
The term "site" merits some discussion in this context. In some portions of the piping plover's range, breeding sites are naturally discrete and their limits are easily defined. In other areas, habitat is more continuous, and current use by piping plovers may be highly dispersed. In still other areas, once continuous stretches of habitat have been subdivided by shoreline stabilization structures, creating two or more smaller sites where larger ones once existed. Some sites have several landowners; in other cases, a single landownership contains several piping plover nesting sites. Some states define their sites in terms of the nearest access point (as a means of communicating the location of nesting concentrations), thereby subdividing some continuous stretches of habitat. One state defines an island to be a site, while another considers the clusters of breeding pairs at each end of a barrier island to be separate sites. A site, therefore, is an ambiguous concept, often artificially imposed on habitat areas. This limits the usefulness of current or potential numbers of breeding pairs in an area as a means of evaluating the importance of a site to the conservation of this species.
Capacity estimates (column 4) represent a conservative appraisal of carrying capacity in 1993. As noted on pages , these estimates were developed for the purpose of facilitating the population viability analysis, Appendix E. However, this recovery plan is premised on the recognition that piping plover habitat is inherently dynamic, and that the carrying capacity of individual sites is subject to change over time. These carrying capacity estimates, which reflect habitat conditions and piping plover breeding densities observed in 1993, should not be interpreted as site-specific management goals. Any use of carrying capacity projections for local management purposes or as a measure of management effectiveness must be based on current habitat conditions and updated as those conditions change over time. For example, the Massachusetts Division of Fisheries and Wildlife reviewed and revised its estimates of carrying capacity in 1995, as an important component of the conservation planning strategy for their application for incidental take under Section 10 of the ESA (see Appendix H).
The depth of available information about piping plover breeding activities varies among states and, in some cases, within states. Virginia biologists noted that due to the highly dynamic character of their unstabilized barrier islands, habitat suitability and carrying capacity of individual islands is especially subject to fluctuations over time. However, they expressed confidence that overall carrying capacity within Virginia can be maintained if natural coastal formation processes remain unimpeded. Biologists in New York and North Carolina have expressed particular concern about the accuracy of their site capacity estimates and caution that new information may warrant revised projections. As in Virginia, North Carolina biologists cautioned that suitability of individual sites fluctuates over very short time frames.
Other Rare Species Co-Occurring on Sites:
AO American oystercatcher
AP Amaranthus pumilus
AT Arctic tern
BP brown pelican
BS black skimmer
Cdd Cicindela dorsalis dorsalis
Cdm Cicindela dorsalis media
CT common tern
GBT gull-billed tern
LT least tern
LOG loggerhead turtle
PF peregrine falcon (breeding)
WP Wilson's plover
F Federally-listed species
H historic occurrence
S State-listed species
Owner:
P Private (except TNC and TTOR)
S State
TNC The Nature Conservancy
TTOR The Trustees of Reservations
NPS National Park Service
NASA National Aeronautics and Space Administration
Corps U.S. Army Corps of Engineers
USCG U.S. Coast Guard
NES National Estuarine Sanctuary
FWS U.S. Fish and Wildlife Service
C County
M Municipal
U Unknown
NOTE: In all states except Maine, Massachusetts, and some parts of Virginia, the
State holds title to the intertidal zone. To save space on this table, state ownership
of this area has not been shown for each site. However, the intertidal zone is an
extremely important component of piping plover habitat.
