FWS Focus

Overview

Characteristics
Overview

Grizzly bears, Ursus arctos horribilis, are a member of the brown bear species, U. arctos, that occurs in North America, Europe and Asia. The subspecies U. a. horribilis is limited to North America and historically existed throughout much of the western half of the contiguous United States, central Mexico, western Canada and most of Alaska. Prior to 1800, an estimated 50,000 grizzly bears were distributed in one large contiguous area throughout all or portions of 18 western States, including Washington, Oregon, California, Idaho, Montana, Wyoming, Nevada, Colorado, Utah, New Mexico, Arizona, North Dakota, South Dakota, Minnesota, Nebraska, Kansas, Oklahoma and Texas. Grizzly bears were probably most common in the Rocky Mountains, along the Upper Missouri River and in California. Grizzly bears were less common or did not occur in large expanses of the North American deserts and Great Plains ecoregions.  

With the arrival of Europeans to North America, grizzly bears were seen as a threat to livestock and human safety and, therefore, an impediment to westward expansion and settlement. In the 1800s, in concert with European settlement of the American West and government-funded bounty programs which aimed at eradication, grizzly bears were shot, poisoned and trapped wherever they were found. The resulting declines in range and population were dramatic with rapid extinction of populations from most of Mexico and from the central and southwestern United States and California. Grizzly bears were reduced to close to 2% of their former range in the 48 contiguous states by the 1930s, with a corresponding decrease in population, approximately 125 years after first contact with European settlers. In the early 20th century, new regulations were designed to stop future extirpations. In some areas, the protections came too late. By 1975, grizzly bear populations in the 48 contiguous states had been reduced to between 700 to 800. Although significant numbers remained in Alaska and northern Canada, individuals were restricted largely to the confines of national parks and wilderness areas in Washington, Idaho, Montana and Wyoming. Grizzly bears were relegated to these areas in the 48 contiguous states primarily because of limited human influences.  

The 1993 U.S. Fish and Wildlife Service Recovery Plan identified six ecosystems, with recovery zones at the core of each, to further recovery efforts. Each recovery zone represents an area large enough and of sufficient habitat quality to support a recovered grizzly bear population. The plan recognized that grizzly bears will move and reside permanently in areas outside the recovery zones and that connectivity between recovery areas would be necessary for isolated populations to increase and sustain themselves at recovery levels. 

The recovery zones identified are: 

  • The Greater Yellowstone, referred to as GYE, in northwestern Wyoming, eastern Idaho and southwestern Montana 
  • The Northern Continental Divide, referred to as NCDE, of north-central Montana 
  • The North Cascades area of north-central Washington 
  • The Selkirks, referred to as SE, area of northern Idaho, northeast Washington and southeast British Columbia 
  • The Cabinet-Yaak, referred to as CYE, area of northwestern Montana and northern Idaho 
  • The Bitterroot, referred to as BE, in the Bitterroot Mountains of central Idaho and western Montana

Currently, there are at least 1,923 individuals in the 48 contiguous states, with 727 in the GYE demographic monitoring area, 1,092 in the NCDE, about 60 in the CYE and a minimum of 44 in the United States portion of the SE, although some bears have home ranges that cross the international border, as documented by C.M. Costello and L. Roberts in 2021 and M.A. Haroldson and others also in 2021. In the GYE, this estimate does not capture the entire distribution of grizzly bears. In addition, grizzly bears have been verified in areas between ecosystems; however, there are likely few resident grizzly bears in the 48 contiguous states outside of the GYE, NCDE, CYE and SE. There are currently no known populations within the North Cascades or the Bitterroot Mountains of central Idaho and western Montana.

Estimated distribution, or current range, represents areas in which grizzly bears are known to have established home ranges and continuously reside. Ecosystems are generally considered to be the larger area surrounding the recovery zones in which grizzly bears may be anticipated to occur as part of the same population. The Species List Area captures current range and additional areas of low-density peripheral occurrences and transitory individuals. Grizzly bears are expanding on the landscape, can disperse large distances and are not easily detectable. Developed through a standardized protocol, the Species List Area includes additional areas of verified outlier locations gathered by our state, federal and Tribal partner agencies, such as verified sightings, mortalities, conflicts and radio-collared individuals outside of current range.

Grizzly bears in the 48 contiguous states are currently protected as a threatened species. It is illegal to harm, harass or kill these bears, except in cases of self-defense or the defense of others. Grizzly bear conservation is complex and only made possible through a variety of partnerships with the Interagency Grizzly Bear Committee, state wildlife agencies, Native American Tribes, federal agencies, universities and other organizations. 

