Structure Condition Services Stressors
Macroinvertebrates inhabiting streams are sensitive to pollutants and runoff, and thus, serve as bioindicators of water quality. They typically require high levels of dissolved oxygen and low turbidity in the water. Here, we used the species richness of macroinvertebrates found in Ranch Brook in Underhill, Vermont. The current year is scored as the difference between 0 and the target (maximum value +10% of the range).
While there is a slight positive trend in the richness of sensitive species (i.e. Ephemeroptera, Plecoptera, and Trichoptera taxa) at Ranch Brook over the last 19 years, richness values have stayed within a consistent range of 20-27 species. These values are typical of small, high-elevation, low productivity Vermont reference streams. Variation in richness values on a year-to-year basis can be affected by variability in environmental conditions, including flow regime. While it would not be expected that species richness would continue to increase significantly in this forested headwater stream, it is possible that increasing stream temperatures or extreme flood events associated with climate change could cause an eventual decline.
Aaron Moore, Environmental Scientist; Vermont Agency of Agriculture, Food and Markets (2020)
The score is calculated using a target value and the historical range of the the entire long-term dataset. The higher the score, the closer this year's value is to the target.
Once the score is computed for each year, the trend in scores over time is calculated. If the trend is significantly positive or negative, the long-term trend is marked as increasing or decreasing respectively.
Distance between 0 and target (scaled 1-5)
Data maximum + 10% of range
|Directionality of scores||
No change from the long-term mean is better.
|Minimum value used in scoring||
|Maximum value used in scoring||
Data maximum + 10% of range
Species richness was collected from the Vermont Integrated Watershed Information System1. We selected one location, Ranch Brook (site #502032) in Underhill VT, where species richness metrics were computed for macroinvertebrates. Data from other locations in the state did not have annually-resolved data with a sufficient long-term record to warrant inclusion. We used the EPT Richness score as computed by the dataset authors2. EPT richness is a count of the unique number of taxa identified in the sample that belong to a trio of particularly sensitive macroinvertebrate orders - Ephemeroptera (mayflies), Plecoptera (stoneflies), and Tricoptera (caddisflies). In cases where a specimen could not be identified to the species level, it was only counted as unique taxon if no other specimens were identified to that level or below. In some cases, there were multiple samples in a single year. In these cases, we took the mean of the EPT Richness scores as the value for the year. The target for these data was set to be the maximum value plus 10% of the range. The annual score was computed as the difference between the lower scoring bound of 0 (indicating no EPT taxa were identified) and the target, scaled between 1 and 5.
Timber harvested from Vermont's forests provide jobs and income to the state, and support the maintenance of forest land.
Aquatic species that live in forested streams provide an assessment of the health of the surrounding forest.
The ability of forests to support big game species for hunting is an important service on which many Vermonters rely.
The amount of carbon stored by forests helps offset rising atmospheric carbon dioxide concentrations.
Maple syrup production is an iconic staple of Vermont's landscape and is reliant on the continued health of maple trees.
The number of people using Vermont's forests for camping and hiking provides a measure of the value of our forests for recreational uses.
The number and diversity of bird species that live and use forested habitats provides a sense of the quality of Vermont's forestlands for a variety of species.