|
SITE |
1993 NESTING PAIRS | 1993 PRODUCTIVITY (Chicks/Pair) | ESTIMATED CAPACITY (Pairs) | MIGRATORY PLOVER USE | OTHER RARE SPECIES | OWNER |
| SOUTH CAROLINA | ||||||
| Waites Island (SC-1) |
1 |
U |
2 |
spring, fall, winter use |
WP,LT,AO |
State/university |
| NORTH CAROLINA | ||||||
| Bodie Island (So. end) (NC-1) |
0 |
- |
2 |
frequent use; winter use
also |
WP, LT, AO |
NPS |
| Cape Hatteras Point (NC-2) |
5 to 6 |
0.66 |
12 |
fall migration |
GBTS, WP, BSS, AT, APF, CT,
LT, Sooty tern, AO, LOGF |
NPS |
| Currituck Outer Banks (NC-3) |
2 |
0.5 |
10 |
spring and fall migration |
APF, LT |
FWS/P |
| Figure 8 Island (NC-4) |
0 |
- |
2 |
migratory and winter use
(increasing) |
APF, LOGF, AO, LT, CT, BS |
P |
| Hatteras Inlet (No. side) (NC-5) |
3 |
0.66 |
8 |
frequent use |
APF, BSS, CT, LT, AO, WP,
GBTS |
NPS |
| Holden Beach/Shallote Inlet (NC-6) |
4 |
1.0 |
6 |
winter use |
APF, LOGF, AO, willet, Sesuvium
portulacastrum |
P |
| Long Beach/Lockwood Folly's Inlet (NC-7) |
0 |
- |
1 |
winter use |
APF, LOGF, AO, WP, willet |
P |
| North Core Banks (NC-8) |
28 |
0.68 |
51 |
significant numbers;
winter use also |
APF, LT, LOGF, GBTS, BSS, CT,
WP, AO |
NPS |
| Ocracoke Island (No. and So. ends) (NC-9) |
3 |
0.33 |
8 |
low numbers |
APF, LT, LOGF, AO, CT |
NPS |
| Pea Island NWR (NC-10) |
0 |
- |
1 |
LOGF, LT, CT, AO, BSS, GBTS |
FWS | |
| Rachel Carson's Estuary/
Bird Shoals (NC-11) |
0 |
- |
1 |
migratory and winter use |
WP, LT, AO, BSS, CT, GBTS,
willet |
NES |
| Shackleford Banks (NC-12) |
0 |
- |
3 |
some winter use |
GBTS, WP, CT, BSS, LT, AO,
willet |
NPS |
| South Core Banks (NC-13) |
7 |
1.0 |
16 |
significant use |
APF, GBTS, BSS, LOGF, CT, LT,
WP, AO |
NPS |
| Sunset Beach (NC-14) |
0 |
- |
1 |
LT, CT, BSS, APF, LOGF |
P | |
| Topsail Beach (NC-15) |
1 |
U |
1 |
APF, LOGF, LT, CT, BSS, AO,
WP, LOGF, willet |
P | |
| VIRGINIA | ||||||
| Assateague/Tom's Cove Hook (VA-1) |
17 |
1.24 |
35 |
Cdm, LTS, WPS, AO |
FWS | |
| Assateague/Wash Flats (VA-2) |
0 |
0 |
10 |
PFF, LTS |
FWS | |
| Assateague/Wild Beach (VA-3) |
10 |
0.8 |
25 |
Cdm, AO, LTS |
FWS | |
| Assawoman Island (VA-4) |
10 |
2.0 |
20 |
WPS, LTS, Cdm, AO, CT, GBTS,
BS |
FWS | |
| Cedar Island (VA-5) |
12 |
U |
20 |
WPS, LTS, CT, Cdm, AO, BS |
FWS/P/TNC | |
| Cedar Sandbar (VA-6) |
0 |
- |
5 |
LTS, CT, GBTS, BS, AO, Cdm |
FWS/P | |
| Cobb Island (VA-7) |
4 |
U |
10 |
WPS, PFF, LTS, CT, AO, heronry,
BS, GBTS |
TNC | |
| Craney Island (VA-8) |
5 |
1.4 |
15 |
WPS, LTS, Am. avocet,
black-necked stilt, short-eared
owl |
Corps | |