Bear Safety 

Learn the characteristics of bears and what you can do to prevent human-bear conflict. Check out our Bear Safety page. For more information on living and recreating in grizzly bear country, visit the Interagency Grizzly Bear Committee's bear safety page.

Scientific Name

Ursus arctos horribilis
Common Name
brown bear
grizzly bear
FWS Category
Mammals
Kingdom

Location in Taxonomic Tree

Identification Numbers

TSN:

Characteristics

Characteristic category

Physical Characteristics

Characteristics
Size & Shape

They can be distinguished from black bears by longer, less curved front claws, humped shoulders and a more concave facial profile.

Weight

Grizzly bears are generally larger and heavier than other bears. Adult males average 400 to 600 pounds (200 to 300 kilograms) and adult females 250 to 350 pounds (110 to 160 kilograms) in the 48 contiguous states.

Color & Pattern

Their coloration varies from light brown to nearly black. The coat features longer guard hairs over a dense underfur with tips that are usually silver or golden in color โ€“ hence the name grizzly.

Characteristic category

Life Cycle

Characteristics
Life Span

Grizzly bears are long-lived mammals, generally living to be around 25 years old, although some wild bears have lived for over 35 years.

Life Cycle

Grizzly bears have three life stages: dependent young, subadults and adults. Dependent young are usually less than 2 years old and depend on and are associated with their mother, relying on her for food, protection, and survival. There are two primary sub-categories of dependent young: cubs, defined as cubs born during the most recent denning season and less than one year old, and yearlings.

Grizzly bears have a promiscuous mating system. Mating occurs from May through July, with a peak in mid-June.  Although females mate in spring and early summer, their fertilized embryos do not implant into the uterus for further development until late fall. Fat stores obtained by female grizzly bears at the end of fall are positively correlated with earlier birth dates and faster growth rates of their cubs. Additionally, a body fat threshold may exist below which females may not produce cubs, even when bred. Cubs are born in the den in late January or early February and nurse for 3 to 4 months inside the den and after den emergence, but also increasingly eat foods with their mother once outside the den.  Yearlings den with their mother but do not nurse in the den. Outside of the den, yearlings eat the same foods as their mother, but also occasionally nurse.

Shortly after den emergence, 2-year-old offspring generally leave their mother to become subadults. Subadults are typically not sexually mature enough to breed; however, a small percentage of 3-year-old females do breed and produce cubs as 4-year-olds. Some subadults, generally males, may disperse away from their mother and establish their own home range.

Adult bears are more than 4-years-old and have reached sexual maturity. Some bears may not breed until they are older than 5-years-old, but they have the ability to reproduce once they reach the adult stage. Adults generally live into their mid- to late-20s, although some wild bears have lived over 35 years. Female reproductive senescence starts around age 25 for those long-lived individuals.

Age of first reproduction, which averages 5.8 to 6.3 years, litter size, which averages 2.1 to 2.19 cubs per litter, and inter-birth interval, which is the average number of years between litters, averages 2.78 to 3.4 years, may be related to nutritional state and, or, density dependent effects and varies between ecosystems. Grizzly bears have one of the slowest reproductive rates among terrestrial mammals, resulting primarily from these reproductive factors: late age of first reproduction, small average litter size and the long inter-birth interval. Given these factors, it may take a female grizzly bear 10 or more years to replace herself in a population. The slow reproductive rate should also be understood in the context of having one of the longer life spans of terrestrial mammals. To that end, Ursus arctos in 90th percentile for longevity. With a population being made up of numerous overlapping generations, it is possible for mothers, daughters and granddaughters to be reproductively active at the same time. Grizzly bear females typically cease reproducing some time in their mid-to-late 20s.

Characteristic category

Habitat

Characteristics
Habitat

Grizzly bears use a variety of habitats. In general, a grizzly bearโ€™s individual habitat needs and daily movements are largely driven by the search for food, water, mates, cover, security or den sites. The available habitat for bears is also influenced by people and their activities. Human activities are the primary factor impacting habitat security and the ability of bears to find and access foods, mates, cover and den sites. Other factors influencing habitat use and function for grizzly bears include overall habitat productivity, which is defined by food distribution, quality and abundance. Overall habitat productivity is also defined by the availability of habitat components, like denning areas and cover types. Additionally, grizzly bear social dynamics, learned behavior and preferences of individual grizzly bears, as well as grizzly bear population density and random variation are important aspects. Water is an important habitat requirement as well; however, we have no information to suggest that water is limiting in the habitat that bears currently occupy, but may have limited distribution in portions of historical range. 

