 2. The native forest water balance and changes in streamflow after harvesting , 1994 .

[9]  R. D. Harr,et al.  Water flux in soil and subsoil on a steep forested slope , 1977 .

[10]  K. N. Eshleman,et al.  The Role of Organic Acids in the Acid‐Base Status of Surface Waters at Bickford Watershed, Massachusetts , 1985 .

[11]  Ross Woods,et al.  The changing spatial variability of subsurface flow across a hillside , 1996 .

[12]  A. J. Pearce,et al.  Hydrology and related changes after harvesting native forest catchments and establishing pinus radiata plantations. Part 1. Introduction to study , 1994 .

[13]  Steven J. Eisenreich,et al.  Export of dissolved organic carbon and acidity from peatlands , 1989 .

[14]  J. Hewlett Factors affecting the response of small watersheds to precipitation in humid areas , 1967 .

[15]  A. Pearce,et al.  Rainfall Interception In A Multi-Storied, Evergreen Mixed Forest: Estimates Using Gash's Analytical Model , 1981 .

[16]  K. Bencala,et al.  Effects of asynchronous snowmelt on flushing of dissolved organic carbon: a mixing model approach , 2000 .

[17]  H. Shibata,et al.  Hydrobiogeochemistry of forest ecosystems in Japan: major themes and research issues , 2001 .

[18]  K. Bencala,et al.  Hydrological controls on dissolved organic carbon during snowmelt in the Snake River near Montezuma, Colorado , 1994 .

[19]  K. Bencala,et al.  Response characteristics of DOC flushing in an alpine catchment , 1997 .

[20]  Lawrence E. Band,et al.  Regulation of Nitrate‐N Release from Temperate Forests: A Test of the N Flushing Hypothesis , 1996 .

[21]  Diane M. McKnight,et al.  The relationship between soil heterotrophic activity, soil dissolved organic carbon (DOC) leachate, and catchment‐scale DOC export in headwater catchments , 1999 .

[22]  Kevin Bishop,et al.  Groundwater dynamics along a hillslope: A test of the steady state hypothesis , 2003 .

[23]  Keith Beven,et al.  The role of bedrock topography on subsurface storm flow , 2002 .

[24]  J. Buttle,et al.  Nitrogen chemistry of subsurface storm runoff on forested Canadian Shield hillslopes , 1999 .

[25]  A. J. Stewart,et al.  Influence of dissolved humic materials on carbon assimilation and alkaline phosphatase activity in natural algal‐bacterial assemblages , 1982 .

[26]  D. A. McKie A study of soil variability within the Blackball Hill soils, Reefton, New Zealand , 1978 .

[27]  M. Tani Runoff generation processes estimated from hydrological observations on a steep forested hillslope with a thin soil layer , 1997 .

[28]  J. Buttle,et al.  Runoff Production in a Forested, Shallow Soil, Canadian Shield Basin , 1995 .

[29]  J. Buttle,et al.  Controls on runoff components on a forested slope and implications for N transport , 2001 .

[30]  A. Pearce,et al.  Storm runoff generation in humid headwater catchments 1 , 1986 .

[31]  J. McDonnell,et al.  Flow Pathways on Steep Forested Hillslopes: the Tracer, Tensiometer and Trough Approach , 1998 .

[32]  J. Webster The hydrologic properties of the forest floor under beech/podocarp/hardwood forest, North Westland , 1977 .

[33]  I. Foster,et al.  Short term fluctuations in dissolved organic matter concentrations in streamflow draining a forested watershed and their relation to the catchment budget , 1982 .

[34]  K. Bencala,et al.  Overview of a simple model describing variation of dissolved organic carbon in an upland catchment , 1996 .

[35]  H. Seip,et al.  Dissolved organic carbon fractions in soil and stream water during variable hydrological conditions at Birkenes, southern Norway. , 1992 .

[36]  C. Neal,et al.  Soil water in the riparian zone as a source of carbon for a headwater stream , 1990 .

[37]  J. McDonnell,et al.  Quantifying contributions to storm runoff through end‐member mixing analysis and hydrologic measurements at the Panola Mountain Research Watershed (Georgia, USA) , 2001 .

[38]  D. Siegel,et al.  Climate-driven flushing of pore water in peatlands , 1995, Nature.

[39]  K. Oe Sources and flowpaths of dissolved organic carbon during storms in two forested watersheds of the Precambrian Shield , 1998 .

[40]  George M. Hornberger,et al.  Modeling transport of dissolved silica in a forested headwater catchment: Implications for defining the hydrochemical response of observed flow pathways , 2001 .

[41]  P. Kortelainen,et al.  Content of Total Organic Carbon in Finnish Lakes and Its Relationship to Catchment Characteristics , 1993 .

[42]  B. Wilcox,et al.  Lateral subsurface flow pathways in a semiarid Ponderosa pine hillslope , 1998 .

[43]  T. Moore,et al.  Sources, Sinks, and Fluxes of Dissolved Organic Carbon in Subarctic Fen Catchments , 1992 .

[44]  T. Moore,et al.  Dynamics of dissolved organic carbon in forested and disturbed catchments, Westland, New Zealand: 1. Maimai , 1989 .

[45]  M. Dosskey,et al.  Forest sources and pathways of organic matter transport to a blackwater stream: a hydrologic approach , 1994 .

[46]  Brian L. McGlynn,et al.  Distributed assessment of contributing area and riparian buffering along stream networks , 2003 .

[47]  J. Reuter,et al.  Importance of heavy metal-organic matter interactions in natural waters , 1977 .

[48]  R. Woods,et al.  A connection between topographically driven runoff generation and channel network structure , 1997 .