The release of phosphorus to porewater and surface water from river riparian sediments

被引:72
作者
Surridge, Ben W. J. [1 ]
Heathwaite, A. L.
Baird, Andrew J.
机构
[1] Univ Sheffield, Catchment Sci Ctr, Kroto Res Inst, Sheffield S3 7HQ, S Yorkshire, England
[2] Univ Lancaster, Ctr Environm, Ctr Sustainable Water Management, Lancaster LA1 4YQ, England
[3] Univ London, Queen Mary, Dep Geog, London E1 4NS, England
关键词
PHOSPHATE RELEASE; SOIL-PHOSPHORUS; DISSOLVED SUBSTANCES; ORGANIC PHOSPHORUS; FLOODPLAIN FOREST; NUTRIENT DYNAMICS; NITRATE REMOVAL; WETLAND SOILS; STREAM; IRON;
D O I
10.2134/jeq2006.0490
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Sediments can be both a source and a sink of dissolved phosphorus (P) in surface water and shallow groundwater. Using laboratory mesocosms, we studied the influence of flooding with deionized water and simulated river water on P release to solution using sediment columns taken from a riparian wedand. The mesocosm incubation results showed that rather than retaining nutrients, sediments in the riparian zone may be a significant source of R Concentrations of dissolved P in porewater reached more than 3 mgL(-1) and in surface water over 0.8 mg L-1 within a month of sediment inundation. The reductive dissolution of P-bearing iron (Fe) oxides was the likely mechanism responsible for P release. Dissolved P to Fe molar ratios in anaerobic samples were approximately 0.45 when columns were flooded with water that simulated the chemistry of the adjacent river. This suggests there was insufficient Fe in the anaerobic samples to precipitate all P if the solutions were oxygenated or transported to an aerobic environment. If the anaerobic wetland solutions were delivered to oxygenated rivers and streams adjacent to the riparian zone, the equilibrium concentration of P in these systems could rise. The timing of P release was inversely related to the nitrate(NO3-) concentration in floodwater. This indicates that in riparian zones receiving low nitrate loads, or where NO3- loads are being progressively reduced, the risk of dissolved P release may increase. These findings present particular challenges for restoration and management in riparian areas.
引用
收藏
页码:1534 / 1544
页数:11
相关论文
共 85 条
[1]   Groundwater samples do not reflect bacterial densities and activity in subsurface systems [J].
Alfreider, A ;
Krossbacher, M ;
Psenner, R .
WATER RESEARCH, 1997, 31 (04) :832-840
[2]   EFFECT OF NITRATE CONCENTRATION IN LAKE WATER ON PHOSPHATE RELEASE FROM THE SEDIMENT [J].
ANDERSEN, JM .
WATER RESEARCH, 1982, 16 (07) :1119-1126
[3]  
Baldwin DS, 2000, REGUL RIVER, V16, P457, DOI 10.1002/1099-1646(200009/10)16:5<457::AID-RRR597>3.0.CO
[4]  
2-B
[5]   Reactive "organic" phosphorus revisited [J].
Baldwin, DS .
WATER RESEARCH, 1998, 32 (08) :2265-2270
[6]   Biogeochemical cycling of phosphorus: Insights from oxygen isotope effects of phosphoenzymes [J].
Blake, RE ;
O'Neil, JR ;
Surkov, AV .
AMERICAN JOURNAL OF SCIENCE, 2005, 305 (6-8) :596-620
[7]   EXCHANGE OF PHOSPHORUS ACROSS THE SEDIMENT - WATER INTERFACE [J].
BOSTROM, B ;
ANDERSEN, JM ;
FLEISCHER, S ;
JANSSON, M .
HYDROBIOLOGIA, 1988, 170 :229-244
[8]   Phosphorus dynamics along a river continuum [J].
Bowes, MJ ;
House, WA ;
Hodgkinson, RA .
SCIENCE OF THE TOTAL ENVIRONMENT, 2003, 313 (1-3) :199-212
[9]   Immobilization and bacterial utilization of dissolved organic carbon entering the riparian zone of the alpine Enns River, Austria [J].
Brugger, A ;
Wett, B ;
Kolar, I ;
Reitner, B ;
Herndl, GJ .
AQUATIC MICROBIAL ECOLOGY, 2001, 24 (02) :129-142
[10]   PHYSICOCHEMICAL CHARACTERISTICS OF A COLLOIDAL IRON PHOSPHATE SPECIES FORMED AT THE OXIC-ANOXIC INTERFACE OF A EUTROPHIC LAKE [J].
BUFFLE, J ;
DEVITRE, RR ;
PERRET, D ;
LEPPARD, GG .
GEOCHIMICA ET COSMOCHIMICA ACTA, 1989, 53 (02) :399-408