Grizzly bears use a variety of cover types to rest and shelter. Grizzly bears often select bed sites with horizontal and vertical cover, especially at day bed sites suggesting that bed site selection is important for concealment from humans. The interspersion of open areas as feeding sites associated with cover are important, probably because diverse habitat complexes, such as forest interspersed with moist grass-forb meadows, provide both abundant food and cover. Generally, areas with vegetative cover are important to grizzly bears for use as bedding sites. Beds underneath any type of vegetative cover, not necessarily always forest cover, provide bears shade during the hottest parts of the day and a place to sleep at night. 

The six ecosystems occur in mountainous ecoregions and each ecosystem provide the habitat heterogeneity necessary for adequate food, denning and cover resources. Because there are limited opportunities to increase or control these habitat components, the objective for grizzly bear habitat management has been, and continues to be, to reduce or mitigate the risk of human-caused mortality and displacement. An effective habitat management tool for reducing grizzly bear mortality risk on public lands is managing motorized access to ensure bears have secure areas away from humans. 

Unmanaged motorized access: 

  • Increases human interaction and potential grizzly bear mortality risk
  • Increases displacement from important habitat
  • Increases habituation to humans
  • Decreases habitat where energetic, meaning food, requirements can be met

Managing motorized access on public lands helps ameliorate these impacts. Other habitat management tools that minimize displacement and reduce grizzly bear mortality risk include regulating livestock allotments and developed sites on public lands. Implementing food storage orders on public lands also reduces mortality risk for both humans and grizzly bears. Requiring users and recreationists in grizzly bear habitat to store their food, garbage and other bear attractants in bear-proof, inaccessible ways reduces encounters and human-grizzly bear conflicts. In addition, encouraging users and recreationists to carry bear spray, and know how to use it, helps reduce the potential for injury to people and bears. 

Characteristic category

Food

Characteristics
Food

The 48 contiguous states provide highly diverse landscapes which contain a wide array of habitat types and bear foods across and within the ecosystems. Plant communities vary from grasslands at lower elevations, which are defined as less than 6,230 feet (1,900 meters) to shrub fields that are created by fires, avalanches or timber harvest, to conifer forests at mid-elevations and subalpine and alpine meadows at higher elevations, defined as greater than 7,870 feet (2,400 meters). Grizzly bears are opportunistic omnivores and display great diet plasticity - even within a population. As such, individuals shift their diet according to foods that are most nutritious, for example, available foods that are high in fat, protein, and, or, carbohydrates. An extensive literature review documented more than 260 species of foods that grizzly bears consume in the Greater Yellowstone Ecosystem, which represents four of the five kingdoms of life. The ability to use whatever food resources are available is likely one reason brown bears are the most widely distributed bear species in the world, occupying habitats from deserts to alpine mountains and everything in between. This ability to live in a variety of habitats and eat a wide array of foods makes grizzly bears a generalist species. In contrast, specialist species like mountain lions, eat only a few specific foods or live in only one or two specific habitat types. Morphological adaptations that support a diverse diet include crushing molars and the greatest intestinal length relative to body length of any carnivore.

Grizzly bear diets are highly variable among individuals, seasons and years, and between ecosystems. They opportunistically seek and consume whatever plant and animal foods are available to them. Grizzly bears will consume almost any food available including living or dead mammals or fish, insects, worms, plants, human-related foods and garbage. In areas where animal matter is less available, berries, grasses, roots, bulbs, tubers, seeds and fungi are important in meeting protein and caloric requirements. Grizzly bears often sample new foods so that they have alternative options in years when preferred foods are scarce. In the Greater Yellowstone Ecosystem, it has been noted that, after 10 years of food habits data collection, new feeding strategies continued to appear annually in this population.

In addition, grizzly bears opportunistically prey on livestock, agricultural crops, like grain, corn, garbanzo beans and melons, as well as other human foods. Cattle and sheep depredation rates are generally higher where bear densities are higher, and in later summer months. In the Greater Yellowstone and Northern Continental Divide ecosystems, depredation is generally higher where livestock is more abundant, such as areas with livestock allotments and privately owned ranchland. Livestock grazing is less common in the Cabinet-Yaak and Selkirks ecosystems, and depredation rates are correspondingly lower. Grizzly bears also opportunistically prey on small livestock, such as chickens, llamas, and goats, which primarily occur on private land.

