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Fish and Wildlife Service, Interior.
We, the U.S. Fish and Wildlife Service, determine threatened status for the salmon-crested cockatoo (Cacatua moluccensis) under the Endangered Species Act of 1973, as amended (Act). This final rule implements the Federal protections provided by the Act for this species. We are also publishing a special rule for the species.
This rule becomes effective June 27, 2011.
This final rule is available on the Internet at http://www.regulations.gov and comments and materials we received, as well as supporting documentation used in the preparation of this rule, will be available for public inspection, by appointment, during normal business hours at: U.S. Fish and Wildlife Service, 4401 N. Fairfax Drive, Suite 400, Arlington, VA 22203.Start Further Info
FOR FURTHER INFORMATION CONTACT:
Janine Van Norman, Chief, Branch of Foreign Species, Endangered Species Program, U.S. Fish and Wildlife Service, 4401 North Fairfax Drive, Room 420, Arlington, VA 22203; telephone 703-358-2171; facsimile 703-358-1735. If you use a telecommunications device for the deaf (TDD), call the Federal Information Relay Service (FIRS) at 800-877-8339.End Further Info End Preamble Start Supplemental Information
The Endangered Species Act of 1973, as amended (Act) (16 U.S.C. 1531 et seq.), is a law that was passed to prevent extinction of species by providing measures to help alleviate the loss of species and their habitats. Before a plant or animal species can receive the protection provided by the Act, it must first be added to one of the Federal Lists of Threatened and Endangered Wildlife and Plants; section 4 of the Act and its implementing regulations at 50 CFR part 424 set forth the procedures for adding species to these lists.
Previous Federal Action
On May 6, 1991, we received a petition (1991 petition) from the International Council for Bird Preservation to add 53 foreign birds, including the salmon-crested cockatoo, to the List of Endangered and Threatened Wildlife. In response to the 1991 petition, we published a substantial 90-day finding on December 16, 1991 (56 FR 65207), for all 53 species, initiated a status review to determine if listing each of these species was warranted, and sought information from the public and interested parties on the status of these species. On March 28, 1994 (59 FR 14496), we published a 12-month finding on the 1991 petition, along with a proposed rule to list 30 African birds under the Act, which included 15 species from the 1991 petition. In that document, we announced our finding that listing the remaining 38 species from the 1991 petition, including the salmon-crested cockatoo, was warranted but precluded by higher priority listing actions. We made a subsequent warranted-but-precluded finding for all outstanding foreign species from the 1991 petition, including the salmon-crested cockatoo, as published in our annual notice of review (ANOR) on May 21, 2004 (69 FR 29354).
Per the Service's listing priority guidelines (September 21, 1983; 48 FR 43098), our 2007 ANOR (72 FR 20183) identified the listing priority numbers (LPNs) (ranging from 1 to 12) for all outstanding foreign species. The LPN for the salmon-crested cockatoo was LPN 2. With the exception of listing priority ranking of 1, which addresses monotypic genera that face imminent threats of high magnitude, category 2 represents the Service's highest priority.
On July 29, 2008 (73 FR 44062), we published in the Federal Register a notice announcing our annual petition findings for foreign species. We announced that listing was warranted for 30 foreign bird species, including the salmon-crested cockatoo, which is the subject of this proposed rule, and stated that we would “promptly publish proposals to list these 30 taxa.”
On September 8, 2008, the Service received a 60-day notice of intent to sue from the Center for Biological Diversity (CBD) and Peter Galvin regarding alleged violations of section 4 of the Act for the failure to promptly publish listing proposals for the 30 “warranted” species identified in our 2008 ANOR (73 FR 44062). On June 15, 2009, the Service entered into a settlement agreement with CBD (CBD, et al. v. Salazar, 09-cv-02578-CRB), in which we agreed to submit to the Federal Register a proposed listing rule for the salmon-crested cockatoo by October 30, 2009.
On November 3, 2009, we published in the Federal Register (74 FR 56770) a proposed rule to list the salmon-crested cockatoo as threatened under the Act and a special rule for the species under section 4(d) of the Act. Following publication, we implemented the Service's peer review process and opened a 90-day comment period to solicit scientific and commercial information on the species from all interested parties.
Summary of Comments and Recommendations
We base this rule on a review of the best scientific and commercial information available, including all information we received during the public comment period. In the November 3, 2009, proposed rule, we requested that all interested parties submit information that might contribute to development of a final rule. We also contacted appropriate scientific experts and organizations and invited them to comment on the proposed listing. We received 13 comments from members of the public.
We reviewed all comments we received for substantive issues and new information regarding the proposed listing of this species, and we address those comments below. Overall, the commenters supported the proposed listing, although two commenters objected to the special rule. Three comments included additional information for consideration; all other comments simply supported the proposed listing without providing scientific or commercial data.
In accordance with our policy published on July 1, 1994 (59 FR 34270), we solicited expert opinions from five individuals with scientific expertise that included familiarity with the species, the geographic region in which the species occurs, and conservation biology principles. We did not receive responses from any of the peer reviewers from whom we requested comments.
Comment (1): Several commenters provided supporting data and information regarding the species biology, ecology, life history, population estimates, threat factors, and current conservation efforts.Start Printed Page 30759
Our Response: We thank all the commenters for their interest in the conservation of this species and thank those commenters who provided information for our consideration in making this listing determination. Most information submitted was duplicative of the information contained in the proposed rule; however, some comments contained information that provided additional clarity or support to, but did not substantially change, the information already contained in the proposed rule. This information has been incorporated into this rule. Substantial comments are addressed below.
Comment (2): One commenter had serious concerns with the proposed special rule and requested it be rewritten or withdrawn. Specific objections included:
Comment (2a): The commenter stated that it is difficult to determine the exact origin and status (captive or wild) of salmon-crested cockatoos. Most birds probably still come from the wild. The date of capture is not usually documented, and there appears to be little success in breeding this cockatoo in Indonesia. Wild and Indonesian captive-bred cockatoos would likely carry contagious diseases with them if admitted into the United States as pets. Furthermore, the commenter states that without protection against import and export of these birds, there is little incentive to cease illegal exports from Indonesia, which would foster continued collection from the wild.
Our Response: Most of the salmon-crested cockatoos imported into or exported from the United States are personal pets that owners took with them when traveling from and returning to the United States. The concerns of the commenter are applicable to trade in the domestic and international markets of Indonesia and surrounding countries, which are not subject to the Act's regulations on import and export of listed species, and therefore, not subject to the special rule. The special rule allows for import and export of certain cockatoos into and from the United States without a permit under the Act. However, all imports and exports of salmon-crested cockatoos, including those exempt from a permit under the Act as provided in the special rule, are still subject to the Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES, TIAS 8249) and the Wild Bird Conservation Act (WBCA, 16 U.S.C. 4901-4916) and their implementing regulations at 50 CFR part 23 and 50 CFR part 15, respectively, including permit application requirements on the origin of birds in trade (e.g., wild or bred in captivity). Under the provisions of WBCA, any individual importing their pet bird into the United States for the first time must reside outside of the United States for at least 12 continuous months; thus, there is little incentive to import foreign specimens. Furthermore, to control diseases, the U.S. Department of Agriculture's Animal and Plant Health Inspection Service requires veterinary health certificates and health inspections for birds imported into the United States that meet certain requirements, and quarantine for other birds, as well as research, commercial, and zoological birds imported into the United States.
Comment (2b): This commenter stated that the special rule would not have favorable effects to “enhance the propagation or survival of the species,” nor is it “necessary and advisable to provide for the conservation of the species” as stated in the proposed rule.
Our Response: We disagree with the commenter, and after careful consideration, we find that the special rule is necessary and advisable to provide for the conservation of the species. As the special rule indicates, importation of salmon-crested cockatoos, for purposes such as enhancement of propagation or survival of specimens, taken from the wild after January 18, 1990, would require certain conditions be met under 50 CFR § 17.32 in order for permits to be issued for such activities.
Under section 4(d) of the Act, the Secretary may issue, for threatened species, regulations necessary and advisable to provide for the conservation of the species. In this case, the special rule would allow the import and export of salmon-crested cockatoos held in captivity before January 18, 1990 (date the species was added to CITES Appendix I), whether taken from the wild or captive-bred, and of captive-bred salmon-crested cockatoos, without a permit issued under the Act, provided that the import or export complies with CITES and WBCA. CITES ensures that international trade in animal and plant species is not detrimental to the survival of wild populations by regulating the import, export, and reexport of CITES-listed animal and plant species. The purpose of the WBCA is to promote the conservation of exotic birds and to ensure that imports of exotic birds into the United States does not harm them. The best available commercial data indicates that the current threat to the salmon-crested cockatoo stems from illegal trade in the domestic and international markets of Indonesia and surrounding countries; the general prohibitions on import and export under the Act and 50 CFR 17.31 only extend within the jurisdiction of the United States and would not regulate such activities. Most salmon-crested cockatoo imports into and exports out of the United States are pets traveling with their owners. We did not find that import and export of salmon-crested cockatoos held in captivity before January 18, 1990 or bred in captivity contributes to either the species' habitat destruction or illegal trade. Thus, we find that the import and export requirements of the proposed special rule provide the necessary and advisable conservation measures that are needed for this species, while allowing U.S. citizens to continue traveling with their pet birds.
