Pacific Flyway Data Book, 2025

Migratory Game Bird Monitoring: Estimates of Abundance, Harvest, and Hunter Activity

U.S. Fish and Wildlife Service
Division of Migratory Bird Management
Pacific Flyway Office
http://www.pacificflyway.gov

11 September 2025

Introduction

The following abundance, harvest, and hunter activity data have been assembled for use by State and U.S. Fish and Wildlife Service (USFWS) personnel in formulating recommendations for migratory bird hunting seasons in the Pacific Flyway. This collection of information can also serve as a desk-top reference for providing responses to inquiries from agency personnel, the media, and the public.

These data represent an extraordinary collaborative effort by many individuals from State, Federal, and other organizations. Thank you to all cooperators who have contributed toward this significant effort.

Some migratory bird surveys were not conducted in 2020 and 2021 because of the coronavirus pandemic. Consequently, some tables are missing data from these years as a result of no surveys being conducted.

Please note that abundance estimates are indices to abundance and not absolute population size. Abundance indices are either counts or estimates of a proportion of a population. The indices provide a measure of the relative abundance of a population over time.

Data Tables
Each data table represents a data asset and is uniquely numbered for ease of reference. See the table of contents for a list of available data tables. The data table number is the appropriate reference number for any figure or table produced for a data asset, particularly for questions and the supporting data. The sequential numbers assigned to each table and figure in this document is of no significance for reference and may change with each document update.

Document Navigation
There is an interactive table of contents to facilitate quickly locating data of interest. Data tables are organized into sections, each with a data type theme (e.g., abundance, harvest). Click on the section heading to expand the table of contents and see available data tables. Click on the primary heading or Introduction section in the table of contents to collapse all sections.

Time Series Statistics
Time series statistics are provided in a table for the primary monitoring data included in graphs. Missing values in the time series statistics table means that the statistic is not estimable. In these cases, missing values were used rather than “N/A” for aesthetics in the statistics table.

Figure and Data Access
Any figure in this document can be copied with a right mouse click over the figure of interest and then selecting “Copy image” or “Save image as.” Also, all data and figures in this report may be downloaded for use from an online portal. Each table and figure is referenced by the data table number it is associated with. Contact the Pacific Flyway Office for the URL of the online portal.

Technical Details
This report provides original data and calculations in support of cooperative Pacific Flyway Council and USFWS harvest strategy assessments and to help inform harvest management decisions for all migratory game bird populations. See the Pacific Flyway Council’s website for migratory game bird population management plans (http://www.pacificflyway.gov/management.asp). Unless otherwise noted, harvest management prescriptions apply to the hunting season starting the year after the title year of this data book so long as the data in the respective data table are current through the title year.

Original data are provided by the USFWS Headquarters Migratory Bird Program, USFWS Alaska Region, USFWS Mountain-Prairie Region, and the States. In some cases, Pacific Flyway Council management indices are derived from these data to help inform harvest management decisions. We note the original source of data before each data table and note how any management indices are calculated. The original data are generally included in annual USFWS and State population status and harvest reports and survey memos. Any use of the data should be by permission of the agency or agencies that provided the data (see Suggested Citations, below).

VCF and Fall Projection Estimates
A visibility correction factor (VCF; or fall projection adjustment factor) is applied to survey data for dusky Canada geese, cackling (minima) cackling geese, and Pacific white-fronted geese based on models fit to the data. Similarly, percent Ross’s geese in the California white goose survey is calculated based on a fitted model. Documentation of how these models were fit and estimates derived are in separate documents and available upon request of the USFWS Pacific Flyway Representative’s Office.

Missing Data and Moving 3-year Averages
Missing data from all or part of a survey year results in no management indices being calculated for that year. The only exception is for the winter counts including snow geese (so long as there are counts in at least California and Skagit-Fraser River Delta areas), brant (so long as there are counts in North America and Mexico), and tundra swans (so long as there are counts in the U.S. Atlantic and Mississippi flyways and Ontario, Canada). The total winter count is interpreted as the minimum known population size with no variance.

Moving 3-year averages are calculated as the 3 most recent available abundance estimates, and is an ad hoc way of reducing annual observation variance in survey estimates.

Suggested Citations
Any use or reference to the data provided in this report should be cited accordingly. Please contact the appropriate State or Federal representative for survey and citation information. State and Federal representatives contact information may be found on the Pacific Flyway Council’s website at http://www.pacificflyway.gov/contacts.asp.

Pacific Flyway Data Book:
U.S. Fish and Wildlife Service. 2025. Pacific Flyway Data Book, 2025. U.S. Department of Interior, Fish and Wildlife Service, Division of Migratory Bird Management, Pacific Flyway Office, Washington D.C.

USFWS Alaska Region:
Frost, C. J., D. E. Safine, J. B. Fischer, and E. E. Osnas. 2025. Alaska Goose, Swan, and Crane Population Indices. U.S. Department of Interior, Fish and Wildlife Service, Alaska Region, Migratory Bird Management, Anchorage. https://doi.org/10.7944/mxfs-0y52

Abundance (Primary Data)

Data Table 1: Brant, Pacific (fall)

Original data source: Brant Fall Photographic Survey at Izembek Lagoon, AK; USFWS Alaska Region. Data maintained by USFWS Alaska Region.

Provided in the table below are abundance (Estimate) and standard error (SE) of brant in fall. Also provided are the number of replicate surveys (Reps) and abundance moving 3-year average (M3yr) and standard error (M3yr.SE).

Table 1. Pacific brant abundance in fall, 2017-2024.
Year Estimate SE Reps M3yr M3yr.SE
2017 377,029 96,602 3 NA NA
2018 227,450 37,501 3 NA NA
2019 272,468 57,500 2 292,316 68,422
2020 NA NA NA NA NA
2021 NA NA NA NA NA
2022 201,576 53,760 5 233,831 50,341
2023 245,074 69,703 3 239,706 60,704
2024 188,820 50,101 4 211,823 58,477

Figure 1: Pacific brant abundance in fall. Circles are annual estimates with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The blue dashed reference line is the Pacific Flyway Council’s population objective. The red dashed reference lines represent threshold values in the harvest strategy decision and the red reference line is the closure threshold.
Time series statistics
Parameter Estimate SE L95%CI U95%CI
1-year index 188,820 50,101 90,622 287,018
3-year indexa 211,823 58,477 97,208 326,439
LTA 264,719
Objective 322,000
% change from LTA -29
% change from obj -34
Mgmt index (n years) 3
a 2022, 2023, 2024

Harvest Strategy
Management index: Total brant in fall.

Management thresholds:
>293,000 Liberal
>243,000 Moderate
≥102,000 Restrictive
Closed

If the population declines to a level which prescribes a closed season, a restrictive hunting season may not resume until the 3-year average population index exceeds 112,000 brant.

Management prescription: Restrictive.

Note that the management prescription applies to the 2025 hunting season.

Regulatory alternatives:
Liberal
AK: 107 days and 4-bird bag, Sep 1-Jan 26
WA: 37 days and 2-bird bag, Saturday closest to Sep 24-Jan 31
OR: 37 days and 2-bird bag, Saturday closest to Sep 24-Dec 15
CA: 37 days and 2-bird bag, Saturday closest to Sep 24-Dec 15
Moderate
AK: 107 days and 2-bird bag, Sep 1-Jan 26
WA: 27 days and 2-bird bag, Saturday closest to Sep 24-Jan 31
OR: 27 days and 2-bird bag, Saturday closest to Sep 24-Dec 15
CA: 27 days and 2-bird bag, Saturday closest to Sep 24-Dec 15
Restrictive
AK: 51 days and 2-bird bag, Sep 1-Jan 26
WA: 16 days and 2-bird bag, Saturday closest to Sep 24-Jan 31
OR: 16 days and 2-bird bag, Saturday closest to Sep 24-Dec 15
CA: 16 days and 2-bird bag, Saturday closest to Sep 24-Dec 15
Closed

Data Table 2: Cackling Goose, Aleutian

Original data source: Pacific Flyway Cooperative Aleutian Cackling Goose Mark-resight Survey; California, Oregon, and USFWS Pacific Flyway Office. Data maintained by USFWS Pacific Flyway Office.

Provided in the table below are abundance (Estimate) and standard error (SE) of Aleutian cackling geese from direct counts (1975–1995) and from estimation using mark-resight methods (1996–2024; closed-robust design model). Also provided are the abundance moving 3-year average (M3yr) and standard error (M3yr.SE). Mark-resight abundance estimates may change with each annual data update because they are based on model fit to the full time series of mark-resight data.

Table 2. Aleutian Cackling goose abundance in winter, 1975-2025.
Year Estimate SE M3yr M3yr.SE Method
1975 790 NA NA NA Direct count
1976 900 NA NA NA Direct count
1977 1,280 NA 990 NA Direct count
1978 1,500 NA 1,227 NA Direct count
1979 1,590 NA 1,457 NA Direct count
1980 1,740 NA 1,610 NA Direct count
1981 2,000 NA 1,777 NA Direct count
1982 2,700 NA 2,147 NA Direct count
1983 3,500 NA 2,733 NA Direct count
1984 3,800 NA 3,333 NA Direct count
1985 4,200 NA 3,833 NA Direct count
1986 4,300 NA 4,100 NA Direct count
1987 5,000 NA 4,500 NA Direct count
1988 5,400 NA 4,900 NA Direct count
1989 5,800 NA 5,400 NA Direct count
1990 6,300 NA 5,833 NA Direct count
1991 7,000 NA 6,367 NA Direct count
1992 7,680 NA 6,993 NA Direct count
1993 11,680 NA 8,787 NA Direct count
1994 15,700 NA 11,687 NA Direct count
1995 19,150 NA 15,510 NA Direct count
1996 15,451 558 16,767 NA Mark-resight
1997 20,394 763 18,332 NA Mark-resight
1998 32,453 1,071 22,766 825 Mark-resight
1999 35,551 3,122 29,466 1,956 Mark-resight
2000 34,278 1,347 34,094 2,058 Mark-resight
2001 NA NA NA NA NA
2002 NA NA NA NA NA
2003 72,856 2,711 47,561 2,511 Mark-resight
2004 110,732 4,299 72,622 3,036 Mark-resight
2005 87,155 4,558 90,248 3,941 Mark-resight
2006 100,262 4,532 99,383 4,465 Mark-resight
2007 107,634 7,585 98,350 5,740 Mark-resight
2008 112,621 6,782 106,839 6,431 Mark-resight
2009 84,489 11,913 101,581 9,045 Mark-resight
2010 106,871 8,467 101,327 9,302 Mark-resight
2011 101,650 7,009 97,670 9,358 Mark-resight
2012 132,735 10,071 113,752 8,607 Mark-resight
2013 162,465 14,689 132,283 11,050 Mark-resight
2014 150,452 13,084 148,551 12,759 Mark-resight
2015 209,572 18,273 174,163 15,501 Mark-resight
2016 154,381 13,140 171,468 15,031 Mark-resight
2017 164,036 17,991 175,996 16,636 Mark-resight
2018 169,665 14,566 162,694 15,368 Mark-resight
2019 193,086 25,627 175,596 19,938 Mark-resight
2020 122,042 12,053 161,598 18,386 Mark-resight
2021 173,830 16,117 162,986 18,813 Mark-resight
2022 232,462 28,354 176,111 20,075 Mark-resight
2023 186,439 33,124 197,577 26,838 Mark-resight
2024 160,855 22,858 193,252 28,423 Mark-resight
2025 204,576 38,341 183,957 32,092 Mark-resight

Figure 2: Aleutian cackling goose abundance in winter. Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The blue dashed reference line is the Pacific Flyway Council’s minimum population objective.
Time series statistics
Parameter Estimate SE L95%CI U95%CI
1-year index 204,576 38,341 129,428 279,724
3-year indexa 183,957 32,092 121,056 246,857
LTA 69,717
Objective 60,000
% change from LTA 193
% change from obj 241
Mgmt index (n years) 1
a 2023, 2024, 2025

Harvest Strategy
Management index: Total Aleutian cackling geese in winter.

Management thresholds: N/A.

Management prescription: N/A.

Regulatory alternatives:
Regulations fixed until changed.

Data Table 3: Cackling Goose, Cackling (minima)

Original data source: Yukon Kuskokwim Delta Coastal Zone Survey and USFWS Pacific Flyway Office coordinated mark-resight program; USFWS Alaska Region, Alaska, British Columbia, Washington, Oregon, and California. Data maintained by USFWS Alaska Region and USFWS Pacific Flyway Office.

Provided in the table below are abundance and standard error (SE) of cackling (minima) cackling geese from mark-resight methods (Markresight) in fall, Yukon Kuskokwim Delta Coastal Zone Survey in spring (Total), and projected fall (Fall) abundance from the spring estimate. Spring abundance is projected to fall abundance via a fixed correction factor (estimate = 3.4225, SE = 0.1616) for visibility bias. Also provided are the projected fall abundance moving 3-year average (M3yr) and standard error (M3yr.SE).

Table 3. Cackling (minima) cackling goose abundance in spring and fall, 1985-2025.
Year Markresight Total Total.SE Fall Fall.SE M3yr M3yr.SE
1985 NA 17,923 1,272 61,341 5,230 NA NA
1986 NA 15,892 987 54,389 4,244 NA NA
1987 NA 17,251 1,129 59,041 4,766 58,257 4,764
1988 NA 23,310 1,328 79,777 5,906 64,402 5,020
1989 92,062 24,360 1,302 83,370 5,946 74,062 5,566
1990 94,237 30,491 1,808 104,355 7,913 89,167 6,654
1991 148,628 28,488 1,628 97,500 7,230 95,075 7,077
1992 149,542 43,054 2,152 147,351 10,132 116,402 8,516
1993 184,844 44,144 1,960 151,080 9,794 131,977 9,144
1994 198,558 61,794 2,383 211,488 12,891 169,973 11,027
1995 202,969 67,115 2,838 229,698 14,559 197,422 12,571
1996 193,531 71,906 3,606 246,094 16,953 229,093 14,895
1997 256,715 83,797 3,257 286,793 17,538 254,195 16,401
1998 215,644 60,633 2,954 207,515 14,080 246,801 16,261
1999 306,065 67,081 3,216 229,582 15,449 241,297 15,753
2000 273,108 70,341 2,997 240,739 15,310 225,945 14,959
2001 206,249 73,931 3,484 253,026 16,882 241,115 15,896
2002 177,794 47,306 2,024 161,904 10,317 218,556 14,443
2003 251,594 68,492 3,206 234,412 15,588 216,447 14,542
2004 NA 50,578 2,378 173,103 11,535 189,806 12,682
2005 NA 63,358 2,882 216,839 14,219 208,118 13,883
2006 NA 69,338 2,970 237,305 15,129 209,082 13,713
2007 NA 73,984 3,014 253,206 15,790 235,783 15,059
2008 NA 83,645 3,700 286,271 18,522 258,928 16,546
2009 NA 66,414 2,511 227,301 13,748 255,593 16,139
2010 NA 81,013 4,566 277,264 20,391 263,612 17,775
2011 242,467 52,965 1,920 181,272 10,789 228,612 15,505
2012 272,493 59,534 2,824 203,751 13,638 220,762 15,473
2013 259,323 91,708 5,056 313,867 22,788 232,963 16,550
2014 NA 81,963 4,364 280,515 19,967 266,045 19,183
2015 NA 104,290 5,507 356,928 25,288 317,104 22,785
2016 NA 94,028 3,656 321,805 19,682 319,750 21,799
2017 NA 82,113 3,296 281,029 17,415 319,921 21,057
2018 NA 58,083 2,550 198,788 12,817 267,207 16,882
2019 NA 58,606 2,644 200,576 13,099 226,798 14,596
2020 NA NA NA NA NA NA NA
2021 NA 58,049 2,811 198,671 13,438 199,345 13,120
2022 NA 67,146 3,328 229,805 15,735 209,684 14,139
2023 NA 44,961 2,272 153,877 10,644 194,118 13,434
2024 NA 36,258 1,677 124,093 8,202 169,258 11,946
2025 NA 36,339 1,712 124,369 8,297 134,113 9,118

Figure 3: Cackling (minima) cackling goose abundance in fall. Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The blue dashed reference line is the Pacific Flyway Council’s population objective. The red dashed reference lines represent threshold values in the harvest strategy decision and the red reference line is the closure threshold.
Time series statistics
Parameter Estimate SE L95%CI U95%CI
1-year index 124,369 8,297 108,107 140,631
3-year indexa 134,113 9,118 116,242 151,984
LTA 201,429
Objective 250,000
% change from LTA -38
% change from obj -46
Mgmt index (n years) 3
a 2023, 2024, 2025

Harvest Strategy
Management index: Minima cackling geese projected in fall.

Management thresholds:
>275,000 Liberal
≥225,000 Standard
≥80,000 Restrictive
Closed

Management prescription: Restrictive.

Regulatory alternatives:
Regulations fixed until changed.

After a closure and when the population increases above a 3-year average index of 110,000, limited hunting may be considered.

Data Table 4: Cackling Goose, Taverner’s

Original data source: Yukon Kuskokwim Delta Coastal Zone Survey, Waterfowl Breeding Population and Habitat Survey strata in Alaska (i.e., strata 9–11), and Arctic Coastal Plain Survey; USFWS Alaska Region. Data maintained by USFWS Alaska Region.

Provided in the table below are abundance and standard error (SE) of Taverner’s cackling geese in spring by survey and area including Yukon Kuskokwim Delta Coastal Zone Survey (YKDCZ), Waterfowl Breeding Population and Habitat Survey (WBPHS; strata 9–11), and Arctic Coastal Plain Survey (ACP). Also provided are the total (Total) abundance and total abundance moving 3-year average (M3yr) and standard error (M3yr.SE).

Table 4. Taverner's cackling goose abundance in spring, 1985-2025.
Year YKDCZ YKDCZ.SE WPBHS9 WPBHS9.SE WPBHS10 WPBHS10.SE WPBHS11 WPBHS11.SE ACP ACP.SE Total Total.SE M3yr M3yr.SE
1985 3,798 1,789 16,035 2,822 7,700 5,698 15,047 4,825 NA NA NA NA NA NA
1986 2,288 586 17,774 1,693 8,112 7,233 9,474 3,018 NA NA NA NA NA NA
1987 4,514 957 22,218 7,319 5,225 2,543 4,570 1,412 NA NA NA NA NA NA
1988 8,551 1,633 14,973 2,036 4,812 810 17,945 4,360 NA NA NA NA NA NA
1989 8,567 1,387 23,280 2,927 3,850 2,058 11,146 2,059 NA NA NA NA NA NA
1990 7,812 1,862 25,405 2,201 3,575 1,367 9,697 2,145 NA NA NA NA NA NA
1991 7,070 1,203 26,951 4,544 5,912 1,784 30,762 22,758 NA NA NA NA NA NA
1992 7,714 1,592 23,763 2,877 11,550 5,365 15,381 6,095 NA NA NA NA NA NA
1993 8,461 2,096 19,126 3,378 5,362 2,333 9,920 1,400 NA NA NA NA NA NA
1994 7,003 1,406 24,922 3,687 5,225 2,367 13,486 4,814 NA NA NA NA NA NA
1995 6,488 1,713 19,996 2,697 3,300 2,664 8,805 5,081 NA NA NA NA NA NA
1996 6,598 1,293 25,792 5,057 6,600 4,718 14,155 6,249 NA NA NA NA NA NA
1997 6,351 1,052 20,092 2,270 6,050 1,881 15,827 5,227 NA NA NA NA NA NA
1998 10,350 1,277 21,155 3,859 5,638 1,474 12,929 2,847 NA NA NA NA NA NA
1999 12,920 2,204 17,678 2,925 3,988 2,524 13,709 4,336 NA NA NA NA NA NA
2000 9,709 2,597 12,600 2,042 3,850 778 13,152 7,027 NA NA NA NA NA NA
2001 7,706 1,529 14,669 1,980 4,125 2,447 20,954 13,369 NA NA NA NA NA NA
2002 5,982 1,100 13,353 2,584 6,738 2,987 9,362 742 NA NA NA NA NA NA
2003 9,075 1,869 17,114 2,974 6,600 1,420 10,811 3,017 NA NA NA NA NA NA
2004 7,825 2,928 12,882 1,840 5,225 2,318 6,910 2,328 NA NA NA NA NA NA
2005 7,248 2,272 14,199 1,994 3,162 1,354 10,477 4,372 NA NA NA NA NA NA
2006 9,510 1,983 15,515 2,220 4,950 651 8,136 1,833 NA NA NA NA NA NA
2007 5,848 1,691 10,155 1,700 5,225 493 7,356 2,472 27,175 5,263 55,760 6,309 NA NA
2008 10,572 2,037 21,627 8,864 8,388 3,441 6,019 1,631 5,013 714 51,619 9,886 NA NA
2009 7,697 1,698 9,967 1,783 4,950 2,178 6,465 1,099 19,847 2,989 48,926 4,577 52,102 7,268
2010 9,135 2,112 18,148 1,145 5,500 2,069 7,802 2,090 16,345 3,052 56,930 4,872 52,492 6,890
2011 5,911 1,210 11,942 1,738 2,750 986 5,573 1,090 9,699 1,679 35,875 3,076 47,244 4,249
2012 9,069 3,598 9,967 2,128 4,675 1,042 7,914 1,143 14,670 2,788 46,295 5,258 46,367 4,503
2013 9,345 2,517 5,360 1,738 3,025 369 5,684 1,683 3,714 660 27,128 3,572 36,433 4,077
2014 13,148 4,921 6,488 2,923 8,662 3,655 6,910 1,094 7,312 1,153 42,521 6,975 38,648 5,448
2015 19,964 5,704 6,137 1,854 2,727 289 4,681 2,801 8,393 1,138 41,903 6,723 37,184 5,961
2016 8,042 2,095 12,224 3,506 6,875 1,605 6,688 2,729 16,537 2,325 50,366 5,667 44,930 6,480
2017 9,302 3,715 7,242 1,332 11,412 4,717 3,009 636 15,476 3,527 46,442 7,118 46,237 6,532
2018 15,633 4,949 6,958 2,966 7,700 1,506 4,458 1,851 9,865 1,584 44,615 6,442 47,141 6,436
2019 11,231 3,331 9,497 3,294 5,775 1,077 3,009 854 13,214 1,564 42,726 5,127 44,594 6,283
2020 NA NA NA NA NA NA NA NA NA NA NA NA NA NA
2021 21,782 8,676 5,642 1,236 5,133 2,567 3,790 1,379 NA NA NA NA NA NA
2022 11,695 4,586 9,027 3,532 2,750 986 4,012 1,216 18,746 2,671 46,230 6,565 44,524 6,079
2023 8,191 1,937 2,633 1,250 4,950 1,678 4,681 3,021 9,240 1,181 29,695 4,318 39,551 5,417
2024 6,596 2,156 5,266 1,125 6,600 3,082 4,377 1,815 15,453 2,264 38,293 4,882 38,073 5,341
2025 5,756 1,781 7,146 3,919 3,300 952 2,229 759 15,184 2,303 33,616 5,031 33,868 4,754

Figure 4: Taverner’s cackling goose abundance in spring. Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates.
Time series statistics
Parameter Estimate SE L95%CI U95%CI
1-year index 33,616 5,031 23,754 43,477
3-year indexa 33,868 4,754 24,551 43,185
LTA 44,083
Objective
% change from LTA -24
% change from obj
Mgmt index (n years) 1
a 2023, 2024, 2025

Harvest Strategy
Management index: Total Taverner’s cackling geese in spring.

Management thresholds: N/A.

Management prescription: N/A.

Regulatory alternatives:
Regulations fixed until changed.

Data Table 5: Canada Goose, Dusky

Original data source: Copper River Delta Survey and Middleton Island Survey; USFWS Alaska Region and Alaska Department of Fish and Game. Data maintained by USFWS Alaska Region, Alaska Department of Fish and Game, and USFWS Pacific Flyway Office.

Provided in the table below are abundance and standard error (SE) of dusky Canada geese in spring by social group including breeding, total, and flocked birds (Breeding, Total, Flocked). Also provided are the total birds on Middleton Island (Middleton). Breeding birds are expanded by a fixed correction factor (estimate = 3.3416, SE = 0.3244) for visibility bias, which are then added to the flocked and Middleton Island estimates to derive adjusted total (Adjtotal) dusky Canada geese. Additionally provided are the total abundance moving 3-year average (M3yr) and standard error (M3yr.SE).

Table 5. Dusky Canada goose abundance in spring, 1986-2025.
Year Breeding Breeding.SE Total Total.SE Flocked Flocked.SE Middleton Middleton.SE Adjtotal Adjtotal.SE M3yr M3yr.SE
1986 4,735 676 5,416 646 680 573 80 0 16,584 2,799 NA NA
1987 4,048 372 5,205 451 1,156 297 84 0 14,769 1,836 NA NA
1988 4,281 217 4,935 257 654 108 90 0 15,051 1,572 15,468 2,135
1989 4,389 249 6,582 464 2,194 312 75 0 16,934 1,680 15,584 1,699
1990 4,220 367 5,209 526 989 291 93 0 15,183 1,865 15,723 1,710
1991 2,739 266 3,620 322 881 168 249 0 10,283 1,270 14,133 1,624
1992 4,156 219 6,378 634 2,223 564 473 0 16,582 1,637 14,016 1,609
1993 3,715 195 6,004 370 2,289 357 473 0 15,176 1,416 14,014 1,449
1994 3,852 188 5,454 331 1,602 239 473 0 14,946 1,420 15,568 1,494
1995 3,364 127 3,709 170 346 67 473 0 12,059 1,174 14,060 1,342
1996 2,910 104 3,514 157 604 85 1,497 0 11,824 1,010 12,943 1,213
1997 3,386 99 4,126 152 740 101 1,168 0 13,222 1,152 12,368 1,114
1998 3,691 166 5,066 284 1,375 199 1,168 0 14,877 1,336 13,308 1,174
1999 2,649 118 3,091 152 442 72 1,168 0 10,462 949 12,854 1,156
2000 2,523 107 3,016 126 493 67 1,309 0 10,233 896 11,857 1,078
2001 2,859 119 3,249 137 390 63 1,309 0 11,252 1,012 10,649 954
2002 3,152 126 4,058 204 906 137 1,416 0 12,856 1,115 11,447 1,012
2003 2,321 92 3,254 167 932 110 1,416 0 10,105 822 11,404 991
2004 2,822 128 3,243 158 420 69 1,499 0 11,350 1,013 11,437 991
2005 4,199 276 5,582 444 1,382 251 1,499 0 16,914 1,666 12,790 1,222
2006 2,771 135 3,198 155 427 87 1,453 0 11,139 1,010 13,134 1,268
2007 2,557 117 2,991 141 434 53 1,453 0 10,431 919 12,828 1,244
2008 2,333 104 2,617 115 285 43 1,317 0 9,396 834 10,322 924
2009 1,555 73 1,819 121 264 82 1,317 0 6,778 566 8,869 788
2010 2,316 95 2,703 134 387 67 1,249 0 9,374 818 8,516 750
2011 2,846 139 3,684 242 838 140 1,249 0 11,597 1,044 9,250 833
2012 3,338 150 3,913 203 575 81 1,193 0 12,922 1,197 11,298 1,031
2013 NA NA NA NA NA NA NA NA NA NA NA NA
2014 3,522 197 4,551 258 1,029 147 1,780 0 14,579 1,329 13,032 1,195
2015 4,230 220 6,096 429 1,866 334 2,112 223 18,113 1,610 15,204 1,389
2016 3,516 236 4,087 282 570 111 3,536 449 15,856 1,464 16,182 1,472
2017 3,014 186 3,579 234 565 164 2,288 308 12,924 1,211 15,631 1,438
2018 2,299 118 3,234 225 935 178 3,414 510 12,030 1,003 13,603 1,240
2019 3,304 253 6,905 2,028 3,601 1,999 3,414 510 18,055 2,476 14,336 1,693
2020 NA NA NA NA NA NA NA NA NA NA NA NA
2021 2,902 152 3,353 191 451 71 1,913 365 12,060 1,134 14,049 1,675
2022 2,870 149 3,712 234 842 140 1,913 365 12,346 1,127 14,154 1,701
2023 2,167 142 2,974 251 807 182 1,570 116 9,618 876 11,341 1,052
2024 1,764 101 2,448 195 684 126 1,570 116 8,150 688 10,038 915
2025 2,664 161 3,985 270 1,321 207 1,574 128 11,797 1,048 9,855 883

Figure 5: Dusky Canada goose abundance in spring. Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The blue dashed reference line is the Pacific Flyway Council’s population objective. The red dashed reference line is a restriction threshold in the harvest strategy decision and the red reference line is the severe restriction threshold.
Time series statistics
Parameter Estimate SE L95%CI U95%CI
1-year index 11,797 1,048 9,743 13,852
3-year indexa 9,855 883 8,125 11,585
LTA 12,866
Objective 20,000
% change from LTA -8
% change from obj -51
Mgmt index (n years) 3
a 2023, 2024, 2025

Harvest Strategy
Management index: Total dusky Canada geese in spring.

Management thresholds:
≥7,500 Standard
≥5,000 Restrictive
Very Restrictive

Management prescription: Standard.

Note that the Very Restrictive alternative is prescribed if the dusky Canada goose index is less than 5,000 geese in any year.

Regulatory alternatives:
Oregon and Washington Permit Zones
Standard
Closed season for dusky Canada geese
Restrictive
Additional restrictions, including the closure of all Canada goose hunting, will be considered
Very Restrictive
Oregon and Washington will implement regulations to ensure the hunting of Canada and cackling geese occurs only on or over agricultural fields or pastures with crops or forage that may be damaged by geese. Standard seasons for harvest of Canada and cackling geese other than dusky Canada geese in the permit zones may resume when the dusky Canada goose population (based on the 3-year average index) exceeds 10,000 geese

Alaska (GMU 6A-6D)
Standard
4 dusky Canada geese daily bag limit
Restrictive
2 dusky Canada geese daily bag limit
Very Restrictive
Closed season for dusky Canada geese, open to other Canada geese by permit only

Data Table 6: Canada Goose, Lesser

Original data source: Waterfowl Breeding Population and Habitat Survey (WBPHS) strata in Alaska (i.e., strata 1–4, 12); USFWS Alaska Region. Data maintained by USFWS Alaska Region.

Provided in the table below are abundance and standard error (SE) of lesser Canada geese in spring by area (WBPHS strata 1-4, 12) and in total. Also provided are the total abundance moving 3-year average (M3yr) and standard error (M3yr.SE).

Table 6. Lesser Canada goose abundance in spring, 1964-2025.
Year WPBHS1 WPBHS1.SE WPBHS2 WPBHS2.SE WPBHS3 WPBHS3.SE WPBHS4 WPBHS4.SE WPBHS12 WPBHS12.SE Total Total.SE M3yr M3yr.SE
1964 110 120 150 142 0 0 1,929 1,655 125 107 2,314 1,669 NA NA
1965 1,100 682 0 0 352 364 1,234 840 0 0 2,687 1,142 NA NA
1966 0 0 0 0 141 136 284 265 0 0 425 298 1,808 1,180
1967 3,740 3,038 450 426 2,159 1,135 7,020 3,168 109 103 13,478 4,555 5,530 2,716
1968 385 422 0 0 775 363 8,370 4,826 438 284 9,968 4,866 7,957 3,852
1969 3,410 3,735 0 0 705 345 3,645 1,593 0 0 7,760 4,076 10,402 4,510
1970 2,805 2,748 0 0 705 393 8,505 4,209 657 620 12,671 5,080 10,133 4,694
1971 220 241 0 0 2,466 1,003 5,400 3,166 109 103 8,195 3,331 9,542 4,224
1972 0 0 0 0 705 393 2,700 1,180 0 0 3,405 1,243 8,090 3,580
1973 220 216 0 0 1,832 500 4,050 1,097 274 258 6,375 1,252 5,992 2,176
1974 330 162 150 142 14,655 14,539 5,940 1,642 109 103 21,184 14,633 10,321 8,510
1975 0 0 0 0 986 543 4,590 995 1,368 1,291 6,944 1,718 11,501 8,537
1976 0 0 0 0 1,127 437 1,755 625 109 103 2,992 769 10,373 8,518
1977 770 488 150 142 1,057 394 1,890 815 821 775 4,688 1,295 4,875 1,319
1978 0 0 0 0 1,832 653 4,995 2,124 109 103 6,936 2,224 4,872 1,551
1979 110 108 0 0 1,620 678 4,590 1,693 219 82 6,539 1,829 6,054 1,823
1980 0 0 450 464 1,691 539 10,530 3,173 219 207 12,890 3,258 8,788 2,511
1981 330 235 375 255 2,677 1,001 13,770 3,564 1,259 1,017 18,411 3,855 12,613 3,099
1982 1,210 1,056 150 155 1,550 666 9,990 4,167 3,119 2,685 16,019 5,114 15,773 4,149
1983 220 216 0 0 1,550 883 1,620 548 0 0 3,390 1,062 12,607 3,748
1984 990 970 2,325 2,199 1,127 371 9,180 3,538 219 207 13,841 4,298 11,083 3,905
1985 385 377 0 0 705 432 7,830 3,152 657 620 9,576 3,263 8,936 3,175
1986 1,430 1,401 150 142 775 671 4,320 2,114 0 0 6,675 2,627 10,031 3,465
1987 220 216 150 142 705 253 2,970 1,070 547 516 4,592 1,242 6,948 2,523
1988 440 332 525 496 986 400 3,780 750 1,040 981 6,771 1,429 6,013 1,870
1989 715 701 0 0 423 221 5,940 2,012 0 0 7,078 2,142 6,147 1,651
1990 770 754 750 774 2,748 1,721 7,290 3,229 109 103 11,667 3,817 8,505 2,658
1991 495 485 2,175 1,726 1,409 568 0 0 219 125 4,298 1,885 7,681 2,751
1992 4,290 4,203 0 0 845 503 2,565 1,137 1,423 1,196 9,123 4,544 8,363 3,595
1993 495 485 150 155 282 200 4,860 1,379 109 103 5,896 1,487 6,439 2,967
1994 1,925 1,886 150 142 2,889 2,447 10,530 3,761 1,204 698 16,698 4,919 10,572 3,960
1995 715 592 675 541 705 345 7,020 2,669 438 342 9,552 2,829 10,715 3,387
1996 1,100 1,078 300 195 1,339 681 4,725 2,116 219 207 7,683 2,487 11,311 3,577
1997 715 575 300 195 564 266 2,970 783 438 251 4,986 1,056 7,407 2,258
1998 880 862 0 0 141 141 4,590 1,636 109 103 5,720 1,857 6,130 1,893
1999 110 108 2,175 1,919 141 145 2,295 953 930 380 5,651 2,183 5,453 1,764
2000 3,960 3,761 375 255 493 262 3,240 1,791 1,204 811 9,272 4,259 6,881 2,964
2001 110 93 0 0 1,033 452 4,590 1,822 328 155 6,062 1,886 6,995 2,970
2002 990 847 600 320 1,127 472 1,890 780 328 226 4,936 1,305 6,756 2,793
2003 110 108 150 142 352 254 5,265 2,150 383 216 6,260 2,183 5,753 1,828
2004 440 431 600 619 916 336 3,915 1,681 438 95 6,309 1,876 5,835 1,824
2005 314 328 0 0 282 187 3,645 1,356 602 245 4,843 1,428 5,804 1,855
2006 330 132 0 0 634 388 2,700 772 547 41 4,211 875 5,121 1,452
2007 0 0 375 387 986 692 2,970 1,457 5,199 3,660 9,530 4,018 6,195 2,513
2008 1,650 1,617 0 0 423 221 7,200 3,400 985 665 10,258 3,830 8,000 3,244
2009 605 593 0 0 564 329 4,455 1,941 766 287 6,390 2,076 8,726 3,422
2010 0 0 450 285 581 239 4,860 1,730 930 878 6,822 1,975 7,823 2,761
2011 0 0 150 142 423 221 1,080 695 1,915 1,808 3,568 1,954 5,593 2,002
2012 1,344 954 0 0 1,127 876 1,350 875 0 0 3,822 1,563 4,737 1,841
2013 NA NA NA NA NA NA NA NA NA NA NA NA NA NA
2014 122 131 0 0 436 323 540 380 1,751 657 2,849 835 3,413 1,523
2015 183 173 0 0 141 136 7,020 5,629 1,259 300 8,603 5,641 5,091 3,414
2016 0 0 600 567 986 606 2,160 465 657 452 4,403 1,054 5,285 3,348
2017 244 230 0 0 1,350 665 1,080 718 1,368 1,291 4,043 1,636 5,683 3,445
2018 0 0 0 0 0 0 1,080 541 930 422 2,010 686 3,485 1,191
2019 122 115 0 0 564 329 11,340 6,988 1,040 811 13,066 7,043 6,373 4,194
2020 NA NA NA NA NA NA NA NA NA NA NA NA NA NA
2021 NA NA NA NA NA NA NA NA NA NA NA NA NA NA
2022 122 115 0 0 282 291 4,590 4,301 0 0 4,994 4,313 6,690 4,785
2023 NA NA NA NA NA NA NA NA NA NA NA NA NA NA
2024 122 115 0 0 0 0 2,571 1,645 0 0 2,694 1,649 6,918 4,862
2025 367 346 0 0 291 291 9,720 4,130 547 516 10,925 4,187 6,204 3,598

Figure 6: Lesser Canada goose abundance in spring. Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates.
Time series statistics
Parameter Estimate SE L95%CI U95%CI
1-year index 10,925 4,187 2,719 19,130
3-year indexa 6,204 3,598 -849 13,257
LTA 7,404
Objective
% change from LTA 48
% change from obj
Mgmt index (n years) 1
a 2022, 2024, 2025

Harvest Strategy
Management index: Total lesser Canada geese in spring.

Management thresholds: N/A.

Management prescription: N/A.

Regulatory alternatives:
Regulations fixed until changed.

Data Table 7: Canada Goose, Western PFP

Original data source: Waterfowl Breeding Population and Habitat Survey (WBPHS) strata in Alberta and Montana (i.e., strata 76, and portions of strata 26–29 and 41–42); and State/Provincial Waterfowl Breeding Population Surveys in British Columbia, eastern Washington, eastern Oregon, and northeast California; USFWS Headquarters, British Columbia, Washington, Oregon, and California. Data maintained by USFWS Headquarters, Canadian Wildlife Service Pacific and Yukon Region, Washington, Oregon, California, and USFWS Pacific Flyway Office.

Provided in the table below are abundance and standard error(SE) of Pacific Flyway Population western Canada geese by survey (WBPHS in Alberta and Montana, and state/provincial surveys in British Columbia, Washington, Oregon, California) and in total for the State survey areas (State) and for all surveys combined (Total) in spring. Also provided are the total abundance moving 3-year average (M3yr) and standard error (M3yr.SE).

Table 7. Pacific Flyway Population western Canada goose abundance in spring, 2010-2025.
Year WBPHS WBPHS.SE BC BC.SE WA WA.SE OR OR.SE CA CA.SE State State.SE Total Total.SE M3yr M3yr.SE
2010 162,421 23,611 33,296 4,154 18,696 4,353 31,642 4,416 33,155 8,178 116,789 33,985 279,210 41,382 NA NA
2011 128,327 17,146 33,566 4,507 31,176 7,258 38,062 5,349 36,476 14,552 139,280 37,843 267,607 41,546 NA NA
2012 184,960 22,519 35,787 4,834 29,308 5,925 40,920 5,699 42,181 14,288 148,197 43,246 333,157 48,758 293,325 44,030
2013 200,545 20,814 34,370 4,812 26,577 7,789 37,107 4,109 68,248 20,484 166,302 68,982 366,848 72,054 322,537 55,663
2014 146,746 15,934 34,120 3,863 38,832 8,779 39,671 5,068 31,209 14,497 143,831 33,040 290,577 36,682 330,194 54,512
2015 234,091 28,564 35,285 3,359 33,347 8,121 43,167 6,690 44,322 16,368 156,121 45,678 390,212 53,873 349,212 56,094
2016 319,990 34,525 39,980 5,200 24,678 6,375 40,968 6,851 44,323 11,234 149,949 45,597 469,939 57,193 383,576 50,063
2017 240,038 26,345 39,359 5,106 27,461 5,331 40,801 7,648 55,224 20,731 162,846 56,238 402,884 62,103 421,012 57,822
2018 316,119 38,653 34,646 3,532 36,662 8,491 49,646 9,647 52,121 14,984 173,076 53,798 489,195 66,244 454,006 61,957
2019 237,515 28,542 31,737 3,945 43,749 9,974 41,679 7,379 48,588 14,417 165,752 50,302 403,267 57,835 431,782 62,156
2020 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
2021 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
2022 328,298 36,271 26,213 3,314 31,808 8,827 37,622 4,684 46,359 10,039 142,001 47,540 470,299 59,796 454,254 61,397
2023 259,223 27,356 20,698 2,212 24,570 6,360 22,189 3,668 60,353 14,900 127,809 60,838 387,032 66,705 420,200 61,563
2024 214,602 33,290 20,795 2,084 22,756 4,342 27,875 4,065 34,242 10,048 105,668 34,817 320,270 48,171 392,534 58,724
2025 276,178 31,282 28,887 2,694 28,746 7,158 29,505 4,520 62,034 17,442 149,172 62,667 425,350 70,041 377,551 62,385

Figure 7: Pacific Flyway Population western Canada goose abundance in spring. Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The blue dashed reference line is the Councils’ minimum population objective.
Time series statistics
Parameter Estimate SE L95%CI U95%CI
1-year index 425,350 70,041 288,070 562,629
3-year indexa 377,551 62,385 255,276 499,825
LTA 374,654
Objective 200,000
% change from LTA 14
% change from obj 89
Mgmt index (n years) 3
a 2023, 2024, 2025

Harvest Strategy
Management index: Total western Canada geese in spring.

Management thresholds: N/A.

Management prescription: N/A.

Regulatory alternatives:
Regulations fixed until changed.

Data Table 8: Emperor Goose

Original data source: Yukon Kuskokwim Delta Coastal Zone Survey; USFWS Alaska Region. Data maintained by USFWS Alaska Region.

Provided in the table below are abundance and standard error (SE) of emperor geese in spring. Also provided are the abundance moving 3-year average (M3yr) and standard error (M3yr.SE).

Table 8. Emperor goose abundance in spring, 1985-2025.
Year Total Total.SE M3yr M3yr.SE
1985 19,253 1,392 NA NA
1986 11,580 865 NA NA
1987 10,625 1,003 13,819 1,109
1988 13,066 1,022 11,757 966
1989 14,203 1,029 12,631 1,018
1990 14,645 1,083 13,971 1,045
1991 12,464 1,089 13,771 1,067
1992 12,927 818 13,345 1,005
1993 15,522 1,105 13,638 1,013
1994 16,842 934 15,097 959
1995 17,729 1,105 16,698 1,051
1996 23,885 2,431 19,485 1,633
1997 22,446 1,453 21,353 1,755
1998 20,047 980 22,126 1,731
1999 19,651 1,337 20,715 1,273
2000 16,632 877 18,777 1,083
2001 26,338 1,384 20,874 1,221
2002 18,726 1,132 20,565 1,150
2003 20,588 1,548 21,884 1,365
2004 20,986 1,068 20,100 1,267
2005 20,550 1,291 20,708 1,317
2006 24,997 1,534 22,178 1,311
2007 25,126 1,648 23,558 1,498
2008 21,811 1,095 23,978 1,445
2009 20,287 1,175 22,408 1,329
2010 19,760 1,072 20,619 1,115
2011 20,659 1,184 20,235 1,145
2012 20,159 1,647 20,193 1,325
2013 29,390 2,171 23,403 1,715
2014 30,685 2,763 26,745 2,241
2015 27,767 1,694 29,281 2,252
2016 33,277 2,384 30,576 2,323
2017 29,145 1,684 30,063 1,949
2018 29,509 1,680 30,644 1,945
2019 25,790 1,472 28,148 1,615
2020 NA NA NA NA
2021 23,297 1,200 26,199 1,464
2022 27,977 1,488 25,688 1,393
2023 23,357 1,480 24,877 1,396
2024 17,223 1,040 22,852 1,352
2025 22,180 1,168 20,920 1,243

Figure 8: Emperor goose abundance in spring. Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The blue dashed reference line is the Pacific Flyway Council’s population objective. The red dashed reference line is the threshold where restrictions are considered and the red reference line is the closure threshold.
Time series statistics
Parameter Estimate SE L95%CI U95%CI
1-year index 22,180 1,168 19,890 24,470
3-year indexa 20,920 1,243 18,483 23,357
LTA 20,998
Objective 34,000
% change from LTA 6
% change from obj -35
Mgmt index (n years) 1
a 2023, 2024, 2025

Harvest Strategy
Management index: Total emperor geese in spring.

Management thresholds:
≥28,000 Standard
≥23,000 Consider Restrictions
Closed

Management prescription: Closed.

Regulatory alternatives:
Standard
Quota of 1,000 birds
Consider Restrictions
Restrictions considered including quota of 500 birds
Closed

Data Table 9: Ross’s Goose

Original data source: Lincoln (harvest/harvest rate) estimates of adult abundance in summer; USFWS Headquarters. Data maintained by USFWS Headquarters.

Provided in the table below are adult abundance (Estimate) and standard error (SE) of Ross’s geese in summer. Also provided are the abundance moving 3-year average (M3yr) and standard error (M3yr.SE).