Food resources are especially important during the period leading up to hibernation when grizzly bears must consume energetically rich foods to build up fat reserves to survive denning and post-denning periods. Fat stores provide a source of energy and insulate the bear from cold temperatures during hibernation. Also, fat stores obtained by female grizzly bears at the end of fall are positively correlated with earlier birth dates and quicker growth rates of their cubs. Additionally, a body fat threshold may exist below which females may not produce cubs, even when bred; studies have shown that females with less than 20% body fat are unlikely to produce cubs. However, we are unaware of a minimum body fat threshold for survival during the denning period.

Characteristic category

Behavior

Characteristics
Behavior

Grizzly bears hibernate in winter; hibernation is a life history strategy bears use to cope with seasons of low food abundance. In preparation for hibernation, bears increase their food intake dramatically during a period called hyperphagia. Hyperphagia occurs throughout the two to four months prior to den entry, which runs August through November. During hyperphagia, excess food is converted into fat, and grizzly bears may gain as much as 3.64 pounds a day (1.65 kilograms a day). Grizzly bears must consume foods rich in protein and carbohydrates in order to build up fat reserves to survive denning and post-denning periods. Fat stores are crucial to the hibernating bear as they provide a source of energy and insulate the bear from cold temperatures, and are equally important in providing energy to the bear upon emergence from the den when food is still sparse relative to metabolic requirements. However, we are unaware of a minimum body fat threshold for survival during the denning period and documentation of natural mortality in independent-age bears is low for non-collared individuals.

Grizzly bears in the 48 contiguous states hibernate in dens for four to six months each year, typically entering dens between October and December, with males entering their dens later than females. Females give birth to cubs in the den in late January to early February. On average, males exit dens from early March to late April. Females typically emerge from their dens from mid-March to mid-May, with females with cubs emerging later from mid-April to late-May. 

Grizzly bears typically hibernate alone in dens, except for females with young and subadult siblings who occasionally hibernate together. Grizzly bears usually dig dens on steep slopes where wind and topography cause an accumulation of deep snow and where the snow is unlikely to melt during warm periods. Most dens are located at higher elevations, above 8,000 feet (2,500 meters) in the Greater Yellowstone Ecosystem and 6,400 feet (1,942 meters) in the Northern Continental Divide Ecosystem, and on slopes ranging from 30 to 60 degrees. In the Cabinet-Yaak Ecosystem, the majority of den sites occurred above 5,248 feet (1,600 meters), often on northerly and easterly aspects, though all aspects were used. In the Selkirks Ecosystem, the majority of dens were located above 5,248 feet (1,600 meters), often on easterly aspects, but all aspects were used. The North Cascades Ecosystem contains large areas at high elevations with isolated, steep, snow-packed slopes and many natural caves to serve as potential den sites. Additional areas associated with ridge systems stemming from major volcanic peaks may provide den sites at lower elevations within the North Cascades. In 1991, Davis and Butterfield assessed the northern part of the Bitterroot Ecosystem recovery zone and areas to the immediate north, and concluded that deep snow and mountainous terrain provides adequate denning habitat.

Denning increases survival during periods of food scarcity and inclement weather. During this period, bears do not eat, drink, urinate or defecate. Hibernating grizzly bears exhibit a marked decline in heart and respiration rate, but only a slight drop in body temperature. Due to their relatively constant body temperature in the den, hibernating grizzly bears may be aroused and have been known to exit or relocate dens when disturbed by seismic or mining activity or other human activities. Dens are rarely used twice by an individual, although individuals usually use the same general area from year-to-year. Females display stronger area fidelity than males and generally stay in their dens longer, depending on reproductive status. Females with cubs usually spend a few weeks close to their den upon emergence, unlike solitary bears.

Geography

Characteristics
Range

Adult grizzly bears are normally solitary except when breeding or when females have dependent young, but they are not territorial and home ranges of adult bears frequently overlap. Home range size is affected by resource availability, sex, age and reproductive status. Generally, females with cubs-of-the-year or yearlings have the smallest home range sizes.  The large home ranges of grizzly bears, particularly males, enhance maintenance of genetic diversity in the population by enabling males to mate with numerous females.