We have no information to suggest that interstate commerce activities are associated with threats to the salmon-crested cockatoo or will negatively affect any efforts aimed at the recovery of wild populations of the species. At the same time, the prohibitions on take under 50 CFR 17.31 would apply under this special rule and any interstate commerce activities that could incidentally take cockatoos will require a permit under 50 CFR 17.32. Furthermore, allowing interstate commerce of birds captive-bred and reared in the United States will preclude U.S. demand for salmon-crested cockatoos obtained from international markets, which would otherwise contribute to the illegal capture and trade of wild birds. Therefore, we find the prohibitions and authorizations contained within this special rule are all that is necessary and advisable for the conservation of the salmon-crested cockatoo.
Comment (2c): The commenter also stated that interstate exchange is not hindered by listing and listing would not hinder the exchange of cockatoos between breeders within the United States, implying that the special rule is not needed to allow this type of activity.
Our Response: Section 4(d) of the Act states that the Secretary may extend to threatened species prohibitions provided for endangered species under section 9. Our implementing regulations for threatened wildlife (50 CFR 17.31) incorporate the section 9 prohibitions for endangered wildlife, except when a special rule is promulgated. Under section 9(a)(1)(E) and (F) of the Act, it is unlawful for a person, subject to the jurisdiction of the United States, to deliver, receive, carry, transport, or ship in interstate or foreign commerce or sell or offer for sale in interstate commerce or foreign commerce any such species. The special rule would allow for Start Printed Page 30760interstate commerce to accommodate, for example, breeders and owners of pet cockatoos within the United States. In addition, as stated above, allowing interstate commerce of birds captive-bred and reared in the United States will preclude any U.S. demand for salmon-crested cockatoos obtained from international markets, which would otherwise contribute to illegal capture and trade of this species.
Comment (3): Another commenter also objected to the special rule. Objections included:
Comment (3a): By allowing the import and export of certain captive salmon-crested cockatoos and interstate commerce, the United States will encourage additional illegal capture in Indonesia and allow wild birds to be imported under false pretenses, which will contribute to the cockatoo's decline. Significant covert trade persists in Indonesia. Traders are able to obtain illegal permits; salmon-crested cockatoos have been classified as white cockatoos (Cacatua alba), a legally traded species in Indonesia. The incentive to conduct illegal capture and trade is high, and parrot trapping accounts for 25 to 30 percent of the impoverished forest people of Seram's cash income.
Our Response: The best available commercial data indicates that the current threat to the salmon-crested cockatoo stems from illegal trade, including the actions described by the commenter, in the domestic and international markets of Indonesia and surrounding countries. The Act cannot regulate the illegal trade of this species within the domestic and international markets of Indonesia. Although the import and export of salmon-crested cockatoos taken from the wild and held in captivity before January 18, 1990 and captive-bred salmon-crested cockatoos would not require a permit under the Act (See Our Response to Comment (2b) above), the import or export of these birds in the United States must comply with CITES and WBCA regulations. Most imports of salmon-crested cockatoos into and exports from the United States are pets traveling with their owners. We have no evidence to suggest that this type of activity contributes to either the species' habitat destruction or illegal capture and trade. Furthermore, allowing interstate commerce of birds captive-bred and reared in the United States will preclude any U.S. demand for salmon-crested cockatoos obtained from international markets, which would otherwise contribute to the illegal capture and trade of this species.
Comment (3b): The commenter stated that the Service's assessment of the conservation needs of the salmon-crested cockatoo, based on its perceived success of the 1990 Appendix-I CITES listing, is unsound. The Service states that international trade of the species has gone down considerably since the listing of the species in Appendix I under CITES; however, this assertion is based only on officially reported trade information. In actuality, and in spite of the CITES Appendix-I listing and an Indonesian export ban, the salmon-crested cockatoo continues to be illegally captured on Seram and exported for international pet trade.
Our Response: The Service acknowledges that even with the salmon-crested cockatoo listed as an Appendix-I species under CITES and Indonesian laws put in place to protect salmon-crested cockatoos, illegal capture and trade are still concerns for the continued existence of this species. However, the best available commercial data indicate that illegal capture and international trade are centered in Indonesia and the bird markets of surrounding countries, not in the United States where the prohibitions of the Act and the special rule will apply on the effective date of this rule (see DATES). As most of the salmon-crested cockatoos imported into and exported from the United States are pet birds traveling with owners, we believe that the special rule does not contribute to the threats facing the salmon-crested cockatoo.
Summary of Changes From Proposed Rule
We fully considered the comments we received from the public on the proposed rule when developing this final listing of the salmon-crested cockatoo. This final rule incorporates changes to our proposed listing based on the comments that we received that are discussed above and newly available scientific and commercial information. Reviewers generally commented that the proposed rule was very thorough and comprehensive. We made some technical corrections based on new, although limited, information. None of the information, however, changed our determination that listing this species as threatened is warranted.
Cockatoos are a distinct group of parrots (order Psittaciformes), distinguished by the presence of an erectile crest (Cameron 2007, p. 1; Collar 1989, p. 5) and the lack of dyck texture in their feathers, which produces blue and green coloration in the plumage of other parrots (Brown and Toft 1999, p. 141). The salmon-crested cockatoo (also known as the Seram, Moluccan, pink-crested, or rose-crested cockatoo) is the largest and the most striking of Indonesia's white cockatoos (Kinnaird 2000, p. 14). Its body length is 46-52 centimeters (cm) (15.6-20 inches (in)), and its plumage varies from pale salmon-pink to whitish-pink. It has a long backward-curving, deep salmon-pink crest; the bill is large and gray-black; and the underwing and undertail are yellow-orange (BirdLife International (BLI) 2000, p. 242; Forshaw 1989, p. 141; Juniper and Parr 1998, pp. 280-281; Sweeney 2000, p. 130). Sexual dimorphism is exhibited by iris color; dark brown to black in adult males, reddish brown to red in females, and brown in immature birds (del Hoya et al. 1997, p. 278; Forshaw 1989, p. 141; Peratino 1979, p. 125).
In 1751, Edwards described and pictorially delineated the salmon-crested cockatoo (Lint 1951, p. 223) and, in 1788, J.F. Gmelin named the species Psittacus moluccensis (Forshaw 1989, p. 141; Lint 1951, p. 223). In 1937, Peters (1937, p. 175) used the name Kakatoe moluccensis (Gmelin) in the Check-list of Birds of the World. In 1992, Andrew (1992, p. 21) used the name Cacatua moluccensis in the first published checklist of the birds of Indonesia. This name continues to be the recognized scientific name (Integrated Taxonomic Information System (ITIS) 2008, p. 1; Sibley and Monroe 1990, p. 112), and the alternative genus name Kakatoe is now obsolete (del Hoya et al. 1997, p. 278).
Some references (ITIS 2008, p. 1; Sibley and Monroe 1990, p. 112) place cockatoos in the family Psittacidae with lories and true parrots, whereas others (CITES 2008a, p. 1; Cameron 2007, p. 1) place cockatoos in a separate family, Cacatuidae. Of the 21 cockatoo species, 11 are in the genus Cacatua (Cameron 2007, pp. 1-3).
The closest relatives of the salmon-crested cockatoo, which is restricted to the South Moluccas, Indonesia (in the east central Indonesian island chain), are the umbrella cockatoo, which is restricted to the North Moluccas, and the blue-eyed cockatoo, which is restricted to the island of New Britain off the northeast coast of New Guinea (Cameron 2007, pp. 38-39, 51). In a biogeographic analysis of the mitochondrial DNA (mtDNA) phylogeny, Brown and Toft (1999, pp. 150-151) suggest that these three species may have had a common Start Printed Page 30761ancestor that occupied an ancient landmass comprising Halmahera (a North Moluccan island) and Bismarck. The breakup of this landmass created two populations, and the subsequent dispersal of cockatoos from the North Moluccas to the South Moluccas created another population, which became the salmon-crested cockatoo (Cameron 2007, p. 56).
Range and Distribution
Cockatoos are only found in Australasia—a few archipelagos in Southeast Asia (Philippines, Indonesia, East Timor, Tanimbar, Bismarck, and Solomon), New Guinea, and Australia—suggesting that the modern species arose after the breakup of Gondwanaland, a southern supercontinent that existed 200-500 million years ago. The 19th century naturalist Alfred Russel Wallace was among the first to note the break in Australasian and Asian fauna. Wallace's line runs between the islands of Bali and Lombok, Borneo and Sulawesi, and south of the Philippines. Cockatoos are present on Lombok and Sulawesi, but not on Bali and Borneo. The line represents the western edge of a zone of overlap between Australasian and Asian fauna (known as Wallacea), with the eastern edge defined by the Australian continental shelf (Lydekker's Line) (Cameron 2007, pp. 1-3; White and Bruce 1986, p. 32).
The oceanic islands of Wallacea have a high level of endemism, which resulted in many islands being identified as Endemic Bird Areas (EBA) (Cameron 2007, p. 56). BLI designates EBAs by mapping bird species with restricted ranges of less than 50,000 square kilometers (km2) (19,300 square miles (mi2)) that overlap. The unique biodiversity concentrated in these small areas is particularly vulnerable; thus, EBAs represent priority areas for global biodiversity conservation (BLI 2008i, p. 1; Collar 2000, p. 27; Stattersfield et al. 1998, pp. 39, 45). The salmon-crested cockatoo is included in the Seram EBA (BLI 2003, p. 1; Stattersfield et al. 1998, pp. 528-531).
The salmon-crested cockatoo is endemic to the island of Seram (alternate spelling, Ceram), with records from adjacent islands of Haruku, Saparua, and Ambon (formerly called Ambonia) in the South Moluccas (BLI 2001, p. 1662; Juniper and Parr 1998, p. 281; Forshaw 1989, p. 141; Peters 1937, p. 175). The species resides in lowland rain forests up to 1,000 meters (m) (3,608 feet (ft)), remains locally common in Manusela National Park, and appears to be mostly distributed in the eastern part of the island (BLI 2008a, p. 2; Isherwood et al. 1998, p. 18). For a listing of specific distribution records of the salmon-crested cockatoo, see BLI (2001, p. 1662).