Table 9. Ross's goose abundance in summer, 1989-2023.
Year Estimate SE M3yr M3yr.SE
1989 122,967 75,859 122,967 76,796
1990 260,543 161,660 191,755 88,982
1991 184,576 114,119 189,362 70,645
1992 91,489 56,582 178,869 68,008
1993 NA NA 138,032 63,634
1994 111,532 44,589 101,510 36,425
1995 436,216 271,326 273,874 136,767
1996 NA NA 273,874 136,767
1997 391,660 98,868 413,938 143,224
1998 740,682 149,628 566,171 89,541
1999 708,306 138,152 613,549 75,358
2000 1,167,070 246,388 872,019 107,950
2001 1,642,862 404,123 1,172,746 165,028
2002 1,818,419 288,162 1,542,784 187,072
2003 1,133,114 189,555 1,531,465 178,101
2004 1,658,615 235,288 1,536,716 140,171
2005 1,385,010 171,256 1,392,246 118,050
2006 1,403,605 156,848 1,482,410 112,526
2007 2,586,016 333,733 1,791,543 136,295
2008 3,072,466 400,035 2,354,029 181,439
2009 1,946,855 317,704 2,535,112 203,712
2010 3,097,982 428,789 2,705,768 223,653
2011 2,653,779 351,631 2,566,206 216,019
2012 3,090,652 421,429 2,947,471 232,573
2013 3,735,736 486,685 3,160,056 241,654
2014 5,891,908 813,300 4,239,432 346,925
2015 1,907,986 223,189 3,845,210 326,445
2016 3,073,936 346,549 3,624,610 303,531
2017 2,638,395 389,028 2,540,106 187,891
2018 2,926,479 539,289 2,879,603 249,721
2019 2,537,495 339,399 2,700,790 248,084
2020 NA NA 2,731,987 320,775
2021 NA NA 2,537,495 339,234
2022 1,076,130 167,045 1,076,130 165,723
2023 3,409,133 474,160 2,242,631 251,201

Figure 9: Ross’s goose abundance in summer. Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The blue dashed reference line is the Pacific Flyway Council’s minimum population objective.
Time series statistics
Parameter Estimate SE L95%CI U95%CI
1-year index 3,409,133 474,160 2,479,779 4,338,487
3-year indexa 2,242,631 251,201 1,750,278 2,734,985
LTA 1,783,083
Objective 150,000
% change from LTA 91
% change from obj 2,173
Mgmt index (n years) 1
a 2021, 2022, 2023

Harvest Strategy
Management index: Adult Ross’s geese in summer.

Management thresholds:
≥100,000 Standard
Restrictive

Management prescription: Standard.

Regulatory alternatives:
Regulations fixed until changed.

Data Table 10: Snow Goose, WIP and WAP

Original data source: Pacific Flyway Cooperative Light Goose Winter Survey; Washington, Oregon, and California. Data maintained by Washington, Oregon, and California.

Provided in the table below are abundance of Wrangel Island Population and Western Arctic Population lesser snow geese by area including Skagit-Fraser River Deltas in Washington and British Columbia (Sk-Fr), Oregon-Washington Columbia River east (ColR.E), Oregon-Washington Columbia River west (ColR.W), balance of Oregon (OR), California (CA), and in total (Total). In California, the percentage of the white geese count that are Ross’s geese (CARoss%) are recorded periodically and is modeled to estimate the percentage of Ross’s geese smoothed over all years (CARossAdj%). The number of lesser snow geese in California (CASnow) is derived by subtracting the percentage of the white goose count that are Ross’s geese and is the metric used to monitor abundance of Western Arctic Population lesser snow geese in winter. In the Skagit-Fraser area, the percentage of the lesser snow goose count that are juveniles (Juv%) is reported and used to derive the number of adult snow geese in the Skagit-Fraser count (AdultSk). Adult snow geese is the metric used to monitor abundance of Wrangel Island Population lesser snow geese in winter. Also provided are moving 3-year averages for snow geese in California (M3yrCA) and adult snow geese in the Skagit-Fraser (M3yrSk). So long as there are counts in Sakgit-Fraser and California, the total winter count is interpreted as the minimum known population size with no variance.

Table 10. Wrangel Island Population and Western Arctic Population lesser snow geese in winter, 1979-2024.
Year Sk-Fr ColR.E ColR.W OR CA Total CARoss% CARossAdj% CASnow M3yrCA Juv% AdultSk M3yrSk
1979 35,600 NA NA NA 492,500 528,100 NA 36.3 313,674 NA NA NA NA
1980 22,400 NA NA NA 181,800 204,200 NA 37.0 114,500 NA 19.0 18,144 NA
1981 48,600 NA NA NA 711,300 759,900 NA 37.7 443,388 290,521 NA NA NA
1982 26,100 NA NA NA 328,000 354,100 NA 38.2 202,542 253,477 5.8 24,586 NA
1983 24,500 NA NA NA 523,100 547,600 NA 38.8 320,287 322,072 0.0 24,500 22,410
1984 26,600 NA NA NA 439,700 466,300 NA 39.2 267,201 263,344 12.6 23,248 24,112
1985 46,200 NA NA NA 503,600 549,800 NA 39.6 304,032 297,173 24.0 35,112 27,620
1986 39,900 NA NA NA 481,800 521,700 NA 40.0 289,256 286,830 25.0 29,925 29,428
1987 47,700 NA NA NA 477,600 525,300 NA 40.2 285,432 292,906 40.0 28,620 31,219
1988 43,800 NA NA NA 397,200 441,000 NA 40.4 236,545 270,411 NA NA NA
1989 32,200 NA NA NA 431,700 463,900 41.9 40.6 256,451 259,476 NA NA NA
1990 31,700 NA NA NA 676,800 708,500 43.6 40.7 401,471 298,156 NA NA NA
1991 39,100 NA NA NA 651,000 690,100 NA 40.7 386,012 347,978 28.6 27,917 28,821
1992 34,300 NA NA NA 605,000 639,300 36.9 40.7 358,970 382,151 NA NA NA
1993 49,100 NA NA NA 520,100 569,200 NA 40.6 309,120 351,367 NA NA NA
1994 42,600 NA NA NA 435,600 478,200 NA 40.4 259,608 309,232 8.5 38,979 31,839
1995 37,000 NA NA NA 464,400 501,400 NA 40.2 277,819 282,182 5.4 35,002 33,966
1996 45,800 NA NA NA 320,500 366,300 NA 39.9 192,656 243,361 NA NA NA
1997 47,000 NA NA NA 369,400 416,400 NA 39.5 223,343 231,272 16.2 39,386 37,789
1998 47,100 NA NA NA 307,200 354,300 NA 39.1 187,002 201,000 13.2 40,883 38,424
1999 28,600 NA NA NA 550,400 579,000 NA 38.7 337,658 249,334 15.6 24,138 34,802
2000 56,300 NA NA NA 600,500 656,800 38.4 38.1 371,617 298,759 20.3 44,871 36,631
2001 52,000 NA NA NA 396,200 448,200 NA 37.5 247,560 318,945 21.1 41,028 36,679
2002 73,100 NA NA NA 523,700 596,800 NA 36.9 330,690 316,622 26.7 53,582 46,494
2003 66,800 NA NA NA 521,000 587,800 NA 36.1 332,756 303,669 12.8 58,250 50,953
2004 68,141 NA NA NA 682,128 750,269 NA 35.3 441,027 368,158 15.3 57,715 56,516
2005 80,040 NA NA NA 630,686 710,726 34.8 34.5 413,117 395,633 32.7 53,867 56,611
2006 83,148 NA NA NA 719,810 802,958 NA 33.6 478,050 444,065 21.2 65,521 59,034
2007 94,856 NA NA NA 978,622 1,073,478 NA 32.6 659,455 516,874 21.8 74,177 64,522
2008 NA NA NA NA 900,403 NA 31.3 31.6 616,066 584,524 NA NA NA
2009 78,989 NA NA NA 827,055 906,044 NA 30.5 574,956 616,826 40.0 47,393 62,364
2010 63,641 NA NA NA 800,156 863,797 NA 29.3 565,535 585,519 4.4 60,841 60,804
2011 69,964 NA NA NA 1,027,887 1,097,851 25.6 28.1 739,051 626,514 20.6 55,551 54,595
2012 67,198 NA NA NA 824,432 891,630 NA 26.8 603,354 635,980 18.6 54,699 57,030
2013 69,685 NA NA NA 1,275,890 1,345,575 NA 25.5 950,929 764,445 23.8 53,100 54,450
2014 66,501 NA NA NA 1,141,579 1,208,080 31.9 24.1 866,908 807,064 8.5 60,835 56,211
2015 81,195 7,930 11,892 44 NA NA NA 22.6 NA NA 26.8 59,435 57,790
2016 103,617 15,447 14,215 16 1,773,493 1,906,788 NA 21.1 1,400,062 1,072,633 33.4 69,009 63,093
2017 86,553 33,274 18,080 0 1,217,295 1,355,202 11.5 19.5 980,401 1,082,457 15.4 73,224 67,222
2018 109,993 52,841 18,241 26 1,232,663 1,413,764 NA 17.8 1,013,214 1,131,226 20.6 87,334 76,522
2019 NA 160,825 24,394 30 1,414,392 NA NA 16.1 1,186,920 1,060,178 NA NA NA
2020 133,306 153,690 NA NA NA NA NA 14.3 NA NA 30.0 93,314 84,624
2021 120,725 119,771 35,748 276 NA NA NA 12.5 NA NA 16.1 101,288 93,979
2022 91,608 64,745 19,445 2 1,093,828 1,269,628 17.1 10.5 978,445 1,059,526 4.6 87,394 93,999
2023 66,355 162,586 17,171 25 1,238,593 1,484,730 NA 8.6 1,132,330 1,099,232 NA NA NA
2024 NA 136,897 15,204 3,203 1,077,086 NA NA 6.5 1,006,561 1,039,112 NA NA NA

Figure 10: Western Arctic Population lesser snow goose abundance in winter in California. Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The blue dashed reference line is the Pacific Flyway Council’s minimum population objective.
Time series statistics
Parameter Estimate SE L95%CI U95%CI
1-year index 1,006,561
3-year indexa 1,039,112
LTA 496,415
Objective 300,000
% change from LTA 103
% change from obj 246
Mgmt index (n years) 3
a 2022, 2023, 2024

Harvest Strategy
Western Arctic Population of Lesser Snow Geese

Management index: Total lesser snow geese in winter in California.

Management thresholds:
≥300,000 Standard Restrictive

Management prescription: Standard.

Regulatory alternatives:
Regulations fixed until changed.

Figure 11: Wrangel Island Population lesser snow goose adult abundance in winter in Skagit-Fraser River Delta areas. Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The blue dashed reference line is the Pacific Flyway Council’s minimum population objective.
Time series statistics
Parameter Estimate SE L95%CI U95%CI
1-year index 87,394
3-year indexa 93,999
LTA 50,166
Objective 70,000
% change from LTA 74
% change from obj 34
Mgmt index (n years) 3
a 2020, 2021, 2022

Wrangel Island Population of Lesser Snow Geese

Management index: Total adult lesser snow geese in winter in Skagit-Fraser River Delta areas.

Management thresholds:
≥70,000 Standard
Restrictive

Management prescription: NA.

Regulatory alternatives:
Regulations fixed until changed.

Data Table 11: White-fronted Goose, MP

Original data source: Lincoln (harvest/harvest rate) estimates of adult abundance in summer and adult harvest rate; USFWS Headquarters. Data maintained by USFWS Headquarters.

Provided in the table below are adult abundance (N) and standard error (N.SE) of Midcontinent Population white-fronted geese in summer and harvest rate (h) and standard error (h.SE). Also provided are the moving 3-year average abundance (N.M3yr) and harvest rate (h.M3yr) and associated standard errors (N.M3yr.SE and h.M3yr.SE).

Table 11. Midcontinent Population white-fronted goose adult abundance in summer and harvest rate, 1976-2024. Note that moving 3-year averages are calculated as the most recent three years regardless of missing data so long as there are at least 2 years of data.
Year N N.SE N.M3yr N.M3yr.SE hrate hrate.SE h.M3yr h.M3yr.SE
1976 399,195 66,443 NA NA 0.096 0.015 NA NA
1977 524,380 91,402 NA NA 0.090 0.015 NA NA
1978 519,507 76,873 481,028 45,693 0.109 0.014 0.098 0.008
1979 563,147 83,512 535,678 47,999 0.090 0.012 0.096 0.008
1980 NA NA 541,327 56,429 NA NA 0.099 0.009
1981 NA NA 563,147 83,398 NA NA 0.090 0.012
1982 NA NA NA NA NA NA NA NA
1983 NA NA NA NA NA NA NA NA
1984 NA NA NA NA NA NA NA NA
1985 NA NA NA NA NA NA NA NA
1986 777,215 362,356 777,215 369,101 0.058 0.034 0.058 0.034
1987 933,857 256,517 855,536 223,489 0.051 0.014 0.055 0.018
1988 1,291,574 358,819 1,000,882 190,626 0.038 0.011 0.049 0.013
1989 1,665,397 495,742 1,296,943 220,419 0.039 0.012 0.043 0.007
1990 3,246,087 870,907 2,067,686 354,519 0.023 0.006 0.033 0.006
1991 2,334,895 787,297 2,415,460 430,746 0.029 0.010 0.030 0.006
1992 1,033,830 200,690 2,204,937 405,170 0.068 0.012 0.040 0.006
1993 1,644,665 503,783 1,671,130 325,404 0.031 0.010 0.043 0.006
1994 2,026,828 465,967 1,568,441 239,580 0.040 0.009 0.047 0.006
1995 1,483,184 313,371 1,718,226 252,733 0.044 0.009 0.039 0.005
1996 1,769,749 376,424 1,759,920 229,307 0.054 0.011 0.046 0.006
1997 1,792,679 258,978 1,681,871 189,040 0.065 0.008 0.054 0.005
1998 2,240,477 381,031 1,934,302 201,373 0.043 0.007 0.054 0.005
1999 1,560,488 190,607 1,864,548 166,108 0.068 0.007 0.058 0.004
2000 2,669,886 351,903 2,156,950 183,532 0.056 0.006 0.056 0.004
2001 2,178,293 292,694 2,136,222 166,434 0.051 0.006 0.058 0.004
2002 2,872,882 450,864 2,573,687 216,679 0.035 0.005 0.047 0.003
2003 1,508,710 183,533 2,186,628 189,936 0.052 0.005 0.046 0.003
2004 1,884,996 225,501 2,088,863 176,849 0.043 0.004 0.043 0.003
2005 2,485,176 332,154 1,959,627 147,601 0.040 0.004 0.045 0.003
2006 3,009,015 419,688 2,459,729 195,573 0.030 0.003 0.037 0.002
2007 3,604,007 452,423 3,032,733 233,757 0.041 0.004 0.037 0.002
2008 3,702,986 478,901 3,438,670 259,141 0.032 0.003 0.034 0.002
2009 3,493,229 490,570 3,600,074 273,144 0.023 0.003 0.032 0.002
2010 2,917,507 381,870 3,371,241 260,245 0.035 0.004 0.030 0.002
2011 2,909,280 350,174 3,106,672 238,521 0.028 0.003 0.029 0.002
2012 2,723,369 311,246 2,850,052 200,520 0.036 0.003 0.033 0.002
2013 3,622,743 458,362 3,085,131 219,152 0.029 0.003 0.031 0.002
2014 3,765,799 527,504 3,370,637 256,895 0.034 0.004 0.033 0.002
2015 2,286,219 346,798 3,224,920 262,591 0.035 0.005 0.033 0.002
2016 3,006,259 394,816 3,019,426 248,350 0.043 0.004 0.037 0.003
2017 2,362,190 311,431 2,551,556 202,343 0.050 0.005 0.043 0.003
2018 2,803,648 377,088 2,724,032 206,038 0.038 0.004 0.044 0.003
2019 2,300,256 375,028 2,488,698 202,565 0.044 0.006 0.044 0.003
2020 NA NA 2,551,952 261,368 NA NA 0.041 0.004
2021 3,194,655 531,447 2,747,455 323,945 0.027 0.004 0.035 0.004
2022 1,278,379 172,583 2,236,517 277,603 0.054 0.006 0.040 0.004
2023 2,749,577 342,915 2,407,537 216,014 0.038 0.004 0.039 0.003
2024 NA NA NA NA 0.049 0.006 0.047 0.003

Figure 12: Midcontinent Population white-fronted goose abundance in summer. Circles are annual estimates of abundance with 95% and 70% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The blue dashed reference line is the Councils’ minimum population objective and the restriction threshold if abundance is below 1.2 million geese AND adult harvest rate is above 0.075. The red reference line is the closure threshold.
Time series statistics for abundace
Parameter Estimate SE L95%CI U95%CI
1-year index 2,749,577 342,915 2,077,464 3,421,689
3-year indexa 2,407,537 216,014 1,984,149 2,830,925
LTA 2,159,666
Objective 1,200,000
% change from LTA 27
% change from obj 101
Mgmt index (n years) 3
a 2021, 2022, 2023

Figure 13: Midcontinent Population white-fronted goose adult harvest rate. Circles are annual estimates of harvest rate with 95% and 70% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence intervals (shaded area) fit to the annual estimates. The red dashed reference line is the restriction threshold if abundance is below 1.2 million geese (minumum population objective) AND adult harvest rate is above 0.075.
Time series statistics for harvest rate
Parameter Estimate SE L95%CI U95%CI
1-year index 0.049 0.006 0.037 0.061
3-year indexa 0.047 0.003 0.040 0.053
LTA 0.047
Objective
% change from LTA 3.722
% change from obj
Mgmt index (n years) 3.000
a 2022, 2023, 2024

Harvest Strategy
Management index: Adult white-fronted geese in winter and harvest rate.

Management thresholds:
N≥1,200,000 or h≤7.5 Standard
N<1,200,000 and h>7.5 Restrictive
N<250,000 Closed

Management prescription: Standard.

Regulatory alternatives:
Only the alternatives for the Pacific Flyway are shown here, and specifically Alaska. See the management plan for other flyway and state specific alternatives.
Standard and Restrictive
Season length is 107 days, bracket dates September 1 and January 26, and the daily bag limit is 4 geese

Decision framework: The Management prescription is based on two state variables; abundance and harvest rate. The probability distribution of the most recent 3-year averages relative to threshold values is used in a decision-analysis framework for setting harvest regulations. Eighty five percent of the distribution (confidence in the parameter estimate) must be below or above critical thresholds to prescribe a specific regulatory alternative. The 85% distribution corresponds to a confidence interval (CI) of 70% for the parameter estimate. Thus, if the upper or lower 70% CI for the parameter falls below or above the critical threshold value, then >85% of the distribution is below or above the threshold. The season is closed when >85% of the distribution for the most recent 3-year average population size is below 250,000 geese. A restrictive regulatory alternative is prescribed when >85% of the distribution for the most recent 3-year average population size is below 1,200,000 geese AND >85% of the distribution for the most recent 3-year average harvest rate is above 7.5%. A standard regulatory alternative is prescribed when conditions are not meet for either the restrictive or closed season regulatory alternatives.

Data Table 12: White-fronted Goose, PP

Original data source: California Fall Survey of White-fronted Geese and Yukon Kuskokwim Coastal Zone Survey and Waterfowl Breeding Population and Habitat Survey (WBPHS; strata 8 (Bristol Bay) and 9 (YKD Inland); California and USFWS Alaska Region. Data maintained by California, USFWS Alaska Region, and USFWS Pacific Flyway Office.

Provided in the table below are abundance and standard error (SE) of Pacific Population white-fronted geese by survey and area including California Fall Survey (CAfall), and Yukon Kuskokwim Coastal Zone Survey (YKDCZ) and Waterfowl Breeding Population and Habitat Survey (WBPHS; strata 8 and 9). Also provided are the total for all spring survey areas (Spring). Total spring abundance is projected to fall abundance (PrjFall) via a fixed factor (estimated = 3.2334, SE = 0.1006) for visibility bias. Also provided are the projected fall abundance moving 3-year average (M3yr) and standard error (M3yr.SE).

Table 12. Pacific Population white-fronted goose abundance in spring, 1985-2025.
Year CAfall YKDCZ YKDCZ.SE WPBHS8 WPBHS8.SE WPBHS9 WPBHS9.SE Spring Spring.SE PrjFall PrjFall.SE M3yr M3yr.SE
1985 93,900 17,398 841 6,241 3,467 9,563 3,735 33,203 5,165 107,358 17,038 NA NA
1986 107,100 12,988 798 5,273 2,513 8,984 2,872 27,245 3,899 88,093 12,907 NA NA
1987 130,600 14,167 1,247 4,520 2,044 6,665 2,001 25,352 3,121 81,972 10,412 92,475 13,727
1988 124,690 23,459 1,388 4,842 1,358 12,365 2,100 40,666 2,860 131,490 10,117 100,519 11,215
1989 263,350 26,546 2,022 6,672 3,125 9,853 2,723 43,070 4,611 139,264 15,535 117,576 12,276
1990 237,050 36,096 3,315 2,475 903 14,973 2,577 53,544 4,295 173,129 14,901 147,961 13,732
1991 215,655 30,180 1,977 5,596 1,592 11,205 2,604 46,981 3,637 151,910 12,679 154,768 14,424
1992 230,675 32,494 2,140 8,716 4,503 11,012 1,608 52,223 5,238 168,857 17,741 164,632 15,249
1993 253,820 39,976 2,696 1,614 939 19,320 5,259 60,910 5,984 196,946 20,305 172,571 17,203
1994 298,930 55,801 3,177 5,058 3,654 8,694 1,375 69,553 5,033 224,892 17,723 196,898 18,629
1995 251,970 77,149 4,623 3,228 1,331 8,501 1,692 88,878 5,099 287,377 18,764 236,405 18,961
1996 350,850 76,457 4,392 5,380 2,319 27,241 4,775 109,078 6,889 352,693 24,843 288,320 20,683
1997 318,954 82,489 4,561 4,520 3,444 20,286 4,473 107,294 7,258 346,924 25,842 328,998 23,360
1998 413,100 86,930 3,180 2,367 1,143 18,643 4,036 107,940 5,264 349,015 20,199 349,544 23,756
1999 285,514 90,843 6,265 4,304 1,682 25,107 3,966 120,253 7,603 388,828 27,411 361,589 24,679
2000 284,044 86,186 5,853 2,045 1,164 16,080 4,920 104,310 7,734 337,277 27,133 358,373 25,136
2001 337,848 111,746 6,713 7,533 5,867 23,414 6,551 142,693 11,064 461,384 38,563 395,829 31,489
2002 402,565 88,345 5,753 6,564 2,856 16,644 2,916 111,553 7,054 360,696 25,430 386,452 30,930
2003 424,900 117,920 10,007 2,690 1,410 16,644 5,557 137,254 11,533 443,796 39,783 421,959 35,197
2004 337,971 98,802 6,496 2,260 1,211 15,891 1,899 116,953 6,875 378,157 25,161 394,217 30,889
2005 508,890 104,802 6,482 8,071 5,989 17,772 4,371 130,645 9,848 422,428 34,464 414,794 33,682
2006 426,300 136,752 8,244 5,811 2,331 27,739 3,901 170,302 9,413 550,656 34,943 450,414 31,843
2007 476,009 163,757 10,107 2,690 1,536 27,269 6,097 193,717 11,903 626,363 43,158 533,149 37,733
2008 602,699 162,157 10,086 1,291 756 53,025 14,940 216,473 18,042 699,944 62,297 625,654 48,182
2009 457,802 143,307 9,225 6,349 2,492 31,313 11,495 180,969 14,948 585,144 51,671 637,150 52,957
2010 783,648 174,891 15,781 9,792 3,889 42,503 8,751 227,186 18,460 734,584 63,943 673,224 59,552
2011 646,501 168,421 11,668 7,533 3,436 32,535 9,153 208,489 15,223 674,127 53,528 664,619 56,639
2012 831,955 181,861 14,917 4,627 1,983 45,229 12,819 231,718 19,768 749,236 68,067 719,316 62,148
2013 NA 162,885 15,256 6,779 4,147 28,304 14,634 197,968 21,543 640,110 72,482 687,825 65,197
2014 663,257 198,370 28,544 1,184 710 16,268 5,460 215,821 29,070 697,837 96,516 695,728 80,004
2015 634,478 154,044 12,141 1,399 466 18,315 9,463 173,758 15,400 561,829 52,798 633,259 76,063
2016 727,419 206,356 16,707 2,260 1,624 23,884 10,902 232,500 20,016 751,767 68,848 670,477 74,929
2017 743,488 211,446 14,231 450 288 28,869 9,727 240,764 17,240 778,488 60,806 697,361 61,169
2018 646,965 186,626 22,200 1,291 1,087 11,284 3,893 199,201 22,565 644,097 75,700 724,784 68,721
2019 647,040 144,268 13,905 1,076 486 14,105 9,560 159,449 16,881 515,562 56,918 646,049 64,981
2020 NA NA NA NA NA NA NA NA NA NA NA NA NA
2021 NA 126,621 6,732 2,152 1,222 28,586 12,332 157,359 14,103 508,805 48,292 556,155 61,380
2022 NA 170,572 13,651 861 867 37,989 18,424 209,422 22,946 677,146 77,163 567,171 61,984
2023 570,391 118,548 10,434 0 0 13,165 7,794 131,713 13,024 425,881 44,167 537,277 58,415
2024 457,773 107,497 7,969 1,563 1,576 19,371 5,835 128,431 10,002 415,268 34,841 506,098 55,132
2025 NA 124,023 9,448 861 867 20,123 13,667 145,007 16,638 468,864 55,765 436,671 45,732

Figure 14: Pacific Population white-fronted goose abundance in fall. Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The blue dashed reference line is the Pacific Flyway Council’s population objective. The and the red reference line is the closure threshold.
Time series statistics
Parameter Estimate SE L95%CI U95%CI
1-year index 468,864 55,765 359,565 578,163
3-year indexa 436,671 45,732 347,036 526,306
LTA 431,521
Objective 300,000
% change from LTA 9
% change from obj 46
Mgmt index (n years) 3
a 2023, 2024, 2025

Harvest Strategy
Management index: White-fronted geese projected in fall.

Management thresholds:
>300,000 Standard
>100,000 Restrictive
Closed

Management prescription: Standard.

Note that the Restrictive alternative will be prescribed when the most recent moving 3-year average abundance is increasing from below 100,000 to at least 120,000 birds.

Regulatory alternatives:
Regulations fixed until changed.

Harvest management should promote maintenance of the population goal: a 3-year average projected fall index of 300,000 geese. When the population is above objective, the harvest rate should not exceed 15% of the most recent 3-year average index. If the population index drops below the objective level of 300,000, harvest rate should not exceed 10% of the most recent 3-year average projected fall population index. If the 3-year average population index drops below 100,000 geese, all hunting should be suspended throughout the flyway. After a season closure, the 3-year average abundance must exceed 120,000 birds before harvest may be considered.

Data Table 13: White-fronted Goose, Tule

Original data source: Cooperative Pacific Flyway Mark-resight Survey in California, Oregon, and Alaska; California and USFWS Pacific Flyway Office. Data maintained by California.

Provided in the table below are abundance (Estimate) and standard error (SE) of Tule white-fronted geese in fall. Also provided are the estimated number of marked (Marks) geese in the population, estimated ratio (Ratio) of marked geese to total geese, and the abundance moving 3-year average (M3yr) and standard error (M3yr.SE).

Table 13. Tule white-fronted goose abundance in fall, 2003-2024.
Year Marks Marks.SE Ratio Ratio.SE Estimate Estimate.SE M3yr M3yr.SE
2003 47 0.0 373 72.4 17,536 3,404 NA NA
2004 60 0.0 152 44.8 9,115 2,687 NA NA
2005 51 1.3 293 119.5 15,030 6,144 13,894 4,342
2006 81 0.0 412 134.4 33,342 10,890 19,162 7,384
2007 88 0.5 189 40.0 16,640 3,526 21,671 7,501
2008 75 0.5 147 35.4 11,039 2,663 20,340 6,785
2009 54 1.1 248 55.8 13,399 3,026 13,693 3,092
2010 58 0.0 293 79.3 17,002 4,598 13,814 3,530
2011 53 0.5 224 42.4 11,920 2,257 14,107 3,435
2012 59 0.8 273 80.0 16,269 4,763 15,064 4,038
2013 50 0.0 220 65.7 10,975 3,285 13,055 3,586
2014 56 0.4 159 42.3 8,940 2,373 12,062 3,611
2015 59 0.3 164 32.1 9,667 1,900 9,861 2,584
2016 56 0.0 329 91.2 18,445 5,106 12,351 3,431
2017 60 0.5 284 68.8 17,124 4,145 15,079 3,953
2018 45 0.3 155 34.5 6,992 1,557 14,187 3,902
2019 54 0.5 303 90.8 16,446 4,927 13,521 3,825
2020 30 1.6 395 127.2 12,048 3,934 11,829 3,749
2021 25 0.6 463 221.8 11,713 5,625 13,402 4,878
2022 33 2.0 400 190.5 13,029 6,272 12,263 5,368
2023 39 0.0 248 64.9 9,655 2,529 11,466 5,079
2024 26 0.0 258 74.4 6,721 1,934 9,802 4,061

Figure 15: Tule white-fronted goose abundance in fall Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The blue dashed reference line is the Pacific Flyway Council’s minimum population objective.
Time series statistics
Parameter Estimate SE L95%CI U95%CI
1-year index 6,721 1,934 2,931 10,511
3-year indexa 9,802 4,061 1,842 17,762
LTA 14,111
Objective 10,000
% change from LTA -52
% change from obj -2
Mgmt index (n years) 3
a 2022, 2023, 2024

Harvest Strategy
Management index: Total white-fronted geese in fall.

Management thresholds: N/A.

Management prescription: N/A.

Regulatory alternatives:
Regulations fixed until changed.

Data Table 14: Trumpeter Swan, PP

Original data source: Waterfowl Breeding Population and Habitat Survey (WBPHS) strata in Alaska (i.e., strata 1–4, 6, and 7); USFWS Alaska Region. Data maintained by the USFWS Alaska Region.

Provided in the table below are abundance and standard error (SE) of Pacific Population trumpeter swans by WBPHS area (strata 1–4, 6, and 7) and in total (Total) in spring. Also provided are the total abundance moving 3-year average (M3yr) and standard error (M3yr.SE).

Table 14. Pacific Population trumpeter swan abundance in spring, 1964-2025.
Year WPBHS1 WPBHS1.SE WPBHS2 WPBHS2.SE WPBHS3 WPBHS3.SE WPBHS4 WPBHS4.SE WPBHS6 WPBHS6.SE WPBHS7 WPBHS7.SE Total Total.SE M3yr M3yr.SE
1964 110 120 150 155 465 217 0 0 922 819 NA NA NA NA NA NA
1965 220 241 375 200 1,198 603 154 143 205 121 NA NA NA NA NA NA
1966 330 179 0 0 845 347 0 0 205 195 NA NA NA NA NA NA
1967 935 456 1,050 380 913 418 0 0 64 69 NA NA NA NA NA NA
1968 110 108 750 397 493 213 0 0 0 0 NA NA NA NA NA NA
1969 385 271 150 98 986 302 0 0 102 98 NA NA NA NA NA NA
1970 440 261 750 404 845 479 0 0 102 70 NA NA NA NA NA NA
1971 715 235 1,875 663 1,198 418 0 0 359 207 NA NA NA NA NA NA
1972 440 314 1,125 440 1,480 571 0 0 205 121 NA NA NA NA NA NA
1973 110 54 1,200 484 1,057 502 0 0 461 294 NA NA NA NA NA NA
1974 0 0 1,050 579 916 303 135 127 256 125 NA NA NA NA NA NA
1975 330 162 3,450 2,110 775 453 135 127 666 427 NA NA NA NA NA NA
1976 220 108 1,950 512 1,198 459 135 141 359 241 NA NA NA NA NA NA
1977 330 216 2,775 725 1,198 529 0 0 410 390 NA NA NA NA NA NA
1978 330 361 1,725 789 2,114 699 270 283 410 287 NA NA NA NA NA NA
1979 330 194 1,800 901 2,043 706 270 156 615 376 NA NA NA NA NA NA
1980 220 152 2,100 465 2,959 844 0 0 1,281 743 NA NA NA NA NA NA
1981 990 766 2,850 1,614 1,550 570 135 141 1,076 551 NA NA NA NA NA NA
1982 440 295 2,400 816 3,805 1,724 0 0 512 317 NA NA NA NA NA NA
1983 385 189 3,225 896 3,382 1,208 0 0 871 341 NA NA NA NA NA NA
1984 550 269 4,950 2,892 2,607 738 0 0 410 222 740 178 9,257 3,010 NA NA
1985 1,375 559 3,750 1,307 4,086 1,126 0 0 1,025 561 840 210 11,076 1,910 NA NA
1986 385 214 3,600 1,251 2,748 815 0 0 410 150 920 137 8,063 1,522 9,465 2,238
1987 440 253 6,150 3,568 4,650 1,737 270 283 512 138 620 148 12,642 3,992 10,594 2,702
1988 385 108 4,350 1,109 4,861 1,535 135 141 871 250 500 215 11,103 1,931 10,603 2,707
1989 440 321 5,775 2,379 3,452 1,022 405 380 974 456 500 227 11,546 2,685 11,764 2,993
1990 110 108 4,500 1,496 6,693 2,250 0 0 769 382 660 176 12,732 2,737 11,794 2,478
1991 660 244 4,650 1,863 3,241 1,169 675 349 974 425 800 359 11,000 2,308 11,759 2,584
1992 330 126 4,200 621 4,368 1,129 540 270 410 150 680 193 10,528 1,346 11,420 2,208
1993 385 143 3,225 632 4,086 993 675 349 359 197 380 145 9,110 1,260 10,213 1,705
1994 440 332 3,825 961 4,086 772 1,080 648 359 133 720 320 10,510 1,473 10,049 1,362
1995 330 216 3,450 1,203 4,509 1,021 0 0 666 250 1,020 368 9,975 1,653 9,865 1,471
1996 660 396 4,125 886 6,552 1,555 405 380 974 364 1,040 234 13,756 1,921 11,414 1,693
1997 495 331 5,400 1,783 3,945 1,082 270 283 820 228 880 145 11,810 2,148 11,847 1,918
1998 55 54 4,950 1,375 6,834 1,734 0 0 922 390 1,020 82 13,782 2,249 13,116 2,111
1999 385 306 6,225 1,368 12,823 4,313 1,485 1,406 666 255 820 157 22,404 4,757 15,999 3,281
2000 550 209 4,350 1,460 11,273 5,071 10,530 8,815 2,306 742 1,260 241 30,269 10,306 22,152 6,681
2001 385 187 4,950 1,534 7,492 3,212 4,050 2,345 1,281 627 1,200 552 19,358 4,347 24,010 7,018
2002 660 205 3,375 1,004 6,905 1,747 1,215 817 1,076 239 1,080 335 14,311 2,223 21,313 6,584
2003 660 137 6,225 2,721 5,214 1,584 540 348 820 295 1,260 385 14,719 3,207 16,129 3,373
2004 935 294 3,450 1,046 5,989 1,609 540 391 1,281 387 1,480 382 13,675 2,054 14,235 2,546
2005 786 563 3,450 872 5,143 1,706 405 297 820 322 NA NA NA NA NA NA
2006 660 152 8,475 5,058 6,552 2,094 1,350 573 769 256 1,400 379 19,206 5,525 15,867 3,874
2007 605 367 5,400 1,366 9,159 2,945 1,485 734 1,435 582 660 180 18,744 3,404 17,208 3,930
2008 550 225 3,600 835 8,595 2,916 1,662 722 1,281 283 1,260 233 16,948 3,147 18,299 4,164
2009 605 104 3,150 1,001 8,455 2,613 810 538 1,742 411 620 126 15,382 2,884 17,025 3,152
2010 550 283 2,775 372 8,428 3,457 945 485 1,691 380 740 156 15,129 3,546 15,820 3,204
2011 1,161 412 2,925 474 8,948 2,352 1,350 499 1,896 497 720 179 17,000 2,540 15,837 3,019
2012 794 255 4,050 723 9,159 3,076 1,215 645 2,152 553 1,200 406 18,571 3,307 16,900 3,161
2013 NA NA 3,600 887 8,877 2,800 1,080 590 NA NA 960 264 NA NA NA NA
2014 1,039 437 1,341 562 6,466 1,736 3,915 1,774 1,589 451 1,420 302 15,770 2,639 17,114 2,849
2015 244 111 3,000 501 7,680 1,548 1,350 698 2,358 451 1,320 656 15,951 1,944 16,764 2,688
2016 550 189 2,925 387 7,116 1,904 540 391 1,896 525 1,000 235 14,027 2,073 15,249 2,239
2017 794 272 1,575 378 9,900 3,526 810 553 2,255 501 980 297 16,314 3,647 15,431 2,669
2018 733 434 2,775 1,060 6,130 2,156 3,510 876 1,794 404 680 155 15,622 2,629 15,321 2,858
2019 2,383 1,758 1,950 500 6,552 1,525 5,940 3,259 2,409 935 820 132 20,054 4,145 17,330 3,530
2020 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
2021 756 412 2,730 1,269 5,231 1,588 1,890 1,072 2,358 1,122 1,280 271 14,245 2,605 16,640 3,208
2022 856 460 2,550 921 8,455 2,515 2,700 1,338 2,358 723 960 283 17,878 3,127 17,392 3,354
2023 428 182 NA NA 3,488 1,352 2,160 940 1,435 504 520 105 NA NA NA NA
2024 489 285 2,550 904 4,086 1,155 2,314 1,352 2,665 986 680 101 12,785 2,246 14,969 2,684
2025 1,161 330 1,300 624 6,539 1,988 8,640 5,776 2,358 650 1,060 225 21,058 6,188 17,240 4,208

Figure 16: Pacific Population trumpeter swans abundance in spring. Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The blue dashed reference line is the Pacific Flyway Council’s minimum population objective.
Time series statistics
Parameter Estimate SE L95%CI U95%CI
1-year index 21,058 6,188 8,930 33,186
3-year indexa 17,240 4,208 8,993 25,487
LTA 14,737
Objective 10,000
% change from LTA 43
% change from obj 72
Mgmt index (n years) 3
a 2022, 2024, 2025

Harvest Strategy
Management index: Total trumpeter swans in spring.

Management thresholds: N/A.

Management prescription: N/A.

Regulatory alternatives:
Regulations fixed until changed.

Note that the Pacific Flyway Council has not yet determined the objective for this population. Early discussions by the Pacific Flyway Study Committee indicate a possible value of 10,000 birds.

Data Table 15: Trumpeter Swan, RMP US Segment

Original data source: Cooperative Fall Survey of the Rocky Mountain Population Trumpeter Swan US Segment; USFWS headquarters, USFWS Mountain-Prairie Region, USFWS Pacific Region, Idaho, Montana, Oregon, Tribes, and National Park Service. Data maintained by USFWS Headquarters.

Provided in the table below are abundance of Rocky Mountain Population trumpeter swans by age class and in total (Total) in fall. Age classes include adult and subadult birds (White) and cygnets (Gray). Also provided are the proportion of the total for each age class and the moving 3-year average abundance for adult and subadult swans (WhiteM3yr) and in total (TotalM3yr).

Table 15. Rocky Mountain Population US segment trumpeter swans in fall, 1987-2024.
Year White Gray Total White% Gray% White.M3yr Total.M3yr
1967 580 58 638 91 9 NA NA
1968 489 174 663 74 26 NA NA
1969 NA NA NA NA NA NA NA
1970 NA NA NA NA NA NA NA
1971 477 95 572 83 17 515 624
1972 NA NA NA NA NA NA NA
1973 NA NA NA NA NA NA NA
1974 492 89 581 85 15 486 605
1975 NA NA NA NA NA NA NA
1976 NA NA NA NA NA NA NA
1977 454 90 544 83 17 474 566
1978 NA NA NA NA NA NA NA
1979 NA NA NA NA NA NA NA
1980 533 49 582 92 8 493 569
1981 NA NA NA NA NA NA NA
1982 NA NA NA NA NA NA NA
1983 471 76 547 86 14 486 558
1984 496 67 563 88 12 500 564
1985 431 144 575 75 25 466 562
1986 365 87 452 81 19 431 530
1987 417 194 611 68 32 404 546
1988 513 146 659 78 22 432 574
1989 535 63 598 89 11 488 623
1990 468 158 626 75 25 505 628
1991 446 109 555 80 20 483 593
1992 465 98 563 83 17 460 581
1993 303 51 354 86 14 405 491
1994 302 152 454 67 33 357 457
1995 365 62 427 85 15 323 412
1996 380 78 458 83 17 349 446
1997 358 69 427 84 16 368 437
1998 364 105 469 78 22 367 451
1999 347 70 417 83 17 356 438
2000 372 109 481 77 23 361 456
2001 416 71 487 85 15 378 462
2002 347 60 407 85 15 378 458
2003 357 96 453 79 21 373 449
2004 318 106 424 75 25 341 428
2005 430 111 541 79 21 368 473
2006 438 99 537 82 18 395 501
2007 449 133 582 77 23 439 553
2008 450 70 520 87 13 446 546
2009 486 90 576 84 16 462 559
2010 467 127 594 79 21 468 563
2011 497 132 629 79 21 483 600
2012 554 217 771 72 28 506 665
2013 684 144 828 83 17 578 743
2014 607 186 793 77 23 615 797
2015 742 253 995 75 25 678 872
2016 758 237 995 76 24 702 928
2017 823 204 1,027 80 20 774 1,006
2018 852 228 1,080 79 21 811 1,034
2019 794 165 959 83 17 823 1,022
2020 857 173 1,030 83 17 834 1,023
2021 793 201 994 80 20 815 994
2022 726 214 940 77 23 792 988
2023 690 236 926 75 25 736 953
2024 695 308 1,003 69 31 704 956

Figure 17: Rocky Mountain Population US breeding segment trumpeter swan white bird (subadult and adult) abundance in fall. Circles are annual estimates of abundance. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The blue dashed reference line is the Pacific Flyway Council’s population objective.
Time series statistics
Parameter Estimate SE L95%CI U95%CI
1-year index 695
3-year indexa 704
LTA 510
Objective 718
% change from LTA 36
% change from obj -3
Mgmt index (n years) 1
a 2022, 2023, 2024

Harvest Strategy
Management index: Total white (adult and subadult) trumpeter swans in fall.

Management thresholds: N/A.

Management prescription: N/A.

Regulatory alternatives:
Regulations fixed until changed.

Figure 18: Rocky Mountain Population US breeding segment trumpeter swan total abundance in fall. Circles are annual estimates of abundance. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average abundance.

Data Table 16: Tundra Swan, EP

Original data source: Cooperative State-Federal Midwinter Waterfowl Survey in the U.S. Mississippi Flyway; U.S. Atlantic Flyway; and Ontario, Canada. Data maintained by USFWS Atlantic Flyway Office.

Provided in the table below are abundance of Eastern population tundra swans in winter by area including the U.S. Mississippi Flyway (MF), U.S. Atlantic Flyway (AF), Ontario (ON), and in total (Total). Also provided is the total abundance moving 3-year average (M3yr). So long as there are counts in the U.S. Mississippi and Atlantic flyways and Ontario, the total winter count is interpreted as the minimum known population size with no variance.

Table 16. Eastern Population tundra swan abundance in winter, 1982-2025.
Year MF AF ON Total M3yr
1982 72,907 275 0 73,182 NA
1983 86,464 550 500 87,514 NA
1984 81,235 25 100 81,360 80,685
1985 93,909 525 2,500 96,934 88,603
1986 90,766 150 25 90,941 89,745
1987 94,504 250 1,000 95,754 94,543
1988 77,110 375 1,200 78,685 88,460
1989 91,150 125 25 91,300 88,580
1990 90,593 17 9 90,619 86,868
1991 97,424 20 754 98,198 93,372
1992 109,788 327 2,929 113,044 100,620
1993 76,593 858 739 78,190 96,477
1994 84,527 61 184 84,772 92,002
1995 80,222 2,447 2,473 85,142 82,701
1996 79,021 393 113 79,527 83,147
1997 86,120 233 6,027 92,380 85,683
1998 96,544 1,335 2,679 100,558 90,822
1999 109,041 1,618 296 110,955 101,298
2000 103,082 3,364 8,897 115,343 108,952
2001 98,143 46 231 98,420 108,239
2002 103,827 3,661 7,169 114,657 109,473
2003 108,187 2,160 1,379 111,726 108,268
2004 94,975 2,094 13,737 110,806 112,396
2005 68,735 1,054 2,668 72,457 98,330
2006 70,452 1,069 9,746 81,267 88,177
2007 87,840 10,521 16,057 114,418 89,381
2008 88,502 1,826 5,917 96,245 97,310
2009 99,304 552 336 100,192 103,618
2010 91,909 1,302 4,081 97,292 97,910
2011 93,767 2,427 1,445 97,639 98,374
2012 86,793 12,436 13,512 112,741 102,557
2013 98,493 1,035 7,527 107,055 105,812
2014 103,844 848 287 104,979 108,258
2015 107,936 2,964 6,196 117,096 109,710
2016 86,619 12,982 13,992 113,593 111,889
2017 115,425 1,909 1,953 119,287 116,659
2018 111,122 431 61 111,614 114,831
2019 72,365 733 19,721 92,819 107,907
2020 61,354 9,241 7,991 78,586 94,340
2021 76,701 1,677 8,302 86,680 86,028
2022 89,142 1,717 4,871 95,730 86,999
2023 113,420 4,806 19,555 137,781 106,730
2024 48,678 6,986 8,773 64,437 99,316
2025 67,687 1,451 8,067 77,205 93,141

Figure 19: Eastern Population tundra swan abundance in winter. Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual counts. The blue dashed reference line is the Councils’ population objective. The red dashed reference lines represent threshold values in the harvest strategy decision and the red reference line is the closure threshold.
Time series statistics
Parameter Estimate SE L95%CI U95%CI
1-year index 77,205
3-year indexa 93,141
LTA 97,254
Objective 80,000
% change from LTA -21
% change from obj 16
Mgmt index (n years) 3
a 2023, 2024, 2025

Harvest Strategy
Management index: Total tundra swans in winter.