Young, female grizzly bears usually establish home ranges within or overlapping their motherโ€™s. This pattern of home range establishment can make dispersal of females across landscapes a slow process. Radio-telemetry and genetic data suggest females typically establish home ranges an average of 6.1 to 8.9 miles (9.8 to 14.3 kilometers) away from the center of their motherโ€™s home range, whereas males generally disperse farther, averaging 18.6 to 26.0 miles (29.9 to 42.0 kilometers) away from the center of their motherโ€™s home range. Maximum male dispersal distances of 42 to 109 miles (67 to 176 kilometers) have been documented in the Greater Yellowstone and Northern Continental Divide ecosystems. Studies also indicate that females can and do disperse long distances up to 50 to 56 miles (80 to 90 kilometers), typically on the periphery of expanding populations. Although the frequency of long-distance dispersal by females is much lower than males, it can contribute to range expansion and demographic connectivity between populations. 

Home range sizes vary among the ecosystems because of population densities and habitat productivity, as well as methodology. In the 48 contiguous states, observed average annual adult female home ranges vary from 130 to 358 kilometers-squared and average annual adult male home range vary from 475 to 2,162 kilometers-squared.

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Timeline

Explore the information available for this taxon's timeline. You can select an event on the timeline to view more information, or cycle through the content available in the carousel below.

60 Items

Listing

Delisting

Delisting

Listing

Listing

Critical Habitat

Notice

Correction

4d

Uplisting

4d

4d

4d

Uplisting

Uplisting

Uplisting

Uplisting

4d

Uplisting

Downlisting

Delisting

Delisting

Downlisting

NEPA - EIS

Uplisting

NEPA - EIS

Uplisting

NEPA - EIS

Permit

Habitat Conservation Plan

Recovery Plan

NEPA - EIS

Experimental Pop Designation (10j)

NEPA - EIS

NEPA - EIS

NEPA - EIS

Post Delisting Monitoring Plan

Five Year Review

NEPA - EIS

Habitat Conservation Plan

Recovery Plan

Post Delisting Monitoring Plan

Notice

Revision of Entity

Notice

Notice

Recovery Plan

Regulation

Five Year Review

Listing

Uplisting

NEPA - Scoping

Delisting

Listing

Experimental Pop Designation (10j)

NEPA - Scoping

Experimental Pop Designation (10j)

Delisting

Delisting

Revision of Entity

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Listing

Mar 11, 1967

Mar 11, 1967 Listing (Endangered)
Endangered Species List - 1967
  • Publication type: Final
Item 1

Delisting

Jul 30, 1970

Jul 30, 1970 Delisting
Notice of Proposed Rulemaking (Conservation of Endangered Species and Other Fish or Wildlife); 35 FRโ€ฆ
  • Publication type: Final
Item 2

Delisting

Oct 13, 1970

Oct 13, 1970 Delisting
Appendix D - United States List of Endangered Native Fish and Wildlife; 35 FR 16047 16048
  • Publication type: Final
Item 3

Listing

Jan 2, 1975

Jan 2, 1975 Listing (Threatened)
Grizzly Bear, Proposed "Threatened" Status in the 48 Conterminous United States); 50 CFR Pโ€ฆ
  • Publication type: Proposed
Item 4

Listing

Jul 28, 1975

Jul 28, 1975 Listing (Threatened)
Amendment Listing the Grizzly Bear of the 48 Conterminous States as a Threatened Species; 40 FR 3173โ€ฆ
  • Publication type: Final
Item 5

Critical Habitat

Nov 5, 1976

Nov 5, 1976 Critical Habitat
Proposed Determination of Critical Habitat for Grizzly Bear; 41 FR 48757 48759 (Ursus arctos horribiโ€ฆ
  • Publication type: Proposed
Item 6

Notice

Nov 11, 1976

Nov 11, 1976 Notice
(Correction) Proposed Determinatino of Critical Habitat for Grizzly Bear; 41 FR 49859 (Ursus arctosโ€ฆ
  • Publication type: Public Hearing
Item 7

Correction

Nov 22, 1976

Nov 22, 1976 Correction
(Correction) Proposed Determination of Critical Habitat for Grizzly Bear; 41 FR 51430 (Ursus arctosโ€ฆ
  • Publication type: Notice
Item 8

4d

Aug 29, 1985

Aug 29, 1985 4d
Modification of Special Regulations for Grizzly Bear; 50 FR 35086-35089
  • Publication type: Final
Item 9

