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Dive into the research topics where David M. Mushet is active.

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Featured researches published by David M. Mushet.


Wetlands | 2004

The wetland continuum: A conceptual framework for interpreting biological studies

Ned H. Euliss; James W. LaBaugh; Leigh H. Fredrickson; David M. Mushet; Murray K. Laubhan; George A. Swanson; Thomas C. Winter; Donald O. Rosenberry; Richard D. Nelson

We describe a conceptual model, the wetland continuum, which allows wetland managers, scientists, and ecologists to consider simultaneously the influence of climate and hydrologic setting on wetland biological communities. Although multidimensional, the wetland continuum is most easily represented as a two-dimensional gradient, with ground water and atmospheric water constituting the horizontal and vertical axes, respectively. By locating the position of a wetland on both axes of the continuum, the potential biological expression of the wetland can be predicted at any point in time. The model provides a framework useful in the organization and interpretation of biological data from wetlands by incorporating the dynamic changes these systems undergo as a result of normal climatic variation rather than placing them into static categories common to many wetland classification systems. While we developed this model from the literature available for depressional wetlands in the prairie pothole region of North America, we believe the concept has application to wetlands in many other geographic locations.


Wetlands | 1996

Water-Level Fluctuation in Wetlands as a Function of Landscape Condition in the Prairie Pothole Region

Ned H. Euliss; David M. Mushet

We evaluated water-level fluctuation (maximum water depth — minimum water depth/catchment size) in 12 temporary, 12 seasonal, and 12 semipermanent wetlands equally distributed among landscapes dominated by tilled agricultural lands and landscapes dominated by grassland. Water levels fluctuated an average of 14.14 cm in wetlands within tilled agricultural landscapes, while water levels in wetlands within grassland landscapes fluctuated an average of only 4.27 cm. Tillage reduces the natural capacity of catchments to mitigate surface flow into wetland basins during precipitation events, resulting in greater water-level fluctuations in wetlands with tilled catchments. In addition, water levels in temporary and seasonal wetlands fluctuated an average of 13.74 cm and 11.82 cm, respectively, while water levels in semipermanent wetlands fluctuated only 2.77 cm. Semipermanent wetlands receive a larger proportion of their water as input from ground water than do either temporary or seasonal wetlands. This input of water from the ground has a stabilizing effect on water-levels of semipermanent wetlands. Increases in water-level fluctuation due to tillage or due to alteration of ground-water hydrology may ultimately affect the composition of a wetland’s flora and fauna. In this paper, we also describe an inexpensive device for determining absolute maximum and minimum water levels in wetlands.


Proceedings of the National Academy of Sciences of the United States of America | 2016

Do geographically isolated wetlands influence landscape functions

Matthew J. Cohen; Irena F. Creed; Laurie C. Alexander; Nandita B. Basu; Aram J. K. Calhoun; Christopher Craft; Ellen D’Amico; Edward S. DeKeyser; Laurie Fowler; Heather E. Golden; James W. Jawitz; Peter Kalla; L. Katherine Kirkman; Charles R. Lane; Megan Lang; Scott G. Leibowitz; David Bruce Lewis; John M. Marton; Daniel L. McLaughlin; David M. Mushet; Hadas Raanan-Kiperwas; Mark Cable Rains; Lora L. Smith; Susan C. Walls

Geographically isolated wetlands (GIWs), those surrounded by uplands, exchange materials, energy, and organisms with other elements in hydrological and habitat networks, contributing to landscape functions, such as flow generation, nutrient and sediment retention, and biodiversity support. GIWs constitute most of the wetlands in many North American landscapes, provide a disproportionately large fraction of wetland edges where many functions are enhanced, and form complexes with other water bodies to create spatial and temporal heterogeneity in the timing, flow paths, and magnitude of network connectivity. These attributes signal a critical role for GIWs in sustaining a portfolio of landscape functions, but legal protections remain weak despite preferential loss from many landscapes. GIWs lack persistent surface water connections, but this condition does not imply the absence of hydrological, biogeochemical, and biological exchanges with nearby and downstream waters. Although hydrological and biogeochemical connectivity is often episodic or slow (e.g., via groundwater), hydrologic continuity and limited evaporative solute enrichment suggest both flow generation and solute and sediment retention. Similarly, whereas biological connectivity usually requires overland dispersal, numerous organisms, including many rare or threatened species, use both GIWs and downstream waters at different times or life stages, suggesting that GIWs are critical elements of landscape habitat mosaics. Indeed, weaker hydrologic connectivity with downstream waters and constrained biological connectivity with other landscape elements are precisely what enhances some GIW functions and enables others. Based on analysis of wetland geography and synthesis of wetland functions, we argue that sustaining landscape functions requires conserving the entire continuum of wetland connectivity, including GIWs.