Whether this species is native or introduced to Ambon is uncertain. Stresemann (1934, p. 16) reported that the salmon-crested cockatoo did not occur on Ambon. Thus, some scientists follow the view that the species may have been introduced to this island (Forshaw 1989, p. 141; Lever 1987, p. 245; van Bemmel 1948, as cited in White and Bruce 1986, p. 212; Smiet 1985, p. 189; Long 1981, p. 247). The salmon-crested cockatoo was formerly traded in significant numbers, and shipments of birds from Seram transited through Ambon (the capital of the Maluku Province), where undoubtedly some birds escaped. Other scientists suggest that the cockatoos may well be wild birds (Poulsen and Jepson 1996, pp. 159-160; Marsden 1992, pp. 12-13), with the persistence of a small population in northeast Ambon (Poulsen and Jepson 1996, p. 159).
Haruku and Saparua
The status of the salmon-crested cockatoo on Haruku and Saparua is unknown (Metz 1998, p. 10), but the species may be extinct on these two islands (Metz 2002, p. 1; Snyder et al. 2000, p. 68). For Haruku, there is one unspecified locality and date of observation reported (Stresemann 1934, p. 16), but Poulsen and Jepson (1996, p. 160) did not find the species in 1994 or 1996. For Saparua, there is one specimen in the RMNH (Rijksmuseum van Natuurlijke Histoire (Leiden, Netherlands)) recorded in 1923 (BLI 2001, p. 1663).
For purposes of this proposal, we consider the salmon-crested cockatoo's natural range to include Seram and the three islands of Ambon, Haruku, and Saparua. Although the status of the salmon-crested cockatoo is unknown on Haruku and Saparua, the species has been reported from these islands, and we are unaware of any survey that has conclusively found that the species no longer occurs there.
The salmon-crested cockatoo is believed to be a specialist of primary lowland forests (Kinnarid et al. 2003, p. 228). It occurs at altitudes between 100 and 1,000-1,200 m (328 and 3,608-3,926 ft) (BLI 2008a, p. 2; Bowler and Taylor 1993, p. 149; Juniper and Parr 1998, p. 281), but rarely occurs above 600-900 m (1,968-2,952 ft) (Cameron 2007, p. 77; Juniper and Parr 1998, p. 281; Marsden 1992, p. 11; Smiet 1985, p. 189). Marsden (1992, p. 11) found that cockatoos tended to be recorded in mature, open-canopied lowland forests with some very large, tall trees and some low vegetation. Kinnaird et al. (2003, p. 227) found that cockatoo abundance was significantly associated with the presence of potential nest trees (Octomeles sumatranus) and strangling figs (Ficus spp.), a potential food source. Cameron (2007, pp. 77-78) noted that island cockatoos prefer lowland forests over montane forests because lowland forests contain greater plant diversity and, thus, have a more diverse and abundant food supply. They also support larger trees, which are more likely to have cavities needed for nesting—a critical resource because cockatoos are incapable of excavating their own nest cavities. The salmon-crested cockatoo prefers flat or gently sloping terrain.
The highest densities of birds occur in little-disturbed, lowland forests below 300 m (984 ft), and the lowest densities occur in recently logged forests and in non-forested areas (Marsden 1998, p. 608; Marsden 1992, p. 9). However, Marsden and Fielding (1999, p. 444) were unable to find differences in the species' presence based on habitat associations, and Kinnaird et al. (2003, p. 227) found densities did not correspond closely to habitat differences across study sites. Marsden (1992, p. 11) suggested that the apparent differences in cockatoo densities between young logged forests and secondary forests, which have similar vegetation parameters, may be caused by differential trapping pressures and patterns of disturbance, differences in tree species compositions and overall habitat heterogeneity, and differences in cockatoo densities in areas before logging.
Lower densities of birds occur in transition and submontane forests and on the edges of cultivated areas. Birds also occur in open canopy forests with low vegetation and in riverine forests (Juniper and Parr 1998, p. 281). Despite trapping pressure, birds still occur in mature lowland forests near settlements (Juniper and Parr 1998, p. 281; Marsden 1992, p. 11), but they are rarely seen near human habitation (Smiet 1985, p. 189). Marsden (1992, pp. 9, 11) found cockatoos to be rare or irregular in other habitats, including plantations, grassland, rank scrub, and agricultural lands. The species previously occurred in coastal areas (Juniper and Parr 1998, p. 281), before land was converted to human uses (FAO 1981, as cited in Marsden 1992, p. 7). Small numbers of Start Printed Page 30762salmon-crested cockatoo have been observed in forested hills on Ambon. No other information was available on the habitat of this species on Ambon, Haruku, and Saparua.
Seram is a densely wooded island (Metz 1998, p. 10) of 18,625 km2 (7,189 mi2) (Smiet 1985, p. 183)—about the size of New Jersey (Morrison 2001, p. 1). The topography is extremely variable and the interior of the island is rugged and mostly mountainous (Kinnaird et al. 2003, p. 228). The island lies between latitudes 2°46′ and 3°53′ south of the Equator. It is approximately 340 kilometers (km) (211 miles (mi)) long and 55-70 km (34-43 mi) wide in the center. Its highest point is Gunung Binaiya at approximately 3,027 m (9,929 ft) above sea level. It is the second largest island in the Moluccas. This group of about 1,000 islands is also known as the Spice Islands, because they include the original home of both nutmeg (Myristica fragrans) and cloves (Syzgium aromaticum) (Edwards 1993, p. 1).
Seram's wet climate supports mainly evergreen forests (Marsden 1998, p. 606). The alluvial plains originally supported tall lowland forests characterized by the only endemic dipterocarp on the island, Shorea selanica (`meranti'), and also Canarium, Elaeocarpus sphaericus, Calophyllum, Intsia, and Myristica (Coates and Bishop 1997, pp. 16-17; Smiet and Siallagan 1981, p. 7). Shorea selanica has developed remarkable dominance in the lowland forests of north Seram, representing about 30 percent of individual trees and 76 percent of the basal area (Edwards et al. 1993, p. 66). The forest is relatively open-crowned with a sparse understory, with the floor being swept clean by floods during the wet season. Along the major rivers, the lowland forest is characterized by Octomeles sumatrana, Eucalyptus deglupta, Pometia pinnata, Casuarina equisetifolia, Ficus, Litsea, and Eugenia (Coates and Bishop 1997, pp. 16-17).
Most of Seram receives between 2,500 and 3,000 millimeters (mm) (97.5 and 117 inches (in)) of rain per year, with more in the east and northeast. The long monsoonal seasons (Metz 1998, p. 11; White and Bruce 1986, p. 24) and mountainous terrain affect the amount of rainfall. Annual and monthly rainfall is not uniform and varies by region (Kinnaird et al. 2003, p. 228). The island lies outside the main zone of cyclonic storms (Coates and Bishop 1997, p. 22). The lowlands have a humid tropical climate with temperatures at sea level of 25-30 degrees Celsius (°C) (77-86 degrees Fahrenheit (°F)). Temperature decreases with altitude, with a fall of approximately 6 °C (10.8 °F) for every rise of 1,000 m (3,280 ft), leading to a marked temperature gradient within the mountain areas (Edwards 1993, p. 6).
The human population of Seram is concentrated in low-lying areas along the coast and in the west. The mountainous interior supports very few villages (Edwards 1993, p. 7). The majority of Seram is lowland forest or montane forest (see Table 1). While only about 11 percent of the island has been converted to agricultural lands, settlements, and plantations or is considered unproductive, logging concessions cover nearly 50 percent of the island. About 85 percent of Seram lies below 600 m (1,968 ft) and another 10 percent lies between 600 and 1,000 m (1,968 and 3,280 ft). Within this elevation where cockatoos occur, “* * * most of the forest has been classified as production or conversion forest, categories that permit land clearing and forest disturbance” (Kinnaird et al. 2003, p. 230).
|Seram||Manusela NP||Gunung Sahuwai NR||Proposed Wai Bula NR|
|Lowland Forest||14,026.5 km2 (5,414.2 mi2)||1,522.5 km2 (587.7 mi2)||118.9 km2 (45.9 mi2)||561.8 km2 (216.9 mi2).|
|Mangrove Forest||77.6 km2 (30 mi2)||9.6 km2 (3.7 mi2).|
|Montane Forest||1,065.3 km2 (411.2 mi2)||693.9 km2 (267.8 mi2).|
|Swamp Forest||203.5 km2 (78.6 mi2)||14.6 km2 (5.6 mi2).|
|Water Body||1.2 mi2 (3.0 km2).|
|Agriculture||789.1 km2 (304.6 mi2)||50 km2 (19.3 mi2)||9.6 km2 (3.7 mi2).|
|Plantation||22.0 km2 (8.5 mi2).|
|Settlement||21.3 km2 (8.2 mi2)||3.2 km2 (1.2 mi2)||0.5 km2 (0.2 mi2).|
|Unproductive Lands||1,082.2 km2 (417.7 mi2)||53.6 km2 (20.7 mi2)||3.9 km2 (1.5 mi2)|
|Total||17,288.7 km2 (6,676.0 mi2)||2,323.2 km2 (896.8 mi2)||122.8 km2 (47.4 mi2)||596.1 km2 (230.1 mi2).|
Important Bird Areas (IBAs)
BLI (2008b, p. 2) has identified five IBAs that include the salmon-crested cockatoo. A site is recognized as an IBA when it meets criteria “* * * based on the occurrence of key bird species that are vulnerable to global extinction or whose populations are otherwise irreplaceable.” These key sites for conservation are small enough to be conserved in their entirety and large enough to support self-sustaining populations of the key bird species. IBAs are a way to identify conservation priorities (BLI 2008j, pp. 1-2). The following briefly describes the IBAs for the salmon-crested cockatoo.