| Fisherman Island (VA-9) |
0 |
- |
10 |
PFF, Cdm, AO, heronry, royal
tern, sandwich tern |
FWS/P | |
| Grandview Beach (VA-10) |
0 |
- |
15 |
AO, LTS, Cdm |
M | |
| Hog Island (VA-11) |
1 |
U |
5 |
PFF, CT, LTS, AO, heronry, Cdm,
GBTS, BS |
TNC | |
| Metompkin Island, North (VA-12) |
28 |
1.75 (4 pairs) |
50 |
WPS, PFF, CT, LTS, GBTS, BS,
AO, Cdm |
FWS/TNC | |
| Metompkin Island, South (VA-13) |
0 |
- |
10 |
AO, BS, CT, Cdm, GBTS |
TNC | |
| Myrtle Island (VA-14) |
9 |
U |
20 |
Cdm, AO, WPS, CT, GBTS |
TNC | |
| New Island (VA-15) |
0 |
_ |
5 |
AO, CT, BS, Cdm |
S | |
| Parramore Island (VA-16) |
0 |
- |
5 |
PFF, Cdm, AO |
TNC/USCG | |
| Ship Shoal (VA-17) |
1 |
U |
5 |
WPS, Cdm |
TNC | |
| Smith Island (VA-18) |
4 |
U |
10 |
WPS, AO, Cdm |
TNC/P | |
| Wallops Island (VA-19) |
3 |
1.33 |
10 |
PFF, WPS, LTS, AO |
NASA | |
| Wreck Island (VA-20) |
2 |
U |
5 |
WPS, AO, GBTS, CT, BS, heronry |
S | |
| MARYLAND | ||||||
| Assateague Island National Seashore
(MD-1) |
19 |
1.7 |
45 |
fall migration stopover |
CdmS, APFH, CT, LT, WPS, AO,
Susuvium maritimaS, roseate
ternFH, Cicindela lepida, major
migratory shorebird stopover
(esp. in fall) |
NPS/S |
| DELAWARE | ||||||
| Beach Plum Island Nature Preserve (DE-1) |
0 |
- |
2 to 3 |
LT, CTH, GBTH, Cicindela
marginata, Cicindela hirticollis |
S | |
| Cape Henlopen State Park (DE-2) |
2
|
.25 |
6 to 8 |
LT, roseate ternFH, Cicindela
lepida, CT, Forster's ternH, BSH,
PFF, major migratory shorebird
stopover |
S | |
| Delaware Seashore State Park (DE-3) |
1 pair seen
through mid-May |
0 |
8 |
APHF, LT, AO, BSH, CTH, royal
ternH |
S | |
| Fenwick Island State Park (DE-4) |
0 |
- |
1 to 2 |
LT, AO |
S | |
| NEW JERSEY | ||||||
| Avalon Complex - Avalon Dunes and Avalon
North (NJ-1) |
8 |
0.25 |
14 |
LTS, CdmH |
M | |
| Avalon Complex - Townsend's Inlet (NJ-2) |
1 |
1.00 |
5 |
fall migration |
LTS, CdmH |
M |
| Barnegat Light (NJ-3) |
12 |
0.67 |
15 |
spring, post-breeding, fall |
LTS, BSS, CT, AO,
CddFH |
M |
| Brigantine Beach, South (NJ-4) |
8 |
.38 |
20 |
spring |
LTS, CdmH |
M |
| Brigantine Inlet - Brigantine Inlet (NJ-5) |
0 |
- |
6 |
especially in spring |
CdmH |
S |
| Brigantine Inlet - Little Beach (NJ-6) |
19 |
1.1 |
>25 |
probably |
Cdm, LTS |
FWS |
| Champagne Island (Hereford Inlet) (NJ-7) |
0 |
- |
3 |
fall migration |
LTS, BSS, CT, AO, CdmH |
U |
| Coast Guard North (Two Mile Beach)
(NJ-8) |
0 |
- |
5 |
occasional spring |
LTS |
USCG |
| Coast Guard South (NJ-9) |
6 |
0.67 |
8 |
LTS |
USCG/P/M | |
| Holgate (NJ-10) |
14 |
.36 |
25 |
large numbers post-breeding on So. end |
