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Impact Assessment

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Title: Impact Assessment


1
Impact Assessment
  • ESM 206A
  • 21 November 2007

2
Impact assessment
  • What is the impact of one or more management
    techniques on an environmental variable of
    interest?
  • Effects of grazing on biodiversity in California
    grasslands
  • Establishment of marine protected areas in
    Channel Islands how do they affect lobster
    abundance?
  • Has some event caused a change in the
    environment?
  • Power plant goes on line
  • Hurricane
  • Challenge is to establish causation
  • This is a conceptual issue, not a statistical
    issue!

3
San Onofre Nuclear Power Plant
  • Units 2 3 came online in May 1983
  • Cooling water discharge creates turbidity due to
    volume of flow
  • This has potential negative effects on giant
    kelp
  • Reduced light at sea floor reduces growth and
    survival of baby kelp
  • Sediments bury hard substrate
  • Data collected on total area of kelp forest,
    using sidescan sonar
  • Question did the power plants negatively impact
    the kelp bed adjacent to the cooling water
    discharge site?

4
Before-After (BA)
  • Suppose we have data from power plant outflow
    site before and after operation began
  • Is kelp area lower after the power plant went
    online?

5
Two-sample t-test
  • If two samples, X and Y, are from populations
    with the same mean
  • Then the quantity
  • follows a t distribution with
    nx ny 2 degrees of freedom

6
Assumptions of 2-sample t-test
  • Populations from which x and y are sampled are
    normally distributed
  • Test is pretty robust as long as sample sizes are
    similar and 2-tailed tests are being considered
  • The more samples, the better
  • If non-normality is strong, dont put confidence
    in alpha levels below 0.01
  • Populations from which x and y are sampled have
    same variances
  • Violations mean that P values will be somewhat
    too small
  • Use Welchs approximate t test instead

7
Welchs approximate t-test
  • If two samples, X and Y, are from populations
    with the same mean but different variances
  • Then the quantity
  • follows a t distribution with
  • degrees of freedom

8
BA (continued)
9
BA (conclusion)
  • The assumptions of the t-test are moderately
    violated
  • However, P value is extremely small we can be
    confident that the true P is less than a
    reasonable alpha (0.05 or even 0.01)
  • Thus, with high confidence we can reject the null
    hypothesis that the kelp area was the same before
    and after the power plant went online
  • Does this mean the power plant has caused this
    difference?

10
Control-Impact (CI)
  • Suppose we have data from power plant outflow
    site and a control site nearby, but only after
    operation began
  • Is kelp area lower in impact site than control
    site?

11
Again, do a 2-sample t-test
12
CI
  • Conclusion Fail to reject the null hypothesis
    that Control and Impact sites have same amount of
    kelp!
  • Does this mean that power plant has no effect on
    kelp?

13
Before-After Control-Impact (BACI)
  • If we have data from both sites (Control and
    Impact) at both periods (Before and After) then
    we can
  • Use the Control site to control for temporal
    changes in kelp that are unrelated to the power
    plant coming on line
  • Also called a counterfactual
  • Use the Before period to determine the relative
    quality of the two sites before the power plant
  • We want to focus on the difference of
    differences

14
Estimate the effect size
15
Before
After
16
Combining all the information simple BACI using
ANOVA
  • ANOVA (ANalysis Of VAriance) allows us to
    simultaneously compare the means of more than two
    groups
  • Single factor ANOVA simply compare among groups
    (e.g., streamflow at five streams)
  • Null hypothesis all samples are drawn from
    populations with the same means
  • Alternate hypothesis the samples are not all
    drawn from population with the same means
  • We could use this compare our four groups (BC,
    BI, AC, AI), but thats not very interesting

17
Multi-factor ANOVA
  • Each factor is a way of classifying observations,
    and has two or more levels
  • E.g., environmental attitude might differ among
    nationalities (Canadian, American, Mexican) and
    religions (Catholic, Protestant, Jew, Muslim,
    None)
  • ANOVA looks at main effects and interactions
  • Main effects averaging across all levels of
    factor B, do the levels of factor A have
    different means?
  • Do people from Mexico, US and Canada differ in
    their environmental attitudes, regardless of
    religion?
  • Interactions Do the differences between levels
    of factor A depend on which level of factor B you
    are in?
  • Is the difference in attitudes between Jews and
    Catholics different in the three countries?