Located on the western peninsula of Seram, Gunung Sahuwai contains 122.8 km2 (47.4 mi2) of land that was declared a Nature Reserve on November 30, 1993 (SK Menteri Kehutanan No. 805/Kpts-II/1993) (BLI 2008c, p. 2). The Nature Reserve contains 96.8 percent lowland forest and 3.2 percent unproductive lands (see Table 1) (Kinnaird et al. 2003, p. 230). The number of cockatoos here is unknown. The coastal area contains 14 settlements. Most people work as farmers and fishermen. The main commodities are cloves, nutmeg, and coconut for copra. The local people hunt and collect forest products. Conservation concerns for the salmon-Start Printed Page 30763crested cockatoo relate to the clearance of natural habitat for plantation, shifting agriculture, and collection of birds (BLI 2008c, pp. 1-2).
The habitat is forest, and the topography is hilly up to 1,038 m (3,405 ft). The cockatoo was found in this area at one time, but is probably extinct in this area now. The coastal area contains two villages. Most of the people work as dry land farmers and fishermen. The main commodities are clove, nutmeg, cacao, and marine products. Conservation concerns for the salmon-crested cockatoo relate to forest clearance for plantation, firewood collection, and hunting of animals for consumption or pets (BLI 2008d, pp. 1-2).
This area consists of forests and wetlands (BLI 2008e, pp. 1-2). Manusela National Park is located in the central part of Seram and stretches from the north coast to within 5 km (3 mi) of the south coast (Edwards 1993, p. 6). It is 2,323.2 km2 (896.8 mi2) in size and covers approximately 10 to 11 percent of Seram (BLI 2008e, p. 2; Kinnaird et al. 2003, p. 228; Bowler and Taylor 1993, p. 158; Marsden 1992, p. 7; Smiet and Siallagan 1981, p. 3). It was declared a national park on October 14, 1982 (SK Menteri Pertanian No. 736/Mentan/X/1982) (BLI 2008e, p. 2). Based on landsat images from late 1989 and early 1990, habitat and land use for Manusela National Park can be summarized as: 65.5 percent lowland forest; 29.9 percent montane forest; and 4.6 percent agriculture, settlement, and unproductive lands (see Table 1) (Kinnaird et al. 2003, p. 230). Approximately 26 percent of the park is above 1,000 m (3,608 ft), an altitude where the salmon-crested cockatoo generally does not occur, and only 27 percent is below 500 m (1,640 ft), an altitude preferred by the salmon-crested cockatoo (Marsden 1992, p. 7). A road has been built through the park, which increases the risks of logging (Metz 1998, p. 10). Five villages of indigenous people exist as an enclave of the park. Most of the people work as dry land farmers; they also hunt and collect forest products, such as sago, rattan, resin, eaglewood, and parrots (BLI 2008e, p. 1). In 1980, 999 people lived within the park boundaries, and 19,102 lived within 10 km (6 mi) of its boundaries (Smiet and Siallagan 1981, App. 6). Clearing of the land for agriculture and gardens has resulted in a patchwork of cleared fields, secondary vegetation (including large bamboo thickets), old growth forests, and undisturbed primary forests. Conservation concerns for the salmon-crested cockatoo relate to logging, road development, encroachment by plantation companies, mining (Monk et al. 1997, as cited in BLI 2008e, p. 2), shifting agriculture, and parrot catching for trade (BLI 2008e, pp. 1-2).
The habitat is forest and the area has a mountain with the highest peak in Seram. The southern coastal area contains five villages. Most of the people work as farmers and fishermen. Main products are coconut for copra, clove, and cacao (BLI 2008f, p. 1). The Service was unable to find information on the number of salmon-crested cockatoos in this area or activities that may be affecting the conservation of the species in Pegunungan Taunusa.
The habitat is forest in northeastern Seram. BLI (2008f, p. 1) estimates that Wae Wufa, an area inside Wai Bula that is primary lowland and lower montane evergreen forests, has around 40-60 salmon-crested cockatoos. Approximately 596.1 km2 (230.1 mi2) of Wai Bula was proposed as a Nature Reserve in 1981, but the area has never been officially designated as a reserve (Kinnaird et al. 2003, p. 228). Land use for the proposed Nature Reserve can be summarized as follows: 94.2 percent lowland forest; 2.5 percent agriculture and settlement; 2.4 percent swamp forest; and 1.6 percent mangrove forest (see Table 1). Based on density estimates derived from surveys in western Seram, researchers estimated that the area provides habitat for a minimum of 2,500 cockatoos (Kinnaird et al. 2003, pp. 230, 233) (see Factor A for discussion). This estimate differs significantly from the number of cockatoos estimated by BLI to occur inside Wae Wufa. We were unable to reconcile these estimates because we could not find information on the area of Wae Wufa, how much of the cockatoo's suitable habitat within Wai Bula occurs in Wae Wufa, and the basis for the BLI estimate. The coast contains four villages. Most people work as farmers and fishermen. The main plantation products are coconut for copra, cacao, and coffee. The conservation concern for the salmon-crested cockatoo relates to logging (BLI 2008g, pp. 1-2).
The salmon-crested cockatoo is most active in early morning and late afternoon (Metz et al. 2007, p. 36; Juniper and Parr 1998, p. 281), calling loudly when leaving and returning to roost. The cockatoo's call is a wailing cry, which can be heard from a distance of 1 km (0.6 mi), and roosts can easily be located due to the noise. The species is shy and flies off when disturbed. Birds move slowly through the canopy in the early morning and are usually not seen or heard during the heat of the day. They are found in groups of up to 16 birds, although the size of non-breeding flocks appear to have been dramatically reduced due to the recent population decline (Juniper and Parr 1998, p. 281). They fly using a few rapid wing beats, followed by gliding, and then a few more wing beats (Juniper and Parr 1998, p. 281; Forshaw 1989, p. 141).
This species feeds on fruit of the kenari tree (Canarium commune, C. vulgare, and C. indicum) (Metz et al. 2007, p. 37), nuts, seeds, berries, and insects (Forshaw 1989, p. 141; Juniper and Parr 1998, p. 281). Their abundance is positively related to the density of strangling figs, a potentially important food resource (Kinnaird et al. 2003, p. 233). Research by O'Brien et al. (1998, p. 668) showed that figs may be a keystone plant resource for many fruit-eating birds. On the average, figs contain calcium levels 3.2 times higher than other fruits, promoting eggshell deposition and bone growth. Salmon-crested cockatoos are suspected of taking Pandanus spp. fruits (Bishop in prep., as cited in BLI 2001, p. 1665). They pick larvae from fallen, rotting tree trunks (Metz et al. 2007, p. 37). They also eat young coconuts (Cocos nucifera) by chewing through the tough outer covering to get at the pulp and water inside (Juniper and Parr 1998, p. 281; Forshaw 1989, p. 141; Wallace 1864, p. 279). In general, island cockatoos are thought to need to exploit all the available food in order to maintain a healthy population because islands typically contain fewer plant species and the quantity of food is restricted by an islands' relatively small size (Cameron 2007, p. 83).
Its favored nest tree is Octomeles sumatranus (Kinnaird et al. 2003, p. 230). During times of nest building, brooding, and fledging, birds stay close to the nest tree (Metz et al. 2007, p. 36). Courtship display can last up to 20 Start Printed Page 30764minutes, with the male and female perched in the top of an emergent or dead forest tree, raising and lowering their crests, fanning their large face and neck feathers forward to increase the size of the head (Cameron 2007, p. 57), calling loudly, breaking twigs, and making short, weak, fluttering flights. The nest is a high hole in a mature tree (Juniper and Parr 1998, p. 281). The salmon-crested cockatoo removes the bark immediately surrounding the entrance to help prevent predators, such as snakes or monitor lizards, from gaining access to the eggs or chicks, and may also clear the surrounding foliage perhaps to have a better view for the brooding hen. The nest site is fiercely guarded from competitors, such as the Eclectus parrot (Eclectus roratus) (Metz et al. 2007, p. 37).
Little is known about seasonality and breeding biology of the salmon-crested cockatoo in the wild (Kinnaird et al. 2003, p. 228), or other demographic information, such as reproductive effort and success and age-specific mortality rates—information that is important to determine where the primary weak points in the life equation lie (Snyder et al. 2000, p. 9). The cockatoo is thought to breed between July and August or September, and probably a second time at the beginning of the year (Metz and Zimmermann n.d., p. 1). Stresemann (1914, p. 86) observed a pair in a nesting cavity about 25 m (82 ft) up the trunk of a living tree in early May. The cockatoo lines the cavity with wood chips, and usually lays two white eggs, although only one chick is raised (Metz and Zimmermann n.d., p. 1). Both parents help to incubate the eggs during the 28-day incubation period. Young birds take 4-5 years to reach maturity (Juniper and Parr 1998, p. 281).