CddHF, BP, LTS, BSS |
FWS |
| Island Beach State Park (NJ-11) |
0 |
- |
14 |
fairly high numbers in
spring |
LTS, CddFH |
S |
| Mantoloking Beach (NJ-12) |
4 |
1.5 |
8 |
CddFH |
P/M | |
| North Wildwood (NJ-13) |
5 |
0 |
8 |
LTS, CdmH |
M | |
| Ocean City Complex - Longport (NJ-14) |
0 |
- |
4 |
used in spring;
fall use possible |
P | |
| Ocean City Complex - Waverly Beach (NJ-15) |
1 |
0 |
5 |
post-breeding use |
LTS |
M |
| Sandy Hook - Coast Guard Beach (NJ-16) |
6 |
2.00 |
8 |
possible spring use |
LTS, CddF (reintroduction experiment conducted in 1994 and 1995) |
USCG |
| Sandy Hook - Critical Zone (NJ-17) |
5 |
0.6 |
5 |
NPS | ||
| Sandy Hook - Gunnison Beach (NJ-18) |
5 |
2.5 |
20 |
NPS | ||
| Sandy Hook - North Beach (NJ-19) |
9 |
2.2 |
25 |
NPS | ||
| Sea Isle City Complex - Corson's
Inlet (NJ-20) |
5 |
1.2 |
10 |
spring, post-breeding, fall |
LTS, BSS, AO, CdmH |
S |
| Sea Isle City Complex - Sea Isle City
(NJ-21) |
6 |
1.0 |
12 |
M | ||
| Sea Isle City Complex - Strathmere (NJ-22) |
6 |
.33 |
12 |
spring, post-breeding, fall |
LTS, BSS, AO, CdmH |
M |
| Sea Isle City Complex - Whale Beach
(NJ-23) |
4 |
1.00 |
14 |
post-breeding and fall |
LTS |
M |
| South Cape May Meadows (NJ-24) |
3 |
1.33 |
6 |
post-breeding |
LTS, CT, BSS |
TNC |
| NEW YORK | ||||||
| Accabonac Harbor (NY-1) |
4(1) |
6 |
probable |
LTS |
M | |
| Alder Island (NY-2) |
11 |
U |
U |
AO |
M | |
| Breezy Point to Far Rockaway (NY-3) |
221 |
NPS: 1.53 (15
pairs)
private: 0.77 (13
pairs) |
>45 |
post-breeding
concentrations at Breezy
Point in 1988, 1989,
1991, 1993 |
NPS: LTS, roseate ternF, CTS,
APF, BSS
private beach: LTS |
NPS/P/M |
| Cedar Beach Point (NY-4) |
01 |
2 |
U |
LTS, ospreyS |
M | |
| Cedar Point (NY-5) |
41 |
8 |
probable |
LTS |
C | |
| Conkling Point (NY-6) |
21 |
2 to 3 |
U |
LTS, CTS |
P | |
| Corey Creek Mouth (NY-7) |
01 |
0 (1 pair) |
2 |
U |
LTS, ospreyS |
P |
| Crab Creek/Shell Beach (NY-8) |
41 |
11 |
probable |
LTS |
M/P | |
| Crab Meadow Beach (NY-9) |
11 |
3 |
U |
LTS |
M/P | |
| Cutchogue Harbor (NY-10) |
11 |
1.0 |
4 |
U |
LTS, ospreyS |
TNC/P |
| Eatons Neck Point (NY-11) |
01 |
6 |
probable |
LTS, CTS, BSS |
P/USCG | |
| Fire Island (NY-12) |
111 |
1.62 (8 pairs) |
45 |
yes |
LTS, APF, CddFH, Polygonum
glaucum |
NPS/S/C/P/M |
| Fishers Island (NY-13) |
11 |
U |
U |
LTS,AO |
P | |
| Flax Pond Beach (NY-14) |
01 |
2 |
U |
LTS |
M/P/S | |
| Fresh Pond Landing (NY-15) |
11 |
0 |
2 |
U |
LTS, ospreyS |
S |
| Goldsmith Inlet (NY-16) |
01 |
>1 |
U |
LTS |
C | |
| Goose Creek Flanders Bay (NY-17) |