Management thresholds:
>110,000 Liberal
>70,000 Moderate
>50,000 Restrictive
Closed

Management prescription: Moderate.

Note that the Restrictive alternative will be prescribed when the most recent moving 3-year average abundance is increasing from below 50,000 to at least 80,000 swans.

Regulatory alternatives:
The permit allocation in the Atlantic Flyway and Central Flyway combined will be:
Liberal
12,000 permits
Moderate
9,600 permits
Restrictive
7,200 permits
Closed

The regulatory alternative for total permits for the Atlantic and Central Flyways combined is prescribed based on the estimated winter population size from monitoring data. The analytical framework derives a recent 3-year average population size estimate and is compared to threshold values in a decision-analysis framework for prescribing the appropriate regulatory alternative. The recent 3-year average population size estimate must exceed the threshold value to change regulations, either more restrictive or liberal. The season is closed when the recent 3-year average winter population estimate is ≤50,000 swans and will remain closed until the estimate is ≥70,000 swans. A restrictive alternative is prescribed when the estimate is >50,000 and ≤70,000 swans and will remain restrictive until the estimate is ≥80,000 swans. A moderate alternative is prescribed when the estimate is >70,000 and ≤110,000 swans. A liberal alternative is prescribed when the estimate is >110,000 swans. Allocation of permits among States must be approved by the Atlantic and Central Flyway Councils and consistent with the Councils’ management plan for this population.

Data Table 17: Tundra Swan, WP

Original data source: Yukon Kuskokwim Delta Coastal Zone Survey and Waterfowl Breeding Population and Habitat Survey (WBPHS) strata in Alaska (i.e., strata 8–11); USFWS Alaska Region. Data maintained by USFWS Alaska Region.

Provided in the table below are abundance and standard error (SE) of Western Population tundra swans in spring by survey area including Yukon Kuskokwim Delta Coastal Zone Survey (YKDCZ), WBPHS (strata 8–11), and in total (Total). Also provided are the total abundance moving 3-year average (M3yr) and standard error (M3yr.SE).

Table 17. Western Population tundra swan abundance in spring, 1985-2025.
Year YKDCZ YKDCZ.SE WPBHS8 WPBHS8.SE WPBHS9 WPBHS9.SE WPBHS10 WPBHS10.SE WPBHS11 WPBHS11.SE Total Total.SE M3yr M3yr.SE
1985 25,028 2,558 18,509 8,250 38,639 7,373 8,388 6,631 4,235 1,304 94,799 13,215 NA NA
1986 21,844 2,023 11,837 2,690 28,690 3,262 4,538 2,230 3,901 1,640 70,809 5,443 NA NA
1987 20,693 2,976 17,863 7,932 31,298 6,747 3,162 876 3,901 925 76,918 10,905 80,842 10,379
1988 23,057 2,747 9,470 1,722 44,725 13,356 3,162 1,243 2,564 1,004 82,977 13,836 76,901 10,646
1989 32,517 6,596 34,004 14,213 25,792 2,457 9,762 7,974 6,019 1,073 108,095 17,784 89,330 14,453
1990 26,567 4,216 9,685 2,059 44,338 6,999 7,288 5,140 23,518 17,544 111,396 20,130 100,822 17,445
1991 17,692 1,936 15,388 2,754 31,008 3,728 14,575 13,127 6,130 1,488 84,793 14,134 101,428 17,524
1992 18,150 1,951 15,603 3,133 28,303 2,437 4,538 419 5,684 1,683 72,278 4,751 89,489 14,463
1993 19,375 1,535 10,223 2,195 40,281 12,709 4,400 795 5,127 1,344 79,406 13,082 78,826 11,452
1994 18,274 1,315 10,115 2,461 46,367 6,427 3,988 2,342 4,793 1,652 83,536 7,570 78,407 9,147
1995 21,934 1,859 20,230 9,937 67,425 32,418 5,362 2,313 4,458 1,226 119,410 34,058 94,118 21,513
1996 22,418 1,452 13,666 2,730 61,243 18,793 6,462 1,510 6,130 1,664 109,921 19,178 104,289 22,986
1997 27,594 3,180 13,128 3,858 52,549 6,482 7,700 3,368 13,152 6,343 114,123 10,891 114,485 23,426
1998 42,255 4,576 13,882 3,453 53,225 6,888 8,662 6,096 17,722 8,298 135,746 13,650 119,930 14,975
1999 23,709 1,400 14,635 3,995 52,282 11,168 8,112 3,747 8,471 2,325 107,209 12,732 119,026 12,477
2000 26,244 2,880 16,357 3,827 48,615 9,665 7,288 2,811 10,143 4,606 108,646 12,061 117,200 12,831
2001 21,548 1,707 14,420 4,443 39,588 3,118 10,175 5,533 7,914 2,166 93,644 8,227 103,166 11,184
2002 28,999 4,080 17,755 6,158 49,931 11,949 8,112 2,516 11,926 4,277 116,724 14,899 106,338 12,043
2003 21,994 2,295 14,850 2,025 41,938 5,492 8,250 4,111 8,582 2,278 95,614 7,850 101,994 10,821
2004 25,360 2,242 13,236 4,315 51,718 18,588 8,800 3,709 11,703 4,660 110,817 20,116 107,718 15,146
2005 23,361 2,532 24,104 12,840 63,002 16,405 5,500 1,495 6,688 1,532 122,654 21,094 109,695 17,428
2006 30,880 2,552 17,755 4,513 62,531 11,460 4,125 1,044 8,694 2,786 123,985 12,925 119,152 18,409
2007 29,457 3,576 15,926 8,706 80,115 19,499 11,825 1,269 17,388 4,377 154,711 22,126 133,784 19,163
2008 31,597 3,396 12,805 4,762 87,268 27,624 7,150 3,181 35,778 16,039 174,598 32,629 151,098 23,953
2009 26,494 2,583 13,451 5,407 46,922 3,030 7,838 2,954 12,260 2,550 106,965 7,767 145,425 23,199
2010 36,408 4,446 8,286 1,527 44,853 3,993 10,725 6,359 9,920 1,715 110,192 9,023 130,585 20,053
2011 28,846 2,734 15,280 5,950 54,727 14,286 8,800 2,877 11,703 3,368 119,356 16,327 112,171 11,667
2012 38,902 5,582 10,223 851 48,709 6,999 7,425 2,583 9,697 1,324 114,955 9,449 114,834 12,073
2013 18,879 1,692 21,091 14,798 46,264 8,361 9,212 2,811 14,155 3,321 109,602 17,626 114,638 14,906
2014 26,133 4,020 12,267 3,097 43,819 7,785 6,188 3,121 8,471 3,116 96,877 10,287 107,145 12,985
2015 18,953 3,191 13,882 2,597 60,400 16,883 7,379 3,338 24,744 13,327 125,357 22,152 110,612 17,390
2016 29,918 4,511 8,071 1,571 77,388 45,172 6,738 1,945 11,146 3,471 133,261 45,598 118,498 29,865
2017 27,133 4,142 9,225 3,025 39,186 5,270 22,825 12,749 9,028 2,001 107,398 14,853 122,005 30,499
2018 32,531 4,531 12,698 4,524 87,262 24,870 4,675 2,478 14,824 5,142 151,990 26,308 130,883 31,580
2019 34,669 4,633 7,425 1,643 43,819 10,141 5,362 3,112 9,808 2,089 101,084 11,877 120,157 18,742
2020 NA NA NA NA NA NA NA NA NA NA NA NA NA NA
2021 31,018 2,683 13,559 8,110 45,700 8,149 7,379 6,518 21,846 11,630 119,501 17,808 124,192 19,581
2022 27,423 3,150 11,837 3,123 38,177 4,378 7,700 4,260 15,158 7,539 100,295 10,669 106,960 13,808
2023 16,443 952 7,748 1,671 33,099 7,442 4,400 3,186 10,700 3,506 72,390 9,029 97,396 13,070
2024 19,266 1,085 6,513 2,400 31,219 5,841 3,850 635 12,889 3,543 73,736 7,349 82,141 9,117
2025 20,608 1,923 12,698 5,503 20,499 3,305 4,400 2,707 14,712 11,785 72,917 13,824 73,015 10,435

Figure 20: Western Population tundra swan abundance in spring. Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The blue dashed reference line is the Pacific Flyway Council’s minimum population objective.
Time series statistics
Parameter Estimate SE L95%CI U95%CI
1-year index 72,917 13,824 45,821 100,013
3-year indexa 73,015 10,435 52,563 93,466
LTA 107,584
Objective 60,000
% change from LTA -32
% change from obj 22
Mgmt index (n years) 3
a 2023, 2024, 2025

Harvest Strategy
Management index: Total tundra swans in spring.

Management thresholds:
≥60,000 Standard
Restrictive

Management prescription: Standard.

Regulatory alternatives:
Regulations fixed until changed.

Data Table 18: Sandhill Crane, MP

Original data source: Photo-corrected annual spring survey along the Platte River of Nebraska; USFWS Headquarters. Data maintained by USFWS Headquarters.

Provided in the table below are abundance (Estimate) and standard error (SE) of Midcontinent Population sandhill cranes in spring. Also provided are the abundance moving 3-year average (M3yr) and standard error (M3yr.SE).

Table 18. U.S. Midcontinent Population sandhill crane abundance in spring, 1982-2025.
Year Estimate SE M3yr M3yr.SE
1982 417,263 42,331 NA NA
1983 343,378 31,674 NA NA
1984 261,802 24,198 340,814 33,569
1985 514,763 49,650 373,314 36,760
1986 353,040 37,340 376,535 38,492
1987 416,058 65,588 427,954 52,157
1988 463,457 53,213 410,852 53,316
1989 391,995 51,349 423,837 57,068
1990 412,154 50,496 422,535 51,698
1991 340,645 33,897 381,598 45,955
1992 406,457 50,644 386,419 45,693
1993 378,883 50,454 375,328 45,678
1994 477,215 50,910 420,852 50,670
1995 326,181 35,256 394,093 46,117
1996 519,984 62,582 441,127 50,831
1997 534,630 86,889 460,265 65,088
1998 530,848 79,164 528,487 76,883
1999 284,858 35,599 450,112 70,908
2000 490,118 71,754 435,275 65,020
2001 413,498 64,221 396,158 59,274
2002 315,044 42,218 406,220 60,705
2003 348,023 41,263 358,855 50,363
2004 426,534 43,337 363,200 42,281
2005 491,915 47,392 422,157 44,071
2006 216,810 18,054 378,420 38,514
2007 384,118 39,637 364,281 37,162
2008 545,884 76,107 382,271 50,627
2009 565,257 50,923 498,420 57,609
2010 691,534 85,236 600,892 72,228
2011 482,797 44,851 579,863 62,902
2012 339,642 31,609 504,658 58,526
2013 867,061 126,196 563,167 79,448
2014 617,903 60,551 608,202 82,847
2015 386,471 49,504 623,812 85,718
2016 405,716 44,935 470,030 52,078
2017 568,369 72,987 453,519 57,146
2018 1,005,612 105,654 659,899 78,547
2019 945,996 133,127 839,992 106,791
2020 NA NA NA NA
2021 782,462 309,357 911,357 203,787
2022 685,476 85,473 804,645 200,608
2023 1,259,199 159,840 909,046 207,007
2024 420,840 66,572 788,505 111,484
2025 1,406,071 344,510 1,028,703 222,612

Figure 21: Midcontinent Population sandhill crane abundance in spring. Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The blue dashed reference lines represent the Pacific Flyway Council’s population objective range.
Time series statistics
Parameter Estimate SE L95%CI U95%CI
1-year index 1,406,071 344,510 730,831 2,081,311
3-year indexa 1,028,703 222,612 592,385 1,465,022
LTA 500,712
Objective 412,500
% change from LTA 181
% change from obj 149
Mgmt index (n years) 3
a 2023, 2024, 2025

Harvest Strategy
Management index: Sandhill cranes in spring.

Management thresholds: N/A.

Management prescription: N/A.

Regulatory alternatives:
Regulations fixed until changed.

Data Table 19: Sandhill Crane, RMP

Original data source: Rocky Mountain Population (RMP) Sandhill Cranes Fall (September) Staging Area Survey and RMP Cranes Fall (October) Recruitment Survey; USFWS Headquarters and USFWS Southwest Region. Data maintained by USFWS Headquarters, USFWS Southwest Region, and USFWS Pacific Flyway Office.

Provided in the table below are abundance of Rocky Mountain Population sandhill cranes in fall by state (Idaho, Montana, Wyoming, Utah, and Colorado) and in total (Total) and the age ratio (AgeRatio) of juvenile to adult (% juveniles in the population) sandhill cranes in fall. Also provided are the moving 3-year average total abundance (M3yrTotal) and age ratio (M3yrRatio). Additionally provided is allowable harvest (Allowable) based on the Pacific and Central Flyway Councils’ harvest strategy. The current year allowable harvest by state is provided in a subsequent table below.

Table 19. Rocky Mountain Population sandhill crane abundance in fall, 1987-2024.
Year ID MT WY UT CO Total M3yrTotal AgeRatio M3yrRatio Allowable
1987 10,686 1,447 2,327 1,578 1,443 17,481 NA 5.40 6.73 NA
1988 NA NA NA NA NA NA NA NA NA NA
1989 NA NA NA NA NA NA NA NA NA NA
1990 NA NA NA NA NA NA NA NA NA NA
1991 NA NA NA NA NA NA NA NA NA NA
1992 5,801 5,264 2,248 2,810 3,181 19,304 NA 5.20 5.67 NA
1993 NA NA NA NA NA NA NA NA NA NA
1994 NA NA NA NA NA NA NA NA NA NA
1995 6,864 3,681 1,671 1,528 2,284 16,028 17,604 6.40 5.47 513
1996 8,334 2,974 2,526 1,849 1,255 16,938 17,423 9.40 6.57 591
1997 8,132 3,595 2,255 2,450 1,604 18,036 17,001 9.70 8.50 693
1998 8,067 3,415 3,162 2,185 1,273 18,102 17,692 11.20 10.10 966
1999 8,761 3,141 4,205 2,292 1,102 19,501 18,546 8.40 9.77 1,128
2000 9,337 3,598 3,890 2,416 749 19,990 19,198 6.70 8.77 1,163
2001 7,160 4,585 2,626 1,522 666 16,559 18,683 5.80 6.97 829
2002 7,698 4,843 3,038 1,869 1,355 18,803 18,451 5.20 5.90 668
2003 7,822 4,964 3,446 2,546 745 19,523 18,295 7.10 6.03 660
2004 7,152 4,637 3,072 2,239 1,410 18,510 18,945 9.40 7.23 910
2005 7,668 5,588 3,911 2,646 1,052 20,865 19,633 10.80 9.10 1,320
2006 NA NA NA NA NA NA NA NA NA NA
2007 8,262 6,509 3,907 2,401 1,743 22,822 20,732 8.30 9.67 1,744
2008 6,123 6,419 3,826 3,708 1,080 21,156 21,614 9.10 9.10 1,940
2009 6,934 6,329 3,613 2,283 1,162 20,321 21,433 11.50 9.63 1,985
2010 5,776 7,335 3,726 3,242 985 21,064 20,847 8.35 9.65 1,780
2011 5,029 6,642 2,978 1,498 1,347 17,494 19,626 6.55 8.80 1,275
2012 3,432 5,876 3,587 2,109 413 15,417 17,992 7.79 7.56 774
2013 5,228 7,218 3,588 2,732 1,594 20,360 17,757 6.58 6.97 677
2014 6,064 6,555 3,008 2,783 1,258 19,668 18,482 10.31 8.23 937
2015 6,454 9,493 3,596 3,698 1,089 24,330 21,453 11.34 9.41 1,946
2016 5,445 7,507 4,879 3,298 1,135 22,264 22,087 8.84 10.16 2,362
2017 4,066 7,149 3,725 2,994 1,658 19,592 22,062 7.93 9.37 2,168
2018 4,469 7,553 5,101 2,770 1,908 21,801 21,219 7.90 8.22 1,628
2019 4,428 7,511 4,366 3,106 1,879 21,290 20,894 8.92 8.25 1,536
2020 5,096 9,264 6,608 3,222 1,446 25,636 22,909 9.70 8.84 2,378
2021 3,091 7,783 6,059 3,889 3,141 23,963 23,630 8.75 9.12 2,778
2022 3,957 6,844 3,975 2,330 1,526 18,632 22,744 10.78 9.74 2,546
2023 4,200 10,169 5,527 5,631 1,740 27,267 23,287 11.87 10.47 3,006
2024 5,432 7,280 5,952 4,824 1,421 24,909 23,603 9.34 10.66 3,232

Figure 22: Rocky Mountain Population sandhill crane abundance in fall. Circles are annual estimates of abundance (index) with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The blue dashed reference line is the Pacific Flyway Council’s population objective. The red dashed reference line is the restriction threshold in the harvest strategy decision.
Time series statistics
Parameter Estimate SE L95%CI U95%CI
1-year index 24,909
3-year indexa 23,603
LTA 20,091
Objective 19,000
% change from LTA 24
% change from obj 24
Mgmt index (n years) 3
a 2022, 2023, 2024

Harvest Strategy
Management index: Total sandhill cranes in spring.

Management thresholds:
≥15,000 Standard
Restrictive

Management prescription: Standard.

Regulatory alternatives:
Standard
State allocation of allowable harvest according to the formula in the Councils’ management plan
Restrictive
Hunting may be permitted to meet specific management objectives, including alleviation of localized crop damage and distribution concerns

Total allowable harvest for the 2025 hunting season: 3,232 cranes.

Note that the Management prescription and allowable harvest applies to the 2025 hunting season.

State allowable harvest allocations for the 2025 hunting season.
State Allowable
Idaho 324
Montana 611
Wyoming 414
Utah 399
Colorado 0
Arizona 238
New Mexico 1,135
Mexico 110

Data Table 20: Band-tailed Pigeon, Interior

Original data source: North American Breeding Bird Survey; U.S. Geological Survey. Data maintained by U.S. Geological Survey.

Provided in the table below are estimated abundance (Index, birds per route) and lower and upper 95% credible intervals (L95%CI, U95%CI) of Interior band-tailed pigeons in spring. Also provided is the abundance moving 3-year average (M3yr).

Table 20. Interior band-tailed pigeon abundance in spring, 1968-2024.
Year Index L95%CI U95%CI M3yr
1967 0.64 0.26 2.42 NA
1968 0.64 0.26 2.40 NA
1969 0.62 0.26 2.11 0.63
1970 0.61 0.26 2.02 0.62
1971 0.61 0.27 2.00 0.61
1972 0.60 0.27 1.83 0.60
1973 0.57 0.27 1.62 0.59
1974 0.56 0.27 1.51 0.57
1975 0.54 0.26 1.37 0.56
1976 0.53 0.26 1.29 0.54
1977 0.51 0.26 1.18 0.53
1978 0.50 0.26 1.10 0.51
1979 0.49 0.25 1.03 0.50
1980 0.47 0.25 0.97 0.49
1981 0.46 0.25 0.92 0.47
1982 0.44 0.24 0.88 0.46
1983 0.44 0.24 0.87 0.45
1984 0.43 0.24 0.83 0.44
1985 0.41 0.23 0.80 0.43
1986 0.41 0.23 0.77 0.42
1987 0.41 0.23 0.76 0.41
1988 0.40 0.23 0.74 0.41
1989 0.40 0.23 0.73 0.40
1990 0.39 0.23 0.71 0.40
1991 0.39 0.23 0.69 0.39
1992 0.38 0.23 0.67 0.39
1993 0.39 0.24 0.68 0.39
1994 0.40 0.24 0.70 0.39
1995 0.40 0.24 0.70 0.40
1996 0.38 0.23 0.66 0.39
1997 0.36 0.22 0.61 0.38
1998 0.34 0.21 0.59 0.36
1999 0.32 0.20 0.56 0.34
2000 0.30 0.19 0.53 0.32
2001 0.28 0.18 0.49 0.30
2002 0.27 0.17 0.46 0.29
2003 0.26 0.16 0.46 0.27
2004 0.26 0.16 0.45 0.26
2005 0.26 0.16 0.46 0.26
2006 0.25 0.15 0.43 0.26
2007 0.24 0.15 0.42 0.25
2008 0.24 0.15 0.40 0.24
2009 0.23 0.14 0.38 0.24
2010 0.21 0.13 0.35 0.22
2011 0.20 0.12 0.34 0.21
2012 0.19 0.12 0.33 0.20
2013 0.19 0.11 0.32 0.19
2014 0.18 0.11 0.31 0.19
2015 0.18 0.11 0.31 0.18
2016 0.18 0.11 0.31 0.18
2017 0.18 0.11 0.31 0.18
2018 0.18 0.11 0.31 0.18
2019 0.18 0.11 0.32 0.18
2020 0.18 0.11 0.32 0.18
2021 0.18 0.10 0.33 0.18
2022 0.18 0.10 0.33 0.18
2023 0.18 0.10 0.34 0.18
2024 0.18 0.10 0.35 0.18

Figure 23: Interior band-tailed pigeon abundance (index) in spring. Circles are annual estimates of abundance (index) with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.
Time series statistics
Parameter Estimate SE L95%CI U95%CI
1-year index 0.18 0.1 0.35
3-year indexa 0.18
LTA 0.36
Objective
% change from LTA -49.53
% change from obj
Mgmt index (n years) 1.00
a 2022, 2023, 2024

Harvest Strategy
Management index: Band-tailed pigeons per route in spring.

Management thresholds: N/A.

Management prescription: N/A.

Regulatory alternatives:
Regulations fixed until changed.

Figure 24: Band-tailed pigeon abundance (index) in Arizona in spring. Circles are annual estimates of abundance (index) with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Figure 25: Band-tailed pigeon abundance (index) in New Mexico in spring. Circles are annual estimates of abundance (index) with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Figure 26: Band-tailed pigeon abundance (index) in Colorado in spring. Circles are annual estimates of abundance (index) with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Figure 27: Band-tailed pigeon abundance (index) in Utah in spring. Circles are annual estimates of abundance (index) with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 21: Band-tailed Pigeon, Pacific Coast (summer)

Original data source: Pacific Flyway Cooperative Pacific Coast Band-tailed Pigeon Mineral Site Survey; British Columbia, Washington, Oregon, and California. Data maintained by USFWS Pacific Flyway Office.

Provided in the table below are estimated abundance (Index, birds per mineral site) and lower and upper 95% credible intervals (L95%CI, U95%CI) of Pacific Coast band-tailed pigeons in spring. Also provided are the abundance moving 3-year average (M3yr) and lower and upper 95% credible intervals (M3yrL95%CI, M3yrU95%CI).

Table 21. Pacific Coast band-tailed pigeon abundance in spring, 2004-2025.
Year Index L95%CI U95%CI M3yr M3yrL95%CI M3yrU95%CI
2004 157.7 119.7 214.2 NA NA NA
2005 167.0 128.8 223.8 NA NA NA
2006 168.8 131.6 223.0 164.7 128.7 216.8
2007 164.1 129.0 217.2 166.8 131.8 217.8
2008 164.2 128.7 214.3 165.8 131.9 215.0
2009 161.9 126.8 210.9 163.5 130.3 211.1
2010 152.8 119.8 198.5 159.8 127.4 204.9
2011 165.3 131.3 214.8 160.1 128.2 205.2
2012 158.9 125.6 207.9 159.1 127.8 204.2
2013 171.7 136.3 220.3 165.4 133.4 211.3
2014 178.2 141.2 229.5 169.8 136.6 216.0
2015 177.7 142.1 227.1 176.0 142.0 222.7
2016 187.3 149.6 239.1 181.3 146.7 228.6
2017 170.1 136.9 216.7 178.6 145.1 224.3
2018 180.7 145.2 232.4 179.5 146.5 225.8
2019 191.5 153.6 247.1 181.0 147.6 228.6
2020 193.3 154.9 247.9 188.7 153.8 238.7
2021 199.3 159.4 255.8 194.9 158.6 246.4
2022 188.2 150.3 241.0 193.7 157.6 244.6
2023 182.6 147.0 233.0 190.1 154.7 239.7
2024 189.1 150.3 241.7 186.7 151.5 235.7
2025 206.3 165.3 263.6 192.8 156.6 242.8

Figure 28: Pacific Coast band-tailed pigeon abundance (index) in summer. Circles are annual estimates of abundance (index) with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The red dashed reference line is the harvest strategy threshold for restrictive seasons and thered reference line is the closure threshold.
Time series statistics
Parameter Estimate SE L95%CI U95%CI
1-year index 206.30 165.3 263.6
3-year indexa 192.80 156.6 242.8
LTA 174.78
Objective 164.60 130.1 214.4
% change from LTA 18.03
% change from obj 17.13
Mgmt index (n years) 3.00
a 2023, 2024, 2025

Harvest Strategy
Management index: Band-tailed pigeons per mineral site in summer.

Management thresholds:
≥205.8 Standard
≥123.4 Restrictive
Closed

Management prescription: Restrictive.

Note that once the season is closed, the Restrictive alternative will be prescribed when ≤80% of the PPD for the recent 3-year mean abundance is ≤139.9 (15% below the population objective).

Regulatory alternatives:
Standard
4-bird daily bag limit, 9-day season
Restrictive
2-bird daily bag limit, 9-day season
Closed

The decision is based on ≥80% of the distribution of the moving 3-year average above or below the thresholds (mean of the first 5 years of the survey +/- 25%). The decision here was calculated based on an approximation of the distribution of the recent moving 3-year average; see the USFWS harvest memo for more accurate evaluation of the distribution. Once the season is closed, an open season may be prescribed when ≤80% of the PPD for the recent 3-year mean abundance is ≤15% below the population objective (effectively the threshold between a closed and restrictive season is moved up 10% to reduce the likelihood of toggling between open and closed seasons annually).

Figure 29: Band-tailed pigeon abundance (index) in British Columbia in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Figure 30: Band-tailed pigeon abundance (index) in Washington in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Figure 31: Band-tailed pigeon abundance (index) in Oregon in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Figure 32: Band-tailed pigeon abundance (index) in California in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average..

Data Table 22: Mourning Dove, WMU (summer)

Original data source: State and Federal mourning dove banding programs; State-Federal cooperative Harvest Information Program and Parts Collection Survey; and USGS NA Breeding Bird Survey (BBS). Data maintained by each cooperator and the USFWS Headquarters.

Provided in the table below are estimated abundance (Estimate) and lower and upper credible intervals (LCI, UCI) of Western Management Unit Population mourning doves in summer. The level of confidence for credible intervals (CI%) is either 95% or 70%. Also provided is the abundance moving 3-year average (M3yr). Estimates of abundance are based on an integrated population model combining banding, harvest, and BBS data. The future year abundance prediction (Pred; where the prediction value = 1) are based on the average of the previous 3 years with 70% and 95% confidence intervals estimated from the integrated population model.

Table 22. Western Management Unit Population mourning dove abundance in summer, 2007-2025.
Year Estimate LCI UCI Pred CI% M3yr
2007 64,679,069 47,372,141 81,644,953 0 95 NA
2008 55,780,296 40,844,391 70,999,099 0 95 NA
2009 55,806,307 40,547,863 70,720,565 0 95 58,755,224
2010 55,156,259 40,282,401 69,786,958 0 95 55,580,954
2011 52,348,701 38,129,066 66,827,505 0 95 54,437,089
2012 49,833,005 36,241,672 63,244,608 0 95 52,445,988
2013 45,876,176 33,531,643 58,208,835 0 95 49,352,627
2014 50,639,352 37,130,176 64,420,092 0 95 48,782,844
2015 54,225,986 39,383,243 69,167,611 0 95 50,247,171
2016 44,104,136 32,184,622 56,222,338 0 95 49,656,491
2017 41,734,567 30,316,542 53,236,130 0 95 46,688,229
2018 44,243,107 32,219,025 56,221,918 0 95 43,360,603
2019 39,297,143 28,620,519 50,224,561 0 95 41,758,272
2020 38,764,451 28,112,521 49,513,142 0 95 40,768,234
2021 44,916,184 32,758,446 57,408,007 0 95 40,992,593
2022 51,170,144 37,023,903 65,347,696 0 95 44,950,260
2023 53,890,669 38,939,948 69,363,631 0 95 49,992,332
2024 53,939,786 39,016,143 69,428,350 0 95 53,000,200
2025 53,180,215 45,927,181 60,396,607 1 70 NA
2025 53,180,215 39,262,094 68,457,203 1 95 NA

Figure 33: Western Management Unit Population mourning dove abundance in summer. Black circles are annual estimates of abundance with 95% confidence intervals while red circles are predictions based on the average of the previous 3 years with 70% and 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average. The red dashed reference line is the harvest strategy threshold where restrictions are considered and the red reference line is the closure threshold.
Time series statistics
Parameter Abundance SE L95%CI U95%CI
1-year index 53,939,786 39,016,143 69,428,350
3-year indexa 53,000,200
LTA 49,872,497
Objective
% change from LTA 8
% change from obj
Mgmt index (n years) 3
a 2022, 2023, 2024

Harvest Strategy
Management index: Mourning doves in summer.

Management thresholds:
>19,300,000 Standard
≥11,600,000 Restrictive
Closed

Management prescription: Standard.

See also the national mourning dove harvest strategy assessment memo for the decision.

Regulatory alternatives:
Standard
Season length is 60 days, bracket dates are September 1 and January 15, and the daily bag limit is 15 doves
Restrictive
Season length is 60 days, bracket dates are September 1 and January 15, and the daily bag limit is 10 doves
Closed

The posterior probability distribution of the predicted abundance is used in a decision-analysis framework for setting harvest regulations relative to threshold abundance values. The harvest strategy requires that 85% of the distribution (confidence in the parameter estimate) be above the critical abundance threshold to prescribe a specific regulatory alternative. This corresponds to the lower credible interval (CI) of the central 70% distribution for the parameter estimate. Thus, if the lower 70% CI for the predicted abundance falls below the critical abundance threshold value, then the more restrictive regulatory alternative is prescribed. Using the lower credible interval provides incentive to reduce uncertainty in parameter estimation (the spread in the posterior probability distribution) by maintaining and improving monitoring programs. The greater the uncertainty in the parameter estimate, the more frequently a restrictive regulatory alternative likely will be prescribed because one is less confident that the parameter is above the threshold value. Threshold values based on the unit’s approximated maximum sustained yield. In the Western Management Unit, the Restrictive season threshold is at 50% MSY (19.3 million doves) and the Closed season threshold is at 30% MSY (11.6 million doves).

Data Table 23: White-winged Dove, WMU

Original data source: North American Breeding Bird Survey; U.S. Geological Survey. Data maintained by U.S. Geological Survey.

Provided in the table below are estimated abundance (Index, birds per route) and lower and upper 95% credible intervals (L95%CI, U95%CI) of Western Management Unit white-winged doves in spring. Also provided are the abundance moving 3-year average (M3yr) and lower and upper 95% confidence intervals (M3yrL95%CI, M3yrU95%CI). In the Western Management Unit, white-winged doves primarily occur in Arizona and California.

Table 23. Western Management Unit Population white-winged dove abundance in spring, 1968-2024.
Year Index L95%CI U95%CI M3yr M3yrL95%CI M3yrU95%CI
1968 71.43 43.19 121.69 NA NA NA
1969 71.01 43.22 120.06 NA NA NA
1970 70.72 43.43 119.06 71.05 43.51 119.29
1971 70.40 43.78 117.71 70.73 43.80 117.94
1972 70.04 43.94 116.79 70.35 43.85 117.51
1973 69.47 43.69 114.68 70.03 44.34 116.12
1974 69.46 44.16 114.12 69.74 44.20 114.45
1975 68.86 43.98 112.18 69.35 44.14 113.44
1976 68.77 44.44 111.25 69.08 44.52 111.76
1977 68.61 44.29 110.10 68.81 44.60 110.78
1978 68.21 44.42 108.68 68.54 44.77 109.53
1979 67.51 44.34 104.83 68.10 44.80 107.27
1980 66.76 44.06 103.09 67.46 44.48 104.78
1981 66.60 44.21 103.16 66.98 44.41 103.26
1982 65.99 43.87 102.53 66.50 44.30 102.60
1983 65.93 44.23 103.06 66.22 44.35 102.49
1984 66.43 44.89 102.82 66.07 44.63 102.06
1985 66.73 45.03 103.35 66.41 45.05 102.40
1986 67.32 45.46 103.45 66.85 45.54 102.91
1987 67.48 45.65 103.40 67.20 45.69 102.74
1988 67.40 45.44 102.62 67.41 45.79 102.88
1989 67.92 46.06 102.94 67.66 46.04 102.62
1990 67.28 45.75 101.73 67.56 46.16 101.85
1991 66.86 45.63 101.34 67.39 46.33 101.52
1992 67.44 46.19 101.16 67.24 46.31 100.67
1993 67.33 46.22 100.76 67.21 46.29 100.19
1994 67.34 46.45 100.31 67.47 46.65 100.20
1995 68.26 47.36 101.73 67.69 47.11 100.39
1996 69.72 48.34 102.82 68.40 47.77 100.89
1997 70.75 49.22 104.27 69.58 48.56 102.30
1998 71.49 49.78 105.00 70.68 49.46 103.69
1999 72.16 50.48 105.84 71.52 50.19 104.44
2000 74.50 52.20 109.71 72.75 51.15 106.05
2001 75.35 52.93 111.77 74.09 52.28 108.31
2002 76.05 53.18 112.41 75.38 53.01 110.76
2003 75.21 52.59 111.30 75.52 53.07 111.44
2004 74.94 52.23 110.92 75.49 52.90 111.48
2005 74.39 51.80 110.39 74.88 52.46 110.34
2006 73.90 51.30 109.48 74.42 52.16 110.01
2007 73.53 51.33 109.11 73.95 51.81 109.41
2008 73.53 51.11 109.16 73.65 51.72 108.95
2009 72.38 50.23 107.41 73.23 51.20 108.48
2010 69.91 48.93 103.94 72.00 50.24 106.54
2011 69.00 48.18 102.36 70.46 49.59 103.64
2012 68.28 47.52 101.64 69.14 48.53 102.14
2013 66.85 46.41 99.51 68.13 47.77 100.68
2014 66.32 46.32 98.57 67.27 47.15 99.19
2015 65.79 45.94 97.55 66.30 46.59 97.98
2016 64.76 45.17 95.99 65.62 46.13 96.76
2017 65.02 45.66 96.63 65.18 45.91 96.09
2018 65.85 45.88 98.05 65.34 45.86 96.45
2019 66.51 46.01 99.20 65.88 46.06 97.35
2020 68.35 46.85 102.45 67.01 46.55 99.31
2021 70.17 48.18 105.31 68.51 47.38 101.98
2022 72.66 49.48 110.58 70.39 48.48 105.70
2023 74.38 49.94 114.49 72.47 49.50 110.01
2024 75.12 50.38 117.92 74.05 50.31 113.80

Figure 34: Western Management Unit Population white-winged dove abundance (index) in spring. Circles are annual estimates of abundance (index) with 95% confidence intervals. The red line is a moving 3-year average with 70% confidence intervals and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. red dashed reference lines represent threshold values in the harvest strategy decision and the red reference line is the closure threshold.
Time series statistics
Parameter Estimate SE L95%CI U95%CI
1-year index 75.12 50.38 117.92
3-year indexa 74.05 50.31 113.80
LTA 69.45
Objective 50.00
% change from LTA 8.16
% change from obj 48.10
Mgmt index (n years) 3.00
a 2022, 2023, 2024

Harvest Strategy
Management index: Total white-winged doves per route in spring.

Management thresholds:
≥34.0 Standard
≥20.4 Restrictive
≥13.6 Very Restrictive
Closed

Management prescription: Standard.

Regulatory alternatives:
Standard
Season length is 60 days, bracket dates are September 1 and January 15, and the daily bag limit is 15 doves in the aggregate
Restrictive
Season length is 60 days, bracket dates are September 1 and January 15, and the daily bag limit is 10 doves in the aggregate
Very restrictive
Season length is 60 days, bracket dates are September 1 and January 15, and the daily bag limit is 2 doves in the aggregate

The harvest strategy is based on the lower 70% credible interval of the most recent moving 3-year average abundance, which corresponds to 85% of the distribution above the lower 70% credible interval. Threshold values for each alternative are based on the percentage (≥50%, ≥30%, and ≥20% of the long-term average index of abundance modeled from BBS data for white-winged doves in the WMU during 1968–2022 (about 67.993).

The most liberal open season alternative is prescribed when 85% confidence (lower 70% credible interval) in the most recent moving 3-year average BBS index is above the threshold. A closed season is prescribed when either the above conditions for an open season are not met or when the season for the Western Management Unit Population of mourning doves is closed.

Figure 35: White-winged dove abundance (index) in spring in Arizona. Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Figure 36: White-winged dove abundance (index) in spring in California. Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 24a: American Coot

Original data source: North American Breeding Bird Survey; U.S. Geological Survey. Data maintained by U.S. Geological Survey.

Provided in the table below are estimated abundance (Index, birds per route) and lower and upper 95% credible intervals (L95%CI, U95%CI) of American coots in spring in the United States (BBS Core area). Also provided is the abundance moving 3-year average (M3yr).

Table 24a. American coot abundance in spring, 1968-2024.
Year Index L95%CI U95%CI M3yr
1966 3.46 1.65 12.67 NA
1967 2.99 1.77 6.74 NA
1968 2.25 1.41 4.86 2.90
1969 2.74 1.76 5.21 2.66
1970 2.19 1.44 3.90 2.39
1971 2.45 1.61 4.27 2.46
1972 2.61 1.73 4.40 2.42
1973 2.49 1.67 4.09 2.52
1974 2.52 1.67 4.24 2.54
1975 2.70 1.73 4.68 2.57
1976 2.60 1.71 4.37 2.60
1977 2.27 1.58 3.76 2.52
1978 3.17 2.14 5.10 2.68
1979 3.70 2.44 6.09 3.05
1980 2.50 1.79 3.67 3.12
1981 2.37 1.69 3.59 2.86
1982 3.04 2.16 4.60 2.64
1983 3.21 2.28 4.81 2.87
1984 3.69 2.49 5.89 3.31
1985 3.56 2.39 5.87 3.49
1986 3.04 2.05 5.16 3.43
1987 2.88 1.99 4.65 3.16
1988 2.01 1.40 3.29 2.64
1989 1.57 1.15 2.43 2.15
1990 1.33 0.96 2.21 1.64
1991 1.33 0.94 2.25 1.41
1992 1.33 0.98 1.99 1.33
1993 2.33 1.54 4.12 1.66
1994 3.55 2.37 5.71 2.40
1995 4.84 3.17 7.74 3.57
1996 5.67 3.72 9.03 4.69
1997 5.81 3.85 9.09 5.44
1998 5.43 3.64 8.58 5.64
1999 5.07 3.40 8.01 5.44
2000 3.54 2.40 5.50 4.68
2001 2.75 1.89 4.15 3.79
2002 2.01 1.38 3.04 2.76
2003 1.35 0.99 1.94 2.03
2004 1.33 0.96 1.95 1.56
2005 1.20 0.88 1.81 1.29
2006 1.30 0.93 2.14 1.28
2007 2.17 1.46 3.48 1.56
2008 2.04 1.38 3.23 1.84
2009 2.74 1.84 4.27 2.32
2010 3.12 2.09 4.86 2.63
2011 2.90 1.93 4.53 2.92
2012 2.21 1.51 3.36 2.75
2013 2.70 1.79 4.32 2.61
2014 2.13 1.45 3.28 2.35
2015 1.74 1.22 2.59 2.19
2016 1.20 0.88 1.70 1.69
2017 1.18 0.87 1.66 1.37
2018 1.52 1.09 2.18 1.30
2019 1.81 1.25 2.78 1.50
2020 1.50 0.93 2.88 1.61
2021 1.24 0.85 1.89 1.52
2022 1.55 1.04 2.43 1.43
2023 1.45 0.98 2.29 1.42
2024 1.40 0.95 2.15 1.47

Figure 37: American coot abundance (index) in the United States in spring. Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.
Time series statistics
Parameter Estimate SE L95%CI U95%CI
1-year index 1.40 0.95 2.15
3-year indexa 1.47
LTA 2.58
Objective
% change from LTA -45.68
% change from obj
Mgmt index (n years) 1.00
a 2022, 2023, 2024

Harvest Strategy
Management index: American coots per route in spring.

Management thresholds: N/A.

Management prescription: N/A.

Regulatory alternatives:
Fixed until changed.

Data Table 24b: Wilson’s Snipe

Original data source: North American Breeding Bird Survey; U.S. Geological Survey. Data maintained by U.S. Geological Survey.

Provided in the table below are estimated abundance (Index, birds per route) and lower and upper 95% credible intervals (L95%CI, U95%CI) of Wilson’s snipe in spring in the United States (BBS Core area). Also provided is the abundance moving 3-year average (M3yr).

Table 24b. Wilson's snipe abundance in spring, 1968-2024.
Year Index L95%CI U95%CI M3yr
1966 1.56 1.25 1.96 NA
1967 1.53 1.25 1.91 NA
1968 1.54 1.28 1.88 1.54
1969 1.59 1.33 1.91 1.56
1970 1.66 1.40 1.97 1.60
1971 1.70 1.45 2.01 1.65
1972 1.66 1.42 1.95 1.67
1973 1.76 1.52 2.05 1.71
1974 1.92 1.66 2.23 1.78
1975 2.14 1.86 2.49 1.94
1976 1.89 1.65 2.18 1.98
1977 1.84 1.61 2.12 1.96
1978 1.93 1.69 2.23 1.89
1979 2.05 1.80 2.37 1.94
1980 2.00 1.75 2.30 1.99
1981 2.13 1.87 2.46 2.06
1982 2.26 1.98 2.59 2.13
1983 2.33 2.07 2.67 2.24
1984 2.41 2.14 2.75 2.33
1985 2.33 2.06 2.65 2.36
1986 2.18 1.93 2.47 2.31
1987 2.08 1.85 2.36 2.19
1988 1.99 1.77 2.25 2.08
1989 2.01 1.80 2.26 2.03
1990 1.91 1.70 2.16 1.97
1991 1.85 1.65 2.08 1.92
1992 1.81 1.62 2.04 1.86
1993 1.89 1.70 2.13 1.85
1994 1.92 1.72 2.16 1.87
1995 1.96 1.76 2.20 1.92
1996 2.02 1.81 2.27 1.96
1997 2.18 1.95 2.46 2.05
1998 2.25 2.01 2.54 2.15
1999 2.37 2.11 2.67 2.26
2000 2.27 2.02 2.55 2.29
2001 2.26 2.02 2.55 2.30
2002 2.20 1.96 2.49 2.24
2003 2.10 1.88 2.36 2.18
2004 2.10 1.88 2.38 2.13
2005 2.05 1.83 2.32 2.08
2006 1.88 1.68 2.12 2.01
2007 1.98 1.77 2.23 1.97
2008 1.95 1.75 2.20 1.94
2009 1.92 1.71 2.16 1.95
2010 2.16 1.92 2.47 2.01
2011 2.19 1.92 2.53 2.09
2012 1.90 1.67 2.19 2.08
2013 2.13 1.86 2.48 2.07
2014 2.19 1.91 2.57 2.07
2015 2.02 1.77 2.36 2.11
2016 1.87 1.66 2.16 2.03
2017 1.81 1.61 2.08 1.90
2018 1.94 1.72 2.22 1.88
2019 2.16 1.90 2.49 1.97
2020 1.89 1.62 2.27 2.00
2021 1.67 1.47 1.90 1.90
2022 1.91 1.67 2.22 1.82
2023 1.78 1.56 2.06 1.78
2024 1.81 1.58 2.10 1.83

Figure 38: Wilson’s snipe abundance (index) in the United States in spring. Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.
Time series statistics
Parameter Estimate SE L95%CI U95%CI
1-year index 1.81 1.58 2.1
3-year indexa 1.83
LTA 1.98
Objective
% change from LTA -8.77
% change from obj
Mgmt index (n years) 1.00
a 2022, 2023, 2024

Harvest Strategy
Management index: Wilson’s snipe per route in spring.

Management thresholds: N/A.

Management prescription: N/A.

Regulatory alternatives:
Fixed until changed.

Data Table 24c: Virginia Rail

Original data source: North American Breeding Bird Survey; U.S. Geological Survey. Data maintained by U.S. Geological Survey.