Seram—Historical Population Estimates
Historically, there are few quantitative observations of this species in the wild. In 1864, Wallace (1864, p. 279) described the salmon-crested cockatoo as “abundant” on Seram. In 1911, Stresemann (1914, p. 86) reported that the species was fairly common in coastal regions. The species was regarded as locally common in 1970 (Juniper and Parr 1998, p. 281). During 1980 and 1981 (Forshaw 1989, p. 141), Smiet (1985, p. 189) observed that this species was locally common in primary forests up to 900 m (2,952 ft) in the interior and in undisturbed forests, where 10 to 16 birds were seen congregating in roosting trees. He did not see any birds on the western part of the island, although the cockatoo was said to be common there until about 1970. In 1980, small flocks were observed in the south of the island (White and Bruce 1986, p. 212), and cockatoos were frequently seen throughout Manusela National Park below 900 m, except in the southern part of the Mual Plains in the center of the park where they were not common (Smiet and Siallagan 1981, p. 9). In September 1983, Bishop (1992, p. 2) observed four cockatoos in secondary woodland in southwest Seram.
Rangers at the Manusela National Park commented on a dramatic decline in the species in the mid-1980s (Collar and Andrew 1988, p. 69). By 1987, it was the rarest parrot in Manusela National Park (Bishop 1992, p. 2). Due to the international pet trade, Bishop considered the species to be endangered and in need of critical management to avoid imminent extinction (Bishop 1992, p. 1). Between July 20 and September 25, 1987, an Operation Raleigh team found the species to be “very scarce and absent from large tracts of suitable habitat” in Manusela National Park (Bowler 1988, p. 6). During 40 days of field work, they made 54 sightings, resulting in a maximum of 20 individual birds in prime habitat. In addition, birds were observed either singly or in pairs, never in flocks. Encounter rates were the lowest of any parrot species at 0.3 birds per hour in lowland rain forests around Solea at about 100 m (328 ft) and 0.1 per hour in the Kineka area at 600-900 m (1,968-2,952 ft) (Bowler and Taylor 1989, p. 17; Bowler 1988, p. 6). Marsden (1992, pp. 11-12) suggested that the densities of cockatoos, which Bowler and Taylor found in the Manusela National Park enclave, may be naturally low because the forest has been heavily disturbed and the area is at the upper end of the species' altitudinal range. He found it difficult to relate Bowler and Taylor's low figures for lowland forests around Solea to what he found in 1989 (see below). BLI also questioned the validity of the numbers, because Bowler and Taylor are now judged to have worked mainly at higher elevations in Manusela (BLI 2001, pp. 1664, 1668). Metz (1998, p. 10) suggested that the stronghold of this cockatoo is likely on Seram, almost exclusively outside of the borders of the national park.
During 5 weeks beginning December 19, 1989, Marsden (1992, pp. 7-8; Marsden 1998, p. 606) collected field data in Manusela National Park and in lowland habitats in central and northeast Seram, using the variable circular plot method to estimate densities of the salmon-crested cockatoo. Encounter rates were 1.0 bird per hour in primary forests, 2.5 birds in disturbed primary forests, and 0.4 birds in secondary and in recently logged forests. While cockatoo densities were similar in primary (9.1 birds per 1 km2 (0.386 mi2)) and disturbed primary forests (9.8 birds), densities were lower in secondary forests (6.4 birds), and much lower in recently logged forests (1.9 birds), suggesting that large-scale logging might adversely affect the species' population.
Between July and September 1996, the Wai Bula '96 (a conservation expedition from Cambridge University and Universitas Pattimura, Ambon) found the salmon-crested cockatoo to be widely dispersed in northeast Seram in the Wae Fufa Valley (primary lowland and lower montane evergreen forests) and in degraded coastal forests near Hoti (coastal secondary lowland forests), where pairs and small flocks were a common sight. They suggested that the bulk of the population probably occurs in eastern Seram (Isherwood et al. 1998, p. 18). Juniper and Parr (1998, p. 281) reported that the world population was “thought still to be above 8,000.”
Seram—Recent Population Estimates
The most recent research (Kinnaird et al. 2003, p. 232) estimated the total salmon-crested cockatoo population to be 110,385 birds (with confidence limits of a minimum 62,416 and a maximum of 195,242). Based on the research assumptions (see below), we agree with BLI (2001, p. 1664) that “* * * the figure of 62,400 is chosen as the appropriate population figure.”
These numbers were generated by joint population surveys conducted by the Wildlife Conservation Society Indonesia Program, BLI Indonesia Program, and Pelastarian Hutan Dan Konservasi Alam, Ministry of Forestry, Government of Indonesia in May-September 1998. Cockatoo censuses were conducted at seven sites in western and central Seram using line-transect methods (Kinnaird et al. 2003, pp. 228, 230, 234). Five of the sites were considered primary lowland forest and two had been previously logged or were disturbed by humans (Kinnaird et al. 2003, p. 228). Cockatoos were observed at all sites as single individuals or pairs. Estimates of density varied widely among locations, ranging from 0.93 birds per 1 km2 (0.386 mi2) at Kawa to 17.25 birds per 1 km2 at Roho. The mean density was 7.87 birds per 1 km2, which was considered indicative of all sites because it included estimates from primary and logged forests. The researchers were unable to complete the census before the outbreak of civil war; thus, data from the western part of Start Printed Page 30765Seram were used to estimate the number of cockatoos on all of Seram.
The population estimate was generated by working with GIS-based estimates of lowland forest habitat on Seram (14,026 km2 (5,414.2 mi2)) below 600 m (1,968 ft). This is based on the assumption that all lowland forests provide adequate habitat for cockatoos and that densities remain constant across the island (Kinnaird et al. 2003, p. 232). Because these assumptions are unlikely, Kinnaird (2000, p. 15) explained the scenarios considered by the researchers. Cockatoos are fairly tolerant of degraded habitat, but they still need nesting trees and have a preference for areas with lots of large strangling figs. The first scenario involved the number and extent of logging concessions operating on Seram during the 10-year-period from 1989-1999, which resulted in a reduction of 1,200 km2 (463 mi2) of lowland forest habitat for cockatoos. The population estimate still hovered between 90,000 and 100,000 birds. The second scenario looked at continued logging and habitat loss during the next decade, projecting that the population size would decline by another 10 percent. These two estimates may have underestimated cockatoo population size because many logging concessions are not working at full capacity. On the other hand, the estimates ignored additional losses due to the capturing of birds for the pet trade. The population estimate also ignored the variability in how logging companies harvest their concessions (i.e., greater or less than the legal maximum intensity). If logging concessions harvest timber in a conventional manner of up to 1,000 hectare (ha) (2,470 acre (ac)) per year, Kinnaird et al. (2003, p. 233) assumed that cockatoos will persist but at possibly lower densities.
In 1985, Smiet (1985, pp. 193-194) suggested that the relative resilience of most Moluccan parrots under trade pressure and habitat destruction can be attributed to a combination of factors, including: (1) A great reproductive capacity (especially in the smaller species); (2) adaptability to habitat alteration (which tends to provide a relative abundance of flowering and fruiting plants); (3) persistence of some original, undisturbed habitat; and (4) island isolation and lack of predators, parasites, and competitive species. Metz (2005, p. 34), however, cautioned that the current population estimate should not be a “cause for complacency.” He suggested that the number of birds capable of breeding, or the breeding success rate, might be low for this species because: They have a long life span, and many birds might be past breeding age; there is a very high poaching pressure and trappers mostly take adult birds, which depletes the number of breeding birds; and the salmon-crested cockatoo has a slow reproductive cycle and unknown, but possibly low, fledging success rate. These opinions point out the need for further research on this species to better understand its population size and its ability to adapt to the habitat destruction and trade that is occurring on Seram.
Very small numbers of salmon-crested cockatoos are thought to occur in remaining natural forests in the more remote regions of Ambon (Poulsen and Jepson 1996, p. 160). While Smiet (1985, p. 189) lived on the island from 1980 to 1981, he did not see the species there; however, he wrote that the species was said to be common on Ambon until about 10 years ago. In 1992, Marsden (1992, pp. 12-13) reported seeing eight salmon-crested cockatoos and three unidentified cockatoos during brief searches of remaining forest patches on Ambon. He suggested that most free flying salmon-crested cockatoos on Ambon may be wild birds, either resident and possibly breeding or visiting birds from Seram. Local people told him that cockatoos were still present in the area, but rare in other forested areas on the island. Poulsen and Jepson (1996, pp. 159-160) confirmed that wild populations of salmon-crested cockatoos occur on Ambon. On May 28 and June 11, 1995, they observed six to eight cockatoos, in forested hills behind Hila on the north coast of the Hitu Peninsula, overlooking a forested valley at about 300 m (984 ft) and in forest edge around shifting cultivation at about 500 m (1,640 ft).
The salmon-crested cockatoo is protected from capture and trade under Indonesian laws (Republic of Indonesia Law No. 5, 1990, and Law No. 7, 1999) (Kinnaird et al. 2003, p. 228; Kinnaird 2000, p. 14). Intentional violations may lead to imprisonment of up to 5 years and fines up to 100 million IDR (Indonesian rupiah) (which amounts to approximately 10,000 USD (U.S. dollar)). Negligent violations may lead to imprisonment of up to 1 year and fines up to 50 million IDR (5,000 USD). The government may seize and confiscate specimens of protected animals. The Department of Forest Protection and Nature Conservation is responsible for implementing the law, and the Natural Resources Conservation Agency, working with police, Customs, and other enforcement agencies, is responsible for enforcing the law (Shepherd et al. 2004, p. 4).