Uplisting

May 2, 1986

May 2, 1986 Uplisting (Not Substantial)
Findings on Petitions & Initiation of Status Reviews; 51 FR 16363-16365
  • Publication type: 90 day petition finding
Item 10

4d

Jul 17, 1986

Jul 17, 1986 4d
Proposed Revision of Special Regulations for Grizzly Bear; 51 FR 25914- 25919
  • Publication type: Proposed
Item 11

4d

Sep 23, 1986

Sep 23, 1986 4d
Revision of Special Regulations for Grizzly Bear; 51 FR 33753-33760
  • Publication type: Final
Item 12

4d

Oct 17, 1989

Oct 17, 1989 4d
ETWP; Proposed Revision of Special Regulations for the Grizzly Bear; 54 FR 42524 42528
  • Publication type: Proposed
Item 13

Uplisting

Aug 7, 1990

Aug 7, 1990 Uplisting (Substantial)
ETWP; Finding on Petition to Reclassify the Grizzly Bear in the North Cascades Area as Endangered; 5โ€ฆ
  • Publication type: 90 day petition finding
Item 14

Uplisting

Jul 24, 1991

Jul 24, 1991 Uplisting (Warranted But Precluded)
ETWP; Finding on Petition to Reclassify the Grizzly Bear in the North Cascades Area as Endangered
  • Publication type: 12m petition finding
Item 15

Uplisting

Apr 20, 1992

Apr 20, 1992 Uplisting (Revision)
ETWP; Grizzly Bear; Proposed Rule to Remove Special Rule Allowing a Limited Special Hunt and Noticeโ€ฆ
  • Publication type: Proposed
Item 16

Uplisting

Apr 20, 1992

Apr 20, 1992 Uplisting (Not Substantial)
Petitions to change the status of Grizzly Bear Population in Selkirk Ecosystem of Idaho and Washingtโ€ฆ
  • Publication type: 90 day petition finding
Item 17

4d

Aug 19, 1992

Aug 19, 1992 4d (Revision)
Endangered and Threatened Wildlife and Plants; Grizzly Bear, Removal of the Special Rule Allowing aโ€ฆ
  • Publication type: Final
Item 18

Uplisting

Feb 12, 1993

Feb 12, 1993 Uplisting (Warranted But Precluded)
Finding on Petitions to Change the Status of Grizzly Bear Populations in the Cabinet-Yaak Area of Moโ€ฆ
  • Publication type: 12m petition finding
Item 19

Downlisting

Jul 19, 1993

Jul 19, 1993 Downlisting (Not Substantial)
ETWP; Finding on a Petition to Change the Status of Any Grizzly Bear Population in the San Juan Mounโ€ฆ
  • Publication type: 90 day petition finding
Item 20

Delisting

Aug 18, 1993

Aug 18, 1993 Delisting (Not Substantial)
ETWP; Notice of Finding on a Petition to Delist the Grizzly Bear in the Northern Continental Divideโ€ฆ
  • Publication type: 90 day petition finding
Item 21

Delisting

Aug 18, 1993

Aug 18, 1993 Delisting (Not Substantial)
ETWP; Notice of Finding on a Petition to Change the Status of the Grizzly Bear Populations in the Yeโ€ฆ
  • Publication type: 90 day petition finding
Item 22

Downlisting

Sep 9, 1994

Sep 9, 1994 Downlisting (Not Substantial)
ETWP; Notice of Finding on a Petition To Change the Status of the Grizzley Bear Population in the Noโ€ฆ
  • Publication type: 90 day petition finding
Item 23

NEPA - EIS

Nov 17, 1995

Nov 17, 1995 NEPA - EIS
Availability of a Draft Environmental Impact Statement and Receipt of an Application for the Proposeโ€ฆ
  • Publication type: Draft
Item 24

Uplisting

Jun 4, 1998

Jun 4, 1998 Uplisting (Warranted But Precluded)
Finding on Petitions To Change the Status of Grizzly Bear Populations in the North Cascades Area ofโ€ฆ
  • Publication type: 12m petition finding
Item 25

NEPA - EIS

Jan 20, 1999

Jan 20, 1999 NEPA - EIS
Notice of Intent to Prepare an Environmental Impact Statement Regarding Proposed Issuance of an Inciโ€ฆ
  • Publication type: Draft
Item 26

Uplisting

May 17, 1999

May 17, 1999 Uplisting (Warranted But Precluded)
12-month Finding on Petitions To Change the Status of Grizzly Bear Populations in the Selkirk Area iโ€ฆ
  • Publication type: 12m petition finding
Item 27