Provided in the table below are estimated abundance (Index, birds per route) and lower and upper 95% credible intervals (L95%CI, U95%CI) of Virginia rails in spring in the United States (BBS Core area). Also provided is the abundance moving 3-year average (M3yr).

Table 24c. Virginia rail abundance in spring, 1968-2024.
Year Index L95%CI U95%CI M3yr
1966 0.02 0.01 0.04 NA
1967 0.02 0.01 0.03 NA
1968 0.02 0.01 0.03 0.02
1969 0.02 0.02 0.03 0.02
1970 0.02 0.02 0.03 0.02
1971 0.02 0.02 0.03 0.02
1972 0.02 0.02 0.03 0.02
1973 0.02 0.02 0.03 0.02
1974 0.02 0.01 0.03 0.02
1975 0.02 0.01 0.03 0.02
1976 0.02 0.01 0.02 0.02
1977 0.02 0.01 0.02 0.02
1978 0.02 0.01 0.02 0.02
1979 0.02 0.01 0.02 0.02
1980 0.02 0.01 0.02 0.02
1981 0.02 0.01 0.02 0.02
1982 0.02 0.01 0.02 0.02
1983 0.02 0.01 0.02 0.02
1984 0.02 0.01 0.02 0.02
1985 0.02 0.01 0.02 0.02
1986 0.01 0.01 0.02 0.02
1987 0.01 0.01 0.02 0.01
1988 0.01 0.01 0.02 0.01
1989 0.01 0.01 0.02 0.01
1990 0.02 0.01 0.02 0.01
1991 0.02 0.01 0.02 0.02
1992 0.02 0.01 0.02 0.02
1993 0.02 0.01 0.02 0.02
1994 0.02 0.01 0.02 0.02
1995 0.02 0.02 0.02 0.02
1996 0.02 0.02 0.03 0.02
1997 0.02 0.02 0.03 0.02
1998 0.02 0.02 0.03 0.02
1999 0.02 0.02 0.03 0.02
2000 0.02 0.02 0.03 0.02
2001 0.02 0.02 0.03 0.02
2002 0.02 0.02 0.03 0.02
2003 0.02 0.02 0.03 0.02
2004 0.02 0.02 0.03 0.02
2005 0.02 0.02 0.03 0.02
2006 0.02 0.02 0.03 0.02
2007 0.02 0.02 0.03 0.02
2008 0.02 0.02 0.03 0.02
2009 0.02 0.02 0.03 0.02
2010 0.03 0.02 0.03 0.02
2011 0.03 0.02 0.04 0.02
2012 0.03 0.02 0.04 0.03
2013 0.03 0.02 0.05 0.03
2014 0.04 0.03 0.05 0.03
2015 0.03 0.02 0.05 0.03
2016 0.02 0.02 0.03 0.03
2017 0.02 0.02 0.03 0.03
2018 0.02 0.02 0.03 0.02
2019 0.02 0.02 0.03 0.02
2020 0.02 0.02 0.03 0.02
2021 0.02 0.02 0.03 0.02
2022 0.02 0.02 0.03 0.02
2023 0.02 0.02 0.03 0.02
2024 0.02 0.02 0.03 0.02

Figure 39: Virginia rail abundance (index) in the United States in spring. Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.
Time series statistics
Parameter Estimate SE L95%CI U95%CI
1-year index 0.02 0.02 0.03
3-year indexa 0.02
LTA 0.02
Objective
% change from LTA 17.73
% change from obj
Mgmt index (n years) 1.00
a 2022, 2023, 2024

Harvest Strategy
Management index: Virginia rails per route in spring.

Management thresholds: N/A.

Management prescription: N/A.

Regulatory alternatives:
Fixed until changed.

Data Table 24d: Sora

Original data source: North American Breeding Bird Survey; U.S. Geological Survey. Data maintained by U.S. Geological Survey.

Provided in the table below are estimated abundance (Index, birds per route) and lower and upper 95% credible intervals (L95%CI, U95%CI) of sora in spring in the United States (BBS Core area). Also provided is the abundance moving 3-year average (M3yr).

Table 24d. Sora abundance in spring, 1968-2024.
Year Index L95%CI U95%CI M3yr
1966 0.27 0.16 0.92 NA
1967 0.24 0.17 0.40 NA
1968 0.32 0.22 0.50 0.28
1969 0.32 0.23 0.49 0.29
1970 0.28 0.20 0.42 0.31
1971 0.33 0.24 0.49 0.31
1972 0.45 0.32 0.67 0.35
1973 0.29 0.22 0.41 0.36
1974 0.31 0.23 0.45 0.35
1975 0.36 0.25 0.56 0.32
1976 0.20 0.15 0.27 0.29
1977 0.19 0.15 0.26 0.25
1978 0.25 0.19 0.34 0.21
1979 0.24 0.19 0.33 0.23
1980 0.24 0.19 0.32 0.24
1981 0.26 0.20 0.35 0.25
1982 0.30 0.23 0.41 0.27
1983 0.30 0.23 0.40 0.28
1984 0.37 0.28 0.51 0.32
1985 0.30 0.23 0.41 0.32
1986 0.29 0.23 0.39 0.32
1987 0.31 0.24 0.43 0.30
1988 0.19 0.15 0.24 0.27
1989 0.17 0.14 0.21 0.22
1990 0.19 0.15 0.24 0.18
1991 0.20 0.16 0.26 0.19
1992 0.22 0.18 0.28 0.20
1993 0.43 0.33 0.58 0.28
1994 0.69 0.50 0.96 0.45
1995 0.89 0.65 1.23 0.67
1996 0.53 0.40 0.72 0.70
1997 0.50 0.38 0.69 0.64
1998 0.43 0.32 0.57 0.49
1999 0.49 0.37 0.67 0.47
2000 0.33 0.26 0.44 0.42
2001 0.29 0.23 0.38 0.37
2002 0.24 0.19 0.31 0.29
2003 0.25 0.20 0.33 0.26
2004 0.26 0.20 0.36 0.25
2005 0.28 0.21 0.38 0.27
2006 0.22 0.17 0.28 0.25
2007 0.42 0.32 0.56 0.30
2008 0.28 0.23 0.36 0.31
2009 0.59 0.43 0.82 0.43
2010 0.63 0.47 0.86 0.50
2011 0.52 0.39 0.70 0.58
2012 0.28 0.22 0.37 0.48
2013 0.50 0.37 0.69 0.43
2014 0.52 0.39 0.71 0.43
2015 0.51 0.39 0.68 0.51
2016 0.26 0.21 0.33 0.43
2017 0.23 0.19 0.30 0.33
2018 0.36 0.28 0.46 0.28
2019 0.85 0.65 1.15 0.48
2020 0.41 0.25 0.83 0.54
2021 0.22 0.17 0.29 0.50
2022 0.49 0.36 0.67 0.37
2023 0.60 0.44 0.84 0.44
2024 0.49 0.36 0.69 0.53

Figure 40: Sora abundance (index) in the United States in spring. Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.
Time series statistics
Parameter Estimate SE L95%CI U95%CI
1-year index 0.49 0.36 0.69
3-year indexa 0.53
LTA 0.36
Objective
% change from LTA 35.54
% change from obj
Mgmt index (n years) 1.00
a 2022, 2023, 2024

Harvest Strategy
Management index: Sora per route in spring.

Management thresholds: N/A.

Management prescription: N/A.

Regulatory alternatives:
Fixed until changed.

Data Table 24e: Common Gallinule

Original data source: North American Breeding Bird Survey; U.S. Geological Survey. Data maintained by U.S. Geological Survey.

Provided in the table below are estimated abundance (Index, birds per route) and lower and upper 95% credible intervals (L95%CI, U95%CI) of common gallinules in spring in the United States (BBS Core area). Also provided is the abundance moving 3-year average (M3yr).

Table 24e. Common gallinule abundance in spring, 1968-2024.
Year Index L95%CI U95%CI M3yr
1966 0.38 0.21 0.75 NA
1967 0.37 0.21 0.69 NA
1968 0.35 0.21 0.65 0.37
1969 0.37 0.23 0.66 0.36
1970 0.40 0.24 0.69 0.37
1971 0.40 0.24 0.69 0.39
1972 0.40 0.24 0.71 0.40
1973 0.41 0.25 0.71 0.40
1974 0.44 0.27 0.76 0.42
1975 0.47 0.29 0.82 0.44
1976 0.45 0.27 0.78 0.45
1977 0.44 0.27 0.78 0.45
1978 0.49 0.30 0.86 0.46
1979 0.60 0.37 1.04 0.51
1980 0.66 0.41 1.13 0.59
1981 0.67 0.42 1.13 0.65
1982 0.69 0.44 1.14 0.67
1983 0.76 0.48 1.27 0.71
1984 0.71 0.45 1.18 0.72
1985 0.64 0.41 1.05 0.71
1986 0.61 0.40 0.98 0.65
1987 0.57 0.38 0.89 0.61
1988 0.53 0.36 0.81 0.57
1989 0.50 0.34 0.76 0.53
1990 0.46 0.31 0.70 0.50
1991 0.48 0.32 0.73 0.48
1992 0.51 0.35 0.78 0.48
1993 0.51 0.35 0.78 0.50
1994 0.50 0.34 0.75 0.51
1995 0.51 0.35 0.78 0.51
1996 0.55 0.38 0.82 0.52
1997 0.52 0.36 0.77 0.53
1998 0.50 0.34 0.75 0.52
1999 0.44 0.31 0.66 0.49
2000 0.38 0.26 0.58 0.44
2001 0.35 0.24 0.53 0.39
2002 0.34 0.23 0.52 0.36
2003 0.39 0.27 0.60 0.36
2004 0.45 0.31 0.70 0.40
2005 0.49 0.33 0.74 0.44
2006 0.45 0.31 0.67 0.46
2007 0.38 0.26 0.57 0.44
2008 0.30 0.21 0.46 0.38
2009 0.27 0.18 0.42 0.32
2010 0.30 0.20 0.47 0.29
2011 0.28 0.19 0.44 0.29
2012 0.29 0.19 0.45 0.29
2013 0.29 0.19 0.47 0.29
2014 0.31 0.21 0.49 0.30
2015 0.33 0.22 0.52 0.31
2016 0.39 0.26 0.61 0.34
2017 0.44 0.29 0.72 0.39
2018 0.42 0.28 0.68 0.42
2019 0.39 0.26 0.66 0.42
2020 0.38 0.24 0.69 0.40
2021 0.38 0.24 0.70 0.38
2022 0.40 0.25 0.79 0.39
2023 0.41 0.25 0.82 0.40
2024 0.45 0.27 0.92 0.42

Figure 41: Common gallinule abundance (index) in the United States in spring. Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.
Time series statistics
Parameter Estimate SE L95%CI U95%CI
1-year index 0.45 0.27 0.92
3-year indexa 0.42
LTA 0.45
Objective
% change from LTA 0.35
% change from obj
Mgmt index (n years) 1.00
a 2022, 2023, 2024

Harvest Strategy
Management index: Common gallinules per route in spring.

Management thresholds: N/A.

Management prescription: N/A.

Regulatory alternatives:
Fixed until changed.

National Harvest Strategies

Data Table 30: Western Mallard

Original data source: Waterfowl Breeding Population and Habitat Survey (WBPHS) and State/Province Breeding Waterfowl Surveys in British Columbia, Washington, Oregon, and California; USFWS Headquarters, Canadian Wildlife Service Pacific and Yukon and Region, Washington, Oregon, and California. Data maintained by the USFWS Pacific Flyway Office.

Provided in the table below are estimated abundance and standard error (SE) of Western Population mallards (Wmal) in spring. For purposes of the assessment, Western Population mallards consist of two segments: Northern Pacific Flyway (NPF) segment are those breeding in Alaska and Yukon Territory (Federal WBPHS strata 1–12) and Southern Pacific Flyway segment (SPF) are those breeding in the southern Pacific Flyway including California, Oregon, Washington, and British Columbia (State and Provincial surveys). See Table 70 for State and Province totals. Also provided are the abundance moving 3-year average (M3yr) and standard error (SE).

Table 30. Western Population mallard abundance in spring, 1955-2025.
Year NPF NPF.SE SPF SPF.SE Wmal Wmal.SE M3yr M3yr.SE
1955 173,246 62,646 NA NA NA NA NA NA
1956 174,466 61,340 NA NA NA NA NA NA
1957 160,144 23,652 NA NA NA NA NA NA
1958 185,939 29,978 NA NA NA NA NA NA
1959 214,046 23,251 NA NA NA NA NA NA
1960 159,377 17,771 NA NA NA NA NA NA
1961 284,998 34,286 NA NA NA NA NA NA
1962 171,743 16,124 NA NA NA NA NA NA
1963 208,939 24,145 NA NA NA NA NA NA
1964 106,147 12,464 NA NA NA NA NA NA
1965 189,593 26,776 NA NA NA NA NA NA
1966 128,491 16,033 NA NA NA NA NA NA
1967 256,758 28,976 NA NA NA NA NA NA
1968 240,929 30,431 NA NA NA NA NA NA
1969 162,856 20,916 NA NA NA NA NA NA
1970 293,897 33,743 NA NA NA NA NA NA
1971 167,149 22,944 NA NA NA NA NA NA
1972 261,877 27,983 NA NA NA NA NA NA
1973 245,252 26,086 NA NA NA NA NA NA
1974 278,242 31,209 NA NA NA NA NA NA
1975 132,692 16,419 NA NA NA NA NA NA
1976 181,397 23,836 NA NA NA NA NA NA
1977 459,778 55,724 NA NA NA NA NA NA
1978 318,842 36,342 NA NA NA NA NA NA
1979 275,779 36,047 NA NA NA NA NA NA
1980 399,102 39,399 NA NA NA NA NA NA
1981 476,251 48,716 NA NA NA NA NA NA
1982 254,727 29,708 NA NA NA NA NA NA
1983 321,687 28,506 NA NA NA NA NA NA
1984 504,182 52,275 NA NA NA NA NA NA
1985 219,055 24,633 NA NA NA NA NA NA
1986 233,539 26,196 NA NA NA NA NA NA
1987 185,802 19,422 NA NA NA NA NA NA
1988 356,711 36,604 NA NA NA NA NA NA
1989 411,507 34,261 NA NA NA NA NA NA
1990 366,933 37,017 NA NA NA NA NA NA
1991 385,319 36,279 NA NA NA NA NA NA
1992 345,708 38,708 NA NA NA NA NA NA
1993 282,983 29,533 NA NA NA NA NA NA
1994 350,875 37,142 NA NA NA NA NA NA
1995 524,200 67,975 NA NA NA NA NA NA
1996 522,006 43,552 NA NA NA NA NA NA
1997 584,247 51,997 NA NA NA NA NA NA
1998 836,216 67,284 NA NA NA NA NA NA
1999 713,054 69,568 NA NA NA NA NA NA
2000 770,333 52,159 NA NA NA NA NA NA
2001 718,286 54,127 NA NA NA NA NA NA
2002 667,339 50,687 NA NA NA NA NA NA
2003 843,497 66,823 NA NA NA NA NA NA
2004 811,135 63,878 NA NA NA NA NA NA
2005 703,140 54,748 NA NA NA NA NA NA
2006 515,821 46,935 NA NA NA NA NA NA
2007 581,493 55,053 NA NA NA NA NA NA
2008 532,414 46,797 NA NA NA NA NA NA
2009 502,970 44,896 NA NA NA NA NA NA
2010 605,556 53,070 608,696 57,240 1,214,252 78,056 NA NA
2011 415,825 38,767 517,373 46,700 933,198 60,695 NA NA
2012 505,583 51,067 640,892 56,284 1,146,475 75,998 1,097,975 72,001
2013 338,379 38,215 540,322 53,973 878,701 66,132 986,125 67,904
2014 500,879 57,351 492,901 56,628 993,781 80,596 1,006,319 74,487
2015 470,915 50,867 429,020 31,574 899,936 59,870 924,139 69,411
2016 584,200 65,389 484,975 37,319 1,069,175 75,289 987,630 72,454
2017 538,451 51,882 444,400 34,592 982,851 62,357 983,987 66,184
2018 450,750 45,061 574,251 45,055 1,025,001 63,722 1,025,676 67,372
2019 361,060 35,347 525,595 35,895 886,655 50,377 964,836 59,123
2020 NA NA NA NA NA NA NA NA
2021 NA NA NA NA NA NA NA NA
2022 614,444 69,816 427,037 31,955 1,041,481 76,782 984,379 64,533
2023 380,917 42,110 443,463 31,779 824,380 52,756 917,505 61,146
2024 506,629 57,471 431,910 25,726 938,539 62,966 934,800 64,919
2025 389,414 44,835 503,499 41,142 892,913 60,851 885,277 59,022

Figure 42: Western Population mallard abundance in spring. Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.
Time series statistics
Parameter Estimate SE L95%CI U95%CI
1-year index 892,913 60,851 773,646 1,012,180
3-year indexa 885,277 59,022 769,595 1,000,960
LTA 987,263
Objective
% change from LTA -10
% change from obj
Mgmt index (n years) 1
a 2023, 2024, 2025

Figure 43: Western Population mallard Northern Pacific Flyway segment abundance in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Figure 44: Western Population mallard Southern Pacific Flyway segment abundance in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Harvest Strategy
Management index: Western Population Mallards in Northern and Southern Pacific Flyway segments in spring.

Management thresholds:
Liberal
Moderate
Restrictive
Closed
See the Adaptive Harvest Management (AHM) report for the derived threshold values based on the decision framework for western mallards.

Management prescription: See the AHM report for the decision based on the decision framework for western mallards.

Regulatory alternatives:
Liberal
Season length is 107 days, bracket dates are Saturday nearest September 24 and January 31, and the daily bag limit is 7 ducks (no more than 2 female mallards)
Moderate
Season length is 86 days, bracket dates are Saturday nearest September 24 and January 31, and the daily bag limit is 7 ducks (no more than 5 mallards, 2 female)
Restrictive
Season length is 60 days, bracket dates are Saturday nearest October 1 and January 31, and the daily bag limit is 4 ducks (no more than 3 mallards, 1 female)
Closed

Other Duck Species of Special Concern

National harvest strategies exist for duck species of special management concern including northern pintail, scaup, and canvasbacks. See Adaptive Harvest Management (AHM) report for decisions based on decision frameworks for northern pintail and scaup. Also, see the abundance time series for these species in the Waterfowl Breeding Population and Habitat Survey and State/Province Breeding Waterfowl Surveys data tables. The decision for scaup is based on a decision support tool. See the next table for the canvasback decision.

Data Table 31: Canvasback

Original data source: Waterfowl Breeding Population and Habitat Survey (WBPHS) Traditional Survey Area; USFWS Headquarters.

Provided in the table below are estimated abundance (Estimate) and standard error (SE) of canvasbacks in spring. Also provided are the abundance moving 3-year average (M3yr) and standard error (M3yr.SE).

Table 31. Canvasback abundance in spring, 1955-2025.
Year Estimate SE M3yr M3yr.SE
1955 589,257 87,849 NA NA
1956 698,509 93,324 NA NA
1957 626,072 94,732 637,946 92,016
1958 746,830 96,139 690,471 94,739
1959 488,684 50,588 620,529 83,219
1960 605,698 82,438 613,737 78,736
1961 435,251 65,676 509,877 67,499
1962 360,238 43,836 467,062 65,906
1963 506,235 74,904 433,908 62,837
1964 643,636 126,904 503,370 88,763
1965 522,120 52,816 557,330 90,378
1966 663,114 78,043 609,623 91,259
1967 502,576 45,359 562,603 60,381
1968 563,691 101,260 576,460 78,319
1969 503,530 53,696 523,266 71,167
1970 580,100 90,426 549,107 84,288
1971 450,674 55,188 511,435 68,571
1972 425,912 45,959 485,562 66,670
1973 620,451 89,070 499,012 66,059
1974 512,842 56,820 519,735 66,519
1975 595,098 56,065 576,130 69,054
1976 614,389 70,064 574,110 61,321
1977 664,042 74,860 624,510 67,469
1978 373,174 41,492 550,535 63,861
1979 582,004 59,814 539,740 60,286
1980 734,570 83,764 563,249 64,072
1981 620,843 59,108 645,805 68,527
1982 513,265 50,928 622,893 66,090
1983 526,612 58,865 553,573 56,429
1984 530,129 60,150 523,335 56,794
1985 375,929 42,945 477,556 54,551
1986 438,350 41,537 448,136 48,947
1987 450,109 77,894 421,462 56,678
1988 435,048 40,221 441,169 56,008
1989 477,439 48,410 454,198 57,818
1990 539,318 60,326 483,935 50,334
1991 491,151 66,363 502,636 58,841
1992 481,529 97,303 503,999 76,401
1993 472,055 67,642 481,578 78,416
1994 525,604 71,113 493,063 79,792
1995 770,593 92,161 589,417 77,731
1996 848,487 118,334 714,894 95,836
1997 688,754 57,161 769,278 92,671
1998 685,862 63,795 741,034 84,341
1999 716,039 79,121 696,885 67,323
2000 706,754 80,997 702,885 75,034
2001 579,826 52,652 667,539 72,094
2002 486,597 43,819 591,059 61,245
2003 557,575 47,984 541,332 48,286
2004 617,227 64,553 553,800 52,882
2005 520,574 52,945 565,125 55,596
2006 691,013 69,616 609,605 62,761
2007 864,924 86,197 692,170 70,898
2008 488,667 45,378 681,535 69,127
2009 662,135 57,448 671,909 65,293
2010 585,164 50,828 578,655 51,455
2011 691,560 45,987 646,286 51,635
2012 759,935 68,515 678,886 55,954
2013 786,978 57,583 746,158 58,095
2014 685,262 50,702 744,058 59,388
2015 757,281 63,279 743,174 57,419
2016 736,472 68,750 726,338 61,377
2017 732,531 61,685 742,095 64,642
2018 686,084 59,125 718,362 63,318
2019 651,925 49,085 690,180 56,892
2020 NA NA NA NA
2021 NA NA NA NA
2022 586,643 50,570 641,551 53,111
2023 618,898 63,898 619,156 54,923
2024 566,319 52,274 590,620 55,895
2025 686,805 59,562 624,007 58,774

Figure 45: Canvasback abundance in spring. Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average. The red dashed reference line is the restriction threshold in the harvest strategy decision (also the minumum population objective). The red reference line is the closure threshold.
Time series statistics
Parameter Estimate SE L95%CI U95%CI
1-year index 686,805 59,562 570,063 803,546
3-year indexa 624,007 58,774 508,810 739,205
LTA 591,414
Objective 480,000
% change from LTA 16
% change from obj 43
Mgmt index (n years) 1
a 2023, 2024, 2025

Harvest Strategy
Management index: Canvasbacks in spring.

Management thresholds:
≥480,000 Liberal 2
≥460,000 Liberal 1
Closed

Management prescription: Liberal 2.

Regulatory alternatives:
Season length and outside dates based on duck AHM
Liberal 2
Daily bag limit 2
Liberal 1
Daily bag limit 1
Closed

Following the adoption of SEIS 2013 (Department of the Interior 2013), a decision support tool for canvasback harvest management was developed. The decision rules under this prescriptive strategy provide that if the canvasback breeding population (BPOP) in year t is 480,000 or above, the year t+1 regulations will be a Liberal 2 (daily bag limit of 2 canvasbacks). If the canvasback BPOP is 460,000 to 479,999, a Liberal 1 (daily bag limit of 1 canvasback), and the season is closed when BPOP is less than 460,000. The prescription is based on point estimates and does not take the variance of BPOP estimates into account.

Harvest

Data Table 40: Swan

Original data source: Pacific Flyway Cooperative Swan Hunting Season Harvest Survey. Data maintained by Idaho, Montana, Nevada, Utah, and USFWS Pacific Flyway Office.

Provided in the table below are swan hunting season hunter compliance rates by State (Idaho, Montana, Nevada, and Utah) in completing the hunter questionnaire (Qcomp) and submitting parts for species identification of harvested swans (Pcomp).

Table 40a. Swan hunting season hunter compliance rates, 1995-2024.
Season ID.Qcomp ID.Pcomp MT.Qcomp MT.Pcomp NV.Qcomp NV.Pcomp UT.Qcomp UT.Pcomp
1995 NA NA NA NA 0.96 0.96 0.51 0.51
1996 NA NA NA NA 0.94 0.94 0.57 0.57
1997 NA NA NA NA 0.90 0.90 0.51 0.51
1998 NA NA NA NA 0.89 0.89 0.56 0.56
1999 NA NA NA NA 0.91 0.91 0.55 0.55
2000 NA NA 0.81 0.93 0.91 0.91 0.83 0.83
2001 NA NA NA NA 0.93 0.93 0.92 0.92
2002 NA NA 0.82 0.85 0.89 0.89 0.88 0.88
2003 NA NA 0.73 0.77 0.91 0.91 0.96 0.96
2004 NA NA 0.76 0.80 0.93 0.93 0.93 0.93
2005 NA NA 0.82 0.81 0.92 0.92 0.87 0.87
2006 NA NA 0.81 0.80 0.95 0.95 0.90 0.90
2007 NA NA 0.78 0.80 0.92 0.92 0.88 0.88
2008 NA NA 0.88 0.88 0.91 0.91 0.89 0.89
2009 NA NA 0.73 0.83 0.89 0.89 0.97 0.97
2010 NA NA 0.74 0.83 0.96 0.96 0.96 0.96
2011 NA NA 0.76 0.83 0.94 0.94 0.96 0.96
2012 NA NA 0.86 0.80 0.96 0.96 0.94 0.94
2013 NA NA 0.83 0.81 0.93 0.93 0.96 0.96
2014 NA NA 0.81 0.85 0.93 0.97 0.94 0.95
2015 NA NA 0.81 0.87 0.94 0.94 0.94 0.94
2016 NA NA 0.87 0.84 0.91 0.95 0.94 0.94
2017 NA NA 0.84 0.85 0.94 0.94 0.94 0.94
2018 NA NA 0.82 0.76 0.96 0.91 0.95 0.95
2019 NA NA 0.90 0.88 0.93 0.93 0.95 0.95
2020 0.84 0.84 0.83 0.77 0.96 0.96 0.95 0.95
2021 0.92 0.92 0.81 0.70 0.94 0.94 0.92 0.92
2022 0.93 0.93 0.86 0.74 0.93 0.90 0.97 0.97
2023 0.86 0.86 0.76 0.65 0.93 0.93 0.95 0.95
2024 0.89 0.89 0.86 0.81 0.95 0.94 0.97 0.97
Table 40b. Swan hunting season harvest by State (Idaho, Montana, Nevada, and Utah) and in total reported for total swan harvest (Harv) and trumpeter swan harvest (Trum), 1995-2024.
Season ID.Harv ID.Trum MT.Harv MT.Trum NV.Harv NV.Trum UT.Harv UT.Trum Harv Trum
1995 NA NA NA NA 72 0 683 6 755 6
1996 NA NA NA NA 119 1 1,578 12 1,697 13
1997 NA NA NA NA 131 0 1,371 6 1,502 6
1998 NA NA NA NA 185 0 2,041 2 2,226 2
1999 NA NA NA NA 212 0 1,565 0 1,777 0
2000 NA NA 217 4 78 0 666 1 961 5
2001 NA NA NA NA 62 0 271 0 333 0
2002 NA NA 167 4 45 0 548 2 760 6
2003 NA NA 119 4 78 0 796 2 993 6
2004 NA NA 255 8 83 0 657 2 995 10
2005 NA NA 284 17 100 0 899 1 1,284 18
2006 NA NA 169 9 155 1 904 2 1,228 12
2007 NA NA 306 10 217 0 884 0 1,407 10
2008 NA NA 199 1 136 0 731 1 1,066 2
2009 NA NA 292 12 56 0 812 2 1,161 14
2010 NA NA 209 14 118 0 725 0 1,052 14
2011 NA NA 247 16 144 4 695 3 1,086 23
2012 NA NA 294 35 203 0 929 2 1,426 37
2013 NA NA 239 21 26 0 376 5 641 26
2014 NA NA 167 15 25 0 768 2 960 17
2015 NA NA 264 17 8 0 903 4 1,176 21
2016 NA NA 222 19 127 2 812 4 1,162 26
2017 NA NA 112 6 127 4 833 4 1,072 15
2018 NA NA 121 13 233 0 947 5 1,301 19
2019 NA NA 148 8 228 3 1,188 21 1,564 32
2020 18 1 157 17 266 4 1,350 21 1,791 43
2021 18 12 266 62 126 0 1,072 25 1,482 99
2022 11 2 220 22 149 1 885 22 1,264 47
2023 10 1 136 29 72 0 1,004 0 1,223 30
2024 24 13 129 31 179 0 983 0 1,315 45

Figure 46: Swan hunting season harvest. Circles are annual estimates of total swan harvest. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The other colored lines are swan harvest estimates at the state level (red=idaho, green=Montana, yellow=Nevada, orange=Utah)

Figure 47: Trumpeter swan hunting season harvest. Circles are annual estimates of total trumpwter swan harvest. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The other colored lines are swan harvest estimates at the state level (red=idaho, green=Montana, yellow=Nevada, orange=Utah)

Data Table 41: Sandhill Crane, RMP

Original data source: Pacific and Central Flyways Cooperative Swan Hunting Season Harvest Survey. Data maintained by Arizona, Idaho, Montana, New Mexico, Nevada, Utah, Wyoming, and USFWS Pacific Flyway Office.

Provided in the table (a) below is the difference between hunting season allowable and achieved harvest for Rocky Mountain Population sandhill cranes by State. Note that positive numbers are the additional harvest that is allowed. Calculations are based on the Pacific and Central Flyway Councils’ 2016 harvest strategy, estimates prior to 2016 are not applicable.

Provided in the table (b) below is the hunting season harvest for Rocky Mountain Population sandhill cranes by state (Arizona, Idaho, Montana, New Mexico, Utah, and Wyoming) and in total. For Arizona and New Mexico, the harvest of RMP cranes is derived from the estimates of total crane harvest (Harv) and the proportion that are greater subspecies (Comp) and therefore considered RMP cranes. Crane harvest in other states are assumed to be RMP cranes.

Table 41a. Difference between hunting season allowable and achieved harvest of Rocky Mountain Population sandhill cranes by State (Arizona, Idaho, Montana, New Mexico, Utah, and Wyoming), 2016-2024.
Season AZ ID MT NM UT WY
2016 66 29 254 215 132 30
2017 101 139 317 357 71 48
2018 55 53 271 72 43 22
2019 80 54 136 34 54 28
2020 47 19 155 365 37 54
2021 106 1 298 202 63 95
2022 133 17 361 278 91 71
2023 139 32 353 298 113 111
2024 195 23 421 400 94 56
Table 41b. Harvest of Rocky Mountain Population sandhill cranes by state (Arizona, Idaho, Montana, New Mexico, Utah, and Wyoming) and in total, 1981-2024. Also provided for Arizona and New Mexico are the total sandhill crane harvest (Harv) and composition (Comp) of the crane harvest that are the greater subspecies, which are assigned to RMP crane harvest.
Season AZ.Harv AZ.Comp NM.Harv NM.Comp AZ ID MT NM UT WY Total
1981 42 0.50 NA NA 21 NA NA NA NA NA 21
1982 75 0.12 NA NA 9 NA NA NA NA 143 152
1983 55 0.67 NA NA 37 NA NA NA NA 154 191
1984 71 0.58 NA NA 41 NA NA NA NA 101 142
1985 93 0.45 NA NA 42 NA NA NA NA 138 180
1986 141 0.17 NA NA 24 NA NA NA NA 195 219
1987 194 0.32 NA NA 62 NA NA NA NA 190 252
1988 217 0.18 310 NA 39 NA NA 310 NA 128 477
1989 164 0.28 483 NA 46 NA NA 483 54 125 708
1990 129 0.07 79 NA 9 NA NA 79 35 58 181
1991 220 0.20 47 NA 44 NA NA 47 48 101 240
1992 186 0.21 147 NA 39 NA NA 147 NA 168 354
1993 174 0.35 297 NA 61 NA NA 297 28 115 501
1994 117 0.23 416 NA 27 NA NA 416 34 150 627
1995 157 0.21 415 0.65 33 NA NA 270 27 78 408
1996 142 0.19 311 0.76 27 20 NA 236 32 65 380
1997 200 0.11 158 0.72 22 136 NA 114 30 84 386
1998 154 0.24 237 0.76 37 120 NA 180 34 94 465
1999 117 0.18 300 0.66 21 190 NA 198 54 124 587
2000 206 0.18 362 0.71 37 193 NA 257 69 159 715
2001 186 0.14 400 0.72 26 278 86 288 77 142 897
2002 247 0.17 225 0.73 42 194 47 164 60 132 639
2003 189 0.18 307 0.55 34 146 48 169 57 72 526
2004 200 0.15 344 0.55 30 143 49 189 53 123 587
2005 278 0.18 429 0.55 50 188 46 236 62 116 698
2006 225 0.04 564 0.58 9 236 51 327 87 194 904
2007 331 0.13 600 0.46 43 211 68 276 103 138 839
2008 171 0.14 702 0.54 24 185 83 379 101 162 934
2009 389 0.18 942 0.64 70 254 116 603 149 195 1,387
2010 311 0.18 943 0.58 56 253 98 547 190 182 1,326
2011 189 0.19 916 0.57 36 261 84 522 149 161 1,213
2012 368 0.22 745 0.56 81 275 121 417 91 134 1,119
2013 181 0.21 482 0.50 38 135 83 241 96 74 667
2014 236 0.11 345 0.53 26 134 121 183 73 101 638
2015 353 0.19 279 0.52 67 166 137 145 86 104 705
2016 462 0.16 871 0.52 74 258 140 453 72 158 1,155
2017 486 0.14 880 0.51 68 198 150 449 192 193 1,250
2018 729 0.14 1,059 0.64 102 253 154 678 203 189 1,579
2019 238 0.16 964 0.55 38 166 181 530 130 141 1,186
2020 762 0.09 944 0.18 65 172 148 170 137 114 806
2021 788 0.09 1,066 0.59 68 277 163 629 200 194 1,530
2022 862 0.09 1,060 0.67 74 273 174 710 223 277 1,731
2023 621 0.08 1,083 0.56 51 235 138 607 167 215 1,413
2024 338 0.08 1,134 0.58 28 275 167 663 262 318 1,713

Figure 48: Harvest of Rocky Mountain Population sandhill cranes. Circles are annual estimates of total crane harvest. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The other colored lines are crane harvest estimates at the state level (red=Arizona, green=Idaho, yellow=Montana, orange=New Mexico, black=Utah, brown=Wyoming)

WBPHS and State Surveys

Waterfowl Breeding Population and Habitat Survey strata and transects. Yellow shading is the Traditional Survey Area and green shading is the Eastern Survey Area.


Waterfowl abundance is reported for the Waterfowl Breeding Population and Habitat Survey (WBPHS) Traditional Survey Area (TSA) by crew areas including the following:
TSA = WBPHS Traditional Survey Area
Area 1 = Alaska, Yukon Territory, and Old Crow Flats (strata 1–12)
Area 2 = Central and northern Alberta, northeastern British Columbia, and Northwest Territories (strata 13–18, 20, 77)
Area 3 = Northern Saskatchewan, northern Manitoba, and western Ontario (strata 21–25, 50)
Area 4 = Southern Alberta (strata 26–29, 75–76)
Area 5 = Southern Saskatchewan (strata 30–33)
Area 6 = Southern Manitoba (strata 34–40; includes south east Saskatchewan)
Area 7 = Montana and western Dakotas (strata 41–44)
Area 8 = Eastern Dakotas (strata 45–49)

Total ducks includes the following species:
American black duck, American green-winged teal, American wigeon, bufflehead, blue-winged teal, canvasback, gadwall, goldeneye species, mallard, northern pintail, northern shoveler, redhead, ring-necked duck, ruddy duck, scaup species.

Data Table 50: Total Ducks WBPHS

Original data source: WBPHS Traditional Survey Area; USFWS Headquarters.

Table 50. Total duck abundance in the WBPHS Traditional Survey Area in spring, 1955-2025.
Year TSA Area1 Area2 Area3 Area4 Area5 Area6 Area7 Area8
1955 39,603,569 1,781,205 9,820,018 2,165,884 7,363,576 13,983,983 1,617,779 1,177,235 1,693,888
1956 42,035,155 1,846,837 8,299,825 2,090,767 6,447,961 18,563,185 1,748,982 1,138,961 1,898,638
1957 34,197,095 1,490,530 6,774,797 1,867,203 6,220,527 12,754,231 1,874,560 1,113,830 2,101,418
1958 36,528,121 2,060,836 7,997,576 2,403,474 6,681,567 10,133,574 3,606,569 1,140,353 2,504,173
1959 40,089,890 2,429,972 17,176,163 3,133,781 5,759,959 6,211,575 3,106,009 1,094,046 1,178,385
1960 32,080,543 2,075,147 7,980,953 1,941,253 5,671,430 8,049,952 2,247,490 1,048,601 3,065,717
1961 29,828,978 2,101,221 11,564,207 1,968,630 4,807,274 4,466,700 1,752,580 1,153,162 2,015,204
1962 25,038,942 2,666,148 7,260,882 2,537,393 2,891,506 3,522,171 1,134,443 1,154,308 3,872,091
1963 27,609,452 2,538,138 7,347,403 2,410,629 4,015,320 4,091,997 1,754,439 1,273,947 4,177,579
1964 27,768,809 2,226,857 9,098,950 2,900,610 3,930,618 4,483,980 1,594,665 1,084,123 2,449,006
1965 25,903,106 2,025,075 6,823,654 2,518,205 3,757,129 4,268,854 1,461,923 1,447,870 3,600,396
1966 30,574,173 2,312,224 6,619,374 2,411,187 5,480,219 6,795,588 1,338,609 1,568,801 4,048,172
1967 32,688,565 2,329,222 5,579,444 3,618,173 6,223,747 7,927,195 1,865,001 1,747,121 3,398,662
1968 28,971,228 3,790,406 5,224,957 5,080,270 3,736,829 5,851,232 1,091,939 1,098,795 3,096,800
1969 33,760,876 2,507,773 5,149,542 4,678,368 5,054,735 8,298,588 1,775,385 1,628,321 4,668,164
1970 39,676,260 2,794,433 6,190,441 6,088,106 5,329,228 10,641,506 1,934,865 1,544,328 5,153,353
1971 36,905,073 2,187,506 6,759,669 3,774,895 6,454,811 10,445,035 1,330,553 1,270,102 4,682,502
1972 40,748,019 2,739,500 10,303,503 3,521,004 6,465,629 9,049,652 1,663,689 2,015,201 4,989,841
1973 32,573,897 3,096,160 7,767,893 3,446,557 5,489,452 6,857,063 1,271,985 1,359,603 3,285,184
1974 35,422,489 3,252,310 6,018,714 2,929,500 7,688,200 8,821,911 2,041,640 1,116,650 3,553,564
1975 37,792,799 2,170,021 7,397,431 3,183,012 6,454,469 11,016,392 1,590,331 2,166,383 3,814,761
1976 34,342,263 2,825,936 5,108,722 4,092,149 5,528,392 11,213,039 2,344,794 1,500,742 1,728,489
1977 32,048,956 4,848,057 7,697,788 3,990,003 3,818,760 8,289,366 1,082,410 1,140,415 1,182,158
1978 35,505,581 3,578,654 7,240,370 4,831,954 4,237,070 6,430,252 1,403,330 2,430,990 5,352,961
1979 38,622,013 3,073,537 8,021,969 4,341,131 5,409,235 9,309,080 1,545,777 2,115,463 4,805,822
1980 36,224,430 5,243,392 8,023,785 4,413,909 4,896,556 7,515,613 1,468,737 1,302,711 3,359,727
1981 32,267,288 5,259,379 7,826,380 4,907,962 4,708,515 4,580,525 1,396,068 1,396,426 2,192,033
1982 30,784,023 2,963,122 5,949,994 3,618,890 3,546,487 6,864,099 1,548,574 2,321,410 3,971,447
1983 32,635,210 3,479,605 8,166,925 3,790,236 3,046,925 7,348,757 1,330,724 1,636,801 3,835,236
1984 31,004,936 4,010,391 9,104,394 3,062,498 2,725,719 5,121,916 697,433 1,421,463 4,861,122
1985 25,638,252 2,745,684 5,928,982 3,346,847 3,111,103 5,612,458 947,758 928,175 3,017,245
1986 29,092,808 3,302,250 7,082,048 2,621,948 2,532,809 5,417,332 1,637,296 1,228,761 5,270,364
1987 27,412,109 3,362,563 7,307,102 3,195,228 3,040,816 4,260,117 1,125,964 1,425,872 3,694,447
1988 27,361,744 3,874,899 7,521,558 4,190,233 2,702,537 4,141,494 1,041,408 1,234,803 2,654,812
1989 25,112,754 3,590,758 6,820,218 3,548,835 2,449,654 3,380,651 873,403 1,335,105 3,114,130
1990 25,079,166 3,961,323 5,754,399 3,780,593 3,356,705 4,295,831 1,276,475 1,204,509 1,449,331
1991 26,605,595 4,392,449 5,755,659 4,513,529 3,070,198 4,203,776 984,686 1,323,446 2,361,852
1992 29,417,883 3,691,263 5,749,574 5,721,327 3,108,779 5,671,081 1,533,509 1,304,435 2,637,914
1993 26,312,407 3,635,535 5,918,746 4,577,785 3,443,064 3,576,271 872,589 1,506,031 2,782,386
1994 32,523,459 4,289,209 5,331,221 3,906,556 3,553,162 5,876,881 814,655 2,997,219 5,754,555
1995 35,869,640 4,298,317 5,790,068 3,889,127 3,270,109 6,896,092 1,521,973 2,673,314 7,530,639
1996 37,752,965 4,734,672 4,411,957 3,951,675 3,884,673 9,197,009 1,643,179 2,439,748 7,490,053
1997 42,556,343 4,185,762 6,574,765 3,721,623 3,809,144 10,554,579 1,514,687 4,291,013 7,904,770
1998 39,081,907 5,728,457 6,224,887 3,411,397 3,203,784 8,375,979 1,394,197 2,999,117 7,744,089
1999 43,435,799 5,184,532 8,316,165 3,839,189 3,315,025 9,687,396 1,681,824 2,504,798 8,906,871
2000 41,838,270 6,726,566 6,899,974 3,468,043 3,484,683 7,665,038 1,486,193 1,725,883 10,381,891
2001 36,177,460 6,427,121 5,489,402 2,656,262 2,520,783 6,441,812 1,792,923 1,587,812 9,261,345
2002 31,181,128 4,961,417 6,583,730 4,502,382 2,363,558 3,547,374 1,303,546 1,334,251 6,584,871
2003 36,225,121 5,704,917 6,461,001 3,564,180 2,696,066 9,295,864 1,582,276 1,730,737 5,190,081
2004 32,163,986 5,456,172 5,882,220 4,084,527 2,498,793 5,783,368 1,473,840 1,614,801 5,370,264
2005 31,734,935 5,113,856 4,712,530 3,223,493 3,178,226 7,966,659 1,626,997 1,290,149 4,623,025
2006 36,160,330 4,754,502 5,131,564 2,711,268 4,580,690 10,095,517 1,795,934 1,909,836 5,181,018
2007 41,172,191 5,689,815 6,137,361 3,212,072 4,293,057 11,036,231 1,321,546 1,625,416 7,856,693
2008 37,276,466 5,122,777 6,934,379 3,162,429 4,199,429 8,949,437 1,222,875 1,139,234 6,545,905
2009 42,004,841 4,345,259 6,933,755 3,813,012 3,287,868 8,052,927 1,371,363 2,467,783 11,732,874
2010 40,893,777 5,555,837 8,717,117 2,149,444 2,641,326 6,839,266 1,103,507 1,977,203 11,910,078
2011 45,554,287 3,755,695 7,094,613 2,439,305 4,371,665 10,680,675 1,554,026 3,134,876 12,523,433
2012 48,575,264 4,454,823 8,799,317 2,754,351 4,844,730 11,317,699 1,537,535 2,466,578 12,400,230
2013 45,607,319 3,296,294 8,323,318 3,441,241 4,471,154 12,258,341 1,575,034 1,598,823 10,643,114
2014 49,152,231 3,510,092 9,945,622 2,566,499 5,643,685 12,893,274 2,193,064 3,659,864 8,740,130
2015 49,521,695 3,389,463 11,546,133 3,527,214 5,677,678 13,542,131 1,988,198 2,730,169 7,120,709
2016 48,362,830 4,327,471 14,041,008 3,246,303 5,031,893 10,752,604 1,777,337 2,228,860 6,957,356
2017 47,265,648 3,987,272 11,422,720 2,560,729 6,444,258 12,151,560 1,748,036 2,207,210 6,743,863
2018 41,193,231 3,381,387 9,915,761 3,167,375 5,546,108 8,492,473 1,664,788 2,238,572 6,786,767
2019 38,898,901 2,612,134 10,376,817 2,459,593 4,574,722 6,478,728 1,221,617 2,404,469 8,770,820
2020 NA NA NA NA NA NA NA NA NA
2021 NA NA NA NA NA NA NA NA NA
2022 34,657,152 3,831,208 7,655,881 2,787,804 3,010,156 5,993,794 1,744,351 1,751,357 7,882,601
2023 32,304,811 1,920,220 8,348,241 3,138,551 3,192,097 6,508,003 1,152,187 2,161,328 5,884,185
2024 33,988,082 2,449,405 11,247,646 3,290,379 2,685,942 5,476,463 988,669 1,941,611 5,907,968
2025 33,832,452 2,559,645 10,975,217 2,841,902 3,132,332 6,690,026 1,193,097 1,797,819 4,642,413

Figure 49: Total duck abundance in the WBPHS Traditional Survey Area in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 51: Mallard WBPHS

Original data source: WBPHS Traditional Survey Area; USFWS Headquarters.