The species is listed on the IUCN (International Union for Conservation of Nature) Red List as `Vulnerable' because it has suffered a rapid population decline as a result of trapping for the pet bird trade and because of deforestation in its small range. BLI (2004, p. 1) projects the decline will continue and perhaps accelerate. The current population is estimated at 62,400 individuals (BLI 2001, p. 1664), with a decreasing population trend; the decline for the past and the future 10 years or 3 generations is estimated at 30 to 49 percent (BLI 2008b, p. 1). The current trend is justified by the suspected rapid decline of the species due to ongoing and prolific capture for the Indonesian domestic pet trade (BLI 2008b, p. 2). Ongoing threats are habitat loss and degradation due to selective logging and clear-cutting, agriculture, infrastructure development (settlement and hydroelectric projects), and harvesting (hunting and gathering for the domestic and international pet trade) (BLI 2004, pp. 1-2).
The cockatoo is also protected by CITES, one of the most important means of controlling international trade in animal and plant species threatened by trade. CITES is an international agreement through which member countries, or Parties, work together to ensure that international trade in CITES-listed animals and plants is not detrimental to the survival of wild populations by regulating import, export, and re-export. Although almost all Psittaciformes species, including the salmon-crested cockatoo, were included in CITES Appendix II in 1981 (CITES 2008a, p. 1), the species was transferred to CITES Appendix I effective January 18, 1990, because populations were declining rapidly due to uncontrolled trapping for the international pet bird trade (CITES 1989a, pp. 1-7). An Appendix-I listing includes species threatened with extinction whose trade is permitted only under exceptional circumstances, which generally precludes commercial trade. The import of an Appendix-I species requires the issuance of both an import and export permit. Import permits are issued only if findings are made that the import would be for purposes that are not detrimental to the survival of the species in the wild and that the specimen will not be used for primarily commercial purposes (CITES Article III(3)). Export permits are issued only if findings are made that the specimen was legally acquired and trade is not Start Printed Page 30766detrimental to the survival of the species in the wild (CITES Article III(2)). The United States and Indonesia, along with 173 other countries, are members to CITES (CITES 2009, p. 1).
The import of salmon-crested cockatoos into the United States is also regulated by the Wild Bird Conservation Act (WBCA) (16 U.S.C. 4901 et seq.), which was enacted on October 23, 1992. The purpose of the WBCA is to promote the conservation of exotic birds by ensuring that all trade involving the United States is sustainable and is not detrimental to the species. Permits may be issued to allow import of listed birds for scientific research, zoological breeding or display, or personal pet purposes when certain criteria are met. The Service may approve cooperative breeding programs and subsequently issue import permits under such programs. Wild-caught birds may be imported into the United States if they are subject to Service-approved management plans for sustainable use. At this time, the salmon-crested cockatoo is not part of a Service-approved cooperative breeding program and does not have an approved management plan for wild-caught birds (FWS 2008, p. 1).
The IUCN Status Survey and Conservation Action Plan 2000-2004 for Parrots (Snyder et al. 2000, p. 66) identified a need to clarify the status of the salmon-crested cockatoo in the wild, including: (1) Determining the species' relative abundance in each habitat type, and (2) collecting information on the size and distribution of habitat types, trapping, timber extraction, and breeding success of cockatoos in primary and secondary forests because it is unknown if the salmon-crested cockatoo will survive in degraded secondary forests in the long term. At present, inadequate information on the species, its habitat, and the effects of human activities on the species makes it difficult to make recommendations on regional development, such as reserve boundaries, land-use zoning, and possible new provincial forestry and agriculture policies, to ensure the species' survival. The information would also provide a baseline for monitoring and determining the degree to which trade affects the status of this species (Snyder et al. 2000, pp. 66, 69).
Summary of Factors Affecting the Salmon-Crested Cockatoo
Section 4 of the Act and its implementing regulations (50 CFR 424) set forth the procedures for adding species to the Federal Lists of Endangered and Threatened Wildlife and Plants. A species may be determined to be an endangered or threatened species due to one or more of the five factors described in section 4(a)(1) of the Act: (A) The present or threatened destruction, modification, or curtailment of its habitat or range; (B) overutilization for commercial, recreational, scientific, or educational purposes; (C) disease or predation; (D) the inadequacy of existing regulatory mechanisms; or (E) other natural or manmade factors affecting its continued existence. Listing actions may be warranted based on any of the above threat factors, singly or in combination. Each of these factors for the salmon-crested cockatoo is discussed below.
Factor A. The Present or Threatened Destruction, Modification, or Curtailment of the Species' Habitat or Range
The lowland forest habitat of the salmon-crested cockatoo is being impacted by logging (including the failure to use wise logging practices during selective logging), illegal logging, conversion of forests to agriculture and plantations, transmigration of people, oil exploration, and infrastructure development.
Commercial timber extraction is listed by the IUCN Red List to be a continuing major threat to the salmon-crested cockatoo, with a medium impact and a slow decline of the species (BLI 2008b, p. 3). Research that assessed a species-area relationship suggested that deforestation affects endemic bird species restricted to single islands most severely (Brooks et al. 1997, p. 392).
Between 2000 and 2005, Indonesia's forest cover declined by more than 90,000 km2 (34,740 mi2). Lowland areas, which offer important habitat for Indonesia's cockatoos, have been the most severely impacted (Cameron 2007, p. 177; Rhee et al. 2004, chap. 1 p. 2). On the islands of Sumatra and Kalimantan (Indonesian islands to the far west of Seram), the World Bank predicted that all lowland rain forests outside of protected areas would be degraded by 2005 and 2010, respectively (Rhee et al. 2004, p. xviii). In many areas of Indonesia, most commercially valuable forests have already been logged. Thus, major commercial logging enterprises are now focused on islands in Maluku Province, including Seram (BLI 2008k, p. 6; Smiet 1985, p. 181).
The impact of logging has steadily increased on Seram, with logging becoming more intense during the 1990s (BLI 2008k, p. 6). Deforestation in some areas has been extensive through selective logging of Shorea spp. (Ellen 1993, p. 201), such that by 2001, about a fifth of the original forest cover had been cleared (Morrison 2001, p. 1), with most of the coastal areas converted to grassland, agriculture, plantations, or scrub (Marsden 1992, p. 7). Although large areas of contiguous, intact forests remain (Morrison 2001, p. 1), 50 percent of forests, which are spread over the island, are under logging concessions. The north dipterocarp forests are still dominated by the endemic Shorea selanica, a tree especially vulnerable to logging as it grows tall and straight and is much favored by Western and Japanese markets (Edwards 1993, p. 9). Once the primary forest is logged, experience on nearby Indonesian islands shows that secondary forest is generally converted to other uses or logged again rather than being allowed to return to primary forest (Barr 2001, pp. 64, 67; Jepson et al. 2001, p. 859; Grimmett and Sumarauw 2000, p. 8).
Selective logging is the primary technique for the extraction of timber in Indonesia (BLI 2008k, p. 6). In selective logging, the most valuable trees from a forest are commercially extracted (Johns 1988, p. 31), and the forest is left to regenerate naturally or usually with some management until being subsequently logged again. Johns (1988, p. 31), looking at a West Malaysian dipterocarp forest, found that mechanized selective logging in tropical rain forests, which usually removes a small percentage of timber trees, causes severe incidental damage. The extraction of 3.3 percent of trees destroyed 50.9 percent of the forest. He concluded that this type of logging reduced the availability of food sources for frugivores (fruit-eaters). Edwards (1993, p. 9) observed a similar problem on Seram. Timber companies, operating under a selective logging system, caused considerable damage to the surrounding forest, both to trees and soil. Forests selectively logged 15 years before had an open structure with skeletons of incidentally killed trees, serious gulley erosion, and vegetation on waterlogged sites that had been compacted by heavy vehicles. Furthermore, commercial logging uses a network of roads, which can lead to secondary problems (BLI 2008k, p. 6), such as providing access to trappers of parrots.
Since selective logging targets mature trees, it can have a disproportionate impact on hole-nesters, such as cockatoos, because fewer nest sites remain (BLI 2008k, p. 6). Unsustainable logging practices that destroy the forest canopy also reduce habitat available to the salmon-crested cockatoo. Kinnaird et al. (2003, pp. 233-234) found that the Start Printed Page 30767abundance of cockatoos was positively related to the density of its favored nest tree, Octomeles sumatranus, and strangling figs, a potentially important food resource. These trees would be impacted by logging, emphasizing the need to implement wise logging practices, such as those based on reduced-impact logging techniques. However, these techniques, which are recommended under Indonesia's selective logging system, are seldom applied because of the lack of control over harvesting practices, limited understanding of how to implement the measures, and high financial costs (Sist et al. 1998, p. 1). Specifically, the pre- and post-logging inventories are not conducted properly or are not reported truthfully; over-cutting above the annual plan occurs; frequent cutting outside approved boundaries occurs; re-logging is more frequent than recommended; and supervision by the Ministry of Forestry has been ineffective (Thompson 1996, p. 9).
The salmon-crested cockatoo is dependent on little-disturbed lowland forests. In a field study conducted beginning December 19, 1989, for 5 weeks, Marsden (1992, pp. 7-13) looked at the distribution, abundance, and habitat preferences of the salmon-crested cockatoo on Seram. Results suggested that while cockatoo densities were similar in primary and disturbed primary forests, densities were lower in secondary forests, and much lower in recently logged forests (Marsden 1992, p. 9). In total, 84 cockatoos were recorded at 132 stations, either singly or in pairs, on 34 occasions. Groups of more than 4 birds were recorded 3 times, with a maximum group size of 10. Although cockatoos were found at different densities in different land-use types, more cockatoos were present where habitat alterations occurred on a small scale. Cockatoos tended to be recorded in mature, open-canopied lowland forests with some very large, tall trees and some low vegetation. Most significantly, Marsden found that there may have been a reduction of the cockatoo population by about 700 birds for each 100 km2 (86 mi2) of Seram's primary forests that had been selectively logged in the last 6 years. Similarly, the conversion of 100 km2 of locally disturbed secondary forests to plantation could result in the loss of around 600 birds (Marsden 1992, p. 12).