NEPA - EIS

Jan 31, 2000

Jan 31, 2000 NEPA - EIS
Availability of a Draft Environmental Impact Statement and Receipt of an Application for Incidentalโ€ฆ
  • Publication type: Draft
Item 28

Permit

Feb 10, 2000

Feb 10, 2000 Permit (Issued)
Availability of the Record of Decision for the Proposed Modification of a Habitat Conservation Planโ€ฆ
  • Publication type: SHA, HCP, CCAA
Item 29

Habitat Conservation Plan

Feb 16, 2000

Feb 16, 2000 Habitat Conservation Plan (Document Availability (non-FR))
Extension of Comment Period for the Draft Environmental Impact Statement, and Incidental Take Permitโ€ฆ
  • Publication type: Draft
Item 30

Recovery Plan

Mar 2, 2000

Mar 2, 2000 Recovery Plan (Document Availability (non-FR))
Availability of Draft Conservation Strategy for the Grizzly Bear in the Yellowstone Ecosystem
  • Publication type: Draft
Item 31

NEPA - EIS

Mar 15, 2000

Mar 15, 2000 NEPA - EIS
Extension of Public Comment Period for Draft Environmental Impact Statement and Application for an Iโ€ฆ
  • Publication type: Draft
Item 32

Experimental Pop Designation (10j)

Nov 17, 2000

Nov 17, 2000 Experimental Pop Designation (10j) (Non-essential)
Endangered and Threatened Wildlife and Plants: Establishment of a Nonessential Experimental Populatiโ€ฆ
  • Publication type: Final
Item 33

NEPA - EIS

Jan 5, 2001

Jan 5, 2001 NEPA - EIS
Availability of a Final Environmental Impact Statement for the Tacoma Water Department Habitat Conseโ€ฆ
  • Publication type: Final
Item 34

NEPA - EIS

Apr 28, 2003

Apr 28, 2003 NEPA - EIS
Notice of Intent to Prepare an Environmental Impact Statement Regarding Proposed Issuance of an Inciโ€ฆ
  • Publication type: Draft
Item 35

NEPA - EIS

Feb 11, 2004

Feb 11, 2004 NEPA - EIS
Environmental Assessment Regarding Proposed Issuance of an Incidental Take Permit to the Burlingtonโ€ฆ
  • Publication type: Draft
Item 36

Post Delisting Monitoring Plan

Mar 13, 2007

Mar 13, 2007 Post Delisting Monitoring Plan (Document Availability (non-FR))
Endangered and Threatened Wildlife and Plants; Final Conservation Strategy for the Grizzly Bear in tโ€ฆ
  • Publication type: Final
Item 37

Five Year Review

Apr 18, 2007

Apr 18, 2007 Five Year Review (Information Solicitation)
Initiation of 5-Year Reviews of Seven Wildlife Species and Two Plant Species in the Mountain-Prairieโ€ฆ
  • Publication type: Notice
Item 38

NEPA - EIS

Jun 26, 2009

Jun 26, 2009 NEPA - EIS
Montana Department of Natural Resources and Conservation; Draft Environmental Impact Statement Availโ€ฆ
  • Publication type: Draft
Item 39

Habitat Conservation Plan

Oct 1, 2010

Oct 1, 2010 Habitat Conservation Plan (Document Availability (non-FR))
Proposed Issuance of Incidental Take Permits to the Washington Department of Fish and Wildlife for Sโ€ฆ
  • Publication type: Draft
Item 40

Recovery Plan

Mar 22, 2013

Mar 22, 2013 Recovery Plan (Document Availability (non-FR))
Endangered and Threatened Wildlife and Plants; Draft Revised Supplement to the Grizzly Bear Recoveryโ€ฆ
  • Publication type: Draft
Item 41

Post Delisting Monitoring Plan

May 3, 2013

May 3, 2013 Post Delisting Monitoring Plan (Document Availability (non-FR))
Endangered and Threatened Wildlife and Plants; Draft Conservation Strategy for the Northern Continenโ€ฆ
  • Publication type: Final
Item 42

Notice

May 21, 2013

May 21, 2013 Notice
Draft Revised Supplement to the Grizzly Bear Recovery Plan; Extension of Public Comment Period
  • Publication type: Comment Period Extension
Item 43

