Source: UNIVERSITY OF WASHINGTON submitted to NRP
METAL DEPOSITION ALONG AN URBAN-WILDLAND GRADIENT IN THE PUGET SOUND REGION
Sponsoring Institution
National Institute of Food and Agriculture
Project Status
COMPLETE
Funding Source
Reporting Frequency
Annual
Accession No.
1006427
Grant No.
(N/A)
Cumulative Award Amt.
(N/A)
Proposal No.
(N/A)
Multistate No.
(N/A)
Project Start Date
Sep 16, 2015
Project End Date
Sep 30, 2017
Grant Year
(N/A)
Program Code
[(N/A)]- (N/A)
Recipient Organization
UNIVERSITY OF WASHINGTON
4333 BROOKLYN AVE NE
SEATTLE,WA 98195
Performing Department
Forest Ecology
Non Technical Summary
Vehicle emissions associated with exhaust, lubricants, and tire and brake attrition represent a major form of pollution in busy urban centers in the Pacific Northwest; however, few studies have focused on characterizing the extent and impact of metal emissions from vehicle traffic on forest bryophytes and ecosystem health.We intend to evaluate whether metal deposition associated with the transportation sector in the Puget Sound region is altering ecosystem function by influencing forest bryophytes and their associated food webs.
Animal Health Component
(N/A)
Research Effort Categories
Basic
100%
Applied
(N/A)
Developmental
(N/A)
Classification

