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Critical Load Development for Nitrogen and Sulfur Deposition Elizabeth Waddell Air Resources Specialist Pacific West Region 206 220 4287 Elizabeth_waddell@nps.gov Critical Load Development for Nitrogen and Sulfur Deposition Elizabeth Waddell Air Resources Specialist Pacific West Region 206 220 4287 Elizabeth_waddell@nps.gov 1
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Funded by NWCAA Co-sponsored by NWCAA, NPS, USFS, and USGS Focus on NW WA but applicability for most of R10 2 Science Workshop
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Researchers with expertise in nitrogen and sulfur effects on: –Lichens –Soil chemistry –Vegetation –Water chemistry –Mycorrhizae –Diatoms –Deposition monitoring –Deposition modeling –Setting critical loads 3 Participants
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NPS Science Staff USFS NWCAA PSCAA Ecology Tribes 4 Participants
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“the quantitative estimate of an exposure to one or more pollutants below which significant harmful effects on specified sensitive elements of the environment do not occur according to present knowledge.” 5 What is a Critical Load?
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6 N Deposition (kg/ ha /yr) Natural background N deposition Increased NO3 in lakes Changes in tree and soil chemistry Change in alpine plant species Change in algal species Effects on aquatic and terrestrial biota (episodic or chronic acidification)
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Critical load work proceeding at Rocky Mountain NP –1.5 kg N/ha/yr for eutrophication effects of alpine lakes –Current deposition is 3-4 kg N/ha/yr Partnering with CDPHE to identify sources and reduce emissions 7 Critical Loads in Action http://www.cdphe.state.co.us/ap/rmnp.html
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NADP Monitoring –S deposition – declining –N deposition – no trend Between 1 and 2 kg/ha/yr Does not include dry or occult deposition All low elevation sites 8 Current Knowledge – Deposition Monitoring
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9 Current Knowledge – NADP N Deposition Monitoring
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Throughfall Monitoring –Low under canopy Lichens absorbing N? –High in bulk deposition –Inconsistent with NADP or CG Snowfall –Comparable to NADP 10 Current Knowledge – N Deposition Monitoring Research
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11 Current Knowledge – Deposition Modeling Research WSU CMAQ preliminary work based on 36 km grid
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Modeling –Overpredicts dry –Underpredicts wet –No cloud –Limited sensitivity analysis 12 Current Knowledge – Deposition Modeling Research
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Lichens –Sensitive to air pollution –N sensitive lichens absent in areas of “high” nitrogen deposition –Preliminary work with Columbia Gorge throughfall monitoring data yields a CL of 2.4 kg/ha/yr 2.0 dry deposition 0.4 wet deposition 13 Current Knowledge – Ecological Effects
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Acidification effects –Nutrient effects of N expected to occur at lower deposition rates than acidification effects –MAGIC model yielded an “upper bound” CL of 10 kg S/ha/yr for acidification of Lake Eunice (Mt. Rainier) –(Recent documentation of episodic acidification at Lake Eunice due to snowmelt pulse) 14 Current Knowledge – Ecological Effects
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Aquatic Ecosystems –Mine existing water quality databases to identify: Areas which may already be affected by N or S deposition Areas which may be sensitive to additional N –Establish CL for eutrophication of aquatic ecosystems using RMNP work as a model (diatoms) 15 Research Priorities
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Terrestrial Ecosystems –Lichens Collect lichens from NADP and “throughfall” sites; Refine deposition modeling and/or conduct additional monitoring to better establish a deposition gradient and/or use PRISM –Natural Resources Conservation Service (NRCS) soils mapping effort Identify sensitive areas (N and Al) 16 Research Priorities
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Terrestrial Ecosystems –Alpine meadows Fertilization effects research using RMNP as model –Mycorrhizal diversity Similar to lichens in terms of PNW ecological importance and diversity. 17 Research Priorities
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Quantifying actual deposition Adequate to “index” to NADP or other standard monitor 18 Not a Research Priority
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19 Questions?
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