| Appendix 3. Mean
productivity indices and time-constant estimates of adult survival probability, recapture
probability, and proportion of residents from four years (1992-1995) of MAPS data.
A. For 32
species for which at least 200 aged individuals were captured over the four years
(1992-1995) at MAPS stations operated in eastern North America.
| |
Num. Sta.1 |
Num. Aged Ind.2 |
Prod. Index3 |
Num. Ad.4 |
Survival Probability5 |
Recapture Probability6 |
Proportion of residents7 |
M8 |
| Downy Woodpecker (Picoides
pubescens) |
42 |
620 |
0.618 |
262 |
0.713 |
(0.164) |
0.447 |
(0.133) |
0.255 |
(0.098) |
R |
| Acadian Flycatcher (Empidonax
virescens) |
15 |
300 |
0.148 |
275 |
0.701 |
(0.142) |
0.381 |
(0.108) |
0.462 |
(0.163) |
N |
| Traill's Flycatcher (E.
traillii or alnornum) |
13 |
464 |
0.235 |
370 |
0.606 |
(0.105) |
0.747 |
(0.105) |
0.197 |
(0.052) |
N |
| Least Flycatcher (E.
minimus) |
11 |
309 |
0.406 |
244 |
-----9 |
----- |
----- |
----- |
----- |
----- |
N |
| White-eyed Vireo (Vireo
griseus) |
14 |
244 |
0.287 |
188 |
0.731 |
(0.163) |
0.432 |
(0.129) |
0.376 |
(0.141) |
N |
| Red-eyed Vireo (V.
olivaceus) |
42 |
1143 |
0.150 |
182 |
0.543 |
(0.073) |
0.406 |
(0.071) |
0.465 |
(0.104) |
N |
| Blue Jay (Cyanocitta
cristata) |
34 |
224 |
0.372 |
182 |
0.600 |
(0.215) |
0.561 |
(0.220) |
0.165 |
(0.091) |
T |
| Carolina Chickadee (Poecile
carolinensis) |
25 |
321 |
0.581 |
160 |
0.326 |
(0.200) |
0.180 |
(0.249) |
1.000 |
(1.505) |
R |
| Black-capped Chick. (P.
atricapilla) |
29 |
1059 |
0.592 |
484 |
0.455 |
(0.089) |
0.551 |
(0.107) |
0.537 |
(0.159) |
R |
| Tufted Titmouse (Baeolophus
bicolor) |
29 |
682 |
0.588 |
290 |
0.464 |
(0.098) |
0.567 |
(0.116) |
0.643 |
(0.195) |
R |
| Carolina Wren (Thyrothorus
ludovicianus) |
26 |
617 |
0.573 |
282 |
0.347 |
(0.085) |
0.743 |
(0.127) |
0.546 |
(0.178) |
R |
| House Wren (Troglodytes
aedon) |
15 |
539 |
0.406 |
324 |
0.520 |
(0.144) |
0.451 |
(0.157) |
0.344 |
(0.160) |
N |
| Veery (Catharus
fuscesens) |
23 |
893 |
0.264 |
610 |
0.535 |
(0.058) |
0.707 |
(0.063) |
0.543 |
(0.083) |
N |
| Wood Thrush (Hylocichla
mustelina) |
30 |
1205 |
0.273 |
987 |
0.446 |
(0.069) |
0.559 |
(0.085) |
0.432 |
(0.097) |
N |
| American Robin (Turdus
migratorius) |
41 |
1336 |
0.481 |
765 |
0.500 |
(0.114) |
0.155 |
(0.082) |
0.776 |
(0.440) |
T |
| Gray Catbird (Dumetella
carolinensis) |
41 |
3739 |
0.417 |
2276 |
0.453 |
(0.040) |
0.488 |
(0.050) |
0.586 |
(0.082) |
N |
| Blue-winged Warbler (Vermivora
pinus) |
10 |
259 |
0.337 |
193 |
0.431 |
(0.141) |
0.568 |
(0.184) |
0.441 |
(0.212) |
N |
| Yellow Warbler (Dendroica
petechia) |
24 |
1770 |
0.434 |
954 |
0.445 |
(0.062) |
0.495 |
(0.079) |
0.527 |
(0.113) |
N |
| Chestnut-sided Warbler (D.