Table 51. Mallard abundance in the WBPHS Traditional Survey Area in spring, 1955-2025.
Year TSA Area1 Area2 Area3 Area4 Area5 Area6 Area7 Area8
1955 8,777,294 173,246 1,635,090 738,596 1,906,984 3,317,190 424,781 294,570 286,837
1956 10,452,690 174,466 1,472,958 1,091,637 1,757,634 4,691,429 627,975 305,576 331,015
1957 9,296,888 160,144 1,045,916 712,947 1,986,693 3,987,910 712,945 317,684 372,649
1958 11,234,244 185,939 1,385,330 1,244,572 2,072,202 4,533,958 920,607 352,252 539,384
1959 9,024,288 214,046 2,764,253 1,042,198 1,753,018 2,152,157 545,446 337,137 216,033
1960 7,371,652 159,377 760,753 705,948 1,502,358 2,967,483 526,169 342,753 406,811
1961 7,329,954 284,998 2,303,954 705,114 1,330,884 1,649,689 331,411 348,291 375,614
1962 5,535,905 171,743 1,285,875 883,120 983,105 1,125,920 193,720 386,171 506,251
1963 6,748,828 208,939 1,413,733 682,874 1,227,931 1,551,425 327,684 446,620 889,622
1964 6,063,865 106,147 1,364,808 848,278 1,119,407 1,387,258 418,015 353,541 466,411
1965 5,131,702 189,593 725,018 873,704 893,925 1,069,927 271,519 493,121 614,895
1966 6,731,878 128,491 828,963 706,102 1,546,738 1,975,568 333,193 585,739 627,083
1967 7,509,548 256,758 745,024 1,713,404 1,502,441 1,888,409 289,357 572,270 541,885
1968 7,089,238 240,929 942,097 1,580,498 911,963 2,132,153 197,783 385,147 698,668
1969 7,531,615 162,856 705,811 1,807,774 1,121,447 2,179,962 356,523 588,392 608,850
1970 9,985,873 293,897 941,420 2,299,328 1,594,553 2,945,486 447,844 519,181 944,164
1971 9,416,373 167,149 981,425 1,265,078 1,871,286 3,407,249 288,941 475,317 959,928
1972 9,265,550 261,877 1,435,377 1,059,311 1,825,320 2,711,463 431,017 695,747 845,438
1973 8,079,202 245,252 1,047,395 1,213,243 1,729,505 2,369,095 233,686 457,358 783,669
1974 6,880,153 278,242 822,886 854,427 1,576,215 2,073,786 341,429 353,693 579,475
1975 7,726,878 132,692 1,004,359 963,323 1,398,330 2,449,214 379,809 816,172 582,979
1976 7,933,588 181,397 465,460 1,455,808 1,453,591 3,044,740 540,411 257,491 534,689
1977 7,397,061 459,778 944,191 1,366,564 853,258 2,869,326 254,066 343,389 306,489
1978 7,424,968 318,842 951,721 1,796,447 823,488 1,917,559 290,484 539,201 787,225
1979 7,883,440 275,779 1,084,674 1,594,540 983,127 2,244,208 359,782 424,741 916,589
1980 7,706,483 399,102 1,164,920 1,409,205 975,156 2,262,999 414,664 424,829 655,608
1981 6,409,701 476,251 931,305 1,451,147 947,057 1,509,802 352,948 431,993 309,198
1982 6,408,475 254,727 757,380 1,188,225 765,771 1,941,081 419,630 602,153 479,508
1983 6,456,007 321,687 1,278,635 1,041,562 845,564 1,670,142 354,567 487,078 456,773
1984 5,415,271 504,182 715,489 866,029 713,044 1,364,736 176,720 393,524 681,547
1985 4,960,868 219,055 831,328 871,986 802,991 1,173,330 238,763 301,703 521,712
1986 6,124,236 233,539 1,419,972 670,099 698,795 1,542,604 382,585 419,051 757,591
1987 5,789,776 185,802 934,840 1,011,668 753,948 1,273,327 249,911 530,503 849,777
1988 6,369,341 356,711 1,304,591 1,470,827 627,426 1,389,229 273,493 402,546 544,518
1989 5,645,440 411,507 961,780 1,337,471 585,874 951,715 238,337 537,504 621,252
1990 5,452,385 366,933 945,897 1,340,135 778,677 1,253,692 292,954 270,478 203,619
1991 5,444,580 385,319 905,433 1,289,946 769,227 1,031,104 236,481 386,667 440,403
1992 5,976,077 345,708 882,323 1,422,259 733,528 1,293,391 334,241 394,628 569,999
1993 5,708,293 282,983 941,493 1,295,651 753,847 1,036,406 243,692 506,757 647,465
1994 6,980,066 350,875 734,870 1,379,215 848,784 1,380,293 300,840 729,580 1,255,609
1995 8,269,415 524,200 1,010,534 1,381,903 778,457 1,808,542 416,244 855,268 1,494,267
1996 7,941,315 522,006 676,727 1,120,329 793,817 2,142,740 358,512 811,127 1,516,057
1997 9,939,695 584,247 1,205,629 1,036,931 883,563 2,450,765 436,468 1,337,954 2,004,138
1998 9,640,364 836,216 1,054,582 1,058,440 950,114 2,448,699 439,468 1,068,030 1,784,814
1999 10,805,682 713,054 2,040,801 1,150,627 1,031,842 2,528,577 514,435 689,187 2,137,160
2000 9,470,212 770,333 1,288,093 1,048,981 833,157 2,266,723 367,667 622,005 2,273,253
2001 7,903,955 718,286 979,033 603,318 743,759 1,649,653 445,965 463,284 2,300,657
2002 7,503,707 667,339 1,182,336 1,114,789 793,296 1,212,517 400,670 428,286 1,704,474
2003 7,949,743 843,497 851,810 1,103,386 627,097 2,110,665 504,996 506,101 1,402,192
2004 7,425,314 811,135 776,385 1,283,383 600,099 1,609,494 393,429 494,941 1,456,448
2005 6,755,268 703,140 533,133 937,142 671,364 1,728,862 454,765 386,590 1,340,271
2006 7,276,538 515,821 558,073 655,635 900,747 1,831,707 511,286 679,233 1,624,037
2007 8,307,296 581,493 887,452 864,169 830,157 2,155,069 387,183 552,582 2,049,190
2008 7,723,809 532,414 1,079,188 1,046,076 875,215 1,907,131 380,904 353,530 1,549,351
2009 8,512,378 502,970 1,079,740 930,463 753,955 1,866,899 417,281 444,464 2,516,605
2010 8,430,138 605,556 1,423,198 800,616 597,692 1,698,950 350,824 533,391 2,419,912
2011 9,182,591 415,825 974,976 828,352 938,591 2,093,040 521,185 836,886 2,573,736
2012 10,601,516 505,583 1,547,098 1,038,514 1,260,530 2,502,082 401,020 792,513 2,554,176
2013 10,371,890 338,379 1,020,349 1,427,498 1,141,041 2,575,586 448,205 793,888 2,626,945
2014 10,899,822 500,879 1,757,212 1,126,422 1,443,553 2,553,334 601,731 1,013,897 1,902,795
2015 11,643,321 470,915 1,981,061 1,728,364 1,391,683 3,068,413 538,152 766,949 1,697,783
2016 11,792,529 584,200 2,524,465 1,668,640 1,487,897 2,784,121 470,408 628,915 1,643,883
2017 10,488,461 538,451 1,836,830 1,074,123 1,290,954 2,725,103 587,162 658,357 1,777,481
2018 9,255,153 450,750 1,549,853 1,276,799 1,327,872 2,093,517 460,480 559,905 1,535,978
2019 9,423,411 361,060 1,700,754 1,105,252 971,539 1,712,412 441,469 770,594 2,360,332
2020 NA NA NA NA NA NA NA NA NA
2021 NA NA NA NA NA NA NA NA NA
2022 7,434,293 614,444 1,219,314 1,088,267 686,775 1,294,059 513,041 513,986 1,504,407
2023 6,125,722 380,917 1,059,812 928,821 739,986 1,265,721 255,783 530,140 964,543
2024 6,609,303 506,629 1,606,236 1,159,084 629,949 1,162,945 216,376 516,890 811,193
2025 6,463,861 389,414 1,332,350 1,061,762 696,313 1,313,726 335,872 501,753 832,671

Figure 50: Mallard abundance in the WBPHS Traditional Survey Area in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 52: Northern Pintail WBPHS

Original data source: WBPHS Traditional Survey Area; USFWS Headquarters.

Table 52. Northern pintail abundance in the WBPHS Traditional Survey Area in spring, 1955-2025.
Year TSA Area1 Area2 Area3 Area4 Area5 Area6 Area7 Area8
1955 9,775,075 662,213 1,161,390 142,679 1,591,524 5,076,494 213,432 469,606 457,736
1956 10,372,801 676,914 687,713 69,704 1,521,459 6,222,181 284,112 428,270 482,448
1957 6,606,886 399,215 585,165 35,995 1,250,631 3,245,914 192,281 393,643 504,042
1958 6,037,921 752,478 1,133,922 30,537 1,223,870 1,813,032 187,395 371,684 525,003
1959 5,872,740 1,051,707 2,583,695 75,476 832,648 775,041 127,774 341,490 84,909
1960 5,722,160 742,531 697,882 57,746 1,087,483 1,665,516 217,171 324,465 929,366
1961 4,218,159 634,899 1,277,718 132,034 513,319 846,659 97,951 320,516 395,062
1962 3,623,524 864,991 447,030 30,457 328,585 581,072 104,810 322,806 943,772
1963 3,846,015 860,955 307,522 54,976 811,931 823,901 177,122 308,330 501,277
1964 3,291,227 773,552 475,679 60,005 417,623 853,386 114,949 263,068 332,965
1965 3,591,918 586,251 453,537 34,562 777,086 716,564 129,038 333,877 561,003
1966 4,811,934 717,673 202,821 37,728 1,265,152 1,504,782 96,677 326,689 660,412
1967 5,277,693 681,344 148,650 39,693 1,559,463 1,671,102 168,713 411,820 596,908
1968 3,489,395 1,444,503 227,653 81,224 501,554 809,172 54,594 121,990 248,706
1969 5,903,888 645,624 98,275 106,356 1,584,537 1,956,154 266,267 223,033 1,023,642
1970 6,391,987 733,465 165,221 154,714 1,366,414 2,417,173 198,759 355,389 1,000,852
1971 5,847,204 452,464 132,797 75,231 1,763,054 2,222,040 139,535 220,326 841,756
1972 6,978,954 898,932 468,661 36,305 1,716,409 2,261,553 211,972 477,641 907,481
1973 4,356,220 1,120,482 378,960 51,884 1,025,103 1,006,310 73,556 293,865 406,060
1974 6,598,182 937,980 320,614 25,638 2,123,070 2,185,998 301,804 186,259 516,820
1975 5,900,370 651,918 442,791 52,930 1,553,133 2,050,332 216,198 415,914 517,154
1976 5,475,644 854,383 267,420 52,025 956,502 2,549,564 249,401 294,503 251,847
1977 3,926,093 1,931,166 551,600 58,412 345,799 672,535 26,195 222,584 117,802
1978 5,108,179 1,011,857 263,202 77,298 1,087,568 961,787 90,648 581,137 1,034,681
1979 5,376,133 752,148 236,300 33,403 1,456,351 1,579,919 195,928 470,317 651,767
1980 4,508,077 1,816,457 296,128 28,903 842,287 897,591 68,588 192,243 365,880
1981 3,479,479 1,488,696 346,317 56,375 657,342 526,183 59,014 207,576 137,976
1982 3,708,758 788,226 112,303 21,794 576,822 1,222,040 107,096 466,018 414,458
1983 3,510,642 925,329 410,376 26,087 380,814 1,029,352 97,235 205,517 435,931
1984 2,964,801 925,967 460,038 21,347 299,777 492,073 26,871 232,846 505,882
1985 2,515,493 637,131 291,798 10,983 593,397 520,629 40,786 110,129 310,640
1986 2,739,747 882,518 185,630 17,082 242,646 545,934 120,539 212,975 532,423
1987 2,628,344 959,434 231,444 39,548 447,350 343,843 56,304 286,760 263,661
1988 2,005,522 1,142,541 198,857 15,671 171,394 113,754 33,566 135,107 194,632
1989 2,111,902 878,625 213,321 10,544 313,638 363,716 16,783 102,210 213,065
1990 2,256,630 1,102,962 170,079 17,558 317,734 336,665 55,256 198,064 58,312
1991 1,803,384 1,026,244 225,580 28,316 116,271 220,989 23,785 67,519 94,681
1992 2,098,139 899,710 275,123 18,822 103,933 456,880 90,449 120,523 132,699
1993 2,053,418 743,329 228,928 6,841 372,521 240,368 37,524 195,674 228,233
1994 2,972,266 787,540 104,885 13,432 383,404 785,173 47,704 394,437 455,693
1995 2,757,866 809,938 102,228 40,200 198,200 554,227 109,443 300,724 642,907
1996 2,735,862 776,099 56,382 3,708 333,503 807,418 84,460 234,458 439,835
1997 3,557,991 647,490 249,472 22,301 472,805 1,123,865 64,691 416,147 561,220
1998 2,520,649 945,957 186,398 8,958 166,284 551,839 63,689 193,262 404,261
1999 3,057,888 1,021,885 182,712 8,760 114,998 875,231 61,508 206,656 586,139
2000 2,907,559 1,452,235 220,276 15,869 188,826 463,613 44,686 169,478 352,576
2001 3,295,994 1,426,489 174,979 9,909 66,077 680,017 97,079 161,324 680,121
2002 1,789,710 941,985 187,162 11,440 72,984 181,841 31,572 102,367 260,358
2003 2,558,229 848,188 169,798 5,607 251,949 993,374 39,240 121,767 128,306
2004 2,184,602 927,354 193,399 10,334 161,341 473,686 39,665 131,963 246,860
2005 2,560,530 905,431 108,257 8,450 282,273 857,542 67,944 75,022 255,612
2006 3,386,425 1,041,069 125,819 5,851 610,998 1,023,592 57,308 264,336 257,452
2007 3,335,302 1,134,655 234,388 5,430 324,150 960,301 14,908 117,917 543,554
2008 2,612,841 1,249,960 331,197 4,089 240,017 422,765 29,409 50,198 285,206
2009 3,224,957 929,569 243,149 21,463 171,944 444,195 47,846 382,678 984,114
2010 3,508,558 1,163,793 338,009 5,644 241,683 331,830 18,434 176,588 1,232,578
2011 4,428,650 745,505 121,076 9,985 655,024 1,106,403 38,479 279,124 1,473,054
2012 3,473,083 1,175,893 78,534 15,843 357,036 605,083 22,116 244,307 974,271
2013 3,334,993 994,601 234,809 9,537 367,741 824,863 35,652 88,393 779,398
2014 3,220,296 701,066 317,553 5,172 461,002 739,387 49,111 251,516 695,488
2015 3,043,012 668,404 638,529 52,243 259,839 719,989 40,610 196,962 466,437
2016 2,618,468 815,822 798,818 15,574 167,973 288,741 19,358 134,672 377,508
2017 2,889,231 756,963 675,067 9,807 301,074 560,615 30,760 106,208 448,736
2018 2,365,322 650,554 497,470 21,817 343,870 268,640 11,094 193,229 378,647
2019 2,268,466 430,591 529,713 3,365 133,277 163,516 13,851 372,536 621,616
2020 NA NA NA NA NA NA NA NA NA
2021 NA NA NA NA NA NA NA NA NA
2022 1,783,613 786,186 297,031 14,405 67,506 94,325 17,496 88,951 417,712
2023 2,218,505 546,196 389,934 7,602 152,400 285,535 10,945 183,063 642,829
2024 1,974,976 547,633 540,349 7,421 42,641 213,569 6,688 141,792 474,883
2025 2,237,899 712,374 735,645 8,949 124,698 301,807 16,754 100,480 237,191

Figure 51: Northern pintail abundance in the WBPHS Traditional Survey Area in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 53: Gadwall WBPHS

Original data source: WBPHS Traditional Survey Area; USFWS Headquarters.

Table 53. Gadwall abundance in the WBPHS Traditional Survey Area in spring, 1955-2025.
Year TSA Area1 Area2 Area3 Area4 Area5 Area6 Area7 Area8
1955 651,497 582 1,301 4,844 200,319 359,048 27,595 57,809 0
1956 772,639 533 983 1,015 269,942 422,148 18,892 59,127 0
1957 666,826 926 1,566 5,559 187,084 375,700 23,559 60,482 11,951
1958 502,042 121 3,536 NA 219,587 136,737 34,053 61,664 46,344
1959 589,959 1,106 1,768 37,669 275,747 171,409 26,280 62,584 13,395
1960 784,071 713 0 1,367 369,182 227,008 27,597 63,201 95,003
1961 654,832 95 12,931 43,687 279,615 126,780 52,821 66,505 72,397
1962 905,075 486 9,104 12,392 207,811 342,747 38,765 68,100 225,670
1963 1,055,298 0 1,455 23,146 198,773 319,375 70,482 107,072 334,995
1964 873,374 742 9,781 29,124 256,634 317,564 54,384 79,954 125,190
1965 1,260,275 133 7,580 41,808 200,306 481,176 39,122 180,511 309,639
1966 1,680,441 1,392 1,879 30,424 479,606 575,370 78,826 160,052 352,892
1967 1,384,634 1,243 6,650 78,494 415,764 409,166 82,038 148,579 242,700
1968 1,948,955 86 13,410 76,842 491,606 679,884 42,690 136,596 507,841
1969 1,573,390 85 4,289 82,556 338,981 463,498 22,792 146,608 514,581
1970 1,608,072 85 22,685 38,475 343,276 511,537 50,295 103,354 538,365
1971 1,605,616 85 7,607 30,165 362,838 590,171 31,316 87,211 496,223
1972 1,622,943 85 23,022 37,785 444,939 488,815 67,088 27,516 533,693
1973 1,245,616 513 16,412 44,784 281,022 451,507 66,387 44,330 340,662
1974 1,592,352 5,343 8,215 16,939 495,640 644,723 52,797 102,120 266,574
1975 1,643,881 903 6,354 18,842 303,696 744,569 40,137 136,745 392,636
1976 1,244,760 552 6,659 16,873 308,696 679,395 56,163 90,508 85,913
1977 1,298,990 83 34,396 43,773 392,235 607,488 66,910 31,440 122,666
1978 1,557,988 2,042 18,044 28,600 279,676 532,861 44,402 263,188 389,175
1979 1,757,892 735 43,567 20,909 346,447 695,477 66,298 165,988 418,471
1980 1,392,884 702 56,477 44,641 319,614 474,563 119,359 128,892 248,636
1981 1,395,366 2,450 61,724 65,546 309,430 409,483 57,657 219,863 269,214
1982 1,633,765 2,081 58,282 25,034 215,521 619,727 47,725 187,600 477,794
1983 1,519,210 1,386 8,326 19,848 142,293 573,312 49,109 162,365 562,571
1984 1,515,045 3,949 37,570 11,013 204,445 411,816 15,533 118,889 711,830
1985 1,302,986 2,252 18,558 13,888 164,891 588,412 54,735 87,544 372,706
1986 1,547,139 NA 69,548 15,022 226,430 559,866 100,438 104,909 470,926
1987 1,305,607 653 42,271 18,737 127,093 539,128 63,430 85,408 428,887
1988 1,349,928 6,004 68,443 38,167 256,444 376,208 56,534 101,022 447,106
1989 1,414,554 4,915 87,357 21,292 250,164 387,935 60,414 219,199 383,278
1990 1,672,063 4,597 106,608 18,126 414,419 539,476 110,506 120,662 357,669
1991 1,583,655 8,875 81,961 49,419 292,740 507,677 65,251 228,814 348,918
1992 2,032,759 4,395 99,297 14,121 357,967 626,929 105,505 292,888 531,656
1993 1,755,222 654 80,421 37,918 414,289 429,562 78,381 285,259 428,738
1994 2,318,290 2,295 83,702 31,700 511,707 639,777 49,997 360,824 638,288
1995 2,835,729 654 63,768 37,841 410,569 583,604 81,149 685,238 972,906
1996 2,983,991 5,234 74,219 9,775 404,175 930,116 100,573 410,588 1,049,310
1997 3,897,210 1,309 92,728 21,345 308,295 1,155,292 91,466 1,227,281 999,494
1998 3,742,225 333 139,045 7,795 360,238 1,342,039 102,987 496,309 1,293,479
1999 3,235,478 4,913 138,519 9,891 332,528 1,028,707 115,620 378,771 1,226,529
2000 3,158,411 2,724 99,536 11,806 310,857 649,964 85,075 289,355 1,709,093
2001 2,679,157 6,543 111,105 14,754 256,756 715,449 106,253 402,796 1,065,501
2002 2,235,449 987 161,942 27,172 333,366 359,696 131,798 186,535 1,033,952
2003 2,549,028 4,580 75,848 30,366 240,943 1,076,560 94,085 205,988 820,658
2004 2,589,577 1,871 138,332 22,252 289,920 751,787 147,593 205,261 1,032,561
2005 2,179,111 2,654 77,031 18,798 338,207 723,032 120,402 186,673 712,313
2006 2,824,732 1,873 134,872 16,245 455,237 1,202,361 125,178 215,844 673,123
2007 3,355,903 3,211 100,073 14,632 343,378 1,317,263 110,111 265,852 1,201,383
2008 2,727,679 4,000 108,939 9,630 420,325 1,011,218 112,495 200,499 860,572
2009 3,053,516 2,000 66,629 8,817 400,976 1,043,832 117,909 318,918 1,094,435
2010 2,976,662 2,892 50,794 14,351 323,152 913,276 101,726 392,031 1,178,440
2011 3,256,941 1,333 40,782 32,723 346,517 1,020,016 92,232 469,976 1,253,362
2012 3,585,615 631 56,059 30,835 378,294 1,144,311 112,570 253,925 1,608,991
2013 3,351,362 1,638 33,444 12,787 339,544 1,300,439 132,648 217,153 1,313,709
2014 3,811,022 NA 43,194 35,745 565,034 1,454,509 236,345 425,558 1,050,637
2015 3,834,078 2,000 34,379 6,700 564,484 1,462,822 204,861 527,940 1,030,891
2016 3,712,044 10,596 107,140 20,841 652,911 1,473,214 134,792 281,734 1,030,816
2017 4,179,991 1,333 59,176 6,919 872,862 1,495,968 125,205 558,320 1,060,208
2018 2,885,912 NA 50,717 7,738 418,493 1,218,405 100,814 422,204 667,539
2019 3,258,709 431 77,318 4,315 592,184 1,107,385 139,691 409,136 928,249
2020 NA NA NA NA NA NA NA NA NA
2021 NA NA NA NA NA NA NA NA NA
2022 2,684,716 17,307 101,343 10,856 429,270 855,559 144,684 219,619 906,078
2023 2,561,374 NA 60,632 18,320 441,555 966,725 109,183 277,875 687,084
2024 2,284,432 755 124,091 4,827 388,610 649,496 77,061 213,488 826,106
2025 2,412,884 377 154,861 6,603 428,222 871,396 74,474 227,933 649,018

Figure 52: Gadwall abundance in the WBPHS Traditional Survey Area in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 54: American Wigeon WBPHS

Original data source: WBPHS Traditional Survey Area; USFWS Headquarters.

Table 54. American wigeon abundance in the WBPHS Traditional Survey Area in spring, 1955-2025.
Year TSA Area1 Area2 Area3 Area4 Area5 Area6 Area7 Area8
1955 3,216,798 73,215 1,559,563 190,230 582,304 620,429 95,311 61,155 34,592
1956 3,144,990 82,309 1,317,909 50,472 535,550 946,174 122,918 58,996 30,662
1957 2,919,777 156,916 1,340,886 51,527 535,785 634,025 114,992 58,278 27,367
1958 2,551,724 140,750 882,123 63,286 548,883 473,138 353,060 58,677 31,806
1959 3,787,661 107,890 2,120,472 131,248 616,007 472,625 247,479 59,940 32,000
1960 2,987,572 132,206 1,623,260 149,756 539,938 365,228 83,081 63,584 30,519
1961 3,048,266 135,235 1,847,208 132,941 502,309 238,029 117,411 64,044 11,089
1962 1,958,746 180,180 925,316 187,678 380,146 150,209 56,804 68,290 10,123
1963 1,830,808 77,248 879,133 146,872 315,248 237,331 86,458 72,707 15,811
1964 2,589,605 118,482 1,404,337 214,079 346,277 310,129 115,703 71,609 8,990
1965 2,301,124 209,044 1,028,090 252,269 320,911 317,687 130,473 42,650 NA
1966 2,318,376 247,113 984,964 229,101 385,549 302,129 98,086 52,888 18,545
1967 2,325,465 280,898 545,043 191,502 485,275 649,108 52,397 106,312 14,930
1968 2,298,570 347,587 519,929 402,608 467,515 362,775 98,620 95,266 4,270
1969 2,941,435 337,124 683,029 417,153 403,794 831,660 111,666 130,464 26,545
1970 3,469,903 424,670 959,699 635,451 434,256 819,303 52,516 120,313 23,694
1971 3,272,855 321,506 871,807 491,908 502,040 951,415 28,786 85,604 19,788
1972 3,200,102 312,247 1,007,952 292,177 448,432 772,341 108,950 240,047 17,956
1973 2,877,944 334,919 1,054,975 328,265 394,136 474,367 112,370 164,158 14,754
1974 2,671,974 456,844 622,402 220,767 514,484 633,168 87,044 95,446 41,819
1975 2,778,347 224,435 767,975 227,452 384,299 893,723 54,284 168,046 58,133
1976 2,505,181 242,239 620,548 302,918 344,513 720,058 56,285 149,997 68,623
1977 2,575,130 487,050 942,452 296,959 194,907 490,684 25,098 114,686 23,294
1978 3,282,423 626,430 1,069,114 421,826 303,478 519,911 22,592 246,547 72,526
1979 3,106,495 563,676 797,780 329,006 402,492 784,147 60,467 128,494 40,433
1980 3,595,488 741,425 1,100,805 403,273 403,885 610,439 61,201 180,892 93,568
1981 2,946,043 859,750 998,245 417,433 179,810 211,695 34,744 77,277 167,089
1982 2,458,713 464,212 694,013 299,593 199,965 594,333 35,014 135,092 36,492
1983 2,636,238 557,362 674,483 331,179 170,873 675,023 30,392 119,392 77,535
1984 3,002,226 658,399 1,349,482 286,591 158,359 322,256 28,473 117,952 80,715
1985 2,050,681 397,779 755,242 234,711 177,253 290,085 32,847 91,891 70,872
1986 1,736,521 476,903 549,000 166,156 90,165 292,326 39,430 76,737 45,804
1987 2,012,530 462,823 895,317 209,062 110,393 159,427 20,892 107,833 46,783
1988 2,211,090 527,684 925,935 317,269 85,486 194,130 26,943 69,683 63,960
1989 1,972,873 550,813 660,596 363,323 95,932 181,403 24,848 75,198 20,760
1990 1,860,100 536,313 510,948 304,380 123,237 177,271 31,515 170,902 5,535
1991 2,253,971 641,130 788,919 314,279 117,898 234,315 21,737 116,572 19,121
1992 2,208,356 593,239 663,277 267,509 170,304 324,887 23,848 133,616 31,676
1993 2,052,985 537,974 749,843 261,005 198,492 195,205 13,791 80,769 15,907
1994 2,382,249 727,803 479,422 411,865 193,154 261,001 16,234 200,830 91,940
1995 2,614,539 730,022 833,790 199,935 179,760 401,835 13,513 161,536 94,150
1996 2,271,706 818,887 509,622 180,034 191,111 311,817 33,432 147,233 79,570
1997 3,117,617 953,468 1,094,490 199,859 190,539 381,851 20,463 200,506 76,442
1998 2,857,701 1,196,854 744,788 182,934 150,303 305,540 8,751 180,639 87,891
1999 2,920,084 932,276 1,045,763 215,621 179,573 345,527 20,042 103,702 77,579
2000 2,733,146 1,141,269 721,714 146,938 225,193 253,138 19,387 121,592 103,915
2001 2,493,549 1,105,934 727,918 99,837 186,807 177,290 18,164 87,688 89,910
2002 2,334,443 1,036,394 672,771 202,493 77,479 174,479 21,726 46,949 102,152
2003 2,551,448 1,019,528 850,197 191,451 131,605 218,864 15,759 43,397 80,647
2004 1,981,284 897,213 564,511 149,388 116,578 128,062 3,441 65,786 56,305
2005 2,225,079 873,162 583,480 174,273 125,455 294,242 34,177 67,151 73,140
2006 2,171,222 821,865 569,995 105,353 188,566 282,189 16,218 119,891 67,145
2007 2,806,791 1,113,425 842,715 143,022 170,472 324,796 8,552 121,128 82,680
2008 2,486,615 920,977 819,439 90,135 179,790 372,035 11,965 58,307 33,965
2009 2,468,576 805,221 792,820 147,437 132,624 237,428 8,847 215,733 128,467
2010 2,424,633 1,053,340 597,489 73,085 124,301 192,606 11,120 166,464 206,229
2011 2,084,044 620,766 650,402 125,957 199,617 281,493 4,855 92,039 108,916
2012 2,145,004 685,887 679,726 130,225 234,478 243,379 4,916 85,387 81,006
2013 2,644,303 577,206 1,100,458 230,076 197,263 369,144 9,858 43,320 116,979
2014 3,116,654 734,291 1,561,994 74,250 224,291 273,231 13,599 128,954 106,046
2015 3,037,040 541,032 1,505,976 99,421 305,498 251,159 8,281 194,753 130,919
2016 3,411,312 723,962 1,787,571 91,656 237,046 215,369 4,683 197,830 153,195
2017 2,777,067 643,527 1,423,856 71,154 187,684 295,521 6,379 53,522 95,425
2018 2,820,394 597,212 1,326,006 147,215 208,146 271,824 11,654 118,230 140,109
2019 2,832,105 398,134 1,554,990 106,886 251,442 239,871 12,774 152,474 115,533
2020 NA NA NA NA NA NA NA NA NA
2021 NA NA NA NA NA NA NA NA NA
2022 2,186,896 733,950 740,195 204,815 164,257 138,926 13,476 99,520 91,757
2023 1,889,704 110,979 1,029,318 251,366 155,504 111,721 6,473 117,431 106,911
2024 2,922,015 212,467 1,928,289 173,528 72,269 191,344 3,980 113,769 226,370
2025 3,189,464 295,304 2,108,286 230,951 155,353 168,329 2,966 103,582 124,692

Figure 53: American wigeon abundance in the WBPHS Traditional Survey Area in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 55: American Green-winged Teal WBPHS

Original data source: WBPHS Traditional Survey Area; USFWS Headquarters.

Table 55. American green-winged teal abundance in the WBPHS Traditional Survey Area in spring, 1955-2025.
Year TSA Area1 Area2 Area3 Area4 Area5 Area6 Area7 Area8
1955 1,807,165 14,149 973,737 64,697 351,266 359,645 25,164 18,508 0
1956 1,525,315 17,723 770,238 35,572 182,240 484,260 17,830 17,452 0
1957 1,102,890 39,427 566,645 12,349 186,193 251,993 29,587 16,696 0
1958 1,347,428 72,550 792,217 NA 205,077 182,252 74,707 16,124 4,502
1959 2,653,435 77,855 1,982,535 97,097 324,350 110,034 45,866 15,698 NA
1960 1,426,915 25,347 885,305 12,208 262,316 205,506 20,183 16,049 NA
1961 1,729,269 47,269 1,152,447 16,179 320,587 101,737 64,857 16,705 9,488
1962 722,916 44,115 481,424 51,764 63,388 44,166 10,703 17,360 9,996
1963 1,242,290 64,313 893,582 51,400 72,773 73,759 63,606 20,166 2,691
1964 1,561,319 79,696 1,169,305 105,729 114,628 69,109 4,296 18,556 NA
1965 1,281,993 193,203 713,795 74,015 117,249 125,336 32,519 25,876 NA
1966 1,617,319 170,244 939,621 84,276 176,110 114,220 45,879 23,676 63,292
1967 1,593,690 275,091 533,176 101,286 174,972 367,714 75,090 53,898 12,463
1968 1,430,896 315,221 605,463 88,873 121,517 200,706 42,693 31,456 24,967
1969 1,491,016 202,629 257,604 151,370 204,538 408,781 161,478 14,346 90,270
1970 2,182,469 249,677 400,450 171,016 203,628 801,360 74,304 47,926 234,107
1971 1,889,342 321,359 566,347 170,359 263,317 386,865 120,819 21,479 38,798
1972 1,948,224 198,803 858,748 137,992 288,071 232,246 107,022 45,202 80,141
1973 1,949,204 217,550 728,358 123,847 311,867 331,195 117,316 72,231 46,840
1974 1,864,466 404,302 385,275 152,237 404,833 295,379 106,519 33,842 82,079
1975 1,664,842 108,607 564,923 134,450 230,776 412,817 63,428 86,661 63,180
1976 1,547,490 187,942 271,409 213,060 345,644 356,483 110,937 34,738 27,278
1977 1,285,810 207,933 469,994 231,400 151,905 168,132 35,361 17,548 3,537
1978 2,174,210 278,440 805,050 440,726 222,319 233,904 116,559 35,141 42,071
1979 2,071,738 254,062 789,552 333,895 256,774 315,995 36,700 60,885 23,875
1980 2,049,867 316,496 697,285 437,657 224,048 174,346 27,532 18,935 153,568
1981 1,910,501 516,139 758,757 207,967 180,132 140,851 37,264 27,814 41,577
1982 1,535,688 210,326 770,533 180,682 127,493 112,910 32,758 49,723 51,263
1983 1,874,974 260,505 964,870 219,636 136,150 172,386 49,448 25,340 46,640
1984 1,408,237 310,303 585,300 178,597 117,742 132,664 34,851 19,756 29,024
1985 1,475,406 264,973 673,017 134,599 106,661 179,903 19,307 14,219 82,727
1986 1,674,923 384,256 817,482 176,062 78,682 95,852 44,307 14,904 63,378
1987 2,006,242 362,445 1,127,056 209,900 120,282 85,813 37,831 12,248 50,667
1988 2,060,757 385,197 1,054,156 276,268 162,043 92,656 24,523 20,965 44,949
1989 1,841,674 402,147 956,313 173,726 106,049 115,474 36,945 32,719 18,301
1990 1,789,489 473,763 718,217 241,460 132,524 135,727 36,815 47,654 3,329
1991 1,557,776 546,682 453,658 225,742 131,086 131,756 30,382 32,976 5,494
1992 1,773,069 375,993 547,679 446,600 174,434 135,604 49,700 25,249 17,809
1993 1,694,463 444,632 570,783 398,155 175,929 77,817 3,176 11,963 12,008
1994 2,108,448 562,753 697,422 274,185 152,574 253,233 18,675 85,182 64,425
1995 2,300,594 556,196 749,504 308,353 245,312 271,327 35,299 45,021 89,582
1996 2,499,547 757,644 427,782 332,286 314,510 351,231 106,427 85,654 124,014
1997 2,506,585 512,275 608,084 367,697 324,417 418,509 69,069 95,411 111,124
1998 2,087,346 679,010 657,823 246,067 92,234 271,238 44,940 38,177 57,858
1999 2,630,962 679,434 984,397 271,847 190,546 342,245 40,652 68,093 53,748
2000 3,193,525 946,230 1,282,073 188,993 308,129 294,806 60,805 60,204 52,285
2001 2,508,656 1,028,811 741,645 181,401 190,496 202,321 31,463 63,517 69,002
2002 2,333,495 630,952 928,376 339,256 147,019 127,343 25,483 79,423 55,642
2003 2,678,494 1,035,264 766,994 307,813 131,788 272,568 48,436 85,304 30,327
2004 2,460,842 818,738 835,132 374,516 98,430 124,319 27,036 104,098 78,573
2005 2,156,911 713,019 437,456 309,515 158,538 358,954 54,984 82,866 41,579
2006 2,587,219 780,083 750,950 303,237 177,861 400,578 65,445 33,658 75,407
2007 2,890,271 822,805 862,204 307,449 283,152 495,010 33,294 43,626 42,730
2008 2,979,731 654,724 1,068,313 282,083 296,547 560,608 47,818 56,366 13,271
2009 3,443,599 658,474 1,225,393 398,571 175,479 648,384 47,842 174,513 114,942
2010 3,475,937 954,267 1,464,056 105,178 129,694 398,453 48,290 39,010 336,988
2011 2,900,096 641,361 1,250,642 126,177 275,376 421,959 55,249 19,011 110,322
2012 3,471,243 704,803 1,566,914 135,526 274,142 496,509 157,449 19,071 116,830
2013 3,053,444 451,814 1,228,778 358,000 195,500 575,226 60,223 22,518 161,385
2014 3,439,896 475,046 1,716,318 117,559 367,699 465,804 76,446 11,723 209,302
2015 4,080,923 565,591 2,333,261 140,498 327,325 451,796 99,075 56,472 106,905
2016 4,275,441 778,804 2,337,285 116,046 299,756 467,598 140,025 36,304 99,624
2017 3,605,276 616,665 1,816,126 136,116 341,617 472,348 74,600 26,545 121,259
2018 3,042,672 449,023 1,587,179 187,381 189,874 323,947 84,775 49,126 171,367
2019 3,178,219 416,404 1,680,781 218,873 301,495 277,259 71,891 44,677 166,839
2020 NA NA NA NA NA NA NA NA NA
2021 NA NA NA NA NA NA NA NA NA
2022 2,150,890 330,913 1,074,887 212,527 156,478 234,323 40,943 63,068 37,752
2023 2,502,585 126,323 1,581,478 275,941 165,234 186,969 30,740 71,716 64,183
2024 3,005,466 219,762 1,829,338 217,231 86,363 280,344 41,544 63,337 267,547
2025 2,546,250 196,379 1,418,515 156,144 166,000 354,267 33,606 99,366 121,973

Figure 54: American green-winged teal abundance in the WBPHS Traditional Survey Area in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 56: Blue-winged Teal WBPHS

Original data source: WBPHS Traditional Survey Area; USFWS Headquarters.

Table 56. Blue-winged teal abundance in the WBPHS Traditional Survey Area in spring, 1955-2025.
Year TSA Area1 Area2 Area3 Area4 Area5 Area6 Area7 Area8
1955 5,305,238 0 342,817 57,999 1,550,238 2,068,507 470,599 114,433 700,646
1956 4,997,646 0 292,797 64,575 903,759 2,542,739 284,709 115,558 793,509
1957 4,299,499 0 40,330 41,342 908,556 1,924,310 391,256 117,797 875,908
1958 5,456,584 0 201,348 221,457 1,078,543 1,650,704 1,120,162 131,117 1,053,254
1959 5,099,309 0 911,885 147,199 903,562 1,087,019 1,247,586 129,505 672,553
1960 4,292,995 0 417,421 70,785 877,793 1,112,769 699,198 97,343 1,017,686
1961 3,655,304 0 578,862 35,981 897,110 583,022 521,299 193,405 845,625
1962 3,011,051 0 244,421 241,665 346,740 383,752 368,354 140,238 1,285,881
1963 3,723,624 0 128,013 306,825 426,848 504,893 401,535 145,736 1,809,774
1964 4,020,614 0 508,488 444,908 634,556 735,756 358,838 138,975 1,199,093
1965 3,594,457 57 227,581 164,890 494,085 669,095 284,199 236,025 1,518,525
1966 3,733,241 0 141,100 137,311 533,204 909,736 213,050 241,588 1,557,252
1967 4,491,525 1,128 21,248 230,182 712,934 1,395,676 627,614 216,205 1,286,538
1968 3,462,528 1,452 29,994 803,335 325,319 720,229 313,137 135,704 1,133,358
1969 4,138,588 0 46,083 521,952 363,220 966,589 445,767 251,456 1,543,521
1970 4,861,825 9,921 50,600 616,159 440,876 1,552,614 672,922 196,216 1,322,517
1971 4,610,201 2,109 114,266 194,446 714,293 1,291,387 314,268 224,502 1,754,930
1972 4,278,529 0 152,572 205,673 494,851 1,012,888 406,256 294,311 1,711,978
1973 3,332,530 0 48,825 162,834 459,217 887,888 399,443 127,551 1,246,772
1974 4,976,222 0 99,983 69,724 1,209,712 1,312,215 686,767 182,268 1,415,552
1975 5,885,357 0 285,659 183,452 1,108,175 2,360,150 360,989 290,998 1,295,934
1976 4,744,744 0 158,415 395,957 820,335 1,799,610 654,609 433,974 481,843
1977 4,462,839 2,783 635,514 454,609 750,958 1,631,307 292,917 284,207 410,545
1978 4,498,618 3,561 385,951 415,711 393,236 902,361 279,164 319,585 1,799,049
1979 4,875,866 0 280,595 228,824 592,923 1,482,802 440,752 293,195 1,556,775
1980 4,895,079 3,561 470,163 514,304 834,569 1,307,164 290,224 234,364 1,240,730
1981 3,720,649 4,033 411,820 532,598 1,148,075 781,509 253,899 133,044 455,670
1982 3,657,565 0 234,742 391,955 498,144 605,878 289,639 478,301 1,158,906
1983 3,366,531 1,453 149,309 179,399 419,133 963,207 226,642 347,701 1,079,686
1984 3,979,328 4,892 322,463 206,231 429,216 993,592 171,008 229,649 1,622,277
1985 3,502,357 NA 200,587 316,734 295,318 1,327,329 172,344 186,673 1,003,372
1986 4,478,820 5,949 455,829 125,306 361,868 876,499 326,546 186,710 2,140,113
1987 3,528,696 1,546 440,556 215,234 596,632 674,828 203,180 189,797 1,206,923
1988 4,011,108 13,317 580,403 656,721 552,905 755,343 197,853 300,007 954,559
1989 3,125,255 1,057 237,540 449,148 418,152 578,438 176,409 187,383 1,077,128
1990 2,776,382 NA 189,374 268,792 521,168 875,476 268,593 194,599 458,380
1991 3,763,687 NA 207,047 444,672 580,235 936,689 208,517 267,962 1,118,565
1992 4,333,105 NA 314,834 445,877 716,094 1,362,432 376,989 223,865 893,013
1993 3,192,940 2,906 260,586 520,354 526,558 570,072 269,188 192,419 850,858
1994 4,616,162 NA 194,188 223,593 466,610 980,162 92,783 752,000 1,906,825
1995 5,140,010 2,906 166,120 124,061 430,834 1,088,351 301,793 396,430 2,629,515
1996 6,407,422 NA 194,521 120,519 505,871 2,046,644 295,524 441,590 2,802,753
1997 6,124,267 NA 203,804 69,514 358,461 1,974,360 300,397 472,655 2,745,075
1998 6,398,812 NA 339,948 156,556 521,876 1,589,022 257,901 736,908 2,796,600
1999 7,149,486 NA 206,286 175,085 391,543 2,110,905 439,555 558,969 3,267,143
2000 7,431,442 NA 274,876 125,944 577,823 1,622,427 355,035 237,768 4,237,569
2001 5,756,998 NA 119,315 148,146 367,782 1,267,464 484,127 157,748 3,212,416
2002 4,206,479 NA 303,541 306,746 244,160 667,137 230,101 249,248 2,205,546
2003 5,518,162 2,906 314,303 182,141 322,586 1,918,273 419,729 419,403 1,938,820
2004 4,073,034 2,219 400,612 60,411 360,165 1,154,742 282,315 319,771 1,492,800
2005 4,585,518 2,784 247,373 139,219 649,154 1,597,006 338,684 286,389 1,324,910
2006 5,859,567 NA 315,531 81,520 864,306 2,228,084 425,609 346,391 1,598,125
2007 6,707,612 9,330 368,681 121,155 668,503 2,379,813 274,009 276,588 2,609,533
2008 6,640,096 NA 393,323 86,815 817,658 2,317,671 264,875 234,607 2,525,148
2009 7,383,834 NA 248,148 116,131 480,406 1,739,781 302,916 344,580 4,151,873
2010 6,328,511 3,913 278,864 4,521 293,600 1,363,233 211,791 307,798 3,864,790
2011 8,948,451 1,461 144,136 30,576 470,380 2,488,852 392,617 894,204 4,526,224
2012 9,242,268 NA 146,926 50,720 595,745 2,607,562 327,436 661,138 4,852,740
2013 7,731,668 NA 386,098 39,715 751,567 2,758,507 345,148 225,912 3,224,721
2014 8,541,534 NA 377,388 45,956 834,316 3,109,225 474,127 1,177,845 2,522,678
2015 8,547,299 NA 359,937 94,188 1,168,852 3,566,905 522,495 618,183 2,216,738
2016 6,689,361 NA 446,683 134,649 897,674 2,103,710 331,939 638,532 2,136,175
2017 7,888,918 NA 578,857 46,847 1,643,941 2,820,489 300,000 528,433 1,970,351
2018 6,450,456 NA 489,777 71,143 1,171,038 1,700,196 340,721 398,521 2,279,060
2019 5,427,612 NA 711,258 5,217 706,901 931,879 157,593 198,147 2,716,617
2020 NA NA NA NA NA NA NA NA NA
2021 NA NA NA NA NA NA NA NA NA
2022 6,491,075 11,164 670,398 75,050 453,978 1,214,162 353,457 439,944 3,272,923
2023 5,250,313 NA 569,574 61,359 450,907 1,404,676 203,639 551,020 2,009,138
2024 4,598,953 NA 677,159 71,822 587,964 930,224 196,682 441,935 1,693,168
2025 4,431,736 NA 552,230 44,891 573,205 1,108,909 280,068 478,135 1,394,297

Figure 55: Blue-winged teal abundance in the WBPHS Traditional Survey Area in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 57: Northern Shoveler WBPHS

Original data source: WBPHS Traditional Survey Area; USFWS Headquarters.

