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USES OF POWER IN DESIGNING LONG-TERM ENVIRONMENTAL SURVEYS
N. Scott Urquhart Department of Statistics Colorado State University Fort Collins, CO
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OUTLINE FOR TONIGHT Long-Term Environmental Surveys
Agencies involved Sorts of Summaries of Interest Sources of Variation – Major ones A Statistical Model Superimposed on an Adapted Classical Sampling Model Calculation of Power Using this Model Illustrations General Specific Generalizations - as Time Allows
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LONG-TERM ENVIRONMENTAL SURVEYS
Objective: To Establish The Current Status Detect Long-Term Trends Evaluate “Extent” of Various Classes Of the Resource(s) of Interest Usually Ecological or Living Resources Agencies = Who US Environmental Protection Agency (EPA)* States and Tribes, and Local Jurisdictions Response to Legislation Like the Clean Water Act Forest Service – “Forest Health” National Park Service* Soil Conservation Service (not the current name) National Marine Fisheries Service ( “ ) National Wetlands Inventory
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RESPONSES of INTEREST EPA
Variety of Chemical Measures of Water Quality Nitrogen to Heavy Metals to Pesticides Acid Neutralizing Capacity (ANC) Important in Evaluating the Effect of “Acid Rain” Composition of “Bugs” in the Aquatic Community Thought to Contain Better Info on total Effects than Individual Chemicals Fish Populations – Composition, not size Clean Water Act Includes Reporting on Temperature Pollution
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RESPONSES of INTEREST (continued)
National Park Service (Eg: Olympic NP in WA) Vegetation Bird Populations Composition Size of Various Species Streams/Rivers Fish Populations Macroinvertebrate Communities Extent of Intermittent Streams Health of Glaciers Extent – Shrinking with Global Warming?
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RESPONSES of INTEREST (continued II)
Grand Canyon National Park Erosion Around Archeological Resources Near-river Terrestrial Environment (GCMRC)
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SPATIAL EXTENT Generally Large Areas Regions can be very large
This is the Way Congress Writes Laws Regions can be very large 12 Western States ND, SC, MT, WY, CO, ID, UT, NV, AZ, WA, OR, CA Midatlantic Highlands parts of PA, VA, WV, DE, MD Individual States Lands of Several related Tribes, or Even Only One Groups of National Parks Groups of Sanitation Districts, or even Individual Sanitation Districts*
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SUMMARIES of INTEREST Extent by Classes “Status”
Track Changes Between Classes National Wetlands Inventory Major focus Has Very Good Graphic Depiction of Class Changes “Status” Often is summarized as an Estimated Cumulative Distribution Function (cdf) Pose some Interesting Statistical Inference Problems Due to Variable Probability Sampling – Almost Always Needed Spatially Continuous Resources – No List Can Exist
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EXAMPLE OF STATUS, SUMMARIZED BY A cdf
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ESTIMATED CUMULATIVE DISTRIBUTION FUNCTION OF SECCHI DEPTH, EMAP AND “DIP-IN”
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SUMMARIES of INTEREST (continued)
Trends Directional Changes in Responses Reality: Detection of Short-Term Cycles is Beyond the Resources for the Foreseeable Future Great Big Changes Don’t Require Surveys So Interest Lies in Modest-Sized Long-Term Changes in One Direction This means Changes the Scale of 1% to 2% Per Year Usually a Trend for a Region Regional Summaries of Individual Site Trends Sometimes how trend varies in relation to other things
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IMPORTANT COMPONENTS OF VARIANCE
POPULATION VARIANCE: YEAR VARIANCE: RESIDUAL VARIANCE:
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IMPORTANT COMPONENTS OF VARIANCE
( - CONTINUED) POPULATION VARIANCE: VARIATION AMONG VALUES OF AN INDICATOR (RESPONSE) ACROSS ALL LAKES IN A REGIONAL POPULATION OR SUBPOPULATION
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IMPORTANT COMPONENTS OF VARIANCE
( - CONTINUED II) YEAR VARIANCE: CONCORDANT VARIATION AMONG VALUES OF AN INDICATOR (RESPONSE) ACROSS YEARS FOR ALL LAKES IN A REGIONAL POPULATION OR SUBPOPULATION NOT VARIATION IN AN INDICATOR ACROSS YEARS AT A LAKE DETRENDED REMAINDER, IF TREND IS PRESENT EFFECTIVELY THE DEVIATION AWAY FROM THE TREND LINE (OR OTHER CURVE)
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IMPORTANT COMPONENTS OF VARIANCE
