Abstract

The variation in sodium concentrations in waters of natural fens and marshes on the western Canadian landscape provides a background for choosing the appropriate plants for wetland reclamation. Broad tolerances to salinity are especially important for reclamation trials on saline-rich ‘in-pits’ that were left from open-pit oil sands mining. One such species, Carex aquatilis, has been identified as a key species in early reclamation attempts; however, at the Sandhill Wetland on the Syncrude Canada oil sands lease, this species has aggressively colonized, dominating parts of the wetland and limiting species diversity. A second species, also widespread on natural lake shores and marshes, is Carex atherodes, with field observations suggesting a broad tolerance to salinity. Here, we examine the responses of this species to a series of sodium concentrations and compare these to those of C. aquatilis. In particular, we addressed three questions: (1) How do structural attributes of C. atherodes respond to a series of Na+ concentration treatments? (2) Are different structural responses related to the functional attributes of photosynthesis, stomatal conductance, and/or transpiration rate? (3) How do these responses compare to those of C. aquatilis? We implemented a phytotron experiment to test the responses of these two species to either five or six concentrations of sodium, ranging from 20 to 3000 mg Na+ L−1. In general, structural responses of C. atherodes did not differ between 50 and 789 mg Na+ L−1, while performances of all attributes were reduced at 1407 mg L−1. Physiological attributes had high variation, but also had reduced performances at similar treatment levels. In comparison, a clear threshold was present for structural attributes in Carex aquatilis between 1650 and 2148 mg Na+ L−1, while physiological attributes were reduced between 1035 to 1650 mg Na+ L−1. These responses from C. aquatilis were similar to those previously reported. Na+ concentrations in porewater at the Sandhill Wetland in 2019 reached as high as 1200 mg Na+ L−1, with natural subsaline and sodic sites ranging much higher. Although all of the plants in the treatments remained viable at the end of the experiment, these results indicate that Na+ concentrations above 1500–2000 mg Na+ L−1 may inhibit the growth of these two species and decrease their competitive abilities.

Highlights

  • Oil sand deposits lie under 141,000 km2 of the landscape of Alberta, Canada and in 1967, commercial oil sands mining began in northeastern Alberta [1]

  • The highest biomass was produced by C. atherodes exposed to 789 mg Na+ L−1, which decreased dramatically with increasing sodium exposure (Figure 1A)

  • Plants exposed to 789 mg Na+ L−1 produced 1.8 times more aboveground biomass than plants exposed to 1407 mg Na+ L−1 and 5.6 times more aboveground biomass than plants exposed to 2731 mg Na+ L−1

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Summary

Introduction

Oil sand deposits lie under 141,000 km of the landscape of Alberta, Canada and in 1967, commercial oil sands mining began in northeastern Alberta [1]. After mining operations are concluded, these large-scale depressions, or in-pits, are refilled with a variety of tailings and process waters that have relatively high concentrations of cations and anions [4,5,6]. Reclamation of in-pit deposits is legislatively mandated to a return to equivalent land capability [7], and these sites include areas of upland and wetland vegetation that provide a new physical landscape [8]. The salinity (especially Na+) of oil sands landscapes is considerably higher than what is typical of both bogs and fens [12,16], and depending on its severity, high Na+ concentrations can provide a harsh limiting environment for many plants [19,20]. Understanding how desired plants will respond to increased Na+ concentrations is crucial to successful reclamation

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