Table 57. Northern shoveler abundance in the WBPHS Traditional Survey Area in spring, 1955-2025.
Year TSA Area1 Area2 Area3 Area4 Area5 Area6 Area7 Area8
1955 1,642,809 2,530 289,199 6,867 397,210 667,073 54,728 78,979 146,222
1956 1,781,409 2,723 194,706 1,927 404,963 854,377 66,519 76,381 179,813
1957 1,476,104 5,105 104,017 7,931 349,831 637,868 85,433 75,419 210,500
1958 1,383,766 18,179 232,741 3,503 442,257 335,357 83,397 77,352 190,980
1959 1,577,591 14,167 603,841 57,186 321,119 264,463 160,841 78,337 77,637
1960 1,824,513 13,267 202,540 17,426 431,919 604,342 142,542 72,900 339,577
1961 1,382,962 24,007 409,699 16,676 303,463 233,867 121,437 78,229 195,584
1962 1,268,952 13,804 215,592 35,428 196,817 79,804 49,457 86,828 591,222
1963 1,398,436 9,348 129,580 41,211 378,016 196,937 124,473 106,730 412,141
1964 1,718,260 11,750 493,763 103,347 341,960 375,309 119,808 96,488 175,836
1965 1,423,657 28,074 201,416 71,834 276,232 293,647 107,196 84,684 360,573
1966 2,146,961 29,486 192,533 63,181 470,839 809,890 99,257 108,600 373,176
1967 2,314,697 24,225 142,084 47,640 538,540 807,683 170,010 168,133 416,383
1968 1,684,488 150,176 110,788 48,949 394,635 479,420 77,178 144,180 279,161
1969 2,156,783 58,347 65,531 61,772 433,252 777,381 151,188 184,667 424,645
1970 2,230,414 85,431 77,653 70,766 329,082 760,655 126,678 144,170 635,979
1971 2,011,420 37,814 141,064 44,899 423,593 907,672 68,253 125,635 262,490
1972 2,466,458 68,324 197,432 42,166 435,736 921,903 119,047 131,508 550,342
1973 1,619,001 72,394 167,736 38,881 466,095 538,385 47,958 88,589 198,964
1974 2,011,299 139,602 135,281 16,903 587,970 705,214 97,552 112,090 216,687
1975 1,980,758 40,928 145,045 44,519 550,321 730,330 51,295 201,063 217,256
1976 1,748,066 83,955 89,765 20,230 325,035 822,932 157,731 131,593 116,826
1977 1,451,847 199,386 327,871 81,326 220,775 422,711 38,935 67,789 93,054
1978 1,975,298 218,676 85,836 44,191 258,970 426,651 65,159 298,235 577,581
1979 2,406,509 110,648 121,657 25,881 391,405 692,352 85,859 282,819 695,888
1980 1,908,201 392,743 232,671 49,266 388,768 494,687 56,678 67,069 226,319
1981 2,333,551 622,873 260,205 58,844 503,911 335,314 99,799 205,437 247,169
1982 2,147,638 161,282 99,469 41,604 320,364 699,031 135,382 247,130 443,376
1983 1,875,652 186,586 83,435 34,725 200,299 792,829 121,693 150,321 305,765
1984 1,618,247 235,308 163,402 38,201 187,302 370,934 47,806 155,060 420,235
1985 1,702,092 176,998 118,511 37,565 321,237 670,984 76,351 77,839 222,607
1986 2,128,193 264,923 237,038 16,791 220,715 538,761 156,167 129,909 563,889
1987 1,950,177 326,707 223,152 50,989 330,681 375,780 87,331 144,488 411,049
1988 1,680,920 404,050 258,445 88,230 165,576 428,308 99,826 85,261 151,224
1989 1,538,342 294,518 271,973 41,556 227,934 243,769 56,016 86,185 316,391
1990 1,759,343 361,987 261,932 55,164 322,514 447,811 77,326 115,048 117,561
1991 1,716,185 362,656 221,594 53,209 294,468 473,397 66,919 73,929 170,013
1992 1,954,371 365,876 284,670 108,775 241,407 571,923 137,890 48,294 195,536
1993 2,046,469 448,826 263,221 44,132 421,143 327,371 60,507 162,251 319,018
1994 2,912,021 499,960 166,712 58,163 421,445 737,458 42,640 335,557 650,087
1995 2,854,877 464,560 127,581 85,888 267,573 763,877 140,376 139,753 865,269
1996 3,448,958 481,325 117,834 35,676 373,845 1,212,812 176,733 207,100 843,632
1997 4,120,384 497,236 204,387 37,814 443,177 1,660,718 161,391 424,517 691,144
1998 3,183,223 852,469 394,370 43,325 329,423 790,546 91,713 191,142 490,235
1999 3,889,548 658,478 219,006 26,681 408,219 1,281,260 160,899 424,780 710,225
2000 3,520,738 846,385 247,967 36,271 380,429 899,774 175,829 160,551 773,531
2001 3,313,505 666,271 203,692 27,769 267,780 718,127 199,358 151,846 1,078,663
2002 2,318,192 580,831 371,369 38,432 273,949 310,154 100,174 136,341 506,942
2003 3,619,573 670,867 318,274 10,068 448,369 1,437,742 123,026 246,543 364,684
2004 2,810,431 642,604 246,511 32,816 384,649 783,624 142,871 200,028 377,327
2005 3,591,472 666,202 213,074 28,612 547,641 1,313,596 210,530 148,226 463,591
2006 3,680,225 408,631 192,543 11,864 700,753 1,611,641 177,794 163,274 413,726
2007 4,552,843 579,501 345,992 28,171 977,152 1,655,879 115,759 168,582 681,806
2008 3,507,828 465,722 322,333 37,215 617,572 1,183,784 89,552 134,481 657,168
2009 4,376,320 463,818 292,533 15,988 526,801 893,708 136,599 407,907 1,638,969
2010 4,057,429 626,117 296,698 3,667 475,055 794,998 87,073 220,645 1,553,176
2011 4,640,970 322,344 132,881 6,889 877,635 1,496,025 148,478 429,714 1,227,002
2012 5,017,561 376,760 274,657 11,117 914,995 1,857,662 137,772 340,613 1,103,986
2013 4,751,030 226,100 348,463 35,325 852,691 1,705,834 148,999 170,425 1,263,192
2014 5,278,857 372,368 371,612 23,876 914,033 1,711,046 255,034 521,102 1,109,787
2015 4,391,435 396,574 454,468 19,770 887,182 1,692,399 130,760 296,848 513,434
2016 3,966,902 560,476 785,611 17,131 460,942 1,206,910 119,069 209,216 607,547
2017 4,353,052 433,549 584,042 18,988 871,814 1,500,832 125,625 218,453 599,749
2018 4,207,913 367,032 415,035 22,135 1,027,228 1,066,001 109,242 387,236 814,004
2019 3,649,242 321,788 335,070 19,965 715,737 820,411 60,419 309,077 1,066,774
2020 NA NA NA NA NA NA NA NA NA
2021 NA NA NA NA NA NA NA NA NA
2022 3,036,336 373,572 410,469 15,001 325,723 740,784 147,530 231,228 792,029
2023 2,858,356 127,922 419,838 33,362 299,331 923,841 83,182 282,047 688,833
2024 2,645,811 204,567 430,308 17,802 306,279 827,950 62,197 227,788 568,920
2025 2,758,185 178,534 305,260 17,167 396,585 1,016,222 68,414 210,068 565,935

Figure 56: Northern shoveler abundance in the WBPHS Traditional Survey Area in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 58: Canvasback WBPHS

Original data source: WBPHS Traditional Survey Area; USFWS Headquarters.

Table 58. Canvasback abundance in the WBPHS Traditional Survey Area in spring, 1955-2025.
Year TSA Area1 Area2 Area3 Area4 Area5 Area6 Area7 Area8
1955 589,257 48,591 52,742 66,172 96,240 266,234 36,663 9,037 13,579
1956 698,509 50,247 26,406 41,416 98,733 397,376 60,686 8,292 15,353
1957 626,072 59,367 25,063 5,889 100,592 362,043 48,505 7,670 16,943
1958 746,830 39,289 75,646 54,839 168,707 249,673 118,030 7,135 33,511
1959 488,684 77,409 80,638 115,612 78,148 81,192 39,344 6,669 9,671
1960 605,698 85,593 56,821 190,320 58,254 118,071 75,702 6,328 14,609
1961 435,251 14,690 50,009 118,937 63,861 120,986 54,850 6,058 5,859
1962 360,238 22,732 32,739 21,914 54,620 175,656 42,264 5,850 4,463
1963 506,235 69,254 100,405 87,131 77,628 90,882 57,910 5,833 17,193
1964 643,636 77,777 89,014 181,051 83,828 107,655 76,516 5,585 22,211
1965 522,120 66,523 44,632 77,211 100,526 126,493 82,630 3,460 20,645
1966 663,114 96,656 151,538 53,128 68,517 167,823 65,224 1,934 58,294
1967 502,576 48,854 33,354 78,146 97,884 137,480 75,248 1,598 30,012
1968 563,691 140,795 106,678 100,211 57,901 99,523 35,178 3,487 19,918
1969 503,530 63,450 76,527 30,416 26,683 162,416 61,754 5,543 76,742
1970 580,100 42,606 44,076 124,001 49,437 238,949 46,629 4,131 30,271
1971 450,674 46,233 49,169 21,773 39,010 202,092 69,283 5,631 17,483
1972 425,912 92,862 26,701 21,318 65,481 135,333 33,124 13,647 37,446
1973 620,451 127,100 50,780 73,488 54,039 228,926 34,909 15,564 35,645
1974 512,842 81,750 29,007 15,046 100,193 181,819 34,370 2,234 68,423
1975 595,098 39,393 64,269 35,044 78,945 252,884 77,565 2,112 44,885
1976 614,389 48,531 40,110 44,965 52,081 283,277 110,778 24,270 10,378
1977 664,042 168,622 49,316 50,400 64,639 256,461 58,162 7,040 9,401
1978 373,174 48,519 33,318 38,101 51,218 128,997 37,283 7,762 27,976
1979 582,004 62,365 51,826 25,412 53,462 280,931 49,316 22,487 36,204
1980 734,570 152,230 66,440 59,421 62,125 307,205 45,835 7,347 33,967
1981 620,843 133,576 133,507 85,126 49,418 110,099 65,875 5,357 37,885
1982 513,265 100,272 49,927 40,740 73,779 151,895 49,479 12,521 34,651
1983 526,612 109,231 68,981 32,987 49,684 212,701 33,382 6,494 13,152
1984 530,129 118,223 80,016 39,187 26,610 157,655 38,249 6,023 64,166
1985 375,929 80,541 14,107 33,546 56,591 118,752 45,576 3,100 23,715
1986 438,350 84,647 54,994 13,337 59,172 127,229 48,363 2,828 47,780
1987 450,109 99,281 27,809 13,565 53,490 184,156 36,467 980 34,361
1988 435,048 77,259 67,697 49,823 54,769 119,017 37,464 5,673 23,346
1989 477,439 131,649 110,005 34,490 36,657 81,515 33,480 7,048 42,595
1990 539,318 193,058 67,559 40,224 78,128 79,699 51,597 13,337 15,716
1991 491,151 125,852 80,103 38,106 58,413 130,547 43,289 2,059 12,782
1992 481,529 93,592 60,473 113,709 32,760 95,740 60,952 7,626 16,677
1993 472,055 82,469 127,926 52,609 45,856 93,027 32,976 11,556 25,636
1994 525,604 81,169 69,841 81,469 63,970 117,734 28,232 15,422 67,768
1995 770,593 125,595 120,157 32,559 60,492 282,285 91,838 12,222 45,445
1996 848,487 157,513 136,007 49,797 66,975 282,952 83,032 8,782 63,429
1997 688,754 44,986 93,403 50,341 68,518 280,056 63,531 15,857 72,063
1998 685,862 105,259 100,346 38,299 68,550 246,948 66,465 8,573 51,422
1999 716,039 88,957 151,409 45,480 56,133 253,376 70,515 6,876 43,292
2000 706,754 186,670 83,430 36,591 73,179 232,189 63,684 6,899 24,112
2001 579,826 89,029 62,722 31,565 31,885 232,199 56,310 5,851 70,264
2002 486,597 135,323 121,025 37,651 14,481 73,255 63,272 6,288 35,303
2003 557,575 88,976 115,123 13,230 69,687 194,783 41,815 11,357 22,603
2004 617,227 161,344 109,270 49,815 50,159 120,932 70,055 11,978 43,676
2005 520,574 95,049 97,516 39,193 42,688 162,444 47,658 4,788 31,238
2006 691,013 73,236 109,426 12,774 76,283 286,689 87,474 12,305 32,826
2007 864,924 91,717 138,910 34,160 127,296 324,344 77,250 16,751 54,494
2008 488,667 71,924 83,901 23,334 78,940 166,331 30,524 8,723 24,991
2009 662,135 41,301 88,111 48,730 51,880 280,330 48,396 25,980 77,407
2010 585,164 56,884 71,544 18,247 39,136 192,482 34,693 41,055 131,123
2011 691,560 22,487 51,093 30,527 33,131 334,961 67,628 16,965 134,767
2012 759,935 34,998 92,511 26,839 145,592 312,992 52,486 10,431 84,085
2013 786,978 34,505 92,287 30,027 54,318 381,353 61,998 13,462 119,029
2014 685,262 20,863 61,830 22,993 71,445 324,800 59,423 15,423 108,485
2015 757,281 40,808 109,174 35,379 114,350 270,237 37,511 18,103 131,720
2016 736,472 77,946 143,918 35,219 72,085 256,417 67,700 19,998 63,190
2017 732,531 86,565 110,494 36,521 63,725 295,239 76,617 13,585 49,783
2018 686,084 84,853 107,592 42,571 72,545 208,248 80,561 28,502 61,213
2019 651,925 78,336 105,855 24,659 133,180 160,143 56,053 30,131 63,568
2020 NA NA NA NA NA NA NA NA NA
2021 NA NA NA NA NA NA NA NA NA
2022 586,643 31,679 119,042 21,508 70,956 192,554 82,526 13,488 54,889
2023 618,898 55,792 85,240 18,654 59,519 243,109 82,498 15,917 58,169
2024 566,319 68,035 55,726 29,085 45,005 196,880 85,470 14,323 71,795
2025 686,805 52,909 107,634 48,852 48,863 245,845 58,092 12,657 111,953

Figure 57: Canvasback abundance in the WBPHS Traditional Survey Area in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 59: Redhead WBPHS

Original data source: WBPHS Traditional Survey Area; USFWS Headquarters.

Table 59. Redhead abundance in the WBPHS Traditional Survey Area in spring, 1955-2025.
Year TSA Area1 Area2 Area3 Area4 Area5 Area6 Area7 Area8
1955 539,943 77 73,372 54,362 140,504 215,438 42,358 4,985 8,847
1956 757,320 82 66,319 16,487 145,690 449,138 53,460 4,633 21,511
1957 509,086 46 37,478 18,295 105,884 266,765 37,982 4,484 38,152
1958 457,122 0 29,463 NA 127,205 143,540 99,124 4,435 53,355
1959 498,774 0 133,770 0 113,249 108,583 123,685 4,209 15,277
1960 497,783 482 52,896 47,702 71,291 134,155 68,128 4,862 118,267
1961 323,304 49 56,811 52,574 78,127 46,550 31,367 4,185 53,641
1962 507,506 170 98,593 21,547 44,294 150,681 40,430 4,194 147,596
1963 413,426 373 18,157 25,490 79,611 44,602 93,075 5,731 146,387
1964 528,125 53 72,963 50,821 88,569 105,288 97,307 4,257 108,867
1965 599,308 1,303 9,436 56,408 93,321 114,140 148,576 2,983 173,142
1966 713,086 56 16,535 34,214 190,141 124,630 83,569 6,040 257,901
1967 735,691 57 29,065 72,427 194,413 175,999 68,163 12,361 183,206
1968 499,386 58 29,209 83,932 84,971 134,886 38,305 1,377 126,648
1969 633,193 59 9,756 40,181 117,774 137,803 60,186 2,776 264,658
1970 622,252 60 8,254 69,164 74,686 179,593 81,413 2,022 207,060
1971 534,420 60 14,551 29,342 68,723 169,263 65,647 6,595 180,238
1972 550,880 61 17,666 21,487 118,113 158,555 59,523 NA 175,475
1973 500,776 61 19,554 26,728 89,099 176,286 57,499 3,867 127,682
1974 626,322 61 7,896 6,616 155,310 237,626 86,899 1,049 130,865
1975 831,901 62 14,860 19,797 181,735 305,700 66,912 3,486 239,350
1976 665,865 62 6,122 21,055 173,409 311,671 83,148 12,780 57,617
1977 633,962 9,912 33,307 30,341 202,082 224,321 88,131 4,527 41,341
1978 724,648 62 28,690 19,715 133,845 130,314 68,856 10,981 332,185
1979 697,470 901 26,580 11,659 100,666 220,475 73,277 19,922 243,989
1980 728,375 2,408 35,245 34,079 268,364 190,929 42,065 4,372 150,914
1981 594,925 10,231 34,527 70,109 111,109 138,422 108,310 28,814 93,403
1982 616,851 63 13,928 29,027 57,828 123,435 74,196 19,875 298,499
1983 711,902 939 15,160 29,786 60,412 232,232 53,761 21,405 298,208
1984 671,321 186 42,008 11,371 98,329 201,569 16,455 22,607 278,796
1985 578,153 NA 9,776 17,186 133,947 219,554 42,215 3,546 151,929
1986 559,607 1,636 31,598 16,851 123,277 181,600 33,375 7,953 163,317
1987 502,425 186 5,634 17,462 143,546 154,252 44,788 4,985 131,572
1988 441,875 4,360 17,706 21,507 85,673 189,306 46,141 3,653 73,529
1989 510,712 3,378 41,795 7,929 96,588 137,780 27,686 12,470 183,086
1990 480,917 3,625 42,319 19,294 162,824 137,203 74,187 8,292 33,173
1991 445,621 14,619 55,021 27,511 110,780 131,056 73,792 9,625 23,217
1992 595,609 659 83,388 12,793 112,004 150,261 111,235 5,844 119,424
1993 485,418 1,679 72,507 8,494 110,341 85,677 36,783 14,089 155,848
1994 653,468 1,449 30,951 38,463 110,274 183,461 32,356 10,160 246,353
1995 888,484 NA 16,228 16,961 95,242 345,118 125,011 10,049 279,875
1996 834,231 639 23,900 6,957 102,699 293,215 86,549 14,187 306,085
1997 918,286 219 62,402 10,094 188,866 308,498 71,847 15,809 260,552
1998 1,005,079 NA 67,535 31,221 67,548 268,106 158,068 24,300 388,301
1999 973,394 NA 94,805 30,058 180,745 288,320 57,310 13,140 309,017
2000 926,298 622 25,773 40,638 106,769 323,806 87,762 9,830 331,098
2001 712,015 NA 26,272 8,133 53,950 224,287 117,236 12,768 269,369
2002 564,803 4,550 37,934 28,400 112,539 94,886 57,883 16,147 212,464
2003 636,799 2,976 29,301 26,355 96,923 271,324 70,827 22,045 117,049
2004 605,345 2,360 73,356 31,352 78,910 131,193 101,990 24,968 161,214
2005 592,295 224 49,435 13,348 91,349 225,591 97,738 2,851 111,759
2006 916,274 10,080 58,885 5,158 154,266 434,958 101,814 11,825 139,289
2007 1,008,952 1,720 79,565 9,968 178,960 414,189 71,520 5,780 247,251
2008 1,055,962 2,097 93,870 11,964 332,878 383,044 55,902 3,153 173,054
2009 1,044,115 846 28,524 6,213 134,955 285,329 68,768 32,592 486,889
2010 1,064,177 1,401 51,137 3,375 90,305 316,481 107,237 50,061 444,179
2011 1,356,076 846 14,914 16,539 166,718 438,190 64,964 39,547 614,358
2012 1,269,883 NA 16,355 19,338 183,478 382,884 98,792 20,276 548,760
2013 1,202,194 1,039 22,140 4,575 204,086 437,322 70,927 7,371 454,735
2014 1,278,738 NA 59,173 1,648 262,681 541,828 95,451 16,583 301,374
2015 1,195,934 NA 47,147 20,002 167,370 602,832 102,439 7,891 248,253
2016 1,288,793 693 86,599 11,325 218,921 637,236 144,583 19,770 169,665
2017 1,115,350 NA 46,212 11,964 221,032 528,034 131,441 2,123 174,543
2018 999,037 NA 77,822 19,269 244,570 289,944 134,934 30,553 201,944
2019 732,164 423 60,700 3,853 171,773 172,903 30,894 8,344 283,274
2020 NA NA NA NA NA NA NA NA NA
2021 NA NA NA NA NA NA NA NA NA
2022 1,066,624 8,521 84,121 11,953 134,187 262,798 114,474 27,318 423,253
2023 929,942 NA 39,038 3,965 155,216 294,957 129,619 34,686 272,461
2024 782,015 842 60,773 3,729 70,729 260,569 59,677 31,209 294,486
2025 918,168 5,930 164,337 4,128 84,309 306,056 101,495 16,096 235,817

Figure 58: Redhead abundance in the WBPHS Traditional Survey Area in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 60: Scaup WBPHS

Original data source: WBPHS Traditional Survey Area; USFWS Headquarters.

Table 60. Scaup (greater and lesser spp.) abundance in the WBPHS Traditional Survey Area in spring, 1955-2025.
Year TSA Area1 Area2 Area3 Area4 Area5 Area6 Area7 Area8
1955 5,620,130 753,529 2,800,646 519,805 427,241 858,296 171,292 57,300 32,022
1956 5,994,080 785,945 2,648,479 568,414 483,205 1,274,657 147,877 53,878 31,624
1957 5,766,942 612,344 2,523,084 948,456 515,078 898,118 187,491 50,965 31,406
1958 5,350,372 796,797 2,442,658 491,358 490,625 519,954 535,666 49,302 24,012
1959 7,037,610 795,959 4,118,304 598,311 400,167 683,122 360,682 47,979 33,087
1960 4,868,569 831,350 2,630,023 228,937 325,779 484,451 265,420 46,648 55,961
1961 5,380,045 893,245 3,035,070 342,838 393,608 419,505 227,101 44,779 23,899
1962 5,286,098 1,252,000 2,746,477 331,830 231,904 418,844 153,191 44,040 107,812
1963 5,438,402 1,149,391 3,081,749 400,424 358,495 174,445 207,330 44,438 22,130
1964 5,131,798 1,005,518 2,909,274 463,531 400,469 162,858 145,839 41,670 2,640
1965 4,639,964 665,936 2,714,311 494,648 306,502 257,313 130,274 39,675 31,305
1966 4,439,240 827,528 2,592,733 384,382 238,706 193,509 112,444 54,791 35,146
1967 4,927,671 582,826 2,897,293 580,617 346,752 323,387 120,563 44,432 31,801
1968 4,412,682 982,187 2,253,631 698,005 233,992 95,641 83,242 33,843 32,140
1969 5,139,780 909,939 2,707,741 707,966 350,869 305,025 59,758 55,899 42,584
1970 5,662,477 847,809 3,008,370 890,766 367,910 322,829 88,839 47,760 88,194
1971 5,143,262 712,499 3,221,234 535,435 299,466 222,426 101,129 16,481 34,592
1972 7,996,967 772,525 5,483,114 891,762 426,765 242,571 69,223 67,038 43,968
1973 6,257,416 844,139 3,775,802 641,673 588,899 230,379 66,179 85,111 25,234
1974 5,780,464 799,266 3,081,586 920,676 368,630 377,899 146,280 40,733 45,394
1975 6,460,024 830,445 3,528,071 827,154 382,726 622,166 160,029 40,336 69,097
1976 5,818,746 1,057,363 2,707,301 585,467 625,930 504,645 208,720 66,300 63,020
1977 6,260,238 1,236,560 3,047,468 596,085 477,693 702,247 129,710 44,759 25,715
1978 5,984,411 931,800 2,871,013 715,347 462,961 526,169 231,513 105,365 140,243
1979 7,657,943 869,502 3,849,246 1,041,086 687,495 796,541 89,640 208,558 115,875
1980 6,381,655 1,244,015 3,196,776 587,079 472,963 628,970 161,998 38,966 50,888
1981 5,990,883 1,033,374 3,303,857 629,792 469,335 277,144 114,930 38,902 123,549
1982 5,531,964 853,830 2,730,444 590,831 522,077 496,595 129,652 83,250 125,285
1983 7,173,798 992,949 3,575,832 896,580 491,943 844,809 177,679 74,503 119,503
1984 7,024,320 1,095,502 4,175,201 562,288 367,493 510,174 81,055 98,951 133,656
1985 5,097,956 816,838 2,500,696 831,477 363,182 319,833 113,234 36,058 116,637
1986 5,235,304 795,481 2,527,231 601,469 322,744 468,909 251,898 54,652 212,920
1987 4,862,729 797,827 2,701,361 507,309 256,190 278,187 150,304 57,741 113,810
1988 4,671,351 770,177 2,339,907 538,073 345,157 366,910 109,024 68,607 133,496
1989 4,342,050 768,778 2,467,280 484,854 157,957 208,113 88,955 56,538 109,575
1990 4,293,141 803,390 2,038,157 710,219 307,318 199,330 114,576 45,208 74,943
1991 5,254,899 1,170,594 2,061,038 1,200,918 299,766 265,398 75,251 83,046 98,888
1992 4,639,232 909,988 1,811,641 998,722 288,041 438,565 107,400 23,883 60,993
1993 4,080,144 951,309 1,838,798 552,425 268,358 352,122 44,981 32,427 39,725
1994 4,529,044 1,148,608 1,977,562 382,345 264,964 343,869 118,247 48,865 244,583
1995 4,446,443 946,247 1,784,120 463,912 366,514 518,644 116,142 37,622 213,242
1996 4,217,405 1,056,867 1,476,903 436,132 376,349 462,511 186,676 67,361 154,606
1997 4,112,349 800,166 1,632,592 523,805 347,675 489,482 94,811 69,646 154,173
1998 3,471,916 927,866 1,436,450 253,274 243,105 300,158 61,578 28,975 220,510
1999 4,411,723 955,974 2,133,616 544,986 228,223 287,427 72,369 38,775 150,354
2000 4,026,322 1,219,183 1,620,966 292,975 292,335 272,775 60,064 41,256 226,768
2001 3,694,010 1,148,144 1,475,601 267,246 201,944 320,615 74,164 42,376 163,921
2002 3,524,142 792,048 1,784,303 378,014 146,475 149,681 49,670 49,713 174,237
2003 3,734,444 969,704 1,736,075 354,324 172,052 251,357 48,575 35,081 167,275
2004 3,807,191 982,435 1,624,426 581,560 124,093 184,770 31,442 27,590 250,874
2005 3,386,893 960,708 1,361,394 348,827 126,509 381,266 60,074 16,366 131,749
2006 3,246,663 883,851 1,169,374 334,868 213,921 391,001 96,887 18,610 138,150
2007 3,452,233 1,191,270 1,261,018 271,244 182,318 302,053 50,384 14,865 179,083
2008 3,738,349 1,070,619 1,626,732 405,942 175,531 256,318 59,770 16,327 127,109
2009 4,172,097 820,924 1,685,442 684,463 286,509 323,877 70,097 34,424 266,360
2010 4,244,429 947,143 2,378,279 208,488 127,023 245,534 52,782 14,429 270,751
2011 4,319,289 847,477 2,165,251 367,203 228,434 346,797 84,724 37,509 241,893
2012 5,238,630 849,496 2,839,272 337,565 294,349 521,382 102,061 17,696 276,810
2013 4,165,678 547,712 2,343,201 315,349 150,046 475,426 38,146 13,645 282,153
2014 4,611,054 577,874 2,127,036 200,808 247,348 850,405 163,772 22,059 421,752
2015 4,395,305 587,179 2,214,959 345,405 261,901 470,840 112,256 10,161 392,604
2016 4,991,714 653,481 2,805,401 349,301 256,896 433,311 102,469 14,970 375,885
2017 4,371,725 781,427 2,237,682 314,648 266,373 476,981 70,371 23,884 200,359
2018 3,989,325 669,727 1,964,896 268,152 259,846 409,205 82,130 28,204 307,165
2019 3,590,799 498,562 1,792,922 259,493 352,389 353,019 69,147 30,252 235,016
2020 NA NA NA NA NA NA NA NA NA
2021 NA NA NA NA NA NA NA NA NA
2022 3,655,073 678,151 1,803,141 407,283 282,812 275,430 55,445 25,258 127,553
2023 3,517,135 476,922 1,839,742 426,338 290,700 237,960 51,746 58,097 135,630
2024 4,069,075 553,145 2,191,056 360,758 251,044 274,154 55,757 59,554 323,607
2025 3,667,154 575,227 1,982,894 435,502 249,565 225,121 68,026 17,251 113,567

Figure 59: Scaup (greater and lesser spp.) abundance in the WBPHS Traditional Survey Area in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 61: Ring-necked Duck WBPHS

Original data source: WBPHS Traditional Survey Area; USFWS Headquarters.

Table 61. Ring-necked duck abundance in the WBPHS Traditional Survey Area in spring, 1955-2025.
Year TSA Area1 Area2 Area3 Area4 Area5 Area6 Area7 Area8
1955 451,486 110 240,319 178,452 1,430 27,218 2,133 1,218 606
1956 349,519 105 248,612 55,298 8,813 16,901 17,829 1,362 600
1957 165,523 0 144,020 NA 1,491 10,947 6,955 1,481 629
1958 160,816 0 124,617 NA 4,472 11,669 18,368 1,572 117
1959 599,010 0 502,257 4,991 9,418 27,559 53,155 1,630 NA
1960 278,008 624 218,083 25,169 2,935 13,795 12,795 1,668 2,939
1961 198,383 0 121,889 38,955 10,138 8,352 17,362 1,687 NA
1962 364,515 0 149,867 202,730 2,130 NA 8,095 1,693 NA
1963 461,723 0 128,820 284,009 1,662 20,828 22,903 1,689 1,813
1964 370,986 0 157,374 194,865 3,408 9,638 4,021 1,679 NA
1965 512,484 0 235,624 230,503 11,012 23,183 8,877 3,285 NA
1966 648,175 0 185,642 436,042 4,331 15,984 1,313 974 3,889
1967 493,212 0 141,396 288,158 34,792 10,360 9,984 8,522 NA
1968 489,863 0 98,152 372,987 11,047 1,516 3,244 2,917 NA
1969 374,740 0 62,905 289,257 8,687 6,459 6,626 222 584
1970 673,324 0 159,220 474,650 14,214 13,931 7,454 NA 3,855
1971 658,064 0 155,243 457,837 36,221 7,175 NA NA 1,588
1972 408,775 412 82,678 277,007 30,628 8,531 8,845 NA 674
1973 333,316 0 121,405 190,137 2,002 8,242 11,530 NA NA
1974 346,278 0 64,361 211,053 15,135 42,563 10,454 2,127 584
1975 530,420 0 123,159 309,953 26,015 53,769 16,356 NA 1,168
1976 499,600 0 76,645 347,454 13,482 42,600 16,601 1,429 1,389
1977 535,615 62 202,878 258,676 23,939 38,991 9,046 653 1,370
1978 626,786 128 154,837 344,159 50,884 45,061 27,334 2,008 2,374
1979 453,220 764 91,260 250,201 21,324 46,839 33,768 NA 9,064
1980 688,971 836 121,438 436,803 8,945 55,491 59,765 890 4,803
1981 815,754 9,626 120,313 552,772 29,526 40,994 58,844 890 2,789
1982 600,883 3,853 69,897 383,897 23,699 69,791 28,667 9,508 11,570
1983 780,082 3,501 144,927 386,438 12,682 21,765 32,438 24,940 153,390
1984 729,728 28,656 134,786 449,402 33,597 42,735 8,040 8,016 24,496
1985 628,713 16,298 88,159 458,501 18,727 21,387 16,468 5,181 3,992
1986 566,989 65,933 88,726 331,962 11,687 13,743 17,911 8,300 28,727
1987 732,528 38,287 121,134 477,934 18,557 29,315 29,251 2,598 15,452
1988 737,421 50,457 179,176 398,427 35,327 30,682 26,018 11,581 5,753
1989 543,824 24,751 152,267 263,599 46,509 8,620 15,673 7,225 25,180
1990 632,464 35,023 134,995 372,590 12,421 19,789 29,983 4,413 23,250
1991 657,626 18,669 131,749 442,470 14,924 19,606 19,246 6,371 4,591
1992 1,286,570 35,663 122,426 1,046,040 15,423 16,084 9,140 12,744 29,049
1993 867,927 39,781 209,323 581,132 9,559 12,013 5,887 9,179 1,054
1994 880,088 28,997 225,048 554,042 12,588 15,695 11,879 20,094 11,745
1995 954,961 26,090 211,296 568,026 8,980 36,010 11,679 20,086 72,795
1996 772,691 29,951 143,533 455,827 10,081 82,889 20,526 6,155 23,729
1997 1,192,452 36,999 385,574 616,339 37,449 58,057 27,675 1,222 29,135
1998 1,166,752 60,582 317,606 716,974 11,918 30,771 11,394 2,998 14,508
1999 1,103,225 19,150 365,723 543,853 51,981 57,237 16,596 3,088 45,595
2000 1,278,283 65,473 478,776 595,655 16,220 63,882 41,243 707 16,326
2001 939,669 86,529 256,834 476,891 20,167 36,316 37,998 7,396 17,539
2002 1,490,041 52,132 161,419 1,172,098 7,530 29,672 29,967 4,578 32,645
2003 1,229,696 96,086 322,451 692,958 31,096 27,212 39,984 3,851 16,057
2004 1,142,511 71,668 222,776 754,008 44,081 19,603 19,843 5,149 5,384
2005 1,016,720 78,618 290,904 589,321 12,895 6,927 20,652 5,569 11,834
2006 952,672 83,590 251,006 491,661 21,488 59,318 26,556 15,401 3,652
2007 1,060,457 61,467 238,283 639,654 31,962 22,637 40,462 10,146 15,846
2008 1,010,841 40,901 283,553 579,036 21,395 49,762 24,198 4,480 7,516
2009 1,268,527 28,999 481,195 622,651 24,994 39,289 15,072 18,738 37,589
2010 1,145,670 46,086 625,628 331,987 16,141 57,354 17,428 16,053 34,994
2011 1,005,305 30,577 452,835 276,596 7,800 111,520 9,736 1,506 114,735
2012 1,022,043 30,427 371,174 423,252 7,157 111,462 32,951 2,804 42,816
2013 1,322,988 29,302 531,718 492,859 13,538 101,132 85,812 913 67,715
2014 1,573,864 49,030 681,224 464,352 19,258 176,243 65,159 60,814 57,783
2015 1,503,316 40,902 726,904 397,663 14,008 201,640 72,792 10,440 38,967
2016 1,772,715 56,873 934,562 460,264 42,277 172,888 31,764 27,030 47,056
2017 1,918,026 49,928 1,123,508 435,009 52,178 176,128 51,965 1,296 28,016
2018 1,783,080 38,912 812,462 649,154 43,933 121,632 75,712 6,421 34,854
2019 1,537,694 48,686 859,760 405,695 11,652 101,972 48,957 35,149 25,822
2020 NA NA NA NA NA NA NA NA NA
2021 NA NA NA NA NA NA NA NA NA
2022 1,083,534 53,203 434,730 308,628 26,468 115,725 57,618 7,815 79,347
2023 1,532,462 19,827 541,298 705,825 47,393 84,267 56,237 10,903 66,712
2024 1,423,556 27,310 508,756 679,715 7,807 67,503 34,270 34,440 63,755
2025 1,517,376 27,740 974,834 365,701 26,061 65,707 28,386 10,931 18,017

Figure 60: Ring-necked duck abundance in the WBPHS Traditional Survey Area in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 62: Bufflehead WBPHS

Original data source: WBPHS Traditional Survey Area; USFWS Headquarters.

Table 62. Bufflehead abundance in the WBPHS Traditional Survey Area in spring, 1955-2025.
Year TSA Area1 Area2 Area3 Area4 Area5 Area6 Area7 Area8
1955 366,485 25,420 236,090 58,112 26,140 7,641 12,415 667 0
1956 365,116 26,868 252,953 35,547 36,632 8,806 3,615 695 0
1957 310,673 26,885 213,382 20,501 33,770 14,205 1,197 725 7
1958 321,362 15,714 202,694 45,972 39,475 7,518 9,218 771 0
1959 554,948 43,294 409,513 38,030 44,641 8,968 9,710 792 NA
1960 513,222 37,751 277,597 143,743 32,949 13,422 6,932 828 NA
1961 424,094 25,485 274,641 52,131 53,212 9,498 8,262 865 NA
1962 413,182 46,138 262,226 74,928 22,142 1,987 4,862 900 NA
1963 373,205 37,426 210,776 71,086 26,546 11,196 15,169 1,007 NA
1964 388,535 29,415 276,307 34,590 24,446 13,182 9,632 962 NA
1965 443,254 40,510 252,212 34,591 71,138 22,877 20,486 1,440 NA
1966 486,863 47,808 323,656 52,511 33,434 14,378 13,238 1,434 404
1967 491,468 54,147 256,133 80,575 48,640 18,058 32,589 1,325 NA
1968 578,055 37,159 249,902 217,013 32,448 29,476 10,007 2,050 NA
1969 653,897 32,946 358,755 151,753 44,142 39,162 25,725 1,414 NA
1970 642,280 43,536 306,760 220,532 40,370 20,522 8,379 376 1,805
1971 769,248 44,545 452,695 209,017 33,837 12,612 16,542 NA NA
1972 756,168 40,862 428,648 185,596 53,320 31,727 10,284 5,731 NA
1973 541,076 40,487 299,541 145,058 30,593 17,890 6,368 645 494
1974 663,601 64,846 373,253 156,109 25,989 19,122 22,138 1,694 450
1975 696,678 44,018 390,717 142,217 56,129 43,688 19,533 376 NA
1976 751,937 81,727 327,653 246,038 47,317 23,759 24,146 1,297 NA
1977 653,380 51,062 324,548 185,140 35,200 38,500 18,930 NA NA
1978 880,666 69,757 446,095 225,239 60,638 40,666 35,575 1,942 754
1979 885,028 78,958 453,912 222,471 67,167 42,409 12,588 4,903 2,620
1980 696,621 60,021 369,943 180,066 32,328 23,908 26,860 1,021 2,474
1981 672,831 40,037 304,556 207,362 55,464 29,181 31,977 2,365 1,889
1982 553,100 48,194 249,786 154,741 42,220 24,723 24,075 6,944 2,418
1983 946,749 45,007 517,058 253,778 57,370 36,247 27,154 376 9,759
1984 854,269 37,821 589,281 142,032 25,754 27,630 20,082 5,187 6,482
1985 554,214 36,788 301,089 139,217 16,954 26,868 31,783 1,021 494
1986 638,721 38,657 365,496 134,425 33,818 33,916 26,483 376 5,550
1987 748,248 55,759 479,870 120,633 22,662 32,906 36,418 NA NA
1988 720,175 46,731 446,362 119,305 50,807 20,419 29,024 5,599 1,928
1989 744,198 54,676 445,637 150,226 32,509 21,880 30,472 3,698 5,100
1990 745,490 31,763 407,934 200,378 36,522 31,746 30,184 6,019 944
1991 834,350 40,059 420,323 205,043 80,036 44,311 37,994 5,608 976
1992 1,030,544 32,271 428,798 410,789 67,581 37,561 41,498 5,726 6,318
1993 869,405 29,729 364,254 330,876 79,610 43,876 18,226 358 2,475
1994 765,723 38,319 401,486 183,395 43,090 42,057 40,321 7,235 9,822
1995 832,558 37,931 459,946 172,870 68,323 41,869 41,613 1,174 8,832
1996 879,963 49,745 467,314 173,920 103,462 52,985 29,507 1,294 1,736
1997 1,123,815 40,177 619,714 222,081 91,329 91,615 53,372 3,546 1,980
1998 945,880 46,697 472,410 235,398 73,919 78,803 35,415 2,114 1,124
1999 1,111,666 41,166 601,213 265,930 69,529 88,391 41,731 3,043 663
2000 910,287 39,704 382,714 260,591 70,930 112,810 38,195 3,409 1,934
2001 925,596 54,410 481,770 213,228 59,180 73,669 36,874 1,794 4,671
2002 948,388 38,290 485,954 262,023 47,226 75,350 34,696 542 4,307
2003 1,089,491 46,615 558,124 258,978 82,872 99,374 38,769 3,562 1,195
2004 1,053,228 43,849 532,066 298,785 70,637 55,215 50,455 1,834 387
2005 1,137,042 51,726 619,523 235,941 78,860 91,789 54,903 3,655 644
2006 1,144,396 46,319 606,111 229,867 107,600 101,426 49,737 2,299 1,038
2007 1,151,544 60,963 547,177 275,095 98,154 107,560 59,218 2,266 1,111
2008 1,071,011 56,816 561,513 229,193 60,121 116,041 41,672 1,554 4,100
2009 1,108,861 58,936 503,058 348,068 69,632 85,891 38,713 1,699 2,865
2010 1,415,389 53,456 797,480 273,802 76,700 172,057 34,023 3,832 4,039
2011 1,271,931 55,168 591,973 314,920 99,844 150,098 35,525 5,324 19,079
2012 1,409,406 48,489 745,485 255,944 141,370 182,482 30,125 NA 5,510
2013 1,203,561 43,770 537,395 256,703 76,971 209,058 62,426 547 16,691
2014 1,311,841 43,499 617,994 225,350 126,038 229,216 42,988 616 26,140
2015 1,587,902 42,528 700,610 349,564 123,783 296,113 69,954 NA 5,350
2016 1,353,573 44,086 689,446 204,341 98,543 226,435 85,413 556 4,752
2017 1,329,279 43,181 599,393 275,746 146,902 201,411 51,789 NA 10,857
2018 1,291,366 44,521 602,175 222,612 114,953 235,452 58,246 5,177 8,231
2019 1,154,245 38,205 532,169 192,997 94,533 214,819 54,363 11,679 15,481
2020 NA NA NA NA NA NA NA NA NA
2021 NA NA NA NA NA NA NA NA NA
2022 1,006,243 35,023 405,745 226,378 80,605 185,169 65,379 2,598 5,347
2023 996,305 15,856 438,472 174,429 98,078 210,436 49,324 3,293 6,418
2024 1,394,373 50,101 654,667 260,788 108,345 200,503 101,797 1,129 17,043
2025 1,381,433 60,817 640,918 218,830 106,172 281,784 66,029 NA 6,882

Figure 61: Bufflehead abundance in the WBPHS Traditional Survey Area in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 63: Ruddy Duck WBPHS

Original data source: WBPHS Traditional Survey Area; USFWS Headquarters.

