TY - JOUR
T1 - Determining vegetation metric robustness to environmental and methodological variables
AU - Stern, Jessica L.
AU - Herman, Brook D.
AU - Matthews, Jeffrey W.
N1 - Funding Information:
We thank D. Zaya for assistance with R code; C. Ihssen for help with data management; R. Baranowski, D. Galloway, D. Larsen, D. Lattuca, J. Morton, L. Oliver, D. Price, K. Raposa, R. Sliwinski, L. Spencer, W. Widener, and J. Zylka for assistance with site selection and/or field sampling; C. Castle, B. Charles, S. Tillman, and J. Zinnen for field assistance and manuscript edits; B. Molano-Flores and G. Spyreas for comments on the manuscript, and the U.S. Army Corps of Engineers (USACE) Chicago District, the USACE New England District, the USACE Albuquerque District, the USACE Jacksonville District, the South Florida Water Management District, the Narragansett Bay National Estuarine Research Reserve, the Indiana Department of Natural Resources, the Rhode Island Department of Environmental Management, and Narragansett Bay Save the Bay for property access and equipment use.
Funding Information:
This project was funded by the US Army Corps of Engineers Ecosystem Management and Restoration Research Program (EMRRP) through the Environmental Laboratory of the US Army Corps of Engineers.
Publisher Copyright:
© 2021, The Author(s), under exclusive licence to Springer Nature Switzerland AG.
PY - 2021/10
Y1 - 2021/10
N2 - Land managers need reliable metrics for assessing the quality of restorations and natural areas and prioritizing management and conservation efforts. However, it can be difficult to select metrics that are robust to sampling methods and natural environmental differences among sites, while still providing relevant information regarding ecosystem changes or stressors. We collected herbaceous-layer vegetation data in wetlands and grasslands in four regions of the USA (the Midwest, subtropical Florida, arid southwest, and coastal New England) to determine if commonly used vegetation metrics (species richness, mean coefficient of conservatism [mean C], Floristic Quality Index [FQI], abundance-weighted mean C, and percent non-native species cover) were robust to environmental and methodological variables (region, site, observer, season, and year), and to determine adequate sample sizes for each metric. We constructed linear mixed effects models to determine the influence of these environmental and methodological variables on vegetation metrics and used metric accumulation curves to determine the effect of sample size on metric values. Species richness and FQI varied among regions, and year and observer effects were also highly supported in our models. Mean C was the metric most robust to sampling variables and stabilized at less sampling effort compared to other metrics. Assessment of mean C requires sampling a small number of quadrats (e.g. 20), but assessment of species richness or FQI requires more intensive sampling, particularly in species-rich sites. Based on our analysis, we recommend caution be used when comparing metric values among sites sampled in different regions, different years, or by different observers.
AB - Land managers need reliable metrics for assessing the quality of restorations and natural areas and prioritizing management and conservation efforts. However, it can be difficult to select metrics that are robust to sampling methods and natural environmental differences among sites, while still providing relevant information regarding ecosystem changes or stressors. We collected herbaceous-layer vegetation data in wetlands and grasslands in four regions of the USA (the Midwest, subtropical Florida, arid southwest, and coastal New England) to determine if commonly used vegetation metrics (species richness, mean coefficient of conservatism [mean C], Floristic Quality Index [FQI], abundance-weighted mean C, and percent non-native species cover) were robust to environmental and methodological variables (region, site, observer, season, and year), and to determine adequate sample sizes for each metric. We constructed linear mixed effects models to determine the influence of these environmental and methodological variables on vegetation metrics and used metric accumulation curves to determine the effect of sample size on metric values. Species richness and FQI varied among regions, and year and observer effects were also highly supported in our models. Mean C was the metric most robust to sampling variables and stabilized at less sampling effort compared to other metrics. Assessment of mean C requires sampling a small number of quadrats (e.g. 20), but assessment of species richness or FQI requires more intensive sampling, particularly in species-rich sites. Based on our analysis, we recommend caution be used when comparing metric values among sites sampled in different regions, different years, or by different observers.
KW - Conservation
KW - Floristic quality index
KW - Mean coefficient of conservatism
KW - Monitoring
KW - Natural area management
KW - Vegetation metrics
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U2 - 10.1007/s10661-021-09445-9
DO - 10.1007/s10661-021-09445-9
M3 - Article
C2 - 34519882
AN - SCOPUS:85114775893
SN - 0167-6369
VL - 193
JO - Environmental Monitoring and Assessment
JF - Environmental Monitoring and Assessment
IS - 10
M1 - 647
ER -