pensylvanica) |
10 |
283 |
0.282 |
207 |
0.727 |
(0.146) |
0.540 |
(0.115) |
0.360 |
(0.115) |
N |
| Black-and-white Warbler (Mniotilta
varia) |
20 |
412 |
0.339 |
292 |
0.841 |
(0.200) |
0.190 |
(0.093) |
0.470 |
(0.255) |
N |
| American Redstart (Setophaga
ruticilla) |
21 |
840 |
0.365 |
562 |
0.452 |
(0.123) |
0.244 |
(0.121) |
0.606 |
(0.341) |
N |
| Ovenbird (Seiurus
aurocapillus) |
30 |
1170 |
0.430 |
729 |
0.521 |
(0.090) |
0.452 |
(0.096) |
0.410 |
(0.116) |
N |
| Common Yellowthroat (Geothlypis
trichas) |
38 |
1998 |
0.432 |
1217 |
0.501 |
(0.057) |
0.492 |
(0.064) |
0.482 |
(0.084) |
N |
| Hooded Warbler (Wilsonia
citrina) |
11 |
241 |
0.274 |
193 |
0.620 |
(0.134) |
0.436 |
(0.125) |
0.525 |
(0.187) |
N |
| Eastern Towhee (Pipilo
erythrophthalmus) |
23 |
214 |
0.354 |
135 |
0.304 |
(0.152) |
0.355 |
(0.247) |
1.000 |
(0.827) |
T |
| Field Sparrow (Spizella
pusilla) |
22 |
632 |
0.376 |
529 |
0.523 |
(0.090) |
0.429 |
(0.095) |
0.521 |
(0.149) |
T |
| Song Sparrow (Melospiza
melodia) |
27 |
1655 |
0.600 |
703 |
0.374 |
(0.073) |
0.571 |
(0.106) |
0.515 |
(0.149) |
T |
| Swamp Sparrow (M.
georgiana) |
6 |
319 |
0.608 |
108 |
-----9 |
----- |
----- |
----- |
----- |
----- |
T |
| Northern Cardinal (Cardinalis
cardinalis) |
42 |
1347 |
0.374 |
848 |
0.596 |
(0.068) |
0.422 |
(0.063) |
0.574 |
(0.111) |
R |
| Indigo Bunting (Passerina
cyanea) |
27 |
416 |
0.216 |
376 |
0.452 |
(0.114) |
0.532 |
(0.143) |
0.333 |
(0.123) |
N |
| Red-winged Blackbird (Agelaius
phoeniceus) |
21 |
281 |
0.076 |
328 |
0.353 |
(0.229) |
0.454 |
(0.340) |
0.133 |
(0.131) |
T |
| Common Grackle (Quiscalus
quiscula) |
21 |
341 |
0.486 |
200 |
-----9 |
----- |
----- |
----- |
----- |
----- |
T |
B. For 26 species for which
at least 60 aged individuals were captured over the four years (1992-1995) at MAPS
stations operated in the Sierra Nevada physiographic province.
| |
Num. Sta.1 |
Num. Aged Ind.2 |
Prod. Index3 |
Num. Ad.4 |
Survival Probability5 |
Recapture Probability6 |
Proportion of residents7 |
M8 |
| Red-breasted Sapsucker (Sphyrapicus
ruber) |
7 |
140 |
0.262 |
93 |
0.460 |
(0.154) |
0.357 |
(0.171) |
0.954 |
(0.535) |
T |
| Western Wood-Pewee (Contopus
sordidulus) |
7 |
115 |
0.240 |
80 |
0.303 |
(0.188) |
0.462 |
(0.316) |
1.000 |
(0.863) |
N |
| Willow Flycatcher (Empidonax
traillii) |
2 |
81 |
0.254 |
49 |
0.641 |
(0.205) |
0.397 |
(0.177) |
0.788 |
(0.424) |
N |
| Hammond's Flycatcher (E.
hammondii) |
5 |
107 |
0.262 |
71 |
0.579 |
(0.273) |
0.181 |
(0.163) |
0.985 |
(0.964) |
N |
| Dusky Flycatcher (E.
oberholseri) |
4 |
305 |
0.278 |
230 |
0.570 |
(0.141) |
0.564 |
(0.143) |
0.288 |
(0.112) |
N |
| Cassin's Vireo (Vireo
cassinii) |
2 |
113 |
0.250 |
88 |
0.377 |
(0.242) |
0.482 |
(0.346) |
0.414 |
(0.409) |
N |
| Warbling Vireo (V.
