Introduction
Because of the relatively great complexity of ecological communities, due in part
to the interaction of species and successional change, it is difficult
to consider the influence of all rank factors concurrently. Thus, each
factor is assigned a separate “A”, “B”, “C”
or “D” rating, sequenced and weighted according to priority,
and combined in an algorithm to calculate an EO rank value. This value
is then translated according to an EO rank scale to determine the EO
rank. The process for developing an EO rank for a community is described
in detail below.
Specifications for determining “A”, “B”, “C”,
and “D” ratings for condition, size, and landscape context
factors should be entered into corresponding EO Rank Factor Specifications
fields in the Element Occurrence Specifications.
In addition, the prioritization sequence and weightings used in calculating
an EO rank should be documented in the EO rank specifications. There
are general guidelines for both the sequencing and weighting of rank
factors to be used for calculating EO ranks. For most Elements, the
general guidelines for the rank factor prioritization sequence are determined
according to community pattern type (described below), while the general
guidelines for weighting rank factors apply to any community, regardless
of pattern type. In most cases, community EO rank specifications can
simply incorporate these general guidelines. However, for Elements for
which these general guidelines do not apply, the rationale for the specified
alternative prioritization sequence and/or weightings should be included
in the EO rank specifications.
While the procedure for ranking community EOs may seem complicated,
the actual application of factor weightings and calculation of the final
EO rank can be automated. EO ranks should be reviewed by an ecologist;
in rare cases, adjustment of the rank may be necessary and the reasons
for doing so documented.
Prioritizing EO Rank Factors
The first step in the process of determining a rank for a community
EO is prioritizing the rank factors on the basis of the relative importance
of each factor for that Element. The factor that is most important is
considered the primary rank factor, the factor with less importance
is the secondary rank factor, and the remaining factor, having the least
importance, is the tertiary rank factor.
EO rank specifications developed for a particular Element should indicate
the prioritization sequence of the rank factors. The pattern
type of the community may generally serve as a guide to determining
the prioritization sequence of rank factors that is appropriate for
the Element. A prioritization sequence indicated in the rank specifications
that differs from these general guidelines should include justification
for the modified sequence. In ranking ecological communities for which Element-specific
EO rank specifications have yet to be developed, the general guidelines
may be used to prioritize the rank factors. The following table summarizes
the general guidelines for priority sequencing on the basis of community
pattern type (described in a-d below).
| Community Pattern Type |
Primary
Rank Factor |
Secondary
Rank Factor |
Tertiary
Rank Factor |
| |
size |
landscape context |
condition |
| |
condition |
size |
landscape context |
| |
condition |
landscape context |
size |
| |
landscape context |
condition |
size |
a) Matrix Community Pattern Type
Size and landscape context are generally identified as the primary and
secondary factors for a matrix community type. A matrix community, by
definition, occupies a very large area with high connectivity to other
community types; thus, size and landscape context are typically more
important than condition, which could be quite variable (and in some
cases, difficult to measure).
b) Large Patch Community Pattern
Type
Condition and size are generally identified as the primary and secondary
factors for a large patch community type; however, this sequence is
quite flexible. Because this community type conceptually occupies the
“middle ground” between matrix and small patch types, some
large patch communities may be more similar to matrix types, while others
more closely resemble small patch types, or linear types. In such cases,
the general guidelines for rank factor prioritization for the community
type most similar could be utilized for the large patch type.
c) Small Patch Community Pattern
Type
Condition and landscape context are generally identified as the primary
and secondary factors for a small patch community type. Small patch
types vary much less in size, often contain more specialized species,
and, because of their small size, are sensitive to factors affecting
landscape context.
d) Linear Community Pattern Type
Landscape context and condition are generally identified as the primary
and secondary factors for a linear community type. Linear types, having
a large amount of edge and typically dependent on currents or flow regimes,
are extremely sensitive to factors affecting landscape context. In addition,
linear types often support very specialized species.
Weighting EO Rank Factors
The second step in the process of determining a rank for a community
EO is assigning weightings to each of the rank factors. Weightings are
determined on the basis of the relative influence of the factors on
the viability of the EO. Thus, the weighting of a particular rank factor
is directly related to its position in the prioritization sequence.
According to the general guidelines for weighting EO rank factors, the
values are: primary factor weighting = 4, secondary factor weighting
= 3, and tertiary factor weighting = 2. While these general weightings
apply in most cases, for some Elements a different weighting scheme
may be more suitable. For example, each of the rank factors may have
a relatively equal effect on the viability of an occurrence of some
large patch community types such that all three rank factors should
be weighted equally (e.g., 1-1-1).
The general weightings for rank factors are provided in the EO rank
specifications for most communities. However, in cases where an alternative
weighting scheme is indicated in the specifications, justification for
the modified weightings should be included.