Table 63. Ruddy Duck abundance in the WBPHS Traditional Survey Area in spring, 1955-2025.
Year TSA Area1 Area2 Area3 Area4 Area5 Area6 Area7 Area8
1955 289,859 6 34,732 NA 76,180 128,697 28,904 8,538 12,802
1956 388,665 6 29,593 NA 78,270 231,810 28,602 8,282 12,103
1957 221,282 6 6,904 NA 43,444 126,127 24,925 8,012 11,864
1958 170,712 0 18,693 NA 51,584 66,230 24,560 7,739 1,906
1959 548,219 0 100,268 4,495 79,151 256,132 76,840 7,510 23,823
1960 362,963 0 23,497 2,075 97,861 116,771 60,407 7,372 54,979
1961 343,124 6 67,452 27,378 49,800 71,428 92,851 7,263 26,946
1962 217,951 0 1,225 39,289 21,895 59,550 49,507 7,180 39,305
1963 245,249 0 22,237 17,859 37,418 38,531 98,281 7,178 23,745
1964 223,945 7 7,830 6,302 92,953 34,264 68,705 7,082 6,803
1965 237,499 7 6,408 18,644 93,379 42,614 65,530 247 10,669
1966 326,606 8 17,512 11,523 83,012 77,068 95,751 3,048 38,684
1967 324,318 8 15,342 20,004 111,877 58,726 74,859 1,666 41,836
1968 385,528 9 7,721 83,831 96,722 83,345 87,996 4,782 21,123
1969 273,081 9 36,462 20,708 47,903 54,967 38,626 22,864 51,542
1970 328,355 10 10,367 18,339 66,904 42,062 64,692 3,490 122,490
1971 267,094 11 12,541 8,751 56,720 60,181 52,880 1,321 74,688
1972 343,968 13 45,551 12,559 101,955 67,151 25,835 5,656 85,249
1973 289,609 14 18,841 10,325 38,224 115,961 43,867 3,969 58,408
1974 457,920 15 9,557 9,040 93,341 98,476 55,554 3,095 188,842
1975 678,425 16 21,550 4,453 184,681 80,323 49,940 4,474 332,989
1976 176,162 17 1,566 6,413 33,571 58,362 45,305 1,862 29,066
1977 316,512 18 42,471 7,957 101,483 101,834 34,650 1,156 26,944
1978 362,750 19 8,267 11,790 75,549 49,972 51,087 19,898 146,168
1979 299,172 20 10,692 6,690 42,045 91,103 22,288 32,063 94,272
1980 354,274 20 18,959 29,206 33,938 57,940 80,539 1,299 132,372
1981 633,200 21 53,077 53,920 62,966 49,705 91,792 17,094 304,625
1982 947,872 22 25,888 18,560 116,002 181,908 146,203 22,062 437,227
1983 715,003 23 171,613 24,126 72,906 108,529 55,049 11,369 271,388
1984 554,021 1,451 58,792 8,670 62,324 78,878 31,634 12,366 299,905
1985 390,445 NA 28,715 7,260 43,776 128,272 39,344 7,997 135,081
1986 585,000 NA 112,732 6,548 32,902 120,190 68,533 6,910 237,185
1987 400,819 NA 30,329 6,097 35,823 105,566 79,997 2,531 140,476
1988 268,845 119 17,764 13,529 77,895 61,243 57,384 25,099 15,812
1989 424,424 836 109,224 12,267 65,604 80,122 51,315 6,637 98,419
1990 473,077 653 78,963 32,609 129,916 56,232 68,853 9,196 96,655
1991 449,671 NA 44,059 22,486 193,766 58,480 68,697 37,980 24,203
1992 418,358 NA 106,349 9,637 85,226 116,146 58,390 9,547 33,063
1993 387,202 NA 120,285 51,796 57,054 78,071 22,759 1,817 55,420
1994 342,424 NA 12,559 673 65,536 102,211 14,427 35,599 111,418
1995 510,769 NA 42,748 20,515 128,458 158,131 32,074 6,989 121,854
1996 680,273 837 67,942 15,264 302,195 166,676 38,710 3,351 85,297
1997 499,365 NA 31,486 17,447 87,116 124,098 31,402 9,585 198,230
1998 612,498 NA 210,874 2,018 123,554 82,294 13,732 26,941 153,086
1999 713,746 NA 97,843 21,313 73,405 170,286 43,155 8,318 299,427
2000 654,351 NA 82,532 3,027 74,308 168,207 45,751 2,350 278,175
2001 566,715 1,023 39,850 12,591 51,612 134,255 58,648 29,426 239,311
2002 694,725 NA 126,847 19,909 86,481 69,957 108,487 26,196 256,848
2003 762,987 NA 155,559 27,246 54,857 358,216 40,507 26,336 100,267
2004 782,343 837 99,025 27,042 93,460 229,930 143,271 20,922 167,855
2005 457,078 NA 71,806 16,371 42,708 136,936 41,344 24,003 123,911
2006 521,061 NA 57,817 9,773 58,295 170,637 40,722 26,769 157,049
2007 836,205 NA 39,168 8,191 49,190 516,439 46,597 29,334 147,286
2008 575,743 NA 44,416 2,872 45,805 136,541 45,934 16,451 283,724
2009 582,036 NA 60,621 13,275 64,035 135,425 12,436 64,611 231,633
2010 530,922 NA 112,910 2,077 48,814 101,463 16,930 15,846 232,881
2011 604,520 842 38,563 6,158 36,023 357,736 26,142 13,071 125,985
2012 569,642 NA 38,106 9,449 31,868 290,576 31,660 18,418 149,564
2013 897,999 1,007 59,153 2,664 84,845 500,030 32,565 1,276 216,459
2014 823,032 NA 36,517 9,025 69,154 435,833 40,568 4,072 227,863
2015 844,190 NA 93,733 72,250 60,045 435,772 24,706 16,977 140,707
2016 1,069,145 NA 184,313 1,415 113,351 427,269 77,249 17,487 248,061
2017 1,014,085 NA 54,593 3,163 122,058 553,776 56,916 16,483 207,096
2018 679,333 NA 57,015 26,653 90,367 229,697 77,679 11,265 186,657
2019 514,987 NA 43,989 10,540 101,191 134,438 20,856 32,274 171,699
2020 NA NA NA NA NA NA NA NA NA
2021 NA NA NA NA NA NA NA NA NA
2022 738,917 1,608 47,280 25,113 71,484 347,144 59,189 17,546 169,552
2023 622,284 NA 25,537 8,758 116,988 231,154 36,070 22,504 181,274
2024 680,995 NA 44,016 32,765 65,471 151,950 37,000 80,698 269,096
2025 764,157 NA 55,752 33,243 53,812 323,851 51,185 16,566 229,748

Figure 62: Ruddy Duck abundance in the WBPHS Traditional Survey Area in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 64: Goldeneye WBPHS

Original data source: WBPHS Traditional Survey Area; USFWS Headquarters.

Table 64. Goldeneye (Barrow's and common spp.) abundance in the WBPHS Traditional Survey Area in spring, 1955-2025.
Year TSA Area1 Area2 Area3 Area4 Area5 Area6 Area7 Area8
1955 562,778 27,538 418,422 76,223 15,996 11,811 12,357 430 0
1956 414,815 28,917 289,608 40,289 21,071 21,189 13,281 460 0
1957 228,022 30,149 140,340 6,412 15,495 17,681 17,452 494 0
1958 798,183 39,019 472,588 238,933 9,080 9,812 28,222 529 0
1959 1,732,502 46,539 859,109 762,963 8,734 13,271 41,321 565 NA
1960 530,657 45,906 134,874 274,306 11,372 21,435 42,165 599 NA
1961 673,285 41,243 375,515 220,458 11,241 10,598 13,600 630 NA
1962 792,813 69,789 360,992 332,183 7,929 7,783 13,481 657 NA
1963 302,809 60,891 32,242 196,345 2,440 3,892 6,288 711 NA
1964 319,937 23,720 160,027 120,677 5,860 2,584 6,373 696 NA
1965 343,159 44,441 204,012 73,020 1,457 8,802 11,391 36 NA
1966 247,907 45,769 39,876 142,230 4,880 10,501 2,102 1,346 1,202
1967 288,833 122,644 64,985 68,501 NA 14,327 18,376 NA NA
1968 584,864 130,244 30,331 389,549 5,639 22,506 6,595 NA NA
1969 411,523 94,705 36,774 254,739 8,908 8,731 7,029 637 NA
1970 420,117 63,266 35,666 288,099 3,622 15,492 13,972 NA NA
1971 402,894 81,671 38,921 214,726 20,413 14,262 32,900 NA NA
1972 458,024 92,499 75,381 253,301 15,609 4,575 5,503 11,157 NA
1973 527,719 93,251 39,309 351,594 19,651 20,632 917 2,365 NA
1974 414,745 84,061 58,397 228,654 17,678 13,923 12,033 NA NA
1975 393,424 96,603 37,700 193,389 15,508 16,367 33,856 NA NA
1976 589,326 87,770 69,487 357,281 28,286 15,943 30,559 NA NA
1977 554,807 93,640 91,783 295,733 3,887 64,829 4,299 637 NA
1978 503,146 68,520 119,234 224,655 33,240 14,039 42,505 NA 953
1979 542,187 103,980 184,326 191,071 7,557 35,657 18,506 1,091 NA
1980 556,230 113,376 196,535 173,144 29,566 29,381 12,636 1,592 NA
1981 716,811 62,323 108,170 492,521 4,640 20,143 29,015 NA NA
1982 443,997 76,033 83,402 226,717 6,802 20,752 29,058 1,233 NA
1983 515,761 73,646 103,921 288,059 6,802 16,223 22,175 NA 4,935
1984 712,473 85,552 390,565 216,021 1,727 15,204 656 637 2,111
1985 476,447 97,031 97,397 213,078 16,178 27,120 23,608 1,274 761
1986 626,995 67,808 166,772 318,972 29,908 19,903 20,324 2,547 761
1987 474,423 71,813 46,330 278,839 24,169 22,678 29,565 NA 1,029
1988 373,535 90,292 62,118 161,586 31,635 4,289 23,615 NA NA
1989 403,870 63,108 105,130 182,213 16,087 20,171 16,070 1,091 NA
1990 329,654 47,256 81,418 141,407 19,303 5,714 33,919 637 NA
1991 319,935 51,750 79,173 142,770 10,588 17,991 13,345 4,318 NA
1992 561,508 34,169 69,295 378,446 10,077 44,362 25,160 NA NA
1993 592,296 69,266 90,378 382,228 9,506 34,685 4,718 1,515 NA
1994 486,347 59,441 152,575 222,756 15,063 34,758 322 1,432 NA
1995 651,105 73,979 102,050 395,398 31,397 41,859 5,221 1,202 NA
1996 1,209,365 77,925 39,271 989,700 6,081 53,002 42,518 869 NA
1997 752,838 67,189 90,999 521,320 6,934 37,413 28,105 878 NA
1998 723,879 77,213 102,711 394,404 44,718 66,664 37,420 749 NA
1999 681,845 69,244 54,072 494,437 5,759 29,493 27,438 1,401 NA
2000 894,230 55,738 91,246 639,831 26,529 40,509 38,645 478 1,255
2001 789,063 95,654 88,665 542,721 22,588 10,151 29,283 NA NA
2002 705,198 80,585 58,751 518,201 6,573 21,405 18,046 1,637 NA
2003 764,148 75,732 197,144 336,340 34,241 64,759 55,932 NA NA
2004 567,279 92,544 66,420 345,089 26,271 16,010 20,433 512 NA
2005 490,250 61,139 22,147 284,761 10,586 88,472 23,144 NA NA
2006 880,745 88,084 231,163 426,693 50,371 70,527 13,907 NA NA
2007 800,339 38,258 191,734 448,215 28,213 60,877 32,299 NA 744
2008 640,093 52,622 117,663 336,844 37,636 66,185 27,858 558 729
2009 687,744 32,202 138,391 434,596 13,679 28,559 38,642 947 727
2010 693,268 40,990 231,031 291,515 58,030 60,547 11,154 NA NA
2011 846,139 49,702 465,088 248,979 36,574 33,586 12,211 NA NA
2012 754,542 41,856 346,498 254,292 25,697 59,332 26,181 NA 685
2013 789,230 49,222 385,027 226,127 42,003 44,422 42,429 NA NA
2014 535,933 35,176 216,578 188,917 37,832 28,415 19,310 9,705 NA
2015 630,043 33,530 345,993 135,151 31,357 51,216 24,306 8,490 NA
2016 644,289 20,533 409,198 79,828 25,619 59,382 47,885 1,846 NA
2017 568,817 35,681 276,883 85,886 62,045 49,116 59,206 NA NA
2018 644,894 28,803 377,761 112,444 33,374 55,765 36,746 NA NA
2019 663,209 19,515 391,539 82,367 37,429 88,700 43,658 NA NA
2020 NA NA NA NA NA NA NA NA NA
2021 NA NA NA NA NA NA NA NA NA
2022 712,013 155,489 248,185 125,735 59,657 42,835 79,093 1,019 NA
2023 636,229 59,486 268,329 178,812 19,285 60,930 46,750 2,637 NA
2024 975,425 58,159 596,882 216,457 23,466 69,032 10,170 1,259 NA
2025 814,292 64,639 441,700 166,390 23,174 107,007 7,729 3,003 651

Figure 63: Goldeneye (Barrow’s and common spp.) abundance in the WBPHS Traditional Survey Area in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 65: Canada Goose WBPHS

Original data source: WBPHS Traditional Survey Area; USFWS Headquarters.

Table 65. Canada goose abundance in the WBPHS Traditional Survey Area in spring, 1955-2025.
Year TSA Area1 Area2 Area3 Area4 Area5 Area6 Area7 Area8
1955 1,108,437 610,345 361,627 93,959 NA 5,578 0 36,928 0
1956 1,158,096 594,604 413,999 80,324 692 770 31,516 36,192 0
1957 874,803 624,573 148,574 48,708 17,160 NA 0 35,787 0
1958 818,422 385,786 285,519 58,675 35,377 14,160 3,256 35,648 0
1959 1,200,811 472,587 502,838 150,686 31,231 7,779 0 35,690 NA
1960 1,037,678 626,406 264,636 44,806 50,562 14,951 483 35,833 NA
1961 884,771 565,965 131,254 102,246 37,859 11,428 0 36,018 NA
1962 951,400 742,225 90,671 43,670 24,724 13,905 0 36,204 NA
1963 849,017 506,027 232,526 30,088 34,063 9,914 0 36,399 NA
1964 786,608 624,289 17,672 50,986 37,997 19,162 0 36,502 NA
1965 654,329 383,256 76,636 137,870 24,002 12,829 685 19,052 NA
1966 508,508 261,344 152,656 56,087 19,015 16,943 0 138 2,325
1967 598,203 272,516 138,898 97,202 34,570 8,046 1,192 44,915 863
1968 599,866 351,249 73,080 113,070 15,014 4,923 343 42,187 NA
1969 742,312 384,305 85,286 170,198 23,506 28,629 0 42,867 7,520
1970 726,862 399,002 131,465 85,544 28,388 22,116 9,038 50,445 863
1971 755,964 367,339 122,435 90,883 49,958 47,294 14,788 63,268 NA
1972 496,158 199,166 120,743 67,252 30,538 26,725 16,753 33,666 1,316
1973 452,536 230,747 72,833 56,989 35,658 16,419 15,705 18,823 5,362
1974 467,268 269,202 39,613 62,018 29,195 25,200 15,372 22,772 3,897
1975 464,688 208,640 93,353 65,828 30,151 24,986 13,395 23,733 4,602
1976 420,410 171,849 57,848 97,570 19,807 34,759 6,354 28,251 3,971
1977 456,534 225,481 45,239 89,444 23,833 25,592 14,986 29,575 2,383
1978 657,616 266,008 63,605 205,993 30,234 35,289 20,456 29,250 6,780
1979 624,843 251,270 72,345 156,520 35,517 42,371 17,793 43,693 5,334
1980 552,667 229,166 61,360 123,395 21,053 43,968 30,021 37,313 6,392
1981 727,901 260,563 146,690 138,079 45,574 58,981 29,507 38,168 10,338
1982 683,122 297,158 78,911 98,414 40,301 62,481 22,514 51,660 31,684
1983 750,704 208,369 178,745 140,016 41,675 84,970 38,771 41,473 16,685
1984 686,882 247,176 73,055 114,955 46,810 91,321 29,762 58,294 25,509
1985 784,499 206,558 182,654 142,920 49,560 94,650 32,238 56,165 19,754
1986 805,298 184,820 177,375 144,632 79,626 117,335 39,126 40,769 21,615
1987 958,467 172,934 352,555 158,368 58,972 118,417 27,888 46,341 22,992
1988 1,115,857 196,496 288,852 223,260 95,545 116,221 53,178 108,391 33,914
1989 1,085,366 218,183 166,504 194,374 79,262 162,170 85,257 118,347 61,270
1990 1,110,110 247,388 139,163 212,638 113,796 184,035 42,615 119,018 51,457
1991 1,069,658 282,468 176,844 178,098 66,754 188,664 43,853 85,671 47,304
1992 1,079,908 272,975 164,267 185,508 100,102 140,492 45,423 114,232 56,910
1993 1,070,343 211,801 193,893 200,976 85,085 163,064 53,370 115,405 46,750
1994 1,146,378 296,216 113,618 211,068 129,029 196,620 36,111 102,414 61,301
1995 1,356,617 282,139 205,632 238,288 157,999 220,011 42,492 123,179 86,878
1996 1,359,171 319,049 200,011 222,897 160,180 176,800 48,255 125,166 106,812
1997 1,277,857 297,214 108,257 168,845 109,846 289,587 69,217 105,944 128,947
1998 1,505,661 290,652 153,368 184,178 191,615 373,284 51,407 111,632 149,524
1999 1,557,754 255,682 257,627 311,984 151,764 238,380 41,806 107,447 193,065
2000 1,778,758 249,972 230,446 269,947 269,503 294,412 42,760 144,826 276,892
2001 1,729,295 291,399 241,724 209,284 213,491 289,125 42,041 139,613 302,618
2002 1,627,739 202,847 274,857 297,117 196,938 288,865 72,656 118,581 175,876
2003 1,753,805 304,306 198,853 228,108 193,319 391,948 74,642 85,858 276,772
2004 1,667,902 203,208 212,254 283,647 214,612 267,235 124,172 99,047 263,726
2005 1,714,409 231,086 209,175 298,178 212,194 283,553 58,339 103,295 318,591
2006 1,770,423 281,661 233,093 209,248 181,515 303,543 137,514 112,497 311,352
2007 2,137,543 284,734 310,878 219,235 219,835 380,451 117,456 152,486 452,468
2008 2,380,258 362,447 375,905 332,067 330,786 419,878 125,866 124,389 308,920
2009 2,124,526 265,595 242,286 288,541 187,133 465,839 146,593 127,136 401,403
2010 2,456,433 429,544 386,364 291,662 190,199 396,696 181,268 124,684 456,016
2011 2,567,036 268,905 394,172 362,473 170,072 580,027 176,333 52,238 562,814
2012 2,895,974 265,154 375,449 378,927 250,884 723,905 167,838 90,247 643,570
2013 2,436,483 217,308 355,556 283,117 244,410 490,779 175,570 109,097 560,646
2014 2,353,311 271,723 299,034 452,569 226,157 443,407 142,806 86,062 431,554
2015 2,665,423 167,950 535,750 444,245 270,319 527,645 173,632 128,614 417,268
2016 3,309,739 320,140 490,630 576,314 365,612 728,613 215,400 197,416 415,615
2017 2,757,948 236,875 341,964 454,472 308,791 641,469 187,992 193,899 392,485
2018 2,863,476 184,787 394,585 453,871 357,423 719,921 215,649 175,466 361,772
2019 2,909,203 231,144 452,424 445,134 309,957 660,476 234,623 115,906 459,540
2020 NA NA NA NA NA NA NA NA NA
2021 NA NA NA NA NA NA NA NA NA
2022 3,348,450 144,024 504,247 482,704 439,473 622,739 229,767 189,909 735,587
2023 2,348,012 152,315 495,014 403,622 318,781 429,751 125,981 106,814 315,734
2024 2,428,130 160,745 482,638 517,023 194,150 535,431 152,344 107,578 278,222
2025 2,542,508 202,327 499,545 461,572 295,104 453,425 144,770 126,579 359,184

Figure 64: Canada goose abundance in the WBPHS Traditional Survey Area in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 66: Swan WBPHS

Original data source: WBPHS Traditional Survey Area; USFWS Headquarters.

Table 66. Swan abundance in the WBPHS Traditional Survey Area in spring, 1955-2025.
Year TSA Area1 Area2 Area3 Area4 Area5 Area6 Area7 Area8
1972 93,541 63,642 29,899 NA NA NA NA NA NA
1973 142,825 72,462 69,603 466 163 NA NA 131 NA
1974 137,196 90,065 46,920 20 191 NA NA NA NA
1975 122,421 77,541 7,225 31,209 6,315 NA NA 131 NA
1976 184,301 154,378 27,845 1,362 716 NA NA NA NA
1977 135,360 94,488 36,949 1,525 1,893 NA NA 506 NA
1978 136,923 102,479 24,654 9,660 NA NA NA 131 NA
1979 161,195 112,175 44,387 4,109 NA NA 524 NA NA
1980 166,335 111,175 43,485 11,674 NA NA NA NA NA
1981 194,307 106,905 82,305 5,097 NA NA NA NA NA
1982 179,387 136,281 42,654 134 318 NA NA NA NA
1983 212,834 118,970 86,732 7,133 NA NA NA NA NA
1984 151,516 95,496 51,281 2 199 NA 4,285 253 NA
1985 220,187 140,679 76,368 0 163 NA 2,471 506 NA
1986 165,748 100,721 61,948 NA NA 287 2,792 NA NA
1987 213,241 125,811 83,443 644 NA 300 3,043 NA NA
1988 195,089 135,667 52,760 NA 155 3,450 3,057 NA NA
1989 273,996 215,238 58,587 NA NA NA NA NA 171
1990 303,481 267,220 33,859 NA 357 1,243 NA 354 448
1991 146,926 129,177 16,275 NA NA 199 NA 506 770
1992 203,085 128,746 32,736 40,002 203 NA 1,228 NA 171
1993 172,836 138,026 32,922 1,755 NA 133 NA NA NA
1994 182,207 157,630 19,318 487 NA 502 3,934 335 NA
1995 280,547 175,378 87,124 17,852 NA 133 NA 61 NA
1996 188,847 172,322 14,301 1,133 210 880 NA NA NA
1997 267,960 212,828 43,333 4,546 902 862 5,489 NA NA
1998 214,579 214,579 NA NA NA NA NA NA NA
1999 243,982 194,463 40,956 6,693 395 1,327 NA 148 NA
2000 214,298 174,382 27,313 7,243 155 1,599 3,057 392 156
2001 162,938 136,318 22,937 1,587 610 509 977 NA NA
2002 139,662 116,138 17,693 2,766 803 302 1,743 131 86
2003 144,336 106,783 28,781 4,175 662 75 3,490 NA 370
2004 161,204 116,295 23,798 19,664 464 929 54 NA NA
2005 201,645 154,881 35,210 1,475 1,271 2,525 6,283 NA NA
2006 190,945 164,945 17,851 3,696 1,942 1,404 1,107 NA NA
2007 243,604 202,367 35,371 4,508 NA 974 385 NA NA
2008 192,010 160,623 20,427 2,037 1,687 3,922 3,313 NA NA
2009 199,807 125,198 27,149 44,252 NA 148 2,993 66 NA
2010 169,244 120,466 43,766 3,993 195 585 239 NA NA
2011 195,231 121,916 33,887 37,551 NA 691 717 NA 467
2012 173,652 123,595 45,565 2,583 293 1,057 453 NA 106
2013 152,366 118,128 31,988 793 163 281 506 NA 505
2014 136,439 95,580 28,316 1,108 252 7,621 3,561 NA NA
2015 174,921 118,183 47,526 8,449 NA 198 565 NA NA
2016 167,003 118,092 40,636 6,911 78 460 398 67 359
2017 182,973 117,556 54,125 9,611 177 290 724 NA 490
2018 166,589 110,111 32,187 17,970 1,196 290 4,247 132 456
2019 158,905 104,344 31,546 18,896 589 1,006 2,337 NA 187
2020 NA NA NA NA NA NA NA NA NA
2021 NA NA NA NA NA NA NA NA NA
2022 181,987 113,797 42,808 22,485 276 675 1,447 NA 499
2023 143,071 83,063 24,522 30,490 693 1,954 1,619 730 NA
2024 170,787 83,283 46,962 34,145 1,032 3,276 1,567 NA 523
2025 206,107 90,605 44,154 68,512 343 867 944 NA 683

Figure 65: Swan abundance in the WBPHS Traditional Survey Area in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 67: Merganser WBPHS

Original data source: WBPHS Traditional Survey Area; USFWS Headquarters.

Table 67. Merganser (common, hooded, and red-breasted spp.) abundance in the WBPHS Traditional Survey Area in spring, 1955-2025.
Year TSA Area1 Area2 Area3 Area4 Area5 Area6 Area7 Area8
1955 422,304 1,233 151,416 268,214 NA 455 196 789 0
1956 226,934 1,226 99,215 125,639 NA NA 0 853 0
1957 193,020 418 87,253 104,438 NA NA 0 911 0
1958 441,521 1,363 176,943 256,099 5,940 NA 193 963 21
1959 332,099 139 194,348 132,226 3,960 420 0 1,006 NA
1960 431,242 1,115 175,828 239,763 1,188 11,361 945 1,042 NA
1961 281,354 456 148,953 127,505 396 2,596 376 1,072 NA
1962 319,002 7,721 96,812 213,369 NA NA 0 1,100 NA
1963 364,370 4,706 105,154 243,809 NA 9,399 0 1,302 NA
1964 287,031 597 99,210 172,354 1,584 2,433 9,691 1,162 NA
1965 344,012 2,054 109,084 207,765 9,268 5,219 8,957 1,665 NA
1966 326,022 2,132 78,950 231,160 7,746 NA 4,470 233 1,331
1967 400,185 7,715 58,742 324,226 1,814 NA 0 7,688 NA
1968 272,806 309 19,815 249,696 1,100 989 188 708 NA
1969 377,076 959 30,213 339,148 1,691 1,443 759 2,863 NA
1970 340,272 2,368 48,584 268,300 9,443 8,809 2,768 NA NA
1971 258,049 1,786 17,977 232,374 4,056 1,260 595 NA NA
1972 325,771 6,056 30,633 277,156 4,187 NA 5,599 2,140 NA
1973 286,191 3,755 32,672 235,672 2,101 2,178 7,470 2,343 NA
1974 315,677 3,355 21,125 269,667 NA 455 16,818 4,257 NA
1975 495,385 5,155 33,624 416,094 16,428 7,523 15,145 1,416 NA
1976 355,104 2,199 85,644 256,347 NA 5,323 4,764 827 NA
1977 494,457 7,852 143,165 323,670 4,800 3,364 8,950 2,656 NA
1978 665,003 11,504 168,550 450,802 16,088 6,486 9,624 1,948 NA
1979 491,048 5,535 124,388 308,489 5,678 12,983 27,356 4,073 2,546
1980 649,377 5,230 138,964 434,005 17,961 6,849 45,568 800 NA
1981 557,177 6,721 53,313 413,307 13,594 14,552 47,188 8,502 NA
1982 407,775 8,662 60,497 298,868 15,473 3,431 11,642 3,430 5,772
1983 641,437 7,228 78,522 461,967 15,322 5,941 60,491 NA 11,966
1984 619,018 20,221 116,503 427,788 4,906 17,722 21,659 5,607 4,613
1985 542,473 25,064 75,508 403,917 8,875 1,855 26,003 708 543
1986 445,744 24,710 34,330 363,322 8,645 NA 11,962 2,775 NA
1987 548,077 21,569 69,242 423,606 10,069 6,872 14,228 1,948 543
1988 526,758 24,094 62,811 397,478 21,560 5,817 11,487 3,017 494
1989 440,937 8,420 74,537 320,212 8,593 3,650 19,204 5,241 1,080
1990 447,878 10,141 91,708 292,192 4,982 7,945 34,190 4,548 2,172
1991 543,841 14,142 44,707 440,703 15,245 6,458 11,092 8,923 2,571
1992 547,418 19,222 125,943 372,391 8,721 3,820 16,056 1,266 NA
1993 528,314 23,047 71,091 410,540 6,295 3,548 10,407 3,093 293
1994 801,020 21,038 109,992 649,562 6,943 2,282 6,199 4,499 506
1995 610,362 16,648 70,811 491,555 10,436 7,544 4,408 7,025 1,935
1996 797,726 39,454 31,939 686,363 5,931 4,005 26,171 3,067 797
1997 852,869 25,159 49,740 697,839 9,796 6,455 53,357 9,152 1,371
1998 409,939 24,670 48,519 313,895 5,416 6,773 4,652 4,976 1,037
1999 476,592 15,102 96,031 299,814 8,136 2,623 38,879 16,006 NA
2000 762,848 32,794 187,976 484,305 5,061 9,187 26,394 15,215 1,914
2001 708,932 27,356 109,312 517,384 8,471 21,194 16,060 7,991 1,164
2002 1,048,311 22,772 96,605 893,503 10,460 2,960 10,979 11,032 NA
2003 1,028,957 20,416 116,609 876,838 2,560 2,427 6,618 3,489 NA
2004 1,082,580 22,012 46,745 997,439 4,211 3,078 6,064 1,819 1,211
2005 637,203 36,247 36,445 546,148 1,927 4,141 9,548 2,747 NA
2006 560,923 27,033 66,657 442,098 1,627 3,129 17,994 2,051 333
2007 630,683 36,686 91,875 479,444 2,888 5,285 14,251 255 NA
2008 793,127 27,235 94,530 601,416 7,723 3,590 56,632 1,709 291
2009 703,661 24,499 109,337 528,382 16,411 9,075 10,982 4,974 NA
2010 688,776 30,975 130,363 474,563 21,095 5,586 22,109 1,680 2,406
2011 738,619 29,520 122,272 553,212 7,527 5,974 12,401 4,171 3,541
2012 626,749 33,602 78,057 470,765 23,287 2,147 10,722 6,301 1,869
2013 392,065 18,322 114,678 223,381 7,201 8,853 10,195 3,129 6,307
2014 672,165 29,803 124,487 458,222 2,661 12,161 25,232 11,456 8,142
2015 876,815 32,494 134,966 664,078 20,650 6,743 15,178 767 1,939
2016 911,701 27,156 115,186 727,986 14,851 9,907 10,602 2,248 3,766
2017 999,239 44,457 52,183 862,058 15,762 16,463 4,817 1,675 1,824
2018 876,574 37,441 59,680 750,374 3,082 5,629 13,977 3,995 2,395
2019 662,728 27,392 81,348 505,697 5,776 10,454 8,444 19,360 4,256
2020 NA NA NA NA NA NA NA NA NA
2021 NA NA NA NA NA NA NA NA NA
2022 708,987 20,577 92,501 552,223 6,093 11,528 19,414 4,056 2,594
2023 757,376 31,080 117,758 582,753 5,929 5,026 7,174 1,798 5,859
2024 857,212 31,926 107,124 687,902 3,760 7,134 13,591 3,198 2,577
2025 809,107 45,712 151,130 563,635 10,651 11,920 15,014 4,243 6,803

Figure 66: Merganser (common, hooded, and red-breasted spp.) bundance in the WBPHS Traditional Survey Area in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 68: American Coot WBPHS

Original data source: WBPHS Traditional Survey Area; USFWS Headquarters.

Table 68. American coot abundance in the WBPHS Traditional Survey Area in spring, 1955-2025.
Year TSA Area1 Area2 Area3 Area4 Area5 Area6 Area7 Area8
1955 654,372 85 30,748 NA 141,262 360,714 18,772 49,259 53,532
1956 869,216 238 5,473 NA 108,038 604,698 45,684 46,436 58,649
1957 632,467 5 0 NA 56,605 438,843 27,830 44,431 64,753
1958 424,735 0 0 NA 98,069 127,546 76,960 46,586 75,574
1959 944,514 0 156,775 138,300 169,760 145,323 170,796 54,926 108,634
1960 525,652 0 3,884 41,852 120,075 111,952 87,532 39,973 120,384
1961 584,168 5 62,589 114,327 92,872 70,527 125,400 41,175 77,273
1962 383,055 0 23,713 24,690 19,746 78,951 32,780 38,259 164,916
1963 375,799 6,353 22,846 86,096 82,177 27,371 43,635 45,559 61,762
1964 340,280 6 18,799 86,047 39,957 50,484 37,394 39,997 67,596
1965 397,989 6 5,654 90,386 65,136 63,564 46,199 24,481 102,564
1966 441,544 6 35,540 50,462 48,130 83,356 20,318 32,620 171,112
1967 822,466 6 6,608 105,549 202,542 178,983 74,096 36,993 217,690
1968 1,284,008 6 82,071 581,132 98,780 214,325 46,404 69,579 191,711
1969 775,394 6 13,549 39,187 144,825 203,789 120,689 43,784 209,564
1970 1,168,192 7 9,611 62,932 169,841 450,341 169,108 60,629 245,723
1971 960,145 7 20,484 45,333 99,723 481,517 120,880 18,832 173,369
1972 933,308 7 32,012 26,785 122,608 284,899 159,683 66,982 240,332
1973 1,236,505 7 167,405 99,558 145,425 465,919 69,406 89,131 199,654
1974 1,513,180 7 30,827 21,797 266,979 544,311 230,322 58,588 360,350
1975 2,257,919 7 36,637 52,858 483,329 799,782 282,924 64,175 538,207
1976 2,392,079 7 27,056 67,812 83,519 1,512,966 470,430 110,452 119,837
1977 1,664,828 7 428,722 318,816 285,358 269,357 179,959 114,314 68,295
1978 1,444,124 7 65,559 75,853 168,357 317,848 111,315 158,991 546,194
1979 3,458,968 7 7,730 29,570 417,979 787,159 182,855 528,084 1,505,584
1980 2,956,046 7 415,657 497,244 501,055 634,230 330,575 128,516 448,762
1981 2,682,441 7 198,729 777,010 405,024 395,073 157,473 228,089 521,035
1982 1,668,518 7 68,725 123,476 371,736 175,368 111,878 68,870 748,458
1983 1,820,007 7 138,412 40,315 253,247 546,681 123,936 117,217 600,193
1984 2,903,119 94 91,666 116,860 542,666 507,406 38,308 218,321 1,387,798
1985 1,682,385 NA 69,291 70,032 327,286 530,572 33,778 223,265 428,161
1986 1,699,157 NA 34,233 22,373 282,225 315,049 212,457 39,596 793,224
1987 1,780,300 NA 83,629 255,144 137,883 241,678 77,065 47,711 937,190
1988 3,223,206 NA 232,749 340,855 166,147 930,687 591,810 124,800 836,158
1989 1,640,876 NA 158,090 199,565 349,532 276,168 60,145 110,533 486,844
1990 1,664,462 NA 197,152 61,738 485,709 261,462 151,795 195,396 311,210
1991 1,151,959 NA 92,552 143,595 279,675 366,579 81,071 113,526 74,961
1992 1,380,235 NA 114,937 67,569 307,393 442,607 215,542 19,991 212,197
1993 1,025,062 NA 92,495 167,011 282,101 111,818 32,198 80,306 259,134
1994 1,712,227 NA 50,381 32,252 234,680 383,314 35,778 77,140 898,682
1995 3,438,877 NA 37,511 21,824 232,937 625,223 195,400 67,097 2,258,884
1996 3,131,109 NA 41,342 15,484 234,396 868,111 281,166 81,590 1,609,019
1997 4,915,601 NA 253,835 19,161 377,464 1,661,101 282,918 346,183 1,974,940
1998 3,138,078 NA 467,038 60,300 260,003 594,337 506,699 201,210 1,048,492
1999 3,069,152 NA 159,571 57,896 342,322 823,675 162,542 192,611 1,330,535
2000 3,659,459 NA 615,563 209,259 418,760 848,496 284,810 117,226 1,165,344
2001 1,845,852 NA 87,215 73,741 207,397 679,246 315,350 84,329 398,574
2002 2,518,449 NA 584,907 294,583 376,090 306,829 246,718 65,048 644,275
2003 1,195,485 NA 101,998 12,393 222,264 633,882 107,401 27,219 90,329
2004 1,862,040 NA 294,932 105,426 240,183 536,335 83,747 85,186 516,231
2005 1,591,035 NA 220,265 25,509 240,935 806,864 175,411 18,123 103,928
2006 2,102,263 NA 195,126 19,994 418,974 1,188,247 103,699 23,264 152,958
2007 2,591,169 468 87,724 25,832 444,380 1,406,277 81,656 66,738 478,095
2008 3,625,954 NA 281,459 43,538 667,924 1,640,884 129,965 244,744 617,439
2009 2,259,385 NA 62,253 42,205 321,137 601,935 253,161 128,910 849,784
2010 2,409,179 NA 129,577 5,177 333,652 590,896 46,784 151,379 1,151,715
2011 3,624,396 NA 49,405 9,113 488,029 1,336,121 226,997 117,293 1,397,439
2012 4,700,325 NA 88,659 3,952 498,022 2,333,385 110,731 110,888 1,554,685
2013 2,819,367 NA 41,866 2,153 521,606 1,106,576 141,258 27,334 978,573
2014 4,004,160 NA 45,556 2,907 775,060 1,505,727 208,362 244,294 1,222,254
2015 3,064,423 NA 134,372 12,868 420,134 1,792,217 256,800 114,825 333,209
2016 2,818,801 NA 142,341 5,930 376,842 1,482,890 204,577 120,712 485,510
2017 2,146,931 NA 43,184 1,429 547,897 929,750 161,970 24,550 438,151
2018 1,602,978 NA 58,946 3,300 295,120 356,532 149,497 250,255 489,329
2019 1,644,905 NA 45,703 20,300 543,264 142,118 15,170 118,401 759,949
2020 NA NA NA NA NA NA NA NA NA
2021 NA NA NA NA NA NA NA NA NA
2022 1,175,333 NA 116,452 20,856 275,090 231,645 52,596 23,075 455,618
2023 964,444 NA 41,901 1,374 80,136 194,586 50,929 19,871 575,647
2024 1,254,151 NA 65,150 7,088 152,265 413,800 49,130 79,785 486,934
2025 1,124,421 NA 26,174 11,748 106,508 667,831 107,578 57,575 147,006

Figure 67: American coot abundance in the WBPHS Traditional Survey Area in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 69: Total Ducks State Surveys

Original data source: Breeding Waterfowl Surveys in British Columbia, Washington, Oregon, and California. Data maintained by British Columbia, Washington, Oregon, California, and USFWS Pacific Flyway Office.

Table 69. Total duck abundance in Pacific Flyway States in spring, 1992-2025.
Year BC BC.SE WA WA.SE OR OR.SE CA CA.SE Total Total.SE
1992 NA NA NA NA NA NA 497,441 62,646 NA NA
1993 NA NA NA NA NA NA 666,729 80,275 NA NA
1994 NA NA NA NA 322,756 24,327 483,207 45,480 NA NA
1995 NA NA NA NA 216,204 13,072 589,712 51,521 NA NA
1996 NA NA NA NA 289,169 19,658 843,708 90,314 NA NA
1997 NA NA NA NA 360,117 24,824 824,337 118,571 NA NA
1998 NA NA NA NA 345,661 18,062 706,789 80,937 NA NA
1999 NA NA NA NA 320,633 16,086 850,956 113,428 NA NA
2000 NA NA NA NA 309,715 17,109 562,416 62,535 NA NA
2001 NA NA NA NA NA NA 413,531 47,469 NA NA
2002 NA NA NA NA 260,372 14,095 391,953 34,977 NA NA
2003 NA NA NA NA 244,287 15,058 533,730 55,195 NA NA
2004 NA NA NA NA 226,859 15,128 412,799 41,240 NA NA
2005 NA NA NA NA 207,761 16,286 615,241 66,754 NA NA
2006 364,462 17,990 NA NA 248,538 12,076 649,376 67,641 NA NA
2007 383,892 18,078 NA NA 318,225 34,177 627,606 68,382 NA NA
2008 377,121 22,367 NA NA 220,655 15,464 554,294 58,962 NA NA
2009 349,746 18,122 NA NA 182,499 11,191 510,780 71,563 NA NA
2010 339,250 16,506 200,056 15,348 204,660 11,646 541,368 60,159 1,285,335 65,290
2011 277,775 12,772 155,028 11,931 155,911 7,975 558,491 57,586 1,147,206 60,706
2012 313,715 15,584 167,279 10,538 260,041 15,934 529,703 57,512 1,270,738 62,574
2013 333,558 16,863 156,091 11,902 250,569 14,411 451,275 58,129 1,191,493 63,345
2014 355,815 17,662 172,837 15,802 313,000 37,172 448,749 69,360 1,290,401 82,184
2015 365,779 18,396 191,288 21,141 278,503 18,521 315,577 42,005 1,151,148 53,785
2016 321,342 16,889 119,048 6,972 213,270 12,070 417,363 41,998 1,071,023 47,364
2017 351,280 19,382 239,048 13,435 238,939 14,589 394,956 42,751 1,224,223 50,957
2018 346,286 16,371 277,256 21,680 293,547 21,995 548,821 59,113 1,465,910 68,674
2019 418,861 24,975 244,019 15,531 250,963 14,044 469,768 48,800 1,383,611 58,683
2020 NA NA NA NA NA NA NA NA NA NA
2021 NA NA NA NA 260,062 19,520 NA NA NA NA
2022 390,585 22,445 215,203 20,182 344,034 30,998 379,511 42,562 1,329,334 60,691
2023 369,069 19,276 201,754 15,472 197,490 15,733 495,438 51,647 1,263,750 59,379
2024 437,156 23,086 155,989 11,862 302,089 39,546 373,864 38,606 1,269,097 61,057
2025 416,637 17,791 156,096 9,848 267,222 17,005 474,495 50,323 1,314,449 56,878

Figure 68: Total duck abundance in Pacific Flyway States in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Figure 69: Total duck abundance in British Columbia in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Figure 70: Total duck abundance in Washington in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Figure 71: Total duck abundance in Oregon in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Figure 72: Total duck abundance in California in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 70: Mallard State Surveys

Original data source: Breeding Waterfowl Surveys in British Columbia, Washington, Oregon, and California. Data maintained by British Columbia, Washington, Oregon, California, and USFWS Pacific Flyway Office.

Table 70. Mallard abundance in Pacific Flyway States in spring, 1992-2025.
Year BC BC.SE WA WA.SE OR OR.SE CA CA.SE Total Total.SE
1992 NA NA NA NA NA NA 375,844 59,873 NA NA
1993 NA NA NA NA NA NA 359,008 50,253 NA NA
1994 NA NA NA NA 116,365 13,279 311,692 40,362 NA NA
1995 NA NA NA NA 77,843 7,328 368,526 42,126 NA NA
1996 NA NA NA NA 102,664 8,957 536,709 79,656 NA NA
1997 NA NA NA NA 121,796 12,599 511,344 103,580 NA NA
1998 NA NA NA NA 125,998 10,674 353,901 47,746 NA NA
1999 NA NA NA NA 126,115 9,304 560,063 106,201 NA NA
2000 NA NA NA NA 105,857 8,526 347,559 52,463 NA NA
2001 NA NA NA NA NA NA 302,204 44,361 NA NA
2002 NA NA NA NA 103,493 8,774 265,295 31,385 NA NA
2003 NA NA NA NA 87,914 7,718 337,056 49,485 NA NA
2004 NA NA NA NA 82,461 6,900 262,424 34,483 NA NA
2005 NA NA NA NA 74,102 6,377 317,869 46,930 NA NA
2006 90,404 8,628 NA NA 81,095 6,770 399,436 57,229 NA NA
2007 98,840 7,900 NA NA 92,445 7,420 388,324 54,106 NA NA
2008 81,124 5,914 NA NA 75,363 6,725 297,129 47,349 NA NA
2009 72,505 5,287 NA NA 72,616 5,867 301,960 63,641 NA NA
2010 81,131 6,121 92,911 11,680 66,762 5,657 367,891 55,412 608,696 57,240
2011 69,726 6,872 71,375 9,456 61,556 4,637 314,715 44,975 517,373 46,700
2012 75,561 8,401 89,468 8,203 88,803 7,505 387,061 54,532 640,892 56,284
2013 82,944 7,613 74,406 8,917 84,336 6,431 298,636 52,290 540,322 53,973
2014 82,633 6,805 86,344 10,250 85,259 8,572 238,666 54,606 492,901 56,628
2015 81,377 6,873 86,417 9,041 87,361 8,611 173,865 28,175 429,020 31,574
2016 73,991 6,216 59,864 4,681 87,346 8,038 263,774 35,602 484,975 37,319
2017 70,903 6,944 103,384 9,770 71,720 6,138 198,392 31,863 444,400 34,592
2018 79,309 5,697 124,935 10,013 97,148 11,407 272,859 42,037 574,251 45,055
2019 75,655 7,385 126,243 12,114 83,867 6,992 239,831 32,223 525,595 35,895
2020 NA NA NA NA NA NA NA NA NA NA
2021 NA NA NA NA 76,259 8,574 NA NA NA NA
2022 80,883 5,872 87,374 7,408 79,388 8,645 179,393 29,275 427,037 31,955
2023 70,757 6,058 102,011 10,547 68,587 7,026 202,108 28,506 443,463 31,779
2024 96,676 7,567 86,360 9,553 71,047 6,915 177,828 21,576 431,910 25,726
2025 81,296 5,824 77,037 6,541 79,525 6,856 265,640 39,610 503,499 41,142

Figure 73: Mallard abundance in Pacific Flyway States in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Figure 74: Mallard abundance in British Columbia in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Figure 75: Mallard abundance in Washington in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Figure 76: Mallard abundance in Oregon in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Figure 77: Mallard abundance in California in spring. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 71: Ponds

Original data source: WBPHS Traditional Survey Area; USFWS Headquarters.

Provided in the table below are estimated pond abundance and standard error (SE) in May in Prairie and Parkland Canada (Can), northcentral United States (US), and both areas combined (Total). Estimates are corrected for Visibility bias.