( - CONTINUED - III) RESIDUAL COMPONENT OF VARIANCE HAS SEVERAL SUBCOMPONENTS YEAR*LAKE INTERACTION THIS CONTAINS MOST OF WHAT MOST ECOLOGISTS WOULD CALL YEAR TO YEAR VARIATION, I.E. THE LAKE SPECIFIC PART INDEX VARIATION MEASUREMENT ERROR CREW-TO-CREW VARIATION LOCAL SPATIAL = PROTOCOL SHORT TERM TEMPORAL
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Subsequent slides show the relative amount of variability
BIOLOGICAL INDICATORS HAVE SOMEWHAT MORE VARIABILITY THAN PHYSICAL INDICATORS – BUT THIS VARIES, TOO Subsequent slides show the relative amount of variability Ordered by the amount of residual variability: least to most (aquatic responses) Acid Neutralizing Capacity Ln(Conductance) Ln(Chloride) pH(Closed system) Secchi Depth Ln(Total Nitrogen) Ln(Total Phosphorus) Ln(Chlorophyll A) Ln( # zooplankton taxa) Ln( # rotifer taxa) Maximum Temperature And others, both aquatic and terrestrial
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SOURCE OF COMPONENTS OF VARIANCE FROM GRAND CANYON
Grand Canyon Monitoring and Research Center Effects of Glen Canyon Dam on the Near-River Habitat in the Grand Canyon At Various Heights Above the River Height Is Measured as the Height of the River’s Water at Various Flow Rates Eg: 15K cfs, 25K cfs, 35K cfs, 45K cfs & 60K cfs Using First Two Years’ Data Mike Kearsley – UNA Design = Spatially Balanced With about 1/3 revisited
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ALL VARIABILITY IS OF INTEREST
The Site Component of Variance is One of the Major Descriptors of the Regional Population The Year Component of Variance Often is Small, too Small to Estimate. If Present, it is a Major Enemy for Detecting Trend Over Time. If it has even a moderate size, “sample size” reverts to the number of years. In this case, the number of visits and/or number of sites has no practical effect.
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ALL VARIABILITY IS OF INTEREST ( - CONTINUED)
Residual Variance Characterizes the Inherent Variation in the Response or Indicator. But Some of its Subcomponents May Contain Useful Management Information CREW EFFECTS ===> training VISIT EFFECTS ===> need to reexamine definition of index (time) window or evaluation protocol MEASUREMENT ERROR ===> work on laboratory/measurement problems
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DESIGN TRADE-OFFS: TREND vs STATUS
How do we Detect Trend in Spite of All of This Variation? Recall Two Old Statistical “Friends.” Variance of a mean, and Blocking
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DESIGN TRADE-OFFS: TREND vs STATUS ( - CONTINUED)
VARIANCE OF A MEAN: Where m members of the associated population have been randomly selected and their response values averaged. Here the “mean” is a regional average slope, so "s2" refers to the variance of an estimated slope ---
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DESIGN TRADE-OFFS: TREND vs STATUS ( - CONTINUED - II)
Consequently Becomes Note that the regional averaging of slopes has the same effect as continuing to monitor at one site for a much longer time period.
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DESIGN TRADE-OFFS: TREND vs STATUS ( - CONTINUED - III)
Now, s2, in total, is large. If we take one regional sample of sites at one time, and another at a subsequent time, the site component of variance is included in s2. Enter the concept of blocking, familiar from experimental design. Regard a site like a block Periodically revisit a site The site component of variance vanishes from the variance of a slope.
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STATISTICAL MODEL CONSIDER A FINITE POPULATION OF SITES
{S1 , S2 , … , SN } and A TIME SERIES OF RESPONSE VALUES AT EACH SITE: A FINITE POPULATION OF TIME SERIES TIME IS CONTINUOUS, BUT SUPPOSE ONLY A SAMPLE CAN BE OBSERVED IN ANY YEAR, and ONLY DURING AN INDEX WINDOW OF, SAY, 10% OF A YEAR
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STATISTICAL MODEL -- II
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STATISTICAL MODEL -- III
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STATISTICAL MODEL -- IV
IF p INDEXES PANELS, THEN Sites are nested in panels: p ( i ) and Years of visit are indicated by panel with npj = 0 or npj> 0 for panels visited in year j. The vector of cell means (of visited cells) has a covariance matrix S :
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STATISTICAL MODEL -- V Now let X denote a regressor matrix containing a column of 1s and a column of the numbers of the time periods corresponding to the filled cells. The second elements of contain an estimate of the regional trend and its variance.