01 |
1 |
U |
LTS, CTS |
C | |
| Gull Pond West (NY-18) |
01 |
2 |
U |
LTS |
M/P | |
| Hicks Island/Goff Point (NY-19) |
21 |
>4 |
yes |
roseate ternF, LTS, CTS, BSS, AO |
S | |
| Jessup Neck (NY-20) |
11 |
1.0 |
3 |
yes |
LTS, post-breeding roseate ternsF |
FWS/C |
| Jockey Creek Spoil Island (NY-21) |
01 |
U |
U |
CTS, LTS |
P | |
| Jones Island (NY-22) |
391 |
1.30 (47 pairs) |
50 to 60 |
yes |
roseate ternF, LTS, CT, APF,
CddFH, BSS, Polygonum glaucum |
S/M/P |
| Lionhead Beach (NY-23) |
11 |
3 |
U |
LTS |
P/M | |
| Lloyd Neck East Beach (NY-24) |
01 |
U |
U |
LTS, CTS |
FWS | |
| Lloyd Point (NY-25) |
11 |
4 |
probable |
LTS, CTS |
S/P | |
| Long Beach Island (NY-26) |
191 |
> 21 |
yes |
LTS, CddFH |
M/C/P | |
| Long Beach Peninsula (NY-27) |
01 |
4 |
U |
LTS |
M/P | |
| Long Beach Sag Harbor (NY-28) |
01 |
4 |
U |
LTS |
M | |
| Majors Point to Gibsons Beach (NY-29) |
31 |
6 to 8 |
yes |
LTS, ospreyS, Polygonum
glaucum |
TNC | |
| Marratooka Point to Kimogener Point
(NY-30) |
01 |
2 |
U |
LTS, ospreyS |
P | |
| Mattituck Inlet (NY-31) |
01 |
2 |
U |
ospreyS, LTS, CTS |
M/P | |
| Miamogue Point/Jamesport Town Beach
(NY-32) |
21 |
0 |
3 |
U |
LTS |
M |
| Middle Pond Inlet (NY-33)HTML> | 11 |
0 |
2 |
yes |
LTS |
M/P |
| Mount Misery Point (NY-34) |
01 |
5 |
U |
roseate ternF, LTS, CTS |
C | |
| Old Field Beach (NY-35) |
01 |
4 |
U |
LTS, CTS |
M/C | |
| Orient Beach (NY-36) |
51 |
1.9 (7 pairs) |
12 |
yes |
LTS, ospreyS, Polygonum
glaucum |
S |
| Oyster Pond (NY-37) |
21 |
U |
U |
S | ||
| Pine Neck (NY-38) |
21 |
4 |
U |
LTS |
M | |
| Plum Point (NY-39) |
01 |
U |
U |
LTS |
P | |
| Port of Eygpt (NY-40) |
31 |
3 |
U |
LTS, CTS, BSS, roseate ternF |
P | |
| Red Cedar Point/Red Creek Pond (NY-41) |
11 |
6 |
probable |
LTS, CTS |
P/U | |
| Richmond Creek (NY-42) |
01 |
2 |
U |
LTS |
P | |
| Robins Island (NY-43) |
01 |
2 |
U |
LTS, ospreyS |
P | |
| Sammys Beach Peninsula (NY-44) |
11 |
5 |
probable |
LTS, CTS, roseate ternF, BSS, AO |
M | |
| Sand City (NY-45) |
21 |
>5 |
probable |
LTS, CTS, BSS |
M | |
| Sebonac Creek (NY-46) |
31 |
4 |
probable |
LTS |
P | |
| Sebonac Neck (NY-47) |
31 |
3.5 (2 pairs) |
4 |
probable |
LTS |
M/P |
| Short Beach (NY-48) |
31 |
4 |
U |
LTS |
M | |
| Southhampton Beach to Fairfield Pond Lane
Beach (NY-49) |
41 |
20 to 30 |
probable |
LTS, APF, CddFH |
C/P/M | |
| Towd Neck/Wooley Pond (NY-50) |
01 |
6 |
U |
LTS |
P/M | |
| Upper Beach/Lower Beach (NY-51) |
11 |
5 |
U |
LTS, Polygonum glaucum |
M/C | |
| Youngs Island (NY-52) |
01 |
2 |
U |
LTS, CTS |
M | |