Wetlands | 1999

Influence of agriculture on aquatic invertebrate communities of temporary wetlands in the Prairie Pothole Region of North Dakota, USA

Ned H. Euliss; David M. Mushet

We evaluated the influence of intensive agriculture on invertebrate communities of temporary wetlands as indicated by aquatic invertebrate resting eggs, shells, and cases remaining after wetlands dried. To facilitate the comparison, we sampled 19 wetlands within cropland areas and 19 wetlands within grassland areas. We found resting eggs, shells, and cases of significantly more taxa and greater numbers of cladoceran resting eggs (ephippia), planorbid and physid snail shells, and ostracod shells in wetlands within grasslands than in croplands. We also successfully incubated greater numbers of cladocerans and ostracods from soil samples collected from grassland sites. We were unable to detect differences in the viability of cladoceran ephippia between grassland and cropland wetlands, but our sample size was small due to an absence of ephippia in most cropland wetlands sampled; 74% of the cropland wetlands were devoid of cladoceran ephippia whereas ephippia were well represented in nearly all of our grassland sites. Our results corroborate findings of other investigators that prairie pothole wetlands have been negatively impacted by human activ-, ities. Our study demonstrates that aquatic invertebrates of temporary wetlands have, been negatively impacted by intensive agriculture and suggests that future studies need to assess the influence of agricultural practices on wetland-dependant wildlife.


Wetlands | 2002

FLORISTIC QUALITY ASSESSMENT OF ONE NATURAL AND THREE RESTORED WETLAND COMPLEXES IN NORTH DAKOTA, USA

David M. Mushet; Ned H. Euliss; Terry L. Shaffer

AbstractFloristic quality assessment is potentially an important tool for conservation efforts in the northern Great Plains of North America, but it has received little rigorous evaluation. Floristic quality assessments rely on coefficients assigned to each plant species of a region’s flora based on the conservatism of each species relative to others in the region. These “coefficients of conservatism” (C values) are assigned by a panel of experts familiar with a region’s flora. The floristic quality assessment method has faced some criticism due to the subjective nature of these assignments. To evaluate the effect of this subjectivity on floristic quality assessments, we performed separate evaluations of the native plant communities in a natural wetland complex and three restored wetland complexes. In our first assessment, we used C values assigned “subjectively” by the Northern Great Plains Floristic Quality Assessment Panel. We then performed an independent assessment using the observed distributions of species among a group of wetlands that ranged from highly disturbed to largely undisturbed (data-generated C values). Using the panel-assigned C values, mean C values (


Wetlands | 2015

Geographically isolated wetlands: Rethinking a misnomer

David M. Mushet; Aram J. K. Calhoun; Laurie C. Alexander; Matthew J. Cohen; Edward S. DeKeyser; Laurie Fowler; Charles R. Lane; Megan W. Lang; Mark Cable Rains; Susan C. Walls


Environmental Modelling and Software | 2011

Prototyping an online wetland ecosystem services model using open model sharing standards

Min Feng; Shuguang Liu; Ned H. Euliss; Claudia Young; David M. Mushet

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Environmental Science & Technology | 2010

The Need for Simultaneous Evaluation of Ecosystem Services and Land Use Change

Ned H. Euliss; Loren M. Smith; Shuguang Liu; Min Feng; David M. Mushet; Roger F. Auch; Thomas R. Loveland


Wetlands | 2011

Classifying the Hydrologic Function of Prairie Potholes with Remote Sensing and GIS

Jennifer Rover; Christopher K. Wright; Ned H. Euliss; David M. Mushet; Bruce K. Wylie

) of the restored wetlands rarely exceeded 3.4 and never exceeded 3.9, with the highest values occurring in the oldest restored complex; all but two wetlands in the natural wetland complex had a


Wetlands | 2016

Intermittent Surface Water Connectivity: Fill and Spill Vs. Fill and Merge Dynamics

Scott G. Leibowitz; David M. Mushet; Wesley E. Newton

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Ned H. Euliss

United States Geological Survey

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James W. LaBaugh

United States Geological Survey

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Donald O. Rosenberry

United States Geological Survey

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Craig A. Stockwell

North Dakota State University

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Christopher T. Mills

United States Geological Survey

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Martin B. Goldhaber

United States Geological Survey

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Kyle I. McLean

North Dakota State University

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Laurie C. Alexander

United States Environmental Protection Agency

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Richard D. Nelson

United States Bureau of Reclamation

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