Prairie and Parkland Canada includes the following WBPHS crew areas:
Area 4 = Southern Alberta (strata 26–29, 75–76)
Area 5 = Southern Saskatchewan (strata 30–33)
Area 6 = Southern Manitoba (strata 34–40; includes south east Saskatchewan)

Northcentral U.S. includes the following WBPHS crew areas:
Area 7 = Montana and western Dakotas (strata 41–44)
Area 8 = Eastern Dakotas (strata 45–49)

Table 71. Number of Ponds in May, 1961-2025.
Year Area4 Area5 Area6 Area7 Area8 Can Can.SE US US.SE Total Total.SE
1961 595,735 794,850 586,607 NA NA 1,977,192 165,394 NA NA NA NA
1962 606,153 1,229,341 533,595 NA NA 2,369,089 184,593 NA NA NA NA
1963 777,617 1,024,486 679,923 NA NA 2,482,026 129,302 NA NA NA NA
1964 644,452 1,817,184 909,081 NA NA 3,370,717 173,006 NA NA NA NA
1965 998,829 2,257,381 1,122,604 NA NA 4,378,814 212,224 NA NA NA NA
1966 863,904 2,624,331 1,066,280 NA NA 4,554,515 229,284 NA NA NA NA
1967 919,063 2,652,165 1,119,958 NA NA 4,691,186 272,063 NA NA NA NA
1968 437,956 1,212,458 335,265 NA NA 1,985,679 120,210 NA NA NA NA
1969 859,496 2,225,018 463,097 NA NA 3,547,611 221,944 NA NA NA NA
1970 882,711 2,957,098 1,035,230 NA NA 4,875,039 251,183 NA NA NA NA
1971 981,446 2,317,386 754,575 NA NA 4,053,407 200,405 NA NA NA NA
1972 731,130 2,264,389 1,013,724 NA NA 4,009,243 250,904 NA NA NA NA
1973 1,025,160 1,490,442 433,884 NA NA 2,949,486 197,610 NA NA NA NA
1974 1,394,626 3,546,330 1,449,142 341,979 1,498,809 6,390,098 308,345 1,840,788 197,168 8,230,886 365,994
1975 957,871 3,424,684 937,555 535,406 1,375,429 5,320,110 271,323 1,910,835 116,139 7,230,945 295,135
1976 831,596 2,578,541 1,188,661 412,377 979,161 4,598,798 197,107 1,391,538 99,248 5,990,336 220,684
1977 588,008 1,250,019 439,891 331,424 439,713 2,277,918 120,742 771,137 51,135 3,049,055 131,124
1978 619,872 2,221,846 780,337 637,878 952,514 3,622,055 157,964 1,590,392 81,729 5,212,447 177,854
1979 996,447 3,070,063 792,431 410,145 1,112,041 4,858,941 251,992 1,522,186 70,883 6,381,127 261,771
1980 460,572 1,393,629 286,703 284,474 476,885 2,140,904 107,664 761,359 35,840 2,902,263 113,473
1981 569,299 610,958 262,760 310,841 371,970 1,443,017 75,261 682,811 34,042 2,125,828 82,602
1982 631,097 2,194,731 359,036 562,051 895,907 3,184,864 178,613 1,457,958 86,409 4,642,822 198,416
1983 497,116 2,696,237 712,356 358,133 901,017 3,905,709 208,176 1,259,150 68,686 5,164,859 219,214
1984 537,896 1,525,766 409,405 462,872 1,303,330 2,473,067 196,553 1,766,202 90,759 4,239,269 216,496
1985 828,270 2,958,533 496,284 519,030 807,899 4,283,087 244,149 1,326,929 73,980 5,610,016 255,112
1986 727,517 2,349,649 947,507 733,419 1,001,405 4,024,673 174,414 1,734,824 74,363 5,759,497 189,605
1987 606,766 1,418,910 498,070 558,693 789,058 2,523,746 130,967 1,347,751 46,824 3,871,497 139,086
1988 417,876 1,059,801 632,471 357,511 433,147 2,110,148 132,387 790,658 39,404 2,900,806 138,127
1989 548,860 859,726 284,159 649,596 640,311 1,692,745 89,105 1,289,907 61,713 2,982,652 108,389
1990 772,135 1,382,776 662,381 442,754 248,443 2,817,292 138,274 691,197 45,944 3,508,489 145,707
1991 695,737 1,405,066 393,099 420,580 285,497 2,493,902 110,220 706,077 33,568 3,199,979 115,219
1992 503,220 1,615,926 664,768 462,561 362,402 2,783,915 141,637 824,963 30,813 3,608,877 144,950
1993 689,837 1,087,891 483,409 442,328 908,260 2,261,137 93,965 1,350,587 57,140 3,611,725 109,974
1994 720,376 2,653,118 395,653 962,833 1,252,789 3,769,148 173,940 2,215,621 88,816 5,984,769 195,304
1995 688,738 2,314,362 889,438 825,170 1,617,685 3,892,538 223,833 2,442,856 106,805 6,335,394 248,009
1996 903,866 3,268,868 829,829 902,388 1,577,293 5,002,562 184,856 2,479,681 135,268 7,482,243 229,061
1997 1,100,439 2,992,048 968,497 756,365 1,640,868 5,060,983 180,267 2,397,232 94,391 7,458,216 203,485
1998 559,344 1,470,224 492,107 680,035 1,385,219 2,521,674 133,818 2,065,254 89,212 4,586,928 160,829
1999 716,010 2,535,347 610,678 672,298 2,169,952 3,862,035 157,247 2,842,249 256,836 6,704,284 301,150
2000 553,127 1,403,711 465,656 428,971 1,095,479 2,422,494 96,068 1,524,450 99,895 3,946,944 138,593
2001 425,702 1,535,743 785,762 345,567 1,547,672 2,747,206 115,565 1,893,238 91,481 4,640,444 147,391
2002 476,860 634,919 327,196 347,072 933,977 1,438,975 104,989 1,281,050 63,425 2,720,025 122,659
2003 888,399 2,142,973 490,916 479,755 1,188,051 3,522,288 151,843 1,667,807 67,364 5,190,095 166,115
2004 510,705 1,461,334 540,569 597,396 809,592 2,512,608 130,985 1,406,989 101,715 3,919,596 165,840
2005 750,374 2,414,928 755,244 662,946 797,755 3,920,546 196,676 1,460,701 79,653 5,381,247 212,193
2006 995,829 2,718,951 734,763 614,710 1,029,680 4,449,543 221,455 1,644,390 85,449 6,093,933 237,369
2007 1,225,351 3,000,302 814,567 739,686 1,222,829 5,040,220 261,822 1,962,514 102,519 7,002,734 281,178
2008 848,745 1,608,348 597,691 531,398 845,197 3,054,784 147,649 1,376,595 71,893 4,431,379 164,222
2009 686,677 2,210,464 670,920 1,033,805 1,832,145 3,568,062 147,983 2,865,950 123,065 6,434,012 192,468
2010 678,361 2,668,056 382,276 594,917 2,341,424 3,728,693 203,354 2,936,342 142,264 6,665,035 248,177
2011 1,085,607 3,150,948 656,176 968,592 2,270,905 4,892,732 197,506 3,239,497 127,365 8,132,229 235,012
2012 806,528 2,677,563 401,020 427,756 1,231,101 3,885,110 146,454 1,658,858 52,660 5,543,968 155,634
2013 1,126,500 2,845,885 578,143 382,748 1,958,427 4,550,528 185,462 2,341,175 98,995 6,891,703 210,229
2014 1,218,436 2,743,585 667,868 965,631 1,585,672 4,629,889 168,291 2,551,303 106,538 7,181,192 199,178
2015 1,022,570 2,571,492 556,913 909,848 1,246,903 4,150,975 146,270 2,156,751 86,006 6,307,726 169,682
2016 757,633 2,087,656 649,173 672,255 845,741 3,494,462 147,237 1,517,995 52,727 5,012,457 156,394
2017 1,168,355 2,449,060 712,842 560,933 1,204,797 4,330,258 157,707 1,765,730 92,231 6,095,988 182,696
2018 1,178,976 1,935,672 545,502 752,955 814,285 3,660,150 147,618 1,567,240 90,205 5,227,390 172,998
2019 947,478 1,372,392 535,704 1,098,601 1,036,127 2,855,575 103,804 2,134,727 137,282 4,990,303 172,109
2020 NA NA NA NA NA NA NA NA NA NA NA
2021 NA NA NA NA NA NA NA NA NA NA NA
2022 711,490 2,035,248 726,760 549,422 1,433,968 3,473,498 157,523 1,983,390 98,159 5,456,888 185,603
2023 642,399 2,117,119 554,074 602,228 1,059,265 3,313,593 114,179 1,661,493 75,215 4,975,086 136,727
2024 676,851 1,454,054 550,343 655,301 1,822,942 2,681,247 117,417 2,478,242 125,510 5,159,490 171,871
2025 579,959 1,507,511 464,842 540,157 1,088,004 2,552,312 125,333 1,628,161 75,947 4,180,473 146,548

Figure 78: Number of ponds in May in Prairie and Parkland Canada and northcentral U.S. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long term average.

Figure 79: Number of ponds in May in Prairie and Parkland Canada. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long term average.

Figure 80: Number of ponds in May in northcentral U.S. Circles are annual estimates of abundance with 95% confidence intervals. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long term average.

Abundance (Ancillary Data)

Data Table 80: Brant, Pacific (fall-spring)

Original data source: Fall Izembek Survey and Spring Yukon Kuskokwim Delta Coastal Zone Survey; USFWS Alaska Region. Data maintained by USFWS Alaska Region. Also, fall age ratio data are from USGS Alaska Science Center in Anchorage, and these data are maintained by USGS Alaska Science Center.

Provided in the table below are estimated abundance and standard error (SE) of Pacific Population brant by survey. Surveys include the Fall Izembek Survey (Fall, count with no estimate of variance) and Yukon Kuskokwim Delta Coastal Zone Survey in spring for both breeding (Breeding) and total (Total) brant. Also provided are the Izembek fall age ratio (Ageratio) and standard error (Ageratio.SE). Additionally provided are the total abundance moving 3-year average (M3yr) and standard error (M3yr.SE).

Table 80. Brant abundance in fall and spring, 1986-2025.
Year Fall Breeding Breeding.SE Total Total.SE Ageratio Ageratio.SE M3yr M3yr.SE
1986 113,487 1,880 289 13,000 2,847 0.217 0.017 NA NA
1987 142,930 3,796 572 11,151 1,724 0.476 0.021 NA NA
1988 123,813 3,587 545 18,308 3,115 0.237 0.013 14,153 2,632
1989 146,038 4,111 546 25,434 4,282 0.269 0.016 18,298 3,215
1990 123,977 2,940 365 28,284 5,136 0.229 0.012 24,009 4,259
1991 128,457 4,189 573 19,486 3,056 0.309 0.013 24,401 4,245
1992 109,719 5,917 872 18,227 2,760 0.206 0.008 21,999 3,801
1993 143,539 4,394 515 29,940 4,475 0.305 0.009 22,551 3,511
1994 142,591 5,427 567 28,462 3,435 0.168 0.017 25,543 3,626
1995 147,193 5,543 614 30,859 4,183 0.397 0.019 29,754 4,055
1996 119,263 5,217 554 27,502 3,160 0.226 0.018 28,941 3,619
1997 132,830 6,408 693 28,389 3,786 0.210 0.018 28,916 3,733
1998 105,185 7,718 650 20,699 2,151 0.302 0.025 25,530 3,106
1999 131,134 8,092 816 19,356 2,288 0.241 0.019 22,815 2,840
2000 156,011 7,521 796 21,786 2,764 0.295 0.032 20,614 2,415
2001 112,554 5,198 619 28,109 3,418 0.094 0.008 23,084 2,861
2002 115,839 8,582 831 18,765 1,851 0.214 0.014 22,887 2,754
2003 135,944 3,432 436 19,069 2,169 0.133 0.010 21,981 2,570
2004 134,474 6,990 862 18,268 2,125 0.205 0.014 18,700 2,053
2005 152,712 5,505 627 19,539 2,423 0.357 0.019 18,959 2,243
2006 124,170 10,398 1,430 18,210 2,231 0.243 0.015 18,672 2,263
2007 140,897 8,641 987 18,595 2,253 0.283 0.014 18,782 2,304
2008 130,294 12,105 1,182 26,295 2,518 0.179 0.011 21,033 2,338
2009 169,429 8,660 1,255 22,201 2,185 0.302 0.015 22,364 2,323
2010 150,510 7,971 1,540 22,084 2,599 0.213 0.015 23,527 2,441
2011 126,028 11,804 1,477 15,186 1,719 0.207 0.018 19,824 2,197
2012 154,481 16,360 2,730 20,390 3,311 0.124 0.013 19,220 2,625
2013 157,781 12,891 2,330 21,496 3,754 0.170 0.011 19,024 3,055
2014 171,635 3,775 749 22,226 3,429 0.172 0.010 21,370 3,503
2015 160,984 3,802 501 20,198 2,039 0.181 0.009 21,307 3,163
2016 203,735 13,142 1,424 29,171 3,068 0.213 0.012 23,865 2,906
2017 154,811 11,103 1,806 20,154 2,543 0.128 0.009 23,174 2,584
2018 155,724 14,853 2,001 25,766 2,984 0.256 0.013 25,030 2,874
2019 157,087 12,223 1,376 19,979 2,247 0.305 0.015 21,966 2,609
2020 NA NA NA NA NA NA NA NA NA
2021 NA 9,431 1,431 18,935 2,349 0.315 0.017 21,560 2,547
2022 156,830 6,331 707 17,086 2,120 0.149 0.009 18,667 2,240
2023 NA 8,739 1,167 14,221 1,829 0.392 0.018 16,747 2,110
2024 NA 6,197 798 9,595 1,168 0.342 0.013 13,634 1,752
2025 NA 10,122 1,627 21,510 3,025 NA NA 15,108 2,150

Figure 81: Brant abundance in spring. Circles are annual estimates of abundance. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Figure 82: Brant breeding birds abundance in spring. Circles are annual estimates of abundance. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Figure 83: Brant age ratios in fall. Circles are annual estimates of age ratio. The blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 81: Brant, Pacific Winter

Original data source: Pacific Flyway Cooperative Pacific Brant Winter Survey; USFWS Alaska Region, British Columbia, Washington, Oregon, California and Mexico. Data maintained by USFWS Pacific Flyway Office.

Provided in the table below are abundance (counts) of brant in winter by geographic area including: Alaska (AK), British Columbia (BC), Washington (WA), Oregon (OR), California (CA), Baja Mexico (MX), and Mainland Mexico. Also provided are the total count and moving 3-year average (M3yr). So long as there are counts in North America and Mexico, the total winter count is interpreted as the minimum known population size with no variance.

Table 81. Pacific brant abundance in winter, 1951-2024.
Year AK BC WA OR CA MX.Baja MX.Main Total M3yr
1951 NA NA 21,639 2,110 48,131 93,200 0 165,080 NA
1952 NA NA 16,578 3,200 43,840 102,945 0 166,563 NA
1953 NA NA 27,473 1,509 37,557 87,905 0 154,444 162,029
1954 NA NA 15,376 1,560 28,750 86,316 0 132,002 151,003
1955 NA NA 21,915 1,686 34,070 76,679 0 134,350 140,265
1956 NA NA 15,914 2,073 38,510 52,743 0 109,240 125,197
1957 NA NA 20,701 1,493 35,848 73,380 0 131,422 125,004
1958 NA NA 25,219 2,778 26,560 71,305 4 125,866 122,176
1959 NA NA 10,815 1,121 10,750 71,305 1,400 95,391 117,560
1960 NA NA 17,614 652 3,771 113,087 1,115 136,239 119,165
1961 NA NA 16,675 1,330 6,853 138,625 4,355 167,838 133,156
1962 NA NA 25,815 2,266 23,510 116,245 2,400 170,236 158,104
1963 NA NA 20,400 2,639 2,388 101,575 13,240 140,242 159,439
1964 NA NA 34,169 2,000 8,353 117,470 23,290 185,282 165,253
1965 NA NA 19,938 1,325 3,372 117,350 24,915 166,900 164,141
1966 NA NA 22,175 798 3,284 115,601 19,505 161,363 171,182
1967 NA NA 21,235 1,523 3,824 111,755 41,315 179,652 169,305
1968 NA NA 15,746 865 1,729 111,600 24,400 154,340 165,118
1969 NA NA 10,063 382 166 97,400 35,075 143,086 159,026
1970 NA NA 8,916 963 207 98,200 33,400 141,686 146,371
1971 NA NA 10,915 1,374 130 105,800 31,000 149,219 144,664
1972 NA NA 4,328 1,047 0 91,200 28,200 124,775 138,560
1973 NA NA 5,911 2,544 950 85,500 30,100 125,005 133,000
1974 NA NA 4,977 1,904 470 96,900 26,400 130,651 126,810
1975 NA NA 6,163 1,507 480 80,825 34,455 123,430 126,362
1976 NA NA 7,540 1,769 680 82,783 29,273 122,045 125,375
1977 NA NA 14,111 2,100 0 86,534 44,222 146,967 130,814
1978 NA NA 18,100 1,110 560 106,469 36,648 162,887 143,966
1979 NA NA 8,078 1,255 10 87,860 32,210 129,413 146,422
1980 NA NA 7,665 1,015 135 89,690 47,860 146,365 146,222
1981 3,271 NA 10,107 1,790 540 160,560 21,200 197,468 157,749
1982 NA NA 6,451 706 485 85,105 28,297 121,044 154,959
1983 NA NA 3,113 718 565 81,761 23,157 109,314 142,609
1984 1,611 NA 7,097 930 700 95,170 29,533 135,041 121,800
1985 NA 283 11,793 641 800 101,405 30,163 145,085 129,813
1986 5,338 319 12,026 1,113 706 92,525 22,200 134,227 138,118
1987 7,550 205 14,371 1,133 736 73,825 13,088 110,908 130,073
1988 6,180 263 19,831 1,104 947 99,066 17,630 145,021 130,052
1989 6,918 484 18,538 871 1,033 89,600 18,121 135,565 130,498
1990 5,303 406 13,756 1,399 992 107,545 22,320 151,721 144,102
1991 4,742 591 16,221 1,262 1,340 88,650 19,905 132,711 139,999
1992 7,043 283 13,505 1,397 2,424 78,280 14,905 117,837 134,090
1993 8,369 180 13,058 1,254 9,415 68,280 24,444 125,000 125,183
1994 12,125 382 13,595 666 2,299 83,130 17,135 129,332 124,056
1995 11,381 363 20,231 708 3,987 74,060 22,755 133,485 129,272
1996 10,278 634 6,941 644 2,008 87,280 20,205 127,990 130,269
1997 10,049 500 9,753 669 3,598 108,018 22,720 155,307 138,927
1998 8,562 619 10,881 580 6,091 97,805 14,300 138,838 140,712
1999 10,354 985 15,252 645 4,296 84,965 15,795 132,292 142,146
2000 8,120 1,238 13,859 523 3,389 92,020 16,420 135,569 135,566
2001 17,790 1,254 10,197 695 4,197 78,850 13,010 125,993 131,285
2002 13,576 1,483 13,478 552 4,092 93,995 11,055 138,231 133,264
2003 7,677 1,103 11,455 557 3,124 74,132 8,094 106,142 123,455
2004 12,756 2,117 14,544 528 6,372 71,685 13,270 121,272 121,882
2005 12,041 1,020 14,286 609 5,224 59,960 14,068 107,208 111,541
2006 15,404 1,792 16,305 649 5,069 87,483 14,254 140,956 123,145
2007 28,533 2,078 12,712 702 7,387 65,250 13,932 130,594 126,253
2008 27,422 1,264 19,775 370 4,827 83,856 19,443 156,957 142,836
2009 NA NA NA NA NA NA NA NA NA
2010 28,234 2,699 23,908 NA 13,553 71,688 23,389 163,471 150,341
2011 42,937 2,414 21,457 NA 15,610 61,153 18,897 162,468 160,965
2012 44,252 1,229 17,502 687 2,227 101,571 9,873 177,341 167,760
2013 41,821 2,204 16,454 200 7,448 71,607 23,566 163,300 167,703
2014 48,140 2,104 17,485 511 7,916 68,290 28,869 173,315 171,319
2015 50,316 1,636 10,706 486 4,906 44,533 23,899 136,482 157,699
2016 46,772 3,364 11,811 583 5,105 55,066 17,324 140,025 149,941
2017 44,899 3,677 15,878 405 8,765 67,386 14,710 155,720 144,076
2018 46,067 2,796 12,652 355 2,466 54,076 14,038 132,450 142,732
2019 45,377 2,065 8,194 291 5,353 75,186 24,693 161,159 149,776
2020 49,777 2,729 7,389 256 5,788 66,152 10,793 142,884 145,498
2021 56,563 1,956 9,961 NA 4,646 65,907 11,554 150,587 151,543
2022 67,484 2,589 10,390 385 5,167 62,231 10,434 158,680 150,717
2023 54,497 1,343 7,152 88 6,023 38,829 11,956 119,888 143,052
2024 43,440 1,230 10,042 61 3,246 38,650 11,103 107,772 128,780

Figure 84: Pacific brant abundance in winter. Circles are annual counts of abundance. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual counts. The blue dashed reference line is the Pacific Flyway Council’s population objective. The red dashed reference lines represent threshold values in the harvest strategy decision and the red reference line is the closure threshold. The black dashed reference line is the long-term average.

Data Table 82: Snow Goose, WAP

Original data source: Arctic coastal Plain Survey and Waterfowl Breeding Population and Habitat Survey (WBPHS) strata in Alaska (i.e., strata 3–6, 10 and 11); USFWS Alaska Region. Data maintained by the USFWS Alaska Region.

Provided in the table below are estimated total (Total) and breeding (Breeding) bird abundance and standard error (SE) of Western Arctic Population lesser snow geese in Spring. Also provided are the total abundance moving 3-year average (M3yr) and standard error (M3yr.SE).

Table 82. Western Arctic Population lesser snow goose abundance in spring, 2007-2025.
Year Total Total.SE M3yr M3yr.SE Breeding Breeding.SE
2007 63,398 42,695 NA NA 4,777 3,791
2008 8,272 3,603 NA NA 1,720 913
2009 27,078 13,228 32,916 25,890 9,231 4,200
2010 7,888 3,320 14,413 8,144 641 157
2011 23,388 11,291 19,451 10,222 14,272 6,417
2012 34,553 15,542 21,943 11,256 2,195 700
2013 39,402 15,159 32,448 14,128 2,712 1,492
2014 22,911 10,498 32,289 13,923 328 137
2015 55,061 30,188 39,125 20,423 814 231
2016 22,675 5,586 33,549 18,732 6,299 2,103
2017 52,434 16,123 43,390 20,020 6,012 2,160
2018 35,174 25,293 36,761 17,615 23,989 19,634
2019 60,717 23,686 49,441 22,066 47,090 17,923
2020 NA NA NA NA NA NA
2021 NA NA NA NA NA NA
2022 73,822 21,341 56,571 23,496 32,589 13,753
2023 68,955 28,451 67,831 24,671 53,799 22,238
2024 73,299 22,834 72,025 24,401 27,630 12,452
2025 171,831 56,444 104,695 38,802 41,994 25,350

Figure 85: Western Arctic Population lesser snow goose abundance in spring. Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 83: Snow Goose, WIP

Original data source: Cooperative Snow Goose Nesting Colony Survey on Wrangel Island Russia; Wrangel Island Nature Reserve, USFWS Pacific Flyway Office and Pacific Flyway Council. Data maintained by USFWS Pacific Flyway Office. This monitoring program was discontinued after 2022 due to the difficulty in providing US funds for work on Wrangel Island, Russia.

Provided in the table below are attributes of the Wrangel Island Population lesser snow geese on Wrangel Island in spring-summer. Attributes include abundance of adult (Adult) and breeding (Breeding) birds, proportion of the population that is juvenile (Juv%), total bird (Total) abundance, number of nests (Nests), nest success (Nest.Suc%), mean clutch size (Clutch), average brood size at the nesting colony (Brood.Nest) and brood rearing areas (Brood.Rear), and nesting colony size (Colony.ha). Also provided is the total abundance moving 3-year average (M3yr).

Table 83. Wrangel Island Population lesser snow goose status in spring-summer, 1970-2022.
Year Adult Breeding Juv% Total Nests Nest.Suc% Clutch Brood.Nest Brood.Rear Colony.ha M3yr
1970 120,000 120,000 20 150,000 60,000 96.0 3.7 4 2 2,600 NA
1971 120,000 24,000 9 132,000 12,000 55.0 4.7 3 2 825 NA
1972 106,000 36,000 1 107,000 18,000 45.0 4.2 4 2 950 129,667
1973 85,900 12,000 0 86,000 6,000 67.0 6.0 4 NA 200 108,333
1974 69,500 32,000 1 70,000 15,000 0.0 4.7 NA NA 800 87,667
1975 56,000 56,000 0 56,000 28,000 74.4 3.8 3 2 NA 70,667
1976 46,000 46,000 21 58,000 23,000 79.0 3.7 3 3 1,840 61,333
1977 57,200 10,000 16 68,200 5,000 76.8 5.0 4 NA 400 60,733
1978 64,900 42,000 1 65,400 21,000 80.0 4.2 4 2 2,200 63,867
1979 62,100 60,000 26 84,500 30,000 90.0 3.8 4 NA 1,860 72,700
1980 80,300 20,000 12 90,700 10,000 70.0 5.4 3 NA 315 80,200
1981 86,200 78,000 3 89,000 39,000 95.0 4.0 4 3 2,118 88,067
1982 81,000 28,000 18 100,000 14,000 65.0 4.1 3 3 688 93,233
1983 92,800 3,400 2 95,000 1,700 5.9 4.8 NA NA 125 94,667
1984 85,000 42,000 0 85,000 21,000 83.3 3.7 3 2 1,500 93,333
1985 80,000 50,000 5 85,000 25,000 87.7 3.7 3 2 1,457 88,333
1986 70,000 58,000 20 90,000 29,000 90.0 3.9 4 3 2,100 86,667
1987 85,000 47,000 15 100,000 23,500 80.0 3.7 3 3 1,900 91,667
1988 80,000 13,000 18 80,000 6,500 51.0 5.2 3 3 675 90,000
1989 70,000 60,000 1 70,000 30,000 60.0 3.8 3 NA 1,025 83,333
1990 60,000 53,000 0 60,000 26,500 49.2 3.8 3 2 940 70,000
1991 56,000 41,600 7 60,000 20,800 82.0 4.1 3 3 888 63,333
1992 56,000 46,200 20 70,000 23,100 70.1 4.0 4 4 742 63,333
1993 64,500 52,200 1 65,000 26,100 85.1 3.9 3 NA 910 65,000
1994 52,500 30,000 25 70,000 15,000 13.0 2.8 2 NA 1,000 68,333
1995 64,000 8,800 1 65,000 4,400 50.0 4.7 3 NA 430 66,667
1996 75,000 75,400 0 75,000 37,700 75.4 NA 4 2 740 70,000
1997 70,000 55,200 15 85,000 22,600 71.2 4.0 4 NA 628 75,000
1998 80,000 31,800 10 90,000 15,900 66.0 4.6 4 NA 750 83,333
1999 85,000 20,800 6 90,000 10,400 75.0 4.7 3 NA 278 88,333
2000 87,400 49,600 8 95,000 24,800 87.8 3.5 3 3 738 91,667
2001 92,400 48,000 12 105,000 24,000 87.0 3.6 3 2 900 96,667
2002 NA 60,600 NA 110,000 30,300 81.5 4.0 4 3 855 103,333
2003 NA 55,000 NA 115,000 27,500 77.5 NA NA 2 900 110,000
2004 111,700 56,800 5 117,500 28,400 75.0 3.6 3 NA 838 114,167
2005 NA 95,800 NA 117,500 47,900 82.3 4.2 4 3 900 116,667
2006 100,800 93,200 24 132,500 46,600 87.7 4.0 4 3 875 122,500
2007 NA 79,000 NA 140,000 39,500 84.4 4.0 4 3 1,100 130,000
2008 NA 35,000 NA 140,000 10,000 35.0 4.2 3 NA 500 137,500
2009 NA 108,800 NA 132,500 54,400 79.5 4.1 4 NA 1,600 137,500
2010 127,000 25,000 NA 150,000 8,000 NA 3.6 3 NA 500 140,833
2011 144,800 143,000 4 155,000 71,200 81.0 4.2 4 NA 1,400 145,833
2012 NA NA NA NA NA NA NA NA NA NA NA
2013 NA NA NA 160,000 78,300 75.8 3.7 3 3 1,063 155,000
2014 NA NA NA NA NA NA NA NA NA NA NA
2015 228,500 215,400 5 240,000 107,700 89.1 4.0 4 NA 2,680 185,000
2016 251,000 237,000 20 300,000 118,600 89.5 3.9 4 NA 3,240 233,333
2017 294,800 201,500 15 346,000 109,500 75.5 3.7 3 3 2,810 295,333
2018 297,000 281,800 3 306,000 76,650 73.9 4.8 4 NA 2,435 317,333
2019 NA 313,200 29 442,000 156,600 93.7 4.1 NA NA 7,365 364,667
2020 256,920 428,200 22 685,120 214,100 91.0 3.8 NA 3 9,140 477,707
2021 543,548 356,600 13 624,050 178,300 91.0 3.9 4 3 8,640 583,723
2022 750,000 502,000 NA 750,000 251,000 86.7 3.7 NA NA 10,430 686,390

Figure 86: Wrangel Island Population lesser snow goose abundance in spring-summer. Circles are annual estimates of abundance. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 84: White-fronted Goose, MP

Original data source: Arctic coastal Plain Survey and Waterfowl Breeding Population and Habitat Survey (WBPHS) strata in Alaska (i.e., strata 3–6, 10 and 11); USFWS Alaska Region. Data maintained by the USFWS Alaska Region.

Provided in the table below are estimated total (Total) and breeding (Breeding) bird abundance and standard error (SE) of Midcontinent Population white-fronted geese in Spring. Also provided are the total abundance moving 3-year average (M3yr) and standard error (M3yr.SE).

Table 84. Midcontinent Population white-fronted goose abundance in spring, 2007-2025.
Year Total Total.SE M3yr M3yr.SE Breeding Breeding.SE
2007 256,573 14,881 NA NA 109,562 6,826
2008 255,499 23,426 NA NA 136,810 6,591
2009 241,086 13,936 251,053 17,930 138,148 8,311
2010 259,213 13,145 251,932 17,472 95,928 4,575
2011 318,569 78,608 272,956 46,713 147,766 6,561
2012 360,884 15,439 312,889 46,870 190,753 7,327
2013 NA NA NA NA NA NA
2014 165,130 8,553 281,528 46,514 110,564 4,336
2015 296,160 24,933 274,058 17,637 111,022 6,478
2016 395,085 25,795 285,459 21,293 153,969 9,973
2017 401,743 26,746 364,330 25,836 222,331 12,663
2018 275,226 16,893 357,352 23,566 202,851 12,312
2019 202,388 11,916 293,119 19,517 128,476 7,178
2020 NA NA NA NA NA NA
2021 NA NA NA NA NA NA
2022 247,585 12,633 241,733 13,988 160,565 8,624
2023 178,204 11,256 209,392 11,948 118,715 7,590
2024 235,866 15,143 220,552 13,110 166,953 10,000
2025 334,575 32,114 249,548 21,504 186,545 10,622

Figure 87: Midcontinent Population white-fronted goose abundance in spring. Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 85: Tundra Swan, EP

Original data source: Arctic coastal Plain Survey; USFWS Alaska Region. Data maintained by the USFWS Alaska Region.

Provided in the table below are estimated total (Total) and breeding (Breeding) bird abundance and standard error (SE) of Eastern Population tundra swans in Spring. Also provided are the total abundance moving 3-year average (M3yr) and standard error (M3yr.SE).

Table 85. Eastern Population tundra swan abundance in spring, 2007-2025.
Year Total Total.SE M3yr M3yr.SE Breeding Breeding.SE
2007 13,985 611 NA NA 12,995 622
2008 15,281 1,286 NA NA 12,537 717
2009 13,986 733 14,417 924 12,750 603
2010 15,282 1,091 14,850 1,061 13,420 843
2011 13,771 820 14,346 894 12,903 714
2012 16,329 1,726 15,128 1,270 13,836 641
2013 15,449 1,135 15,183 1,283 10,049 667
2014 13,065 745 14,948 1,268 7,275 499
2015 21,308 3,228 16,607 2,022 10,088 996
2016 15,699 1,116 16,691 2,019 14,404 832
2017 15,369 1,089 17,459 2,070 11,305 657
2018 14,573 1,154 15,214 1,120 14,573 1,154
2019 14,588 1,308 14,843 1,187 12,958 829
2020 NA NA NA NA NA NA
2021 NA NA NA NA NA NA
2022 11,975 727 13,712 1,091 11,129 640
2023 15,634 2,042 14,066 1,461 11,487 830
2024 11,033 996 12,881 1,377 9,536 509
2025 12,865 922 13,177 1,415 12,428 803

Figure 88: Eastern Population tundra swan abundance in spring. Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 86: Sandhill Crane, LCRVP

Original data source: Cooperative Winter Sandhill Crane Survey in Arizona and California; Arizona, California, USFWS Southwest Region. Data maintained by USFWS Pacific Flyway Office.

Provided in the table below are abundance of Lower Colorado River Valley Population sandhill cranes in winter by area including Cibola National Wildlife Refuge (Cibola.NWR), Colorado River Indian Tribe (CR.Tribe), Salton Sea National Wildlife Refuge (Salton.NWR), Gila River (Gila.R), and in total (total). Also provided is the total abundance moving 3-year average (M3yr).

Table 86. Lower Colorado River Valley Population sandhill crane abundance in spring, 1998-2025.
Year Cibola.NWR CR.Tribe Salton.NWR Gila.R Total M3yr
1998 775 596 351 178 1,900 NA
1999 1,200 511 325 163 2,199 NA
2000 820 1,259 235 252 2,566 2,222
2001 961 952 350 134 2,397 2,387
2002 1,003 168 417 52 1,640 2,201
2003 1,200 455 430 0 2,085 2,041
2004 1,341 354 521 312 2,528 2,084
2005 1,513 457 476 191 2,637 2,417
2006 1,141 673 493 360 2,667 2,611
2007 2,322 809 295 450 3,876 3,060
2008 NA NA NA NA NA NA
2009 289 1,216 603 293 2,401 2,981
2010 266 729 904 365 2,264 2,847
2011 553 636 899 327 2,415 2,360
2012 1,097 474 924 151 2,646 2,442
2013 1,629 344 671 434 3,078 2,713
2014 1,981 591 641 140 3,353 3,026
2015 676 720 688 452 2,536 2,989
2016 631 631 862 292 2,416 2,768
2017 940 636 819 321 2,716 2,556
2018 1,076 330 775 215 2,396 2,509
2019 1,171 192 1,062 497 2,922 2,678
2020 1,497 20 1,105 319 2,941 2,753
2021 NA NA NA NA NA NA
2022 941 1,248 1,226 372 3,787 3,217
2023 864 2,186 1,532 137 4,719 3,816
2024 2,792 1,520 735 109 5,156 4,554
2025 439 1,332 464 692 2,927 4,267

Figure 89: Lower Colorado River Valley Population sandhill crane abundance in spring. Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 87: Sandhill Crane, MP

Original data source: Yukon Koskokwim Delta Coastal Zone Survey; USFWS Alaska Region. Data maintained by the USFWS Alaska Region.

Provided in the table below are estimated total (Total) and breeding (Breeding) bird abundance and standard error (SE) of Midcontinent Population sandhill cranes in Spring. Also provided are the total abundance moving 3-year average (M3yr) and standard error (M3yr.SE).

Table 87. Midcontinent Population sandhill crane abundance in spring, 1987-2025.
Year Total Total.SE M3yr M3yr.SE Breeding Breeding.SE
1987 13,777 961 NA NA 12,944 950
1988 15,564 1,539 NA NA 12,208 809
1989 16,182 1,130 15,174 1,234 12,858 718
1990 18,279 1,476 16,675 1,394 14,010 857
1991 20,435 1,689 18,298 1,450 14,095 869
1992 17,188 1,173 18,634 1,461 13,188 845
1993 19,226 1,549 18,950 1,486 15,929 1,024
1994 16,683 1,073 17,699 1,281 13,883 860
1995 18,033 1,340 17,981 1,335 16,693 1,298
1996 16,669 1,841 17,129 1,453 10,240 803
1997 13,456 1,128 16,053 1,467 11,356 766
1998 23,439 1,282 17,855 1,450 17,259 727
1999 18,433 1,352 18,443 1,258 16,095 1,090
2000 17,148 1,203 19,673 1,280 15,048 963
2001 16,083 1,067 17,221 1,213 14,811 985
2002 12,704 1,151 15,312 1,142 12,236 1,107
2003 14,006 979 14,264 1,068 10,927 728
2004 14,199 1,164 13,636 1,101 11,678 988
2005 14,080 1,033 14,095 1,062 11,247 758
2006 15,050 1,309 14,443 1,174 12,525 987
2007 13,220 909 14,117 1,097 12,666 890
2008 15,113 950 14,461 1,071 13,147 772
2009 16,108 1,277 14,814 1,058 13,153 918
2010 19,183 1,595 16,802 1,301 17,250 1,357
2011 13,288 893 16,193 1,288 12,396 815
2012 19,292 2,017 17,255 1,572 17,189 1,454
2013 13,415 1,156 15,332 1,438 12,562 1,140
2014 14,196 2,071 15,634 1,797 12,478 1,629
2015 13,808 1,279 13,807 1,556 11,702 1,212
2016 23,216 3,025 17,073 2,241 17,960 1,208
2017 20,238 1,628 19,087 2,116 17,174 1,224
2018 20,741 2,137 21,398 2,336 16,944 1,242
2019 18,943 1,128 19,974 1,682 17,916 1,068
2020 NA NA NA NA NA NA
2021 18,696 1,406 19,460 1,614 16,852 1,352
2022 13,086 882 16,908 1,159 12,220 769
2023 15,052 1,180 15,611 1,176 13,632 881
2024 12,576 865 13,571 986 11,665 851
2025 10,838 749 12,822 949 10,669 746

Figure 90: Midcontinent Population sandhill crane abundance in spring. Circles are annual estimates of abundance with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 88: Band-tailed Pigeon, Pacific Coast (spring)

Original data source: North American Breeding Bird Survey; U.S. Geological Survey. Data maintained by U.S. Geological Survey.

Provided in the table below are the estimated abundance (Index, birds per route) and lower and upper 95% credible intervals (L95%CI, U95%CI) of Pacific Coast band-tailed pigeons in spring. Also provided is the abundance moving 3-year average (M3yr).

Table 88. Pacific Coast band-tailed pigeon abundance in spring, 1968-2024.
Year Index L95%CI U95%CI M3yr
1968 8.48 4.91 16.41 NA
1969 8.27 4.99 15.31 NA
1970 8.05 4.97 14.20 8.27
1971 7.91 5.01 13.74 8.08
1972 7.64 4.94 12.80 7.87
1973 7.36 4.81 11.93 7.64
1974 6.94 4.62 10.96 7.32
1975 6.60 4.46 10.26 6.97
1976 6.50 4.41 10.07 6.68
1977 6.53 4.46 10.12 6.54
1978 6.55 4.48 10.16 6.53
1979 6.64 4.55 10.24 6.57
1980 7.00 4.82 10.82 6.73
1981 7.15 4.89 11.06 6.93
1982 6.98 4.76 10.89 7.04
1983 6.76 4.59 10.62 6.96
1984 6.13 4.21 9.54 6.63
1985 5.10 3.54 7.72 6.00
1986 4.66 3.24 7.04 5.30
1987 4.41 3.08 6.69 4.72
1988 4.02 2.82 6.03 4.36
1989 3.93 2.77 5.80 4.12
1990 3.72 2.64 5.43 3.89
1991 3.54 2.53 5.12 3.73
1992 3.38 2.43 4.92 3.55
1993 3.33 2.39 4.82 3.42
1994 3.25 2.35 4.70 3.32
1995 3.08 2.23 4.35 3.22
1996 3.11 2.28 4.39 3.15
1997 2.99 2.19 4.16 3.06
1998 3.07 2.26 4.23 3.06
1999 3.11 2.31 4.28 3.06
2000 3.12 2.32 4.26 3.10
2001 3.13 2.33 4.25 3.12
2002 3.13 2.32 4.24 3.13
2003 3.21 2.39 4.35 3.16
2004 3.47 2.58 4.70 3.27
2005 3.71 2.77 5.03 3.46
2006 3.88 2.91 5.24 3.68
2007 4.05 3.04 5.45 3.88
2008 4.42 3.31 5.94 4.11
2009 4.54 3.40 6.18 4.34
2010 4.63 3.46 6.26 4.53
2011 4.71 3.53 6.40 4.63
2012 4.63 3.50 6.24 4.65
2013 4.53 3.42 6.07 4.62
2014 4.59 3.48 6.11 4.58
2015 4.50 3.41 6.01 4.54
2016 4.41 3.34 5.85 4.50
2017 4.54 3.45 6.03 4.48
2018 4.62 3.51 6.16 4.52
2019 4.71 3.59 6.29 4.62
2020 4.84 3.64 6.51 4.72
2021 4.95 3.74 6.63 4.83
2022 4.99 3.77 6.71 4.93
2023 4.98 3.74 6.74 4.98
2024 5.03 3.71 6.86 5.00

Figure 91: Pacific Coast band-tailed pigeon abundance (index) in spring. Circles are annual estimates of abundance (index) with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Figure 92: Pacific Coast band-tailed pigeon abundance (index) in British Columbia in spring. Circles are annual estimates of abundance (index) with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Figure 93: Pacific Coast band-tailed pigeon abundance (index) in Washington in spring. Circles are annual estimates of abundance (index) with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Figure 94: Pacific Coast band-tailed pigeon abundance (index) in Oregon in spring. Circles are annual estimates of abundance (index) with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Figure 95: Pacific Coast band-tailed pigeon abundance (index) in California in spring. Circles are annual estimates of abundance (index) with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Data Table 89: Mourning Dove, WMU (spring)

Original data source: North American Breeding Bird Survey; U.S. Geological Survey. Data maintained by U.S. Geological Survey.

Provided in the table below are abundance (Index, birds per route) and lower and upper 95% credible intervals (L95%CI, U95%CI) of Western Management Unit Population mourning doves in spring. Also provided is the abundance moving 3-year average (M3yr).

Table 89. Western Management Unit Population mourning dove abundance in spring, 1968-2024.
Year Index L95%CI U95%CI M3yr
1968 24.66 21.23 29.07 NA
1969 24.79 21.53 29.05 NA
1970 25.29 22.14 29.30 24.91
1971 24.55 21.65 28.47 24.88
1972 24.51 21.54 28.40 24.78
1973 22.93 20.04 26.75 24.00
1974 26.13 23.34 29.63 24.52
1975 24.72 21.99 28.10 24.59
1976 28.50 24.49 33.87 26.45
1977 27.24 23.74 31.80 26.82
1978 22.69 20.16 25.80 26.14
1979 23.30 20.56 26.93 24.41
1980 24.22 21.38 28.07 23.40
1981 26.52 23.48 30.70 24.68
1982 24.58 21.75 28.55 25.11
1983 20.58 18.03 24.44 23.89
1984 19.65 17.39 22.86 21.60
1985 17.35 15.42 19.97 19.19
1986 16.98 15.09 19.42 17.99
1987 16.18 14.71 17.93 16.84
1988 16.29 14.82 18.00 16.48
1989 16.49 14.99 18.27 16.32
1990 17.86 16.28 19.68 16.88
1991 17.08 15.61 18.83 17.14
1992 17.28 15.87 18.92 17.41
1993 17.33 15.91 19.01 17.23
1994 17.71 16.36 19.21 17.44
1995 15.57 14.35 16.94 16.87
1996 15.51 14.34 16.87 16.26
1997 15.95 14.84 17.22 15.68
1998 16.16 14.98 17.50 15.87
1999 18.13 16.82 19.64 16.75
2000 17.53 16.31 18.96 17.27
2001 16.41 15.19 17.80 17.36
2002 17.07 15.83 18.43 17.00
2003 16.27 15.12 17.57 16.58
2004 17.96 16.64 19.44 17.10
2005 17.23 15.81 18.95 17.15
2006 19.47 18.00 21.13 18.22
2007 18.69 17.41 20.14 18.46
2008 15.66 14.55 16.87 17.94
2009 15.46 14.38 16.68 16.60
2010 14.26 13.18 15.46 15.12
2011 15.24 14.02 16.57 14.98
2012 13.05 12.07 14.14 14.18
2013 13.23 12.27 14.25 13.84
2014 13.79 12.84 14.83 13.36
2015 15.10 14.09 16.23 14.04
2016 13.06 12.14 14.10 13.99
2017 11.26 10.48 12.12 13.14
2018 11.65 10.85 12.52 11.99
2019 11.00 10.19 11.91 11.30
2020 11.55 10.33 13.07 11.40
2021 12.00 11.15 12.93 11.51
2022 13.74 12.72 14.93 12.43
2023 15.72 14.48 17.15 13.82
2024 14.95 13.71 16.38 14.80

Figure 96: Western Management Unit Population mourning dove abundance (index) in spring. Circles are annual estimates of abundance (index) with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Figure 97: Abundance (index) of mourning doves in spring in Arizona Circles are annual estimates of abundance (index) with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.

Figure 98: Abundance (index) of mourning doves in spring in California. Circles are annual estimates of abundance (index) with 95% confidence intervals. The red line is a moving 3-year average and the blue line is a smoothed (Loess model) line with 95% confidence interval (shaded area) fit to the annual estimates. The black dashed reference line is the long-term average.