Revision of Entity

Mar 11, 2016

Mar 11, 2016 Revision of Entity
Proposed Rule: Removing the Greater Yellowstone Ecosystem Population of Grizzly Bears From the Federโ€ฆ
  • Publication type: Proposed Rule
Item 44

Notice

Sep 7, 2016

Sep 7, 2016 Notice
ETWP; Removing the Greater Yellowstone Ecosystem Population of Grizzly Bears From the Federal List oโ€ฆ
  • Publication type: Comment Period Reopening
Item 45

Notice

Dec 7, 2017

Dec 7, 2017 Notice
ETWP; Possible Effects of Court Decision on Grizzly Bear Recovery in the Conterminous United States
  • Publication type: Comment Period Reopening
Item 46

Recovery Plan

Dec 12, 2017

Dec 12, 2017 Recovery Plan (Document Availability (non-FR))
ETWP; Draft Supplement to the Grizzly Bear Recovery Plan: Habitat-Based Recovery Criteria for the Noโ€ฆ
  • Publication type: Draft
Item 47

Regulation

Apr 30, 2018

Apr 30, 2018 Regulation
Endangered and Threatened Wildlife and Plants; Review of 2017 Final Rule, Greater Yellowstone Ecosysโ€ฆ
  • Publication type: Final
Item 48

Five Year Review

Jan 14, 2020

Jan 14, 2020 Five Year Review (Information Solicitation)
Initiation of 5-Year Status Review of Grizzly Bear (Ursus arctos horribilis) in the conterminous Uniโ€ฆ
  • Publication type: Notice
Item 49

Listing

Nov 16, 2020

Nov 16, 2020 Listing
Endangered and Threatened Wildlife and Plants; Review of Domestic Species That Are Candidates for Liโ€ฆ
  • Publication type: CNOR
Item 50

Uplisting

May 3, 2022

May 3, 2022 Uplisting (Warranted But Precluded)
Endangered and Threatened Wildlife and Plants; Review of Species That Are Candidates for Listing asโ€ฆ
  • Publication type: 12m petition finding
Item 51

NEPA - Scoping

Nov 14, 2022

Nov 14, 2022 NEPA - Scoping
Notice of Intent To Prepare North Cascades Ecosystem Grizzly Bear Restoration Plan/Environmental Impโ€ฆ
  • Publication type: Notice
Item 52

Delisting

Feb 6, 2023

Feb 6, 2023 Delisting (Not Substantial)
Endangered and Threatened Wildlife and Plants; 90-Day Findings for Three Petitions To Delist the Griโ€ฆ
  • Publication type: 90 day petition finding
Item 53

Listing

Jun 27, 2023

Jun 27, 2023 Listing
Endangered and Threatened Wildlife and Plants; Review of Species That Are Candidates for Listing asโ€ฆ
  • Publication type: CNOR
Item 54

Experimental Pop Designation (10j)

Sep 29, 2023

Sep 29, 2023 Experimental Pop Designation (10j) (Non-essential)
Endangered and Threatened Wildlife and Plants; Establishment of a Nonessential Experimental Populatiโ€ฆ
  • Publication type: Proposed
Item 55

NEPA - Scoping

Jan 18, 2024

Jan 18, 2024 NEPA - Scoping
Endangered and Threatened Wildlife and Plants; Establishment of an Experimental Population of the Grโ€ฆ
  • Publication type: Notice
Item 56

Experimental Pop Designation (10j)

May 3, 2024

May 3, 2024 Experimental Pop Designation (10j) (Non-essential)
Endangered and Threatened Wildlife and Plants; Establishment of a Nonessential Experimental Populatiโ€ฆ
  • Publication type: Final
Item 57

Delisting

Jan 15, 2025

Jan 15, 2025 Delisting (Not Warranted)
Endangered and Threatened Wildlife and Plants; 12-Month Finding for the Northern Continental Divideโ€ฆ
  • Publication type: 12m petition finding
Item 58

Delisting

Jan 15, 2025

Jan 15, 2025 Delisting (Not Warranted)
Endangered and Threatened Wildlife and Plants; 12-Month Finding for the Greater Yellowstone Ecosysteโ€ฆ
  • Publication type: 12m petition finding
Item 59

Revision of Entity

Jan 15, 2025

Jan 15, 2025 Revision of Entity (Threatened)
Grizzly Bear Listing on the List of Endangered and Threatened Wildlife With a Revised Section 4(d) Rโ€ฆ
  • Publication type: Proposed Rule
Item 60