Estimating production of gilvin from catchment leaf litter during seasonal rains
Song Qiu A B , Arthur J. McComb A , Richard W. Bell A and Jenny A. Davis AA School of Environmental Science, Murdoch University, Murdoch, WA 6150, Australia.
B Corresponding author. Email: s.qiu@murdoch.edu.au
Marine and Freshwater Research 56(6) 843-849 https://doi.org/10.1071/MF04297
Submitted: 7 December 2004 Accepted: 26 April 2005 Published: 27 September 2005
Abstract
The yellow substance, gilvin, is an important component of water quality in natural waters. Quantitative study of gilvin production is difficult since gilvin is not a well defined substance. In the present study, leaf litter from four common tree species of south-western Australia were exposed to rainy weather for 183 days and leachate properties were monitored. The gilvin leaching from litter was estimated using a ‘humic acid (HA) equivalent’ concept, derived by drawing an analogy between the spectrophotometric properties of gilvin and that of humic acid. Gilvin (g440, m−1) was leached from litter primarily during the first few weeks after the commencement of the wet season. On average, 13% less gilvin was leached under ‘flooded’ conditions compared with ‘non-flooded’ conditions. Litter leaching in the presence of soil caused a significant time lag (about a month) for the peak load to occur, and reduced the total gilvin in the leachate through soil–litter interactions. Banksia menziesii leaves produced little gilvin, equivalent to 6.6% of that leached from the flooded gum. The Eucalyptus species, such as flooded gum and jarrah, common in wooded catchments in the region, appeared to be a major player producing yellow-coloured substances under annual rainfall conditions in south-western Australia.
Extra keywords: absorption coefficient, CDOM, g440, leaf litter, yellow substance.
Acknowledgments
This work forms a part of on-going study supported by ARC Large Grant A00105241. The Department of Conservation and Land Management of Western Australia issued permits for field studies.
Bowers, D. G. , Harker, G. E. L. , Smith, P. S. D. , and Tett, P. (2000). Optical properties of a region of freshwater influence (the Clyde Sea). Estuarine, Coastal and Shelf Science 50, 717–726.
| Crossref | GoogleScholarGoogle Scholar |
Qiu, S. , McComb, A. J. , and Bell, R. W. (2002). Phosphorus leaching from litterfall in wetland catchments of the Swan Coastal Plain, southwestern Australia. Hydrobiologia 472, 95–105.
| Crossref | GoogleScholarGoogle Scholar |
Valiela, I. , Teal, J. M. , Allen, S. D. , Van, E. R. , Goehringer, D. , and Volkmann, D. (1985). Decomposition in salt marsh ecosystems: the phases and major factors affecting disappearance of above-ground organic matter. Journal of Experimental Marine Biology and Ecology 89, 29–54.
| Crossref | GoogleScholarGoogle Scholar |
Wrigley, T. J. , and Cowan, M. (1995). Octanol partition coefficients for wetland humus. Water Research 29, 11–15.
| Crossref | GoogleScholarGoogle Scholar |
Wrigley, T. J. , Chambers, J. M. , and McComb, A. J. (1988). Nutrient and gilvin levels in waters of coastal-plain wetlands in an agricultural area of Western Australia. Australian Journal of Marine and Freshwater Research 39, 685–694.
Xiong, S. J. , and Nilsson, C. (1997). Dynamics of leaf litter accumulation and it effects on riparian vegetation – a review. Botanical Review 63, 240–264.
Yacobi, Y. Z. , Alberts, J. J. , Takács, M. , and McElvaine, M. (2003). Absorption spectroscopy of colored dissolved organic carbon in Georgia (USA) rivers: the impact of molecular size distribution. Journal of Limnology 62, 41–46.
Zarcinas, B. A. , Cartwright, B. , and Spouncer, L. R. (1987). Nitric acid digestion and multi-element analysis of plant material by induced coupled plasma spectrometry. Communications in Soil Science and Plant Analysis 18, 131–146.