| Wainscott Pond to Montauk Beach (NY-53) |
61 |
15 to 20 |
probable |
LTS, CddFH |
S/M | |
| West Meadow Beach (NY-54) |
01 |
3 |
U |
M/P | ||
| Westhampton Island (NY-55) |
361 |
0.76 (29 pairs) |
50 to 60 |
yes |
LTS, APF, BSS, CTS, AO, CddFH,
Polygonum glaucum |
M/C/P |
| CONNECTICUT | ||||||
| Goshen Cove (CT-1) |
1 |
2.0 |
3 |
S/P | ||
| Griswold Point (CT-2) |
7 |
.29 |
10 |
LTS, CddFH |
TNC/M/P | |
| Hammonasset Beach (CT-3) |
1 |
0 |
7 |
LTS, AOS |
S/P | |
| Housatonic River Complex - Milford Point
(CT-4) |
3 |
.66 |
8 to 10 |
LTS |
S/FWS | |
| Housatonic River Complex - Short Beach (CT-5) |
1 |
0 |
5 |
LTS |
M | |
| Lewis Gut Complex - Pleasure Beach (CT-6) |
1 |
0 |
10 to 15 |
LTS |
M | |
| Lewis Gut Complex - Long Beach (CT-7) |
6 |
.5 |
15 |
LTS |
M | |
| Sandy Point (CT-8) |
3 |
0 |
15 |
LTS |
M | |
| RHODE ISLAND | ||||||
| Block Island (RI-1) |
0 |
- |
U |
FWS/U | ||
| Briggs Beach (RI-2) |
4 |
0 |
7 |
limited |
P | |
| East Matunuck State Beach (RI-3) |
1 |
U |
3 |
S | ||
| Maschaug Beach (RI-4) |
4 |
4.0 |
8 |
LT |
P | |
| Napatree Point (RI-5) |
4 |
1.0 |
7 |
AO, LT, large concentration of
post-breeding roseate ternsF |
M/P | |
| Ninigret (RI-6) |
2 |
3.0 |
10 |
LT |
FWS/S/P | |
| Quicksand Pond (RI-7) |
8 |
2.6 |
15 |
significant use |
LT |
TNC |
| Trustom Pond (RI-8) |
8 |
0.9 |
10 |
|
LT |
FWS |
| Weekapaug (RI-9) |
0 |
_ |
5 to 10 |
Fire Dist. | ||
| MASSACHUSETTS | ||||||
| Chappaquiddick Island (Norton Point to the Gut)
(MA-1) |
9 |
1.33 |
40 |
LTS, AO, CTS, CddFH |
C/P/S/M/
TTOR | |
| Coast Guard Beach (MA-2) |
8 |
1.25 |
10 |
LTSH |
NPS | |
| Crane Beach (MA-3) |
18 |
1.94 |
25 |
LTS |
TTOR | |
| Cuttyhunk Island (MA-4) |
5 |
2.25 (based on 4
pairs) |
7 |
LTS, CTS |
P | |
| Dogfish Bar, Martha's Vineyard (MA-5) |
4 |
1.25 |
5 |
P | ||
| Duxbury Beach (MA-6) |
4 |
2.0 (based on 4
pairs) |
15 |
LTS |
M | |
| Eel Point (MA-7) |
1 |
3.0 |
5 |
pre-breeding |
AO |
P |
| Great Point/The Galls (MA-8) |
9 |
1.0 |
25 |
use probable, surveys
needed |
LTS, northern harrierS |
FWS/TTOR/
USCG |
| Harding Beach (MA-9) |
1 |
4.0 |
3 |
LTS |
M | |
| Head of the Meadows to Cahoon Hollow (MA-10) |
1 |
3.0 |
10 |
NPS/M | ||
| Horseneck Beach/Gooseberry Neck (MA-11) |
6 |
1.67 |
12 |
CddF |
S/P/M | |
| Jeremy Pt./Great Island (MA-12) |
6 |
1.83 |
10 |
NPS/P | ||
| Little Beach/Barney's Joy (MA-13) |
11 |
2.2 (based on 10
pairs) |
15 |
LTS |
P | |
| Marconi Beach (LeCount Hollow to Nauset Light
Beach) (MA-14) |
9 |
2.44 |
15 |
CddFH |
NPS/M | |
| Monomoy Islands (MA-15) |
4 |
2.0 |
>30 |