Knowledge Area (KA)Subject of Investigation (SOI)Field of Science (FOS)Percent
1410612107050%
1410612113050%
Goals / Objectives
We will assess the extent and impact of transportation related metal deposition on forest ecosystems in the Puget Sound region. The overarching goal of this research is to evaluate patterns of heavy metal deposition along an urban-to-wildland gradient in the Puget Sound region and determine the influence of metal deposition on forest ecosystem health. The four primary objectives of the proposed research are:Evaluate the extent of metal (specifically Zn and Cu) deposition at field sites along an urban-to-wildland gradient and along smaller transportation corridors to remote gradients in the greater Puget Sound region.Use isotopic ratios to help determine pollutant source.Determine the effect of metal on the abundance and diversity of the micro-arthropod community at our field sites.Develop concentration-mortality relationships between Zn and Cu, and micro-arthropods that represent highly susceptible, highly resistant, and the most abundant species.
Project Methods
Over the next two years, we will evaluate heavy metal deposition in the canopy and forest floor of urban, suburban, rural and wilderness settings along gradients of transportation intensity.These data will greatly improve our understanding of metal deposition patterns in association with the transportation sector within the region, which would be useful in the development of policies that aim to minimize the potential long-term impacts of metal deposition on forest epiphytes and ground dwelling bryophytes.1. Metal deposition along an urban wildland gradient:We will deploy 350 resin lysimeters (Susfalk and Johnson, 1996; DeLuca et al., 2008) as metal deposition collectors in a gradient from the Seattle urban corridor to surrounding wilderness areas, both upwind into the Olympic Mountains and downwind into the Cascades. We will place lysimeters both on the forest floor and in the canopy, and simultaneously collect forest floor and epiphytic moss and lichen samples for identification and for metal analyses at approximately 70 field sites. Each location will be georeferenced using a hand held GPS. The lysimeters will remain in place for three months after which they will be retrieved and the resins extracted with 0.5 M HCl. Extracts will be analyzed for an array of metals including Zn, Cu, Fe, Pb, Cr, and Cd by ICP-OES. At each location we place lysimeters, we will also collect replicate epiphytic moss samples from tree branches. Mosses will be identified, dried, acid digested and analyzed for metal content (Bakirdere and Yaman, 2008) also using ICP-OES. We will also use a handheld energy dispersive X-ray fluorescent (XRF) analyzer to assess metal contents of moss and lichen samples in the field.2. Metal source investigations:We will select 30 sites from the 70 sites to evaluate strontium and lead isotope ratios in moss tissue to help identify the origin of metal deposition within the area; this will allow us to differentiate among soil derived metals delivered by canopy throughfall, atmospheric metal deposition from vehicle sources, and long-range metal deposition associated with dust plumes and coal burning in East Asia (Sherman et al. 2015). Moss and lichen digests from a total of twenty sites along with local soil samples (as a reference) will be assessed for (87/86) Sr and (207/206) Pb isotopic ratios.3. Effects on the microarthropod community:For this objective, we will randomly select 20 of our 70 sites located throughout the Puget Sound corridor that collectively represent the gradient from urban to wilderness areas. At each of these 20 sites, we will collect ten 15 cm diameter cores of forest floor moss communities systematically centered on the location of the lysimeters at each chosen site. We will record the surface area and height of all epiphyte samples, which will be individually collected and returned to the laboratory. Samples will be weighed to record wet weight, and then placed into Berlese funnels for drying and to extract the micro-arthropod community. Samples will be weighed again to determine dry weight. We will determine the total abundance of all micro-arthropods, which will be related to dry weight, moisture content, and sample surface area and height. We will also consider the diversity of micro-arthropods at the family level based upon the Simpson diversity index (attempts will be made to identify individuals to the species level, relying on taxonomic expertise available through the USDA Systematic Entomology Laboratory, but a lack of expertise may require us to examine diversity at the family level). Finally, we will relate abundance and diversity at our field sites with the associated metal content determined under Objective 1.4. Concentration-mortality relationships:We will quantify the direct impact of metal deposition to micro-arthropods using manipulative studies under laboratory conditions. We will construct moss microcosms by collecting 140, 15-cm diameter cores of forest floor moss communities in pristine locations that have been identified on the Olympic Peninsula. Metal contamination of moss communities have been shown to be minimal on the peninsula (Wiersman et al. 1987); these locations will likely be dominated by Racomitrium canescens, Hylocomium splendens and/or Ptillium crista-castrensis. Samples will be returned to lab and the mosses identified. Ten of the cores will be randomly selected for determining metal content using methods described under Objective 1. We will also randomly select 10 cores to be assigned to an untreated control group. The remaining 120 cores will be randomly assigned to one of 5 concentrations of Zn or Cu (10 cores per concentration per metal). Exact concentrations will be initialized based upon on results from Objective 1, with higher concentrations chosen along a log10 scale to ensure a high enough concentration to cause 100% mortality of micro-arthropods. After exposing treated cores to Zn and Cu, we will count the number of dead and alive micro-arthropods that represent a highly susceptible, a highly resistant, and the most abundant species, which we will also do for the untreated controls. Mortality in the treated cores will be corrected for control mortality using Abbott's formula (Abbott, 1925, #14).Data Analyses: All metal and bryophyte data from the urban-to-wildland gradient will be analyzed using parametric or non-parametric methods where applicable. Multivariate principle components analysis will be performed on data collected in Objective one to assess the primary drivers of differences in moss community and metal concentration in mosses. Linear and non-linear regression will be used to specifically assess the influence of distance from busy road ways or from the urban core on metal deposition and metal content of mosses and lichen. Analysis of variance will be used to assess the influence of metal concentrations on micro-arthropod abundance and diversity. Mortality data from manipulative studies will be assessed using logit analysis to determine concentration-response relationships. Data will be analyzed using either SPSS or R statistical package.

