Article

Dragonfly Mercury Project: Mount Rainier National Park 2020 Data Summary

A map of Mount Rainier National Park with black circles marking locations new in 2020, white circles resampled locations and squares for locations sampled in 2014-2019.
Dragonfly Mercury Project sample locations in Mount Rainier National Park.

The Dragonfly Mercury Project (DMP) is a national surveillance, monitoring, and research program that brings together citizen engagement and education with scientific efforts to understand mercury (Hg) risks to protected areas. 2020 was the seventh year that Mount Rainier National Park (MORA) participated in the DMP!

A bar graph of total mercury concentrations for three locations: lower deadwood lake, with 100 ng/g, the park mean; wetland 1353, with almost 200 ng/g, higher than the study mean; and Paradise valley pond, with 76 ng/g, under the park mean.
Site (bars), family (points), park (dashed line) and study (dotted line; 2014-2020) mean mercury concentrations in dragonfly larvae collected from MORA in 2020. Park, site, and study mean mercury concentrations are Aeshnid-equivalents, family means are geometric means of raw mercury concentrations.

Summary

Unless noted, all Hg concentrations have been converted to their equivalent concentration in the family Aeshnidae (Eagles-Smith et al. 2020).

The park geometric mean (± standard error) Hg concentration at MORA in 2020 was 113.3 ± 9.2 ng/g dry weight (dw) compared to the overall (across all years of participation) park geometric mean Hg concentration of 98.9 ± 3.1 ng/g dw and the study-wide (2014 – 2020) geometric mean Hg concentration of 151.3 ± 1.0 ng/g dw. Among the three sites sampled from MORA in 2020, geometric mean dragonfly Hg concentrations ranged from 76.0 to 194.7 ng/g dw.
_
Eagles-Smith et al. 2020. A national-scale assessment of mercury bioaccumulation in United States national parks using dragonfly larvae as biosentinels through a citizen-science framework. Environ Sci Technol 54(14):8779–8790. DOI: 10.1021/acs.est.0c01255

Graph of cumulative frequency (0-100) of aeshnid-equivalent total mercury concentration (10-1000 ng/g dw) forming a colored "S" line that is blue in the lower left and rises to red-purple high concentrations/frequencies in the upper right.
Distribution of site mean Aeshnid-equivalent total mercury concentrations among the five Integrated Impairment Index categories. Sites sampled from MORA in 2020 are highlighted and labeled. *The percent of sites across all parks that have lower Hg concentrations than each of the highlighted sites.

Integrated Impairment Index

  • The Integrated Impairment Index classifies Aeshnid-equivalent dragonfly THg concentrations into five categories based on the number of taxa estimated to exceed increasingly severe impairment benchmarks for fish, wildlife, and human health risk. Because the Integrated Impairment Index looks at potential risks to a variety of taxa it provides a more complete estimate of potential health risks than would be seen examining any single benchmark. See Eagles-Smith et al. 2020 for additional details.
  • In 2020, two MORA sites were classified as ‘low risk’ and one site as ‘moderate risk’ for Hg impairment.
  • Across all parks, 24% of sites sampled in 2020 were classified as ‘low risk’ and 51% were classified as ‘moderate risk’.
Line graph of total mercury concentrations per collection year, 2014-2020.
Annual mean total mercury concentrations (Aeshnid-equivalents; ng/g dw ± standard error) in dragonfly larvae collected from MORA between 2014 and 2020. Means are least-squares means from a model that accounts for differences among the sites sampled each year.

Temporal Variation in Dragonfly Hg

In 2020, the mean dragonfly Hg concentration at MORA was similar to the mean concentrations across all sites in 2016 and 2019, but higher than the mean concentrations from 2014, 2015, 2017, and 2018.


What are these data and what do they mean?
We estimated annual mean dragonfly Hg concentrations using a model that takes into account differences in the sites sampled each year of MORA’s participation in the DMP and used a Tukey HSD test to identify differences among annual means. This enables comparisons of Hg concentrations among years and provides insights into temporal variability, despite inconsistencies in which sites were sampled each year. However, any apparent trends in the data must be interpreted cautiously because individual site characteristics have an important influence on dragonfly Hg concentrations. Although these results account for variation due to sampling site, doing so increases the uncertainty in the estimates and thus our power to identify trends.

Two bar graphs showing number of people per site (left) and hours of participation per site (right). Both are below the the study mean.
Average (bars) and total (numbers in bars) public participants (left) and public participant hours (right) contributing to dragonfly collection at MORA in 2020. Bold lines indicate average values across all parks that participated in 2020.

Public Engagement

The DMP engages local communities and promotes scientific curiosity while harnessing the power of public science to study mercury pollution nationwide.

In 2020, 3 public participants were engaged in dragonfly collections at MORA, with an average of 1.0 public participants per site. Across all sampling efforts, public participants contributed an estimated 5.7 hours to dragonfly sampling at MORA in 2020, averaging 1.9 public participant hours per site. Across all sites, 60% of the dragonfly larvae from MORA with field identifications were correctly identified to family.

Summary Table

Site

Site Code

Family

N

ID Accur.

Total Length (mm)

Total Mercury (ng/g dw)a

Mean

Range

Mean

Range

Lower Deadwood Lake

MRNP040

Corduliidae/Libellulidae

11

100%

20.1

17.1 - 21.8

74.9

62.6 - 92.6

Wetland 1353

MRNP077

Corduliidae/Libellulidae

12

0%

15.0

13.4 - 16.9

158.3

76.6 - 315.5

Paradise Valley Pond (lin09)

MRNP137

Aeshnidae

8

100%

22.0

19.3 - 29.8

69.6

60.7 - 86.1

Corduliidae/Libellulidae

2

0%

16.5

15.9 - 17.1

57.3

57.1 - 57.6

Macromiidae

2

100%

22.2

21.1 - 23.3

63.5

58.1 - 69.3

araw Hg concentrations not converted to Aeshnid-equivalents

Mount Rainier National Park

Last updated: July 19, 2022