SOIL PHOSPHORUS RELEASE FROM A RESTORATION WETLAND, UPPER KLAMATH LAKE, OREGON

Many wetland restoration projects are initiated with phosphorus (P) retention as a primary objective. While undisturbed wetlands often are net sinks for P and other nutrients, there is evidence that newly flooded restoration wetlands on former agricultural land initially release P to surface waters....

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Veröffentlicht in:Wetlands (Wilmington, N.C.) N.C.), 2007-12, Vol.27 (4), p.1025-1035
Hauptverfasser: Aldous, Allison R., Craft, Christopher B., Stevens, Carla J., Barry, Matthew J., Bach, Leslie B.
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container_issue 4
container_start_page 1025
container_title Wetlands (Wilmington, N.C.)
container_volume 27
creator Aldous, Allison R.
Craft, Christopher B.
Stevens, Carla J.
Barry, Matthew J.
Bach, Leslie B.
description Many wetland restoration projects are initiated with phosphorus (P) retention as a primary objective. While undisturbed wetlands often are net sinks for P and other nutrients, there is evidence that newly flooded restoration wetlands on former agricultural land initially release P to surface waters. The objectives of this study were to: 1) measure P release from soils to overlying surface waters that would occur when re-flooding agricultural fields to restore a lake fringe wetland connected to Upper Klamath Lake, Oregon; and 2) identify management strategies to abate nutrient release from soils during restoration to minimize P loading to Upper Klamath Lake. We simulated the process of re-flooding soils using mesocosms in a laboratory experiment. The soils were flooded with lake water, and the water was replenished on a weekly basis. The net P flux from soils to surface water was estimated by measuring differences in P concentrations between water that had been in the mesocosms and the lake water used for replenishment. After the flooding experiment, we measured the concentrations of four forms of soil P using a modification of the Hedley procedure, to examine relationships between soil P chemistry and P release. The majority of P was released in the first two days of the experiment, and all detectable P was released by the end of the second month. We estimated that 1–9 g P/m2 were released from the soils to the water column over the course of the experiment, which amounted to 1%–16% of total soil P. Scaling up to the entire wetland, this totals approximately 64 tons P released over 3,000 ha. We did not find any statistically significant relationships between any of the four forms of soil P and the amount of P released in the flooding experiment. Even though we demonstrate here that P is released while undertaking wetland restoration projects on former agricultural land, it is likely to be a temporary process, and once the wetland begins to resume more natural hydrological and biogeochemical functions and vegetation structure, it will re-start the process of soil accretion and P sequestration.
doi_str_mv 10.1672/0277-5212(2007)27[1025:SPRFAR]2.0.CO;2
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While undisturbed wetlands often are net sinks for P and other nutrients, there is evidence that newly flooded restoration wetlands on former agricultural land initially release P to surface waters. The objectives of this study were to: 1) measure P release from soils to overlying surface waters that would occur when re-flooding agricultural fields to restore a lake fringe wetland connected to Upper Klamath Lake, Oregon; and 2) identify management strategies to abate nutrient release from soils during restoration to minimize P loading to Upper Klamath Lake. We simulated the process of re-flooding soils using mesocosms in a laboratory experiment. The soils were flooded with lake water, and the water was replenished on a weekly basis. The net P flux from soils to surface water was estimated by measuring differences in P concentrations between water that had been in the mesocosms and the lake water used for replenishment. After the flooding experiment, we measured the concentrations of four forms of soil P using a modification of the Hedley procedure, to examine relationships between soil P chemistry and P release. The majority of P was released in the first two days of the experiment, and all detectable P was released by the end of the second month. We estimated that 1–9 g P/m2 were released from the soils to the water column over the course of the experiment, which amounted to 1%–16% of total soil P. Scaling up to the entire wetland, this totals approximately 64 tons P released over 3,000 ha. We did not find any statistically significant relationships between any of the four forms of soil P and the amount of P released in the flooding experiment. Even though we demonstrate here that P is released while undertaking wetland restoration projects on former agricultural land, it is likely to be a temporary process, and once the wetland begins to resume more natural hydrological and biogeochemical functions and vegetation structure, it will re-start the process of soil accretion and P sequestration.</abstract><cop>1313 Dolley Madison Boulevard, Suite 402, McLean, Virginia, USA 22101</cop><pub>The Society of Wetland Scientists</pub><doi>10.1672/0277-5212(2007)27[1025:SPRFAR]2.0.CO;2</doi><tpages>11</tpages></addata></record>
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source SpringerLink Journals; BioOne Complete; ProQuest Central
subjects Agricultural land
agricultural soils
ecological restoration
Environmental restoration
eutrophication
Experiments
flooded conditions
Flooding
Floods
Lakes
leaching
Mesocosms
Nutrient release
Nutrients
Phosphorus
phosphorus retention
REGULAR SUBMISSIONS
Restoration
Soil chemistry
soil phosphorus fractionation
Soil water
Soils
Statistical analysis
Surface water
Vegetation
Water circulation
Water column
water quality
wetland restoration
wetland soils
Wetlands
title SOIL PHOSPHORUS RELEASE FROM A RESTORATION WETLAND, UPPER KLAMATH LAKE, OREGON
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