Marsden (1998, pp. 605-611) also looked at changes in bird abundance following selective logging on Seram. Field work was conducted in forested areas in the central and northeast parts of the island. Logged forests usually had sparser canopy and mid-level vegetation cover and denser ground cover than unlogged forests (Marsden 1998, pp. 605, 607-608). Using a point count method to estimate population densities, Marsden (1998, p. 608; 1999, p. 380) found that salmon-crested cockatoo density estimates in unlogged forests below 300 m (984 ft) were more than double those in logged forests. Because the cockatoo is caught for the pet trade, Marsden was unable to separate the effects of habitat change, such as loss of nest holes, from possible effects of logging on capture rates (for example, increased accessibility for trappers to forests by access roads) (Marsden 1998, p. 610). Although Kinnaird et al. (2003, p. 233) found the highest cockatoo densities in primary forest habitat with good structure and lower densities in logged or disturbed sites, they did not find a statistically significant difference in cockatoo densities between logged and unlogged forests. They surmised this may have been because of the intensity of logging or, more likely, reflected the mosaic of habitat types found within their sampling sites. They speculated that there is a continuum of cockatoo densities in logged forests depending on the intensity of logging and access provided to trappers.
Logging concessions are spread over Seram, except there are no concessions in Gunung Sahuai Nature Reserve and only 15 percent of Manusela National Park is under concessions (Kinnaird et al. 2003, p. 231). About half the island (8,271 km2 (3,193 mi2)) is held within logging concessions, with more than 75 percent within lowland habitat favored by the salmon-crested cockatoo (Kinnaird et al. 2003, pp. 227, 233). This means that less than 30 percent of the island's lowland forests (5,096 km2 (1,967 mi2)) is unoccupied by logging concessions. In 1998, Kinnaird et al. (2003, pp. 233-234) were unable to find out the area of land scheduled for logging. However, Kinnaird (2000, p. 15) was able to obtain information from the Ministry of Forestry that showed 12 logging concessions had been operating on Seram during the 10-year period from 1989-1999. If the concessions have been logged at a maximum intensity of 10 km2 (3.86 mi2)/year/concession and logging was conducted in a conventional manner that results in 70 percent damage to the canopy, lowland forest habitat for cockatoos would be reduced by 1,200 km2 (463 mi2), or 8.5 percent, in 10 years. The researcher concluded in 2000 that overall the loss of habitat has not reached a level where it is perceived as a serious threat to cockatoos. However, the cockatoo remains under threat (Kinnaird 2000, p. 15). We have no reason to believe that the effects of logging on the species will be ameliorated in the foreseeable future, but may increase because commercial logging enterprises are now focused on the Maluku Province, including Seram.
The researchers were forced to leave the island because of civil unrest. They suggested that the pressure for land conversion will accelerate dramatically once social and economic stability returns to Seram, especially in the lowlands, and this will be made worse by the 1999 regional autonomy laws that allow for local authorities to determine licensing of forest concessions and exploitation of natural resources. They concluded that the proper management of Seram's logging concessions would determine the future of the salmon-crested cockatoo (Kinnaird et al. 2003, p. 234).
Approximately 14 percent of Seram's forests (or 11.5 percent of lowland forests) are protected in Manusela National Park (2,216.4 km2 (855.5 mi2)) and Gunung Sahuwai Nature Reserve (118.9 km2 (45.9 mi2)). In Manusela National Park, 15 percent of the forest is within logging concessions. In 1981, Smiet and Siallagan (1981, pp. 11-12, 22) reported that large patches of forest in the coastal region of the Mual Plains had been disturbed by logging activities—forests along the southeastern boundary of the park had been cleared up to 400 m (1,312 ft) and planted with clove and coconut plantations. They advocated the development of a buffer zone between the park and the densely populated coastal area because more and more forests at increasing altitudes were being cleared. Kinnaird et al. (2003, p. 233) estimated that the protected areas in Seram provide habitat for a minimum of 7,300 salmon-crested cockatoos based on density estimates derived from their surveys. However, logging has recently occurred inside Manusela National Park, and, once logging has concluded, there are pressures to change the land use to agriculture or plantations (BLI 2008k, p. 7). Kinnaird et al. (2003, p. 233) also estimated that the proposed Wai Bula Nature Reserve, 561.8 km2 (216.9 mi2) of lowland forests located in the northeastern part of Seram, provides habitat for a minimum of 2,500 cockatoos. We believe that this population estimate, which is based on the availability of suitable habitat, may be an overestimate because the Wai Bula area is currently not protected (it was proposed as a nature reserve in 1981 and the probability of it being officially designated is now low) and 93 percent of the area is under logging concessions.Start Printed Page 30768
Illegal logging is considered to be a leading cause of forest degradation in Indonesia (Rhee et al. 2004, chap. 6 p. 7). It is pervasive, and the Indonesian government has been unable to enforce its own forest boundaries (Barr 2001, p. 40). Illegal logging includes overharvesting beyond legal and sustainable quotas, harvesting of trees from steep slopes and riparian habitat, timber harvesting and land encroachment in conservation areas and protection forests, and falsification of documents. Overexploitation of the forests and illegal logging are driven by the wood-processing industry, which consumes at least six times the officially allowed harvest (Rhee et al. 2004, pp. xvii, chap. 6 p. 8). Illegal logging in the national parks is also reported with regularity, and the persons involved are armed and ruthless (Whitten et al. 2001, p. 2).
Although the Indonesian government issued Presidential Instruction No. 4/2005 to eradicate illegal logging in forest areas and distribution of illegally cut timber throughout Indonesia (see Factor C) (FAOLEX 2009, p. 1), illegal logging continues. The Center for International Forestry Research estimated that between 55 and 75 percent of logging in Indonesia is illegal (U.S. Agency for International Development (USAID) 2004, p. 1). Contributing factors include poor forest governance, rapid decentralization of government, abuse of local political powers, complicity of the military and police in some parts of the country, inconsistent enforcement of the law, and dwindling power of the central government (USAID 2004, pp. 3, 9). In December 2000, Jepson et al. (2001, pp. 859-861) found illegal logging crews operating freely in protected areas and forest concessions in Sumatra and Kalimantan, Indonesia. Jepson et al. (2001, pp. 859-861) also claimed that local government officials were in collusion with illegal loggers by turning a blind eye to the practice or providing permits for timber transport. Some government officials, who wanted to stop illegal logging, faced serious intimidation. Jepson et al. concluded that illegal logging was becoming semi-legal and the de facto arrangement for governing Indonesia's forests.
Conversion of Forests to Agriculture and Plantations
Indonesia is a rapidly developing country with a projected population of 235 million by 2015 (Snyder et al. 2000, p. 59). A growing population on Seram has converted forest into cultivated land, with human settlements and plantations typically located in lowland coastal areas (Smiet 1985, pp. 181, 183). Based on data from landsat images from late 1989 and early 1990 (Kinnaird et al. 2003, p. 230), land use in Seram is as follows: 4.6 percent in agriculture, 0.1 percent in plantations, and 0.1 percent in settlements (see Table 1 above). Although these percentages are low, forests continue to be converted for agriculture and plantations.
Near the coast, forests have been replaced with plantations of coconut, oil palm, and spices. Inland, forests on rich alluvial soil, once timbered, are liable to be converted to agricultural fields. Part of the Indonesian government's long-term planning strategy is to develop more efficient agriculture through improved and appropriate techniques to help alleviate poverty. If the plan is carefully implemented, improved agricultural techniques could reduce pressure on areas of natural habitat (BLI 2008k, pp. 7-8). However, Snyder et al. (2000, p. 66) cautioned that, as most of Seram's forests are under timber concessions, the island's development priority could mean that forests over good soil may be converted to wet rice cultivation and other crops, a habitat in which the salmon-crested cockatoo is unable to exist (Snyder et al. 2000, p. 66).
Approximately 6,220 km2 (2,401 mi2) of Seram's lowland forest is slated for conversion to agriculture or plantations (45 percent within logging concessions). By 2028, most of this land will probably be converted to these uses that provide no habitat for cockatoos, resulting in habitat loss for at least 31,000 cockatoos and reducing the total island population to around 30,400 individuals (Kinnaird et al. 2003, p. 233).
Indonesia has long had a policy to resettle people, mainly from Java, to develop the less populated regions of the country, with the Maluku Province being a major destination (BLI 2008k, p. 8). From 1969-1989, some 730,000 families were relocated in Indonesia (Library of Congress 1992, p. 1). While the scale of transmigration has been reduced over the past decade, the recent unrest in Maluku led to large-scale movement of people. In some areas, these movements of people have had serious negative effects on the environment, involving land disputes with indigenous inhabitants (Library of Congress 1992, p. 1), forest clearance for agriculture, unsustainable slash-and-burn farming (BLI 2008k, p. 8), and introduction of wet rice cultivation (Ellen 1993, p. 200).