Progress 10/01/16 to 09/30/17

Outputs
Target Audience: Hoh River Trust City of Seattle, Department of Parks and Recreation Washington State Department of Natural Resources Changes/Problems: Nothing Reported What opportunities for training and professional development has the project provided?Professional development opportunities for graduate student included working to develop research partnerships with city and state urban forest health professionals. How have the results been disseminated to communities of interest?City of Seattle, Green Seattle Partnership Blog (Sept. 21, 2017); http://www.greenseattle.org/pollution-moss-reveal-seattles-traffic-impacts/ What do you plan to do during the next reporting period to accomplish the goals? Nothing Reported

Impacts
What was accomplished under these goals? In the reporting period, the N2 fixation rates and metal concentrations in bryophytes across Acer macrophyllum stands in western Washington was accomplished. An extensive, ground-based sampling approach across an urban-to-wildland gradient from moss samples was used to assess the effect of pollution associated with urbanization on canopy and forest floor bryophyte communities. In addition, intensive sampling was conducted in January 2017 to assess seasonal differences in N2 fixation rates and metal concentrations across sampling locations. Nitrogen fixation rates in canopy moss samples was found to be dependent on sampling season and location. Average N2 fixation rates reached peak levels in spring for both peninsula and urban samples (588.34 and 179.02 μmol per squared meter per day, respectively) and were lowest in fall (18.47 and 5.29 μmol per squared meter per day). In total, moss in canopies of Acer macrophyllum was found to yield 1.13 kg N per hectare per year in the Hoh Rainforest and only 0.009 kg N per hectare per year in the Seattle urban area. For the heavy metal analysis, elevated concentrations of Cd, Cr, Cu, Fe, K, Mg, Mn, Ni, Pb, Sr, Ti, and Zn were found in both intensive and extensive bryophyte samples collected in Seattle across all collection seasons. The elevated concentrations of heavy metals observed in moss samples collected from Seattle may be related to the low the N2 fixation rates observed in the same samples. The results from this study highlight that canopy and ground floor bryophytes have the potential to be used as a low-cost screening tool to evaluate N and heavy metal pollution in urban and rural areas.

Publications

  • Type: Theses/Dissertations Status: Published Year Published: 2017 Citation: Bidwell, AL (2017) Urbanization impacts on epiphytic nitrogen and metal cycling in Acer macrophyllum stands in Western Washington, USA. M.S. Thesis, University of Washington.
  • Type: Conference Papers and Presentations Status: Published Year Published: 2017 Citation: Bidwell AL, Callahan ST, Tobin PC, DeLuca TH (2017) Urbanization impacts on epiphytic nitrogen cycling in Acer macrophyllum stands in the Pacific Northwest. Presentation to the 2017 Annual Meeting of the Ecological Society of America, Aug. 6-11, 2017, Portland, OR.
  • Type: Conference Papers and Presentations Status: Published Year Published: 2017 Citation: Callahan ST, Bidwell AL, DeLuca TH, Tobin PC (2017) Silent springtails: Effects of vehicular pollution on arboreal Collembola. Presentation to the 2017 Annual Meeting of the Ecological Society of America, Aug. 6-11, 2017, Portland, OR.


Progress 09/16/15 to 09/30/17

Outputs
Target Audience: Hoh River Trust City of Seattle, Department of Parks and Recreation Washington State Department of Natural Resources Changes/Problems: Nothing Reported What opportunities for training and professional development has the project provided?Professional development opportunities for graduate student included working to develop research partnerships with city and state urban forest health professionals. Wilderness First Aid safety training and Single-Rope tree climbing techniques training were offered to the graduate student affiliated with this project. How have the results been disseminated to communities of interest?City of Seattle, Green Seattle Partnership Blog (Sept. 21, 2017); http://www.greenseattle.org/pollution-moss-reveal-seattles-traffic-impacts/ What do you plan to do during the next reporting period to accomplish the goals? Nothing Reported

