Site |
Code |
Latitude |
Longitude |
Elevation |
Bog Area |
GSF |
LAI |
Bog |
Bog PC2 |
Forest PC1 |
Forest PC2 |
Tobey
Pond Bog (CT) |
TPB |
42.00333 |
73 |
389 |
2877 |
0.049 |
5.368 |
2.87 |
0.96 |
-0.46 |
-0.79 |
Halls
Brook Cedar Swamp (MA) |
HBC |
42.02889 |
70 |
8 |
11760 |
0.092 |
3.453 |
0.41 |
-1.05 |
-1.15 |
-0.48 |
Chockalog
Bog (MA) |
CKB |
42.04944 |
71 |
152 |
7422 |
0.068 |
2.762 |
-1.32 |
-1.09 |
-0.94 |
-0.38 |
Shankpainter
Ponds (MA) |
SKP |
42.04972 |
70 |
1 |
55152 |
0.219 |
1.587 |
-1.02 |
0.98 |
-0.61 |
0.82 |
Clayton
Bog (MA) |
CB |
42.17444 |
73 |
210 |
73120 |
0.128 |
2.462 |
-2.57 |
1.31 |
-0.70 |
-0.37 |
Round
Pond (MA) |
RP |
42.19417 |
72 |
78 |
10511 |
0.073 |
3.038 |
-2.89 |
0.42 |
-1.57 |
-0.72 |
Ponkapoag
Bog (MA) |
PK |
42.23472 |
71 |
47 |
491189 |
0.141 |
3.695 |
-2.21 |
0.01 |
-0.14 |
-1.23 |
Otis
Bog (MA) |
OB |
42.27139 |
73 |
491 |
89208 |
0.061 |
3.128 |
0.29 |
2.33 |
-1.09 |
2.08 |
Swift
River (MA) |
SWR |
42.30972 |
72 |
121 |
19699 |
0.063 |
3.11 |
-1.19 |
0.06 |
-1.56 |
0.86 |
Arcadia
Bog (MA) |
ARC |
42.555 |
72 |
95 |
1190 |
0.08 |
5.286 |
0.739 |
-3.27 |
-1.54 |
0.07 |
Bourne-Hadley
Ponds (MA) |
BH |
42.5675 |
72 |
274 |
105369 |
0.093 |
2.506 |
0.43 |
0.02 |
-0.93 |
-0.50 |
Quag
Pond (MA) |
QP |
42.57528 |
71 |
335 |
40447 |
0.153 |
2.457 |
-1.76 |
1.31 |
0.26 |
-0.08 |
Hawley
Bog (MA) |
HAW |
42.68639 |
72 |
543 |
36813 |
0.121 |
2.822 |
1.14 |
1.44 |
-0.71 |
-0.22 |
Lake
Jones (MA) |
WIN |
43.32667 |
72 |
323 |
84235 |
0.063 |
4.497 |
1.86 |
-0.26 |
-0.64 |
-0.45 |
North
Springfield (VT) |
SPR |
44.05806 |
72 |
158 |
435 |
0.053 |
3.423 |
0.12 |
-0.27 |
-0.92 |
-0.44 |
Snake
Mountain (VT) |
SNA |
44.28972 |
73 |
313 |
248 |
0.168 |
1.713 |
2.09 |
0.71 |
-0.56 |
-0.69 |
Peacham
Bog (VT) |
PEA |
44.325 |
72 |
468 |
576732 |
0.077 |
3.993 |
-0.16 |
-3.21 |
1.53 |
2.28 |
Chickering
Bog (VT) |
CHI |
44.49917 |
72 |
362 |
38081 |
0.049 |
3.713 |
-0.22 |
0.63 |
1.36 |
-1.08 |
Molly
Bog (VT) |
MOL |
44.54528 |
72 |
236 |
8852 |
0.057 |
4.417 |
2.26 |
0.89 |
7.05 |
-3.38 |
Colchester
Bog (VT) |
COL |
44.76278 |
73 |
30 |
623284 |
0.052 |
3.867 |
0.37 |
-1.58 |
-1.34 |
0.33 |
Moose
Bog (VT) |
MOO |
44.95389 |
71 |
353 |
864970 |
0.062 |
4.795 |
1.20 |
0.84 |
4.79 |
4.57 |
Carmi
Bog (VT) |
CAR |
42.00333 |
72 |
133 |
38023 |
0.059 |
3.047 |
-0.423 |
-1.2 |
-0.12 |
-0.19 |
Variable Units Site code is used in Appendix
E. Latitude and longitude are in decimal degrees; elevation is in meters
above sea-level; bog area is in square meters; global site factor (GSF) is percent
of available light (direct + diffuse) in the understory (see Appendix
B for details of calculations); and leaf area index (LAI) is in (m2
leaf tissue)/(m2 ground area). Decimal fractions of longitude coordinates
are not reported to protect threatened wetland habitats. Bog and forest PC scores
are the first and second principal components derived from field measurements
of plant species composition at each site (Appendix
B, Appendix D).
Site Selection
Sites were selected in consultation
with local conservation agencies (The Nature Conservancy and state Natural Heritage
Programs). Criteria for selection included: high quality, relatively undisturbed
bogs, presence of a population of the northern pitcher-plant Sarracenia purpurea
L. (an ant predator), and representation across a variety of ecological sub-regions
(Bailey 1998). Sites were spread across the states
and covered all of the Vermont ecological sub-regions and 10 of the 13 subregions
of Massachusetts. Pitcher-plant bogs are uncommon in Connecticut, and only one
site was sampled in that state.
Measurement of Geographic Variables
At each site, latitude and longitude
were determined using a Trimble Global Positioning System unit (Trimble Instruments,
Sunnyvale, CA, USA). Subsequently, digital aerial photographs were obtained
for each bog (from state mapping authorities), or, when digital photographs
were unavailable (five sites), photographic prints (from USGS-EROS) were scanned
and digitized. Aerial photographs were used to construct a set of data layers
in a geographic information system (using Arc-View GIS 3.2, ESRI, Redlands,
CA, USA), from which we calculated bog area and perimeter. We did not attempt
to measure the area of surrounding forests, as the forest was generally continuous
for at least several km2 around each bog. Site elevation was determined
from USGS topographic maps (using the software program Topo!, Wildflower Productions,
San Francisco, CA, USA).
Literature Cited
Bailey,
R.G. 1998. Ecoregions: the ecosystem geography of the oceans and continents.
Springer-Verlag, New York, New York, USA.