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TOWARD POWER Ability of a panel plan to detect trend can be expressed as power. We will evaluate power in terms of these ratios of variance components Power depends on the ratios of variance components, the panel plan, and on
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NOW PUT IT ALL TOGETHER Question: “ What kind of temporal design should you use for Northwest National Parks? We’ll investigate two (families) of recommended designs. All illustrations will be based on 30 site visits per year, a reasonable number given resources. General relations are uninfluenced by number of sites visited per year, but specific performance is. We’ll use the panel notation Trent McDonald published.
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RECOMMENDATION OF FULLER and BREIDT
Based on the Natural Resources Inventory (NRI) Iowa State & US Department of Agriculture Oriented toward soil erosion & Changes in land use Their recommendation Pure panel =[1-0] =“Always Revisit” Independent =[1-n]=“Never Revisit” Evaluation context No trampling effect – remotely sensed data No year effects Administrative reality of potential variation in funding from year to year MATH RECOME 100% % 0% %
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TEMPORAL LAYOUT OF [(1-0), (1-n)]
YEAR 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 [1-0] X [1-n]
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FIRST TEMPORAL DESIGN FAMILY
30 site visits per year [1-0] 30 20 10 [1-n] ALWAYS REVISIT NEVER
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POWER TO DETECT TREND FIRST TEMPORAL DESIGN FAMILY NO YEAR EFFECT
Always Revisit Never Revisit
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POWER TO DETECT TREND FIRST TEMPORAL DESIGN FAMILY, MODEST (= SOME) YEAR EFFECT
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POWER TO DETECT TREND FIRST TEMPORAL DESIGN FAMILY BIG (= LOTS) YEAR EFFECT
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SERIALLY ALTERNATING TEMPORAL DESIGN [(1-3)4 ] SOMETIMES USED BY EMAP
YEAR 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 FIA X [(1-3)4 ]
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SERIALLY ALTERNATING TEMPORAL DESIGN [(1-3)4 ] SOMETIMES USED BY EMAP
YEAR 1 2 3 4 5 6 7 8 9 10 11 … FIA X [(1-3)4 ] Unconnected in an experimental design sense Very weak design for estimating year effects, if present
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SPLIT PANEL [(1-4)5 , --- ] YEAR 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 FIA X [(1-4)5 ] AGAIN, Unconnected in an experimental design sense Matches better with FIA Still a very weak design for estimating year effects, if present
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SPLIT PANEL [(1-4)5 ,(2-3)5 ] This Temporal Design IS connected
YEAR 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 FIA X [(1-4)5 ] [(2-3)5 ] This Temporal Design IS connected Has three panels which match up with FIA
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SECOND TEMPORAL DESIGN FAMILY
30 site visits per year [1-4] 30 20 10 [2-3] 5 15
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POWER TO DETECT TREND SECOND TEMPORAL DESIGN FAMILY NO YEAR EFFECT
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POWER TO DETECT TREND SECOND TEMPORAL DESIGN FAMILY SOME YEAR EFFECT
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POWER TO DETECT TREND SECOND TEMPORAL DESIGN FAMILY LOTS OF YEAR EFFECT
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COMPARISON OF POWER TO DETECT TREND DESIGN 1 & 2 = ROWS
YEAR EFFECT NONE SOME LOTS
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POWER TO DETECT TREND VARYING YEAR EFFECT AND TEMPORAL DESIGN
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STANDARD ERROR OF STATUS TEMPORAL DESIGN 1, NO YEAR EFFECT
TOTAL OF 30 SITES 110 SITES VISITED BY YEAR 5 410 SITES VISITED BY YEAR 20
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STANDARD ERROR OF STATUS TEMPORAL DESIGN 2, NO YEAR EFFECT
TOTAL OF 75 SITES TOTAL OF 150 SITES
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GENERALIZATIONS Each site can have its own trend
These very likely differ How should we approach this reality? There is a cdf of trends across the region Variation in trends can be partitioned Components are very similar to those used for responses: Years Rivers Sites within rivers
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ILLUSTRATION Stoddard, J.L., Kahl, J.S., Deviney, F.A., DeWalle, D.R., Driscoll, C.T., Herlihy, A.T., Kellogg, J.H., Murdoch, J.R. Webb, J.R., and Webster, K.E. (2003). Response of Surface Water Chemistry to the Clean Air Act Amendments of EPA/620/R-02/004. US Environmental Protection Agency, Washington, DC.
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FUNDING ACKNOWLEDGEMENT
The work reported here today was developed under the STAR Research Assistance Agreement CR awarded by the U.S. Environmental Protection Agency (EPA) to Colorado State University. This presentation has not been formally reviewed by EPA. The views expressed here are solely those of presenter and STARMAP, the Program he represents. EPA does not endorse any products or commercial services mentioned in this presentation. This research is funded by U.S.EPA – Science To Achieve Results (STAR) Program Cooperative Agreement # CR
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