Impacts
What was accomplished under these goals? During Year 1, researchers spent the fall months scouting field sites and securing necessary sampling permits from a variety of entities (U.S. Forest Service Mt. Baker-Snoqualmie, WA Dept. of Natural Resources Olympic Region and Snoqualmie Region, and City of Seattle Parks and Recreation). Starting in January 2016, sample trees were rigged for seasonal sampling collections, and temperature monitors and metal/nitrogen deposition collectors were placed installed. Pilot samples were also collected from several trees during January to solidify sampling methods and laboratory procedures. The first actual round of sample collection was conducted during April 2016, at which point collected canopy samples from both peninsula ("pristine") and urban ("polluted") sites for laboratory analysis. The second round of fieldwork was conducted at the end of June/ beginning of July, which means half of the field collection data happened during the first year of the project. Researchers began preliminary data analysis on the results for nitrogen fixation and moss tissue metal analysis from the spring and summer sampling rounds. During Year 2, the N2 fixation rates and metal concentrations in bryophytes across Acer macrophyllum stands in western Washington was accomplished. An extensive, ground-based sampling approach across an urban-to-wildland gradient from moss samples was used to assess the effect of pollution associated with urbanization on canopy and forest floor bryophyte communities. In addition, intensive sampling was conducted in January 2017 to assess seasonal differences in N2 fixation rates and metal concentrations across sampling locations. Nitrogen fixation rates in canopy moss samples was found to be dependent on sampling season and location. Average N2 fixation rates reached peak levels in spring for both peninsula and urban samples (588.34 and 179.02 μmol per squared meter per day, respectively) and were lowest in fall (18.47 and 5.29 μmol per squared meter per day). In total, moss in canopies of Acer macrophyllum was found to yield 1.13 kg N per hectare per year in the Hoh Rainforest and only 0.009 kg N per hectare per year in the Seattle urban area. For the heavy metal analysis, elevated concentrations of Cd, Cr, Cu, Fe, K, Mg, Mn, Ni, Pb, Sr, Ti, and Zn were found in both intensive and extensive bryophyte samples collected in Seattle across all collection seasons. The elevated concentrations of heavy metals observed in moss samples collected from Seattle may be related to the low the N2 fixation rates observed in the same samples. The results from this study highlight that canopy and ground floor bryophytes have the potential to be used as a low-cost screening tool to evaluate N and heavy metal pollution in urban and rural areas.

Publications


    Progress 10/01/15 to 09/30/16

    Outputs
    Target Audience:Target audiences included: Hoh River Trust, Seattle City Parks & Recreation, and Washington State Department of Natural Resources (Olympic & Mt. Baker-Snoqualmie Regional Offices). Changes/Problems: Nothing Reported What opportunities for training and professional development has the project provided?Wilderness First Aid safety training and Single-Rope tree climbing techniques training were offered to the graduate student affiliated with this project during the reporting period. How have the results been disseminated to communities of interest?During this reporting period the project was just getting started so outreach was not the main focus. In Year 2, researchers will focus more on disseminating results of the project with community members and affiliated agencies. What do you plan to do during the next reporting period to accomplish the goals?During the next reporting period, researchers will finish the last 2 rounds of seasonal fieldwork and analysis laboratory samples. The graduate student affiliated with this project will begin writing her thesis as well as putting together manuscripts for publication in scientific journals. Findings from the study will be shared with the target audiences (listed above).

    Impacts
    What was accomplished under these goals? During Year 1, researchers spent the fall months scouting fieldsites andsecuring necessarysampling permits from a variety of entities (U.S. Forest Service Mt. Baker-Snoqualmie, WA Dept. of Natural Resources Olympic Region and Snoqualmie Region, andCity of Seattle Parks and Recreation). Starting in January 2016, sample trees were rigged for seasonalsampling collections, and temperature monitors and metal/nitrogen deposition collectors were placed installed. Pilot samples were also collected from several trees during January to solidifysampling methods and laboratory procedures. The first actual round of sample collection was conducted during April 2016, at which point collected canopy samples from both peninsula ("pristine") and urban ("polluted") sites for laboratoryanalysis. The second round of fieldwork was conducted at the end of June/ beginning of July, which means half of the field collection data happened during the first year of the project. Researchers began preliminary data analysis on the results for nitrogen fixation and moss tissue metal analysis from the spring and summer sampling rounds.

    Publications