gilvus) |
7 |
518 |
0.220 |
384 |
0.609 |
(0.116) |
0.533 |
(0.114) |
0.281 |
(0.082) |
N |
| Mountain Chickadee (Poecile
gambeli) |
7 |
211 |
0.513 |
87 |
-----9 |
----- |
----- |
----- |
----- |
----- |
R |
| Red-breasted Nuthatch (Sitta
canadensis) |
5 |
75 |
0.667 |
27 |
-----9 |
----- |
----- |
----- |
----- |
----- |
R |
| Brown Creeper (Certhia
americana) |
5 |
87 |
0.506 |
51 |
-----9 |
----- |
----- |
----- |
----- |
----- |
R |
| Golden-crowned Kinglet (Regulus
satrapa) |
3 |
85 |
0.614 |
27 |
-----9 |
----- |
----- |
----- |
----- |
----- |
R |
| American Robin (Turdus
migratorius) |
7 |
193 |
0.296 |
122 |
0.367 |
(0.201) |
0.244 |
(0.216) |
1.000 |
(0.973) |
T |
| Yellow Warbler (Dendroica
petechia) |
5 |
282 |
0.401 |
145 |
0.607 |
(0.121) |
0.554 |
(0.123) |
0.538 |
(0.169) |
N |
| Yellow-rumped Warbler (D.
coronata) |
7 |
803 |
0.492 |
199 |
-----9 |
----- |
----- |
----- |
----- |
----- |
T |
| Hermit Warbler (D.
occidentalis) |
6 |
264 |
0.552 |
105 |
-----9 |
----- |
----- |
----- |
----- |
----- |
N |
| MacGillivray's Warbler (Oporornis
tolmiei) |
6 |
571 |
0.431 |
272 |
0.576 |
(0.076) |
0.710 |
(0.077) |
0.595 |
(0.111) |
N |
| Wilson's Warbler (Wilsonia
pusilla) |
7 |
759 |
0.408 |
401 |
0.501 |
(0.084) |
0.640 |
(0.099) |
0.435 |
(0.106) |
N |
| Western Tanager (Piranga
ludoviciana) |
5 |
109 |
0.419 |
63 |
-----9 |
----- |
----- |
----- |
----- |
----- |
N |
| Chipping Sparrow (Spizella
passerina) |
5 |
109 |
0.364 |
70 |
-----9 |
----- |
----- |
----- |
----- |
----- |
N |
| Song Sparrow (Melospiza
melodia) |
6 |
394 |
0.525 |
165 |
0.459 |
(0.113) |
0.762 |
(0.120) |
0.627 |
(0.203) |
T |
| Lincoln's Sparrow (M.
lincolnii) |
7 |
420 |
0.458 |
213 |
0.444 |
(0.132) |
0.363 |
(0.152) |
1.000 |
(0.517) |
N |
| White-crowned Sparrow (Zonotrichia
leucophrys) |
2 |
242 |
0.358 |
119 |
0.472 |
(0.124) |
0.469 |
(0.144) |
1.000 |
(0.413) |
T |
| Dark-eyed Junco (Junco
hyemalis) |
7 |
1366 |
0.636 |
404 |
0.483 |
(0.093) |
0.440 |
(0.103) |
0.614 |
(0.187) |
T |
| Purple Finch (Carpodacus
purpureus) |
2 |
170 |
0.186 |
180 |
-----9 |
----- |
----- |
----- |
----- |
----- |
T |
| Cassin's Finch (C.
cassinii) |
5 |
152 |
0.360 |
95 |
-----9 |
----- |
----- |
----- |
----- |
----- |
T |
| Pine Siskin (Carduelis
pinus) |
3 |
204 |
0.365 |
106 |
-----9 |
----- |
----- |
----- |
----- |
----- |
T |
1 Number of
stations at which adults of the species were captured.
2 Number of aged
individuals captured during all four years 1992-1995 at all stations pooled where the
species was a regular breeder.
3 Mean
productivity index over the four years 1992-1995 given as proportion of young in the
catch.
4 Number of adult
individuals captured at all stations pooled where the species was a regular breeder (i.e.,
number of capture histories).
5 Adult survival
probability presented as the maximum likelihood estimate (standard error of the
estimate).
6 Recapture
probability presented as the maximum likelihood estimate (standard error of the
estimate).
7 Proportion of
residents presented as the maximum likelihood estimate (standard error of the
estimate).
8 Migration
strategy: P = permanent resident; T = temperate-wintering migrant; N = Neotropical
migrant.
9 Species for
which data were insufficient to provide estimates for adult survival probability. |