Leaching from restored peatlands: Is there a connection between porewater and runoff quality?

Ecological restoration has emerged as a conservation approach for peatlands, which often experience increased leaching of dissolved organic carbon (DOC) and soluble nitrogen (N tot ) and phosphorus (P tot ) following drainage. Restoration, however, introduces new disturbances that temporarily elevate leaching, while monitoring peatland runoff remains challenging, highlighting the need for new methods to assess restoration success. We studied changes and connections of porewater and runoff quality across three pristine and five drained and restored boreal peatland sites, quantified runoff loads, and developed regression models to estimate loads using porewater data. After restoration, median runoff DOC, N tot , and porewater and runoff P tot concentrations showed respective increases of 35, 34, 67, and 224% compared to the drained state, peaking within 1–4 years before declining. Porewater DOC and N tot levels started decreasing immediately. Porewater concentrations approached near-pristine levels within roughly 4–10 years depending on the parameter and site, whereas runoff levels stayed elevated through tenth year with only site-specific exceptions. Porewater and runoff DOC and N tot were strongly correlated, while P tot correlations varied among drained, restored, and pristine states. DOC, N tot , and P tot loads initially rose after restoration but declined over the following >3 years post-restoration to 61.3, 1.52, and 0.038 kg/ha/yr, typically falling below drained state levels. Regression models overestimated produced annual runoff loads from porewater concentrations by an average of 50.9%. Models predicted DOC most accurately, while performance for N tot and P tot was weaker and varied across sites. • Porewater quality reached natural levels roughly 4–10 years after restoration. • In the 10th year runoff quality remained elevated but lower than in the drained state. • Runoff load increased immediately after restoration but decreased for the later years. • Porewater quality correlated well with runoff quality. • We estimated runoff load from porewater concentrations with varying accuracy.

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Publication Details

Journal
Ecological Engineering
Published
2026-03-07
DOI
https://doi.org/10.1016/j.ecoleng.2026.107953
Primary Topic
Peatlands and Wetlands Ecology
Type
article
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article

Leaching from restored peatlands: Is there a connection between porewater and runoff quality?

Meseret Walle Menberu, Santtu Kareksela, Teemu Tahvanainen, Masoud Irannezhad et al.
Ecological Engineering
Peatlands and Wetlands Ecology
article

Leaching from restored peatlands: Is there a connection between porewater and runoff quality?

Meseret Walle Menberu, Santtu Kareksela, Teemu Tahvanainen, Masoud Irannezhad, Petra Korhonen, Lauri Ikkala, Hannu Marttila, Anna-Kaisa Ronkanen, Lassi Päkkilä
article en

Abstract

Ecological restoration has emerged as a conservation approach for peatlands, which often experience increased leaching of dissolved organic carbon (DOC) and soluble nitrogen (N tot ) and phosphorus (P tot ) following drainage. Restoration, however, introduces new disturbances that temporarily elevate leaching, while monitoring peatland runoff remains challenging, highlighting the need for new methods to assess restoration success. We studied changes and connections of porewater and runoff quality across three pristine and five drained and restored boreal peatland sites, quantified runoff loads, and developed regression models to estimate loads using porewater data. After restoration, median runoff DOC, N tot , and porewater and runoff P tot concentrations showed respective increases of 35, 34, 67, and 224% compared to the drained state, peaking within 1–4 years before declining. Porewater DOC and N tot levels started decreasing immediately. Porewater concentrations approached near-pristine levels within roughly 4–10 years depending on the parameter and site, whereas runoff levels stayed elevated through tenth year with only site-specific exceptions. Porewater and runoff DOC and N tot were strongly correlated, while P tot correlations varied among drained, restored, and pristine states. DOC, N tot , and P tot loads initially rose after restoration but declined over the following >3 years post-restoration to 61.3, 1.52, and 0.038 kg/ha/yr, typically falling below drained state levels. Regression models overestimated produced annual runoff loads from porewater concentrations by an average of 50.9%. Models predicted DOC most accurately, while performance for N tot and P tot was weaker and varied across sites. • Porewater quality reached natural levels roughly 4–10 years after restoration. • In the 10th year runoff quality remained elevated but lower than in the drained state. • Runoff load increased immediately after restoration but decreased for the later years. • Porewater quality correlated well with runoff quality. • We estimated runoff load from porewater concentrations with varying accuracy.

Ecological EngineeringVol. 227
Geological Survey of Finland (FI), University of Eastern Finland (FI), North China University of Water Resources and Electric Power (CN), Finnish Environment Institute (FI), Metsähallitus (Finland) (FI), Yellow River Institute of Hydraulic Research (CN), Australian University, Kuwait (KW), University of Oulu (FI)
Life in Land
Openalex Percentile: Top 39%
Peatlands and Wetlands Ecology
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