United States
               Environmental Protection
               Agency
Environmental Monitoring
and Assessment Program
Research Triangle Park, NC 27709
               Research and Development
EPA/620/SR-94/010    August 1994
EPA      Project Summary
               Forest  Health  Monitoring  1992
               Annual  Statistical Summary
               S.A. Alexander
                 In 1990, the  United States  Depart-
               ment of Agriculture (USDA), Forest Ser-
               vice (FS)  and the United States  Envi-
               ronmental Protection Agency (EPA), ini-
               tiated a cooperative national program
               to monitor the condition of the nation's
               forests. This multi-agency effort, within
               the framework of the  EPA's Environ-
               mental Monitoring and Assessment Pro-
               gram (EMAP), is called the Forest Health
               Monitoring (FHM) program. The  FHM
               program is jointly managed and largely
               funded by the FS and EPA in coopera-
               tion with  other program participants.
               FHM partners provide additional finan-
               cial and personnel support and include
               participating State Forestry agencies,
               United States Department of the Inte-
               rior  (USDI),  Bureau  of Land Manage-
               ment, the Tennessee Valley Authority
               (TVA), and the USDA Soil Conservation
               Service (SCS). Other Cooperators  in-
               clude universities, and three USDI agen-
               cies—U.S. Fish  and Wildlife  Service,
               U.S. Geological  Survey, and  the Na-
               tional Park Service. The National Asso-
               ciation of State Foresters provides es-
               sential program support, guidance, and
               assistance.
                 Data analysis results for the follow-
               ing indicators are presented in the  re-
               port:  tree species  and stand  density
               (mensuration), tree  crown condition,
               tree species diversity, and air pollution
               bioindicator plants. The cumulative dis-
               tribution function methods used in the
               analysis provide a statistical summary
               of most measurements. Tabular  sum-
               maries  were also  prepared in some
               cases. Where  possible, indices  have
               been used in the CDF analysis.
  This Project Summary was developed
by EPA's Environmental Monitoring and
Assessment Program, Research Tri-
angle Park, NC, to announce key find-
ings of the research project that is fully
documented in a separate report of the
same title (see Project Report ordering
information at back).

Introduction
  On FHM Detection Monitoring plots, a
set of indicators is used to classify  forest
health status. These indicators collectively
represent many  components  of  forest
health and are generally responsive to
many types of stresses. The  indicators
are  measured at various sites which are
selected  statistically so  that regional for-
est populations are represented.
  The Project Report summarizes the data
that were collected as a result of the De-
tection Monitoring activities. Chapter two
of the report provides a brief overview of
forest health monitoring. The  remaining
chapters  summarize the data for tree spe-
cies and  stand density, tree crown condi-
tion, tree species  diversity, and air  pollu-
tion bioindicator plants. An overview of
indicator  development, the  plot network,
plot design, and data analysis procedures
are presented in several appendices.

Procedure
  In 1992, Detection Monitoring activities
were conducted in twelve eastern states:
Alabama, Connecticut,  Delaware,  Geor-
gia, Maine, Maryland, Massachusetts, New
Hampshire,  New  Jersey, Rhode Island,
Vermont, and Virginia (Figure 1). Detec-
tion Monitoring was also conducted in Cali-
fornia and Colorado. Those data will be

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included  in the  1993 Annual  Statistical
Summary as part of the  western data
analysis.
  The  cumulative distribution  function
(CDF) methods used  in the analyses pro-
vide a  statistical  summary  of most mea-
surements. Tabular summaries were also
prepared in some cases.  Where possible,
indices have been used in the CDF analy-
sis.

Results and Recommendations

Mensuration
  • Standard Federal Regions 1  and 2
    combined have more dead trees (on
    a per-area basis) than  either Federal
    Region 3 or Federal  Region 4.
  • This  is apparently due to a noticeably
    larger number of dead trees (per area)
    across the major forest type  group-
    ings  of spruce-fir forests and maple/
    beech/birch forests.
  • It would be premature to assume that
    this  reflects  significantly increased
    mortality and reduced regeneration in
    these  major  forest  type  groupings
    without additional  information  on
    changes over time.
  • Basal area per hectare  shows roughly
    the same distribution across all three
    Standard Federal Regions.

