Abstract

Wetland delineations conducted in the United States utilize field indicators as proxy measures of the presence or absence of wetland hydrology. Water-stained leaves provide a practical, qualitative field indicator of wetland hydrology; however, the formation of water-stained leaves has not been elucidated. In response, leaves from six tree species were examined under five treatments to investigate the water-staining process and concomitant timeframes. Results indicate that leaf staining occurred within 14-21 days of continuous exposure to wetland waters and sediment under both laboratory and field conditions. Leaf staining was characterized by readily observable shifts in leaf color (i.e., decreasing Munsell hue, value, and chroma) causing the leaves to appear very dark or black. No color shifts associated with leaf staining occurred in treatments exposed to upland conditions. The timeframe associated with leaf staining corresponds with established wetland hydrology criteria requiring a minimum hydroperiod of 14 consecutive days of soil saturation, flooding, or ponding. Leaves exposed to wetland waters and sediment underwent color shifts significantly faster and to a greater extent than leaves inundated with deionized water, likely as a result of increased microbial abundance and the presence of anaerobic conditions in the simulated wetland treatments. Results suggest that water-stained leaves 1) are a useful and reliable wetland hydrology field indicator for wetland delineation purposes, 2) may provide a proxy measure of wetland hydroperiod, and 3) Munsell color measurements can help differentiate between leaves exposed to wetland and upland conditions.

Highlights

  • The U.S Army Corps of Engineers (USACE) along with the U.S Environmental Protection Agency maintains responsibility for the regulation of certain aquatic resources, including wetlands, in the United States as outlined in the Clean Water Act (National Research Council 1995)

  • Each of the leaf species exposed to inundation (DI, Simulated wetland laboratory treatments (SED), lake fringe wetland (LF)) displayed decreases in hue, value, and chroma during the study, the magnitude and rate of color change varied with treatment and species (Figs. 1 and 2)

  • No significant differences in leaf color were detected at day 7 day (p ≥ 0.352 for all parameters; Tables S1-S8), but after 14 days of inundation leaves exposed to simulated wetland treatments SED and CF (11.0±2.1) displayed lower Munsell hues than the simulated upland treatments UP (33.2±2.0) and UP-SED (31.2±3.4) across all leaf species (p ≤ 0.009)

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Summary

Introduction

The U.S Army Corps of Engineers (USACE) along with the U.S Environmental Protection Agency maintains responsibility for the regulation of certain aquatic resources, including wetlands, in the United States as outlined in the Clean Water Act (National Research Council 1995). The Corps Manual outlines a three-factor approach to wetland identification and delineation based upon the presence or absence of 1) hydrophytic vegetation, 2) hydric soils, and 3) wetland hydrology (Tiner 2016). Several studies have examined the development of hydric soils and hydrophytic vegetation communities and address the application of those factors for wetland delineation. These studies identify the biological, chemical, and physical factors required for hydric soils and hydrophytic plant communities to perform wetland functions. Richardson and Vepraskas (2001) provide an overview of hydric

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