LTS, roseate ternF, CTS, short-eared owlS, northern harrierS |
FWS | |
| Muskeget Island (MA-16) |
7 |
U |
10 |
short-eared owlS |
P/M | |
| Nashawena Island (MA-17) |
2 |
4.0 |
10 |
LTS |
P | |
| Nauset Beach (Chatham & Orleans) (MA-18) |
16 |
2.25 |
50 |
M/P | ||
| Nauset Spit (Plover Island - Orleans)
(MA-19) |
21 |
1.71 |
30 |
LTS, CTS, AO, BS, AT |
M | |
| Plum Island (MA-20) |
10 |
2.1 |
20 |
LTS |
FWS/S | |
| Plymouth Beach (MA-21) |
4 |
1.0 |
10 |
LTS, roseate ternF, CTS, arctic
ternS |
M | |
| Popponesset Spit (MA-22) |
3 |
U |
4 |
LTS |
P/M | |
| Race Point Beach to High Head (MA-23) |
29 |
2.07 |
60 |
LTS, Mertensia maritima |
NPS | |
| Richmond Pond/Cockeast Pond/Acoaxet (MA-24) |
1 |
1.0 |
4 |
P | ||
| Sampson's Island - Dead Neck (MA-25) |
6 |
0.17 |
6 |
P | ||
| Sandy Neck (MA-26) |
15 |
2.47 |
25 |
LTS |
M | |
| Scorton Creek/East Sandwich (MA-27) |
6 |
1.83 |
6 |
M/P | ||
| Scusset Beach (MA-28) |
4 |
2.25 |
5 |
S | ||
| Siasconset/Low Beach/Tom Nevers (MA-29) |
1 |
0 |
>20 |
LTSH, northern harrierS |
USCG/M/P | |
| Smith Point (MA-30) |
0 |
- |
>5 |
possible; need surveys |
post-breeding roseate ternsF |
P/M |
| South Beach Island (MA-31) |
13 |
2.15 |
30 |
LTS, CTS, AO, northern harrierS |
M | |
| South Cape Beach/Washburn Island (MA-32) |
3 |
2.33 |
5 |
LTS |
S | |
| South Shore, Martha's Vineyard (Chilmark Pond
to Edgartown Great Pond) (MA-33) |
6 |
1.67 |
30 |
P, TTOR | ||
| Squibnocket Beach (MA-34) |
4 |
3.0 |
7 |
CddF, APFH |
P | |
| Third Cliff (MA-35) |
3 |
1.67 |
3 |
U.S. Air
Force/M/P | ||
| Town Neck/Springhill - Sandwich (MA-36) |
4 |
0.5 |
6 |
LTS |
M/P | |
| Tuckernuck Island (MA-37) |
0 |
_ |
>5 |
northern harrierS, short-eared
owlS |
P | |
| Wood End/Long Point - Provincetown
(MA-38) |
7 |
2.57 |
15 |
NPS | ||
| MAINE | ||||||
| Crescent Surf/Laudholm Beaches (ME-1) |
5 |
4.0 |
8 |
some migratory use |
LTS, occasional roseate ternF
feeding |
FWS/M/P |
| Goose Rocks/Batson River (ME-2) |
2 |
3.5 |
4 |
LTS |
P | |
| Higgins Beach/Ram Island (ME-3) |
3 |
1.7 |
5 |
P | ||
| Pine Point/Western Beach (ME-4) |
3 |
3.0 |
5 |
LTS (occasional use), harlequin
duck wintering site |
M/P | |
| Reid State Park (ME-5) |
3 |
1.7 |
5 |
|
S | |
| Seawall/Popham/Hunnewell Beach (ME-6) |
15 |
1.7 |
25 |
post-breeding
concentrations |
RTF, LTS |
S/P |
1. Estimates of nesting pairs for New York sites are a drawn from a "window" census and may differ from estimates shown in other reports or from the number of pairs on which productivity data is based.
|
URL address http://pipingplover.fws.gov/
Last updated March 15, 2000