Calculating an EO Rank Value
The third step in the process of determining a rank for a community
EO utilizes the ratings for each of the sequenced rank factors along
with the assigned weightings to calculate an EO rank value. In order
to perform the calculation, numeric equivalents must first be assigned
for “A”, “B”, “C”, and “D”
rank factor ratings as follows:
A rating = 4
B rating = 3
C rating = 2
D rating = 1
The following simple formula may then be used for the calculation:
[(P * x) + (S * y) + (T * z)] ÷ (x + y + z) = EO Rank Value
where
P = numeric equivalent for primary rank factor rating
S = numeric equivalent for secondary rank factor rating
T = numeric equivalent for tertiary rank factor rating
and
x = weighting assigned to primary rank factor
y = weighting assigned to secondary rank factor
z = weighting assigned to tertiary rank factor
Determining a Final EO Rank
The final step in the process of determining a rank for a community
EO translates the calculated EO rank value derived in the previous step
into an “A”, “B”, “C”, or “D”
rank according to the EO rank scale. The rank scale provides a range
of numeric values associated with each EO rank, as shown in the table
below.
| EO Rank |
Numeric Values |
| A |
>3.25 and 4.00 |
| B |
>2.50 and 3.25 |
| C |
>1.75 and 2.50 |
| D |
>1.00 and 1.75
|
A simplified alternative to the process of performing a calculation
to determine an EO rank is the use of a matrix. The matrix displays
all possible combinations of the three ratings initially assigned to
the primary, secondary, and tertiary rank factors for a particular occurrence,
along with the resulting calculated EO rank value and the final EO rank.
As stated above, however, the calculation of a community EO rank will
be an automated process, so this matrix will likely be of limited use,
if any, in the future. The table below illustrates the EO rank matrix
based on the general guidelines for weighting rank factors (i.e., primary
factor = 4, secondary factor = 3, tertiary factor = 2); note that the
use of rank factor weightings that differ from the general guidelines
would result in a different matrix.
|
Rank
factor
ratings |
Calculated
EO rank
value |
EO rank |
Rank
factor
ratings |
Calculated
EO rank
value |
EO rank |
Rank
factor
ratings |
Calculated
EO rank
value |
EO rank |
Rank
factor
ratings |
Calculated
EO rank
value |
EO rank |
|
AAA |
4.00 |
A |
BAA |
3.56 |
A |
CAA |
3.11 |
B |
DAA |
2.67 |
B |
|
AAB |
3.78 |
A |
BAB |
3.33 |
A |
CAB |
2.89 |
B |
DAB |
2.44 |
C |
|
AAC |
3.56 |
A |
BAC |
3.11 |
B |
CAC |
2.67 |
B |
DAC |
2.22 |
C |
|
AAD |
3.33 |
A |
BAD |
2.89 |
B |
CAD |
2.44 |
C |
DAD |
2.00 |
C |
|
ABA |
3.67 |
A |
BBA |
3.22 |
B |
CBA |
2.78 |
B |
DBA |
2.33 |
C |
|
ABB |
3.44 |
A |
BBB |
3.00 |
B |
CBB |
2.56 |
B |
DBB |
2.11 |
C |
|
ABC |
3.22 |
B |
BBC |
2.78 |
B |
CBC |
2.33 |
C |
DBC |
1.89 |
C |
|
ABD |
3.00 |
B |
BBD |
2.56 |
B |
CBD |
2.11 |
C |
DBD |
1.67 |
D |
|
ACA |
3.33 |
A |
BCA |
2.89 |
B |
CCA |
2.44 |
C |
DCA |
2.00 |
C |
|
ACB |
3.11 |
B |
BCB |
2.67 |
B |
CCB |
2.22 |
C |
DCB |
1.78 |
C |
|
ACC |
2.89 |
B |
BCC |
2.44 |
C |
CCC |
2.00 |
C |
DCC |
1.56 |
D |
|
ACD |
2.67 |
B |
BCD |
2.22 |
C |
CCD |
1.78 |
C |
DCD |
1.33 |
D |
|
ADA |
3.00 |
B |
BDA |
2.56 |
B |
CDA |
2.11 |
C |
DDA |
1.67 |
D |
|
ADB |
2.78 |
B |
BDB |
2.33 |
C |
CDB |
1.89 |
C |
DDB |
1.44 |
D |
|
ADC |
2.56 |
B |
BDC |
2.11 |
C |
CDC |
1.67 |
D |
DDC |
1.22 |
D |
|
ADD |
2.33 |
C |
BDD |
1.89 |
C |
CDD |
1.44 |
D |
DDD |
1.00 |
D |
Source: Draft
Element Occurrence Data Standard
|