18
ANOVA in Rcmdr
  • Statistics -gt Means -gt Multi-way ANOVA

19
BACI with ANOVA
Anova Table (Type II tests) Response Kelp
Sum Sq Df F value Pr(gtF) Period
7312 1 11.0990 0.0016300 Site
4779 1 7.2543 0.0096014 PeriodSite 11259
1 17.0902 0.0001359 Residuals 32939 50
--- Signif. codes 0 ''
0.001 '' 0.01 '' 0.05 '.' 0.1 ' ' 1
Averaging over sites, kelp differs between periods
Averaging over periods, kelp differs between sites
The difference in period means depends on which
site you are in or The difference in site means
depends on which period you are in
20
BACI
  • Conclusion Reject the null hypothesis that the
    difference between the impact and control sites
    did not change from Before to After
  • P 0.0001
  • The change was negative relative to control
    site, kelp density in impact site was lower after
    the power plant went online
  • Does this mean that power plant has caused this
    change?

21
We can do even better!
22
Before-After Control-Impact Paired Series (BACIPS)
  • Calculate deltas for each sample time by
    subtracting value at control site from value at
    impact site
  • controls for temporal variability in environment
  • Do a two-sample t-test to see if mean delta
    changes from before to after

23
BACIPS continued
24
BACI BACIPS conclusions
  • Reject null hypothesis that true effect size is
    zero
  • BACIPS gives more power than BACI (much smaller
    P)
  • Could have drawn conclusion sooner
  • Gives more confidence under violation of
    assumptions
  • Does this mean the power plant has caused this
    effect?

25
Impact assessment general considerations
  • We need some way to control for variability that
    might confound our conclusions
  • Temporal changes unrelated to event in question
  • Differences in underlying quality between sites
  • Can also control by including measurements of
    additional variables that might affect response
  • SST, amount of rocky reef, etc.
  • What if monitoring only starts after event occurs?

26
Environmental challenge
  • The problem There is a great deal of controversy
    about how to manage California grasslands for
    biodiversity values. In particular, there is
    debate about whether grazing by cattle is
    promotes or is deleterious to plant diversity
  • Data on plant diversity and relative abundance
    have been collected from plots at Sedgwick
    Reserve where grazing has been either allowed or
    excluded.
  • Your job Using these data, determine whether
    grazing increases or decreases plant diversity.

27
Diversity in Sedgwick grassland plots
28
2-sample t-test of H
29
Paired t-test
  • If observations naturally come in pairs
  • Control treatment plots next to each other
  • Calculate differences, di xi - yi
  • Use one-sample t-test to test H0 md 0

30
Paired t-test
31
2-sample vs paired t-test
  • TWO SAMPLE t-TEST
  • Difference of means
  • Use when observations are independent between
    groups
  • Assumes each population is normally distributed
  • PAIRED t-TEST
  • Mean of differences
  • Use when observations are naturally paired
  • Assumes population of differences is normally
    distributed
  • Both will estimate same mean difference
  • If there is variation among pairs (e.g., due to
    location, soil type, habitat), then paired test
    will have more power to reject null hypothesis

32
Independence and randomness
33
Further Reading
  • Schmitt, R.J., and C.W. Osenberg, eds. 1996.
    Detecting Ecological Impacts. Academic Press, San
    Diego.
  • Stewart-Oaten, A., W.W. Murdoch, and K.R. Parker.
    1986. Environmental impact assessment
    pseudoreplication in time? Ecology 67 929-940.
  • Helsel Hirsch Chapters 5-7.
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