Ethan D. Pawlowski, Lindsey Witthaus, Jason M. Taylor, Matthew T. Moore, Sarah McNamara, Eric Stevens, Quentin D. Read
{"title":"The role of vegetation, drying, and rewetting on water and sediment phosphorus concentrations in an experimental ditch channel experiment","authors":"Ethan D. Pawlowski, Lindsey Witthaus, Jason M. Taylor, Matthew T. Moore, Sarah McNamara, Eric Stevens, Quentin D. Read","doi":"10.1002/agg2.70168","DOIUrl":null,"url":null,"abstract":"<p>Intermittent drying and rewetting of agricultural drainage ditch networks along with vegetation presence play a significant role in phosphorus (P) fate and transport to the receiving water bodies. To examine how vegetation influences the response of P transport to drying and rewetting, we lined six low-gradient (0.01% slope) stainless steel experimental ditches with alluvial sediment and planted vegetation (rice cutgrass, <i>Leersia oryzoides</i>) in three ditches while maintaining bare sediment in the other three ditches. We then added a 26-g P pulse to each ditch and recirculated the ditch water for maximum retention prior to draining. Three subsequent wetting periods, separated by 10-day drying periods, used water with no added P that flowed through the ditches (i.e., water did not recirculate). We monitored discharge, water quality, and P concentrations during the initial P addition and subsequent rewetting periods. Sediment properties, including water-extractable P, were sampled before and after each rewetting period. The vegetated ditches rapidly removed P from the water column, but similar total removal was observed in all ditches following the first wet period. Subsequent rewetting periods released concentrations between 14 and 45 µg P L<sup>−1</sup> in both treatments. Integrated release rates showed 99% P retention in the vegetated ditches and 98% retention in unvegetated ditches after all wet and dry cycles. Water-extractable P was not found to be significantly different based on channel feature, vegetation presence, or time. Our results suggest P is likely retained in both vegetated and unvegetated low-gradient ditches with intermittent flow regimes and similar sediment properties.</p>","PeriodicalId":7567,"journal":{"name":"Agrosystems, Geosciences & Environment","volume":"8 3","pages":""},"PeriodicalIF":1.5000,"publicationDate":"2025-07-13","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"https://onlinelibrary.wiley.com/doi/epdf/10.1002/agg2.70168","citationCount":"0","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Agrosystems, Geosciences & Environment","FirstCategoryId":"1085","ListUrlMain":"https://acsess.onlinelibrary.wiley.com/doi/10.1002/agg2.70168","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"Q3","JCRName":"AGRONOMY","Score":null,"Total":0}
引用次数: 0
Abstract
Intermittent drying and rewetting of agricultural drainage ditch networks along with vegetation presence play a significant role in phosphorus (P) fate and transport to the receiving water bodies. To examine how vegetation influences the response of P transport to drying and rewetting, we lined six low-gradient (0.01% slope) stainless steel experimental ditches with alluvial sediment and planted vegetation (rice cutgrass, Leersia oryzoides) in three ditches while maintaining bare sediment in the other three ditches. We then added a 26-g P pulse to each ditch and recirculated the ditch water for maximum retention prior to draining. Three subsequent wetting periods, separated by 10-day drying periods, used water with no added P that flowed through the ditches (i.e., water did not recirculate). We monitored discharge, water quality, and P concentrations during the initial P addition and subsequent rewetting periods. Sediment properties, including water-extractable P, were sampled before and after each rewetting period. The vegetated ditches rapidly removed P from the water column, but similar total removal was observed in all ditches following the first wet period. Subsequent rewetting periods released concentrations between 14 and 45 µg P L−1 in both treatments. Integrated release rates showed 99% P retention in the vegetated ditches and 98% retention in unvegetated ditches after all wet and dry cycles. Water-extractable P was not found to be significantly different based on channel feature, vegetation presence, or time. Our results suggest P is likely retained in both vegetated and unvegetated low-gradient ditches with intermittent flow regimes and similar sediment properties.