Crown Assessments
  • The  defoliation  of tree crowns was
    examined through analysis of  3 eco-
    logical groups (species, forest types,
    and  crown groups)  that were found
    on 45 or more plots  within any of the
    four  geographical regions  (SFRs 1
    and 2 combined, 3,  4,  and 1-4 com-
    bined).
  • The  crown  variables   dieback and
    transparency were aggregated into a
    plot-level indicator that evaluated the
    defoliation of the  outer  and  inner por-
    tions of the tree crowns.
  • Less than 10 percent of any popula-
    tion for any ecological group fell within
    the subnominal  category,  and less
    than  3  percent  of  any subnominal
    population proportion  was found  in
    the poor category.
  • The  only ecological  groups that de-
    serve a cursory investigation due to
    the low proportions of  populations in
    a subnominal or poor condition are
    one  species  (White ash) and two
    crown groups (Cedar-Juniper; miscel-
    laneous).
  • No forest types  had any significant
    proportions  of the population  in the
    subnominal or poor condition.
Figure 1.  Sites in which detection monitoring occurred in 1982.
Species Diversity of Trees and
Saplings
  • Species density was used as a mea-
    sure of species  diversity of trees and
    saplings in Standard Federal Regions
    1 and 2 combined, Federal Region 3,
    and  Federal Region 4. Two species
    per unit area was used as a prelimi-
    nary subnominal threshold.
  • Standard Federal Region 4 had a sig-
    nificantly higher proportion of plots
    with  subnominal tree species density
    than Federal Region 3. Federal Re-
    gions 1 and 2 combined and Federal
    Region 3 did not differ significantly for
    these proportions.
  • Standard Federal Regions 1  and  2
    combined had a significantly  higher
    proportion of plots with  subnominal
    sapling  species  density  than either
    Federal Region  3 or Federal Region
    4.

Air pollution Bioindicator
Plants
  • Field crews established biomonitoring
    sites, for  determining the presence or
    absence  of ozone injury  conditions,
    at 39 of the 212  forested plots in New
    England.
  • Based on data from  39 biomonitoring
    sites, an estimated 27%+  13% of the
    forested population covered by these
    sites showed foliar symptoms indicat-
    ing the presence of ozone injury.
  •  Most of the plots rated positive  for
    ozone injury were located in rural  ar-
    eas that  are known to be contami-
    nated by  air masses moving into the
    region from  urban-industrial areas to
    the south of New England.
  The  information  in this document has
been funded in  part by the U.S. Environ-
mental Protection  Agency  under  Inter-
agency Agreement number DW12935103-
01 with the USDA Forest  Service and
Interagency  Agreement number  DW-
14935509-01  with  the  USDI  Bureau of
Land Management. It has been subject to
the Agency's  peer  and administrative  re-
view, and it has been approved for  publi-
cation as an EPA document.
  Mention of trade names or commercial
products does not constitute endorsement
or recommendation for use.
  The  report  represents  data  from one
year of EMAP.  Because the probability-
based scientific design used  by the EMAP
necessitates multiple years  of  sampling,
there is uncertainty associated with these
data. This uncertainty will decrease as the
full  power of the  approach is realized.
Similarly,  temporal changes and trends
cannot be reported, as these require mul-
tiple  years  of observation.  Please  note
that this report contains data from demon-
stration studies  in four Standard Federal
Regions.  Appropriate precautions should
be exercised when using this information
for  policy, regulatory  or  legislative pur-
poses.

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   Samuel A. Alexander (also the EPA Project Officer, see below) is with the
     Environmental Monitoring and Assessment Program, Research Triangle Park,
     NC 27709.
   The complete report, entitled "Forest Health Monitoring-1992 Annual Statistical
     Summary," (Order No. PB94-205416/AS; Cost: $ 19.50; subject to change) will
     be available only from:
           National Technical Information Service
           5285 Port Royal Road
           Springfield, VA 22161
           Telephone: 703-487-4650
   The EPA Project Officer can be contacted at:
           Environmental Monitoring and Assessment Program-EMAP Center
           U. S. Environmental Protection Agency
           Research Triangle Park, NC 27709
United States
Environmental Protection Agency
Center for Environmental Research Information
Cincinnati, OH 45268

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