Abstract

Coastal salt marshes are valuable and critical components of tidal landscapes, currently threatened by increasing rates of sea level rise, wave-induced lateral erosion, decreasing sediment supply, and human pressure. Halophytic vegetation plays an important role in salt-marsh erosional and depositional patterns and marsh survival. Mapping salt-marsh halophytic vegetation species and their fractional abundance within plant associations can provide important information on marsh vulnerability and coastal management. Remote sensing has often provided valuable methods for salt-marsh vegetation mapping; however, it has seldom been used to assess the fractional abundance of halophytes. In this study, we developed and tested a novel approach to estimate fractional abundance of halophytic species and bare soil that is based on Random Forest (RF) soft classification. This approach can fully use the information contained in the frequency of decision tree “votes” to estimate fractional abundance of each species. Such a method was applied to WorldView-2 (WV-2) data acquired for the Venice lagoon (Italy), where marshes are characterized by a high diversity of vegetation species. The proposed method was successfully tested against field observations derived from ancillary field surveys. Our results show that the new approach allows one to obtain high accuracy (6.7% < root-mean-square error (RMSE) < 18.7% and 0.65 < R2 < 0.96) in estimating the sub-pixel fractional abundance of marsh-vegetation species. Comparing results obtained with the new RF soft-classification approach with those obtained using the traditional RF regression method for fractional abundance estimation, we find a superior performance of the novel RF soft-classification approach with respect to the existing RF regression methods. The distribution of the dominant species obtained from the RF soft classification was compared to the one obtained from an RF hard classification, showing that numerous mixed areas are wrongly labeled as populated by specific species by the hard classifier. As for the effectiveness of using WV-2 for salt-marsh vegetation mapping, feature importance analyses suggest that Yellow (584–632 nm), NIR 1 (near-infrared 1, 765–901 nm) and NIR 2 (near-infrared 2, 856–1043 nm) bands are critical in RF soft classification. Our results bear important consequences for mapping and monitoring vegetation-species fractional abundance within plant associations and their dynamics, which are key aspects in biogeomorphic analyses of salt-marsh landscapes.

Highlights

  • Salt-marsh ecosystems are transition zones between aquatic and terrestrial systems and provide critical ecological and geomorphological functions in tidal landscapes [1,2,3,4,5]

  • Consistent with observational evidence [2,45,53,74], maps of fractional abundance of each species provided by the “soft” Random Forest (RF) algorithm (Figure 4) emphasize the clear link between vegetation distribution and marsh surface morphology, which is strongly related to the distance to main channels representing the source of sediments delivered to the platform [136]

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Summary

Introduction

Salt-marsh ecosystems are transition zones between aquatic and terrestrial systems and provide critical ecological and geomorphological functions in tidal landscapes [1,2,3,4,5]. Vegetation spatial patterns are characterized by sharply defined patches of typical species associations [41,42,43,44,45,46,47,48,49] This spatial organization, or zonation, can be attributed to the adaptation of halophytes to edaphic conditions [50,51,52,53,54,55,56,57,58], species competition [59,60,61,62], and the capability of halophytes to engineer salt-marsh landscapes via biogeomorphic feedbacks [40,48,49,63]

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