In 1993, a significant oil discovery was made in eastern Seram—the Non-Bula Block, which occupies an area of about 4,572 km2 (1,765 mi2). Development was delayed until 2002 (Lion Energy Limited 2009, p. 2). The average output from the main oil field, the Oseil Field, in the first half of 2006 was 4,300 barrels per day (Entrepreneur 2009, p. 1). The gross oil reserves in that field have been estimated to be about 39 million barrels—7 million barrels of proven reserves, 6 million barrels of probable reserves, and 26 million barrels of possible reserves (International Business Times 2009, p. 1). In 2008, oil was discovered in a new well, which lies 4 km (2.5 mi) from the Oseil Field. The investment firm is currently petitioning the Indonesian government to begin production and export operations from the new field (E&P Magazine 2008, p. 1). Generally, oil development areas cover large tracts of land, but the area occupied by permanent facilities including pipelines and refineries is relatively small. However, oil development can have significant negative impacts on nearby habitat through construction of roads and other buildings, discharge of refineries, and oil spills and leaks (Rhee et al. 2004, chap. 6 p. 31).
Seram is remote, with no airport and only rudimentary ground transportation (Morrison 2001, p. 5). An essential part of regional development is the improvement of roads. However, new roads can cause serious environmental problems (BLI 2008k, p. 8), as shown by the Trans-Seram Highway, which threatens forest habitat by illegal logging, land clearance, and soil erosion (Morrison 2001, p. 5). The excavation of sand for local road construction has affected some habitat on Seram. Previous proposals for a large cement factory, with a quarry and hydroelectric dam, close to Manusela National Park appear to have been abandoned (BLI 2008k, p. 8).
Summary of Factor A
The salmon-crested cockatoo resides in lowland forests predominately between 100-600 m (328-1,968 ft) throughout the island, with the highest densities of birds occurring in little-disturbed forests. Logging and illegal logging are primary threats to the habitat of this species, with the threats occurring throughout the island in lowland forests.
Cockatoos are highly impacted by selective logging of primary forests. Start Printed Page 30769Selective logging, which targets mature trees, has a negative impact on hole-nesters, such as the salmon-crested cockatoo. Research found that the abundance of cockatoos was positively related to the density of its favored nest tree and strangling figs, trees that would be impacted by logging, especially since reduced-impact logging techniques are seldom applied.
Research also found that for every 100 km2 (38.6 mi2) of Seram's primary forests that were selectively logged in the last 6 years, 700 birds were likely lost from the cockatoo population. Similarly, for every 100 km2 of locally disturbed secondary forest that were converted to plantations, 600 birds were likely lost from the cockatoo population. While the estimated densities of cockatoos in logged forests below 300 m (984 ft) were more than half those in unlogged forests, researchers were unable to separate the effects of habitat change from the possible effects of logging on trapping rates (see Factor B).
Once the primary forest is logged, experience on other nearby Indonesian islands shows that the secondary forest is generally converted to other uses or logged again rather than being allowed to return to primary forest. Therefore, although cockatoos may continue to inhabit secondary forests on Seram, the population will be at a substantially lower number. The trend of high loss of primary forests and degradation of secondary forests is of concern because little is known about the reproductive ecology of the salmon-crested cockatoo in the wild, including breeding success in mature forests versus secondary forests, and whether the cockatoo will survive in degraded forests in the long term. Also, the size of groups of cockatoos observed was drastically smaller in research conducted in 1998, where 75 percent of birds were observed as single individuals and 22 percent in pairs, compared to earlier reports, where groups of up to 16 birds were seen.
By 2001, approximately 20 percent of the original forest cover on Seram had been cleared. About 50 percent of the island's forests were held under logging concessions, with more than 75 percent within the salmon-crested cockatoo's favored lowland habitat. Based on information from the Ministry of Forestry in Indonesia, researchers estimated that the cockatoo lost 1,200 km2 (463 mi2), or 8.5 percent, of habitat between 1989 and 1999 due to logging. Although we have no information on the current status of logging concessions or actual logging (legal and illegal) activity on Seram since 1999, we anticipate that the rate of loss of cockatoo habitat due to logging will continue at the 1989-1999 level or increase because commercial logging enterprises are now focused on Seram. We have no information that indicates that this trend will be reversed in the foreseeable future.
In addition, approximately 44 percent of Seram's lowland forests (6,220 km2 (2,401 mi2)) is designated as conversion forest, of which 45 percent is within logging concessions. It is predicted that by 2028 up to 50 percent of the current population (at least 31,000 cockatoos) may be lost as a result of conversion of forests to agriculture and plantations, which provide no habitat for the cockatoo.
Approximately 11.7 percent of Seram's lowland forests are protected in Manusela National Park and Gunung Sahuwai Nature Reserve. Researchers estimated that these protected areas could provide habitat for up to 7,300 salmon-crested cockatoos. However, about 15 percent of the national park is under logging concessions and illegal logging has been occurring. Once the land is logged, the land use is often changed to agriculture.
The resettlement of people on Seram has had negative effects on the environment and the habitat of the salmon-crested cockatoo. These negative effects include forest clearance for agriculture, unsustainable slash-and-burn farming, and introduction of wet rice cultivation. The relatively recent development of oil production on Seram most likely has adversely affected the cockatoo's habitat. Potential development of such a large part of Seram (the current Non-Bula Block occupies one-quarter of the island) is a concern because at one time the salmon-crested cockatoo appeared to be mostly distributed in the eastern part of the island. Although we do not know what forest habitat has been destroyed, we do know that oil development on Seram will have a negative impact on nearby habitat through road building and other construction, discharge of refineries, and oil spills and leaks. Further, an essential part of regional development is infrastructure development, primarily the improvement of roads, which leads to illegal logging and land clearance, as well as facilitates bird trapping.
In summary, extensive logging and conversion of lowland forests to agriculture and plantations, combined with transmigratory human resettlement, oil exploration, and infrastructure development, are likely to destroy much of the lowland rain forests of Seram, the salmon-crested cockatoo's habitat, by 2025. Therefore, we find that the present and threatened destruction, modification, or curtailment of its habitat is a threat to the continued existence of this species throughout all of its range in the foreseeable future.
Factor B. Overutilization for Commercial, Recreational, Scientific, or Educational Purposes
The salmon-crested cockatoo is a very popular pet bird. In the 1980s, it suffered a rapid population decline due to trapping largely for international trade. Below we analyze the impact of international and domestic trade within and surrounding Indonesia and other uses for recreational, scientific, or educational purposes. We also consider and describe programs on Seram to support the conservation of the cockatoo—the release of confiscated cockatoos and local involvement.
International and Domestic Commercial Trade
International wildlife trade is a profitable business and has been identified as contributing to the decline of a number of bird species, including the salmon-crested cockatoo (BLI 2008h, p. 1). The majority of wild-caught birds in international trade are sold as pets (Thomsen et al. 1992, p. 5). In addition, in Indonesia, pet birds, particularly parrots, are an important part of the culture, creating a massive demand for parrots internationally and domestically (BLI 2008k, p. 10). In a survey of bird-keeping among households in five major Indonesian cities, Jepson and Ladle (2005, pp. 442-448) found that as many as 2.5 million birds are kept in the five cities. Of these, 60,230 wild-caught native parrots were kept by 51,000 households, and 50,590 wild-caught native parrots were acquired each year (this annual figure represents a change in ownership and not the number of individuals taken from the wild). The researchers concluded that the level of bird-keeping among urban Indonesians calls for a conservation intervention.
Parrots have been traded for hundreds of years by people living in the Moluccas. Heinroth (1902, p. 120) reported that at the start of the 20th century, trade significantly impacted the salmon-crested cockatoo. Bowler (1988, p. 6) wrote that the salmon-crested cockatoo was severely threatened by extensive trapping for the pet bird trade in the late 1970s, with the government apparently having little control over the number of birds taken from the wild. In the 1980s, extensive trapping of the salmon-crested cockatoo was the most important factor in the species' decline (BLI 2008k, p. 10; Forshaw 1989, p. 141). Smiet reported that trade in live birds flourished on Seram. The salmon-crested cockatoo was a popular pet Start Printed Page 30770traded in large numbers, accounting for 15 percent of the export (Smiet 1985, pp. 181, 189). Smiet (1982, pp. 324-325) also found live cockatoos readily available in the Ambon market.
Based on the most recent CITES annual report data, 74,838 salmon-crested cockatoos were reported as exported from Indonesia between 1981 and 1990 (only 26 of these were reported as bodies, all others were reported as live birds), with international imports (from all exporting countries) averaging 8,393 annually (UNEP-WCMC 2009b, p. 3; 2009a, p. 1). The species was listed in CITES Appendix II in 1981, but the high volume of trade led the CITES Significant Trade Working Group to identify this species as one of particular concern (CITES 1989b, p. 121). A review of CITES annual report trade data available at the time showed that the level of international trade of live birds was having a detrimental effect on wild populations (Inskipp et al. 1988, pp. 185-186, 188). The trade data showed imports of live salmon-crested cockatoos continued to be high in 1986 and 1987, with the 1987 Indonesian harvest quota being exceeded by 3,661 birds (CITES 1989a, p. 5) or 72 percent. The Indonesian government decreased the annual harvest quota from 10,250 in 1984 to 1,000 in 1989, but a CITES document suggested that these national measures to control trade had been ineffective (CITES 1989b, p. 121). Thus, the CITES Parties voted to transfer the salmon-crested cockatoo to CITES Appendix I, effective January 18, 1990. In 1990, field work on Seram revealed a “sharp decline in visible trade” in the salmon-crested cockatoo, although small numbers of birds were still leaving the island (Taylor 1990, p. 14).
Although CITES annual reports are of great value in assessing levels of legal trade and trends of trade, the number of cockatoos traded may be higher than the data reflect. The numbers do not include data from countries that are not CITES Parties or CITES Parties that did not submit annual reports (Inskipp et al. 1988, p. viii); although, in many cases the Parties that these countries traded with did submit records. Also, the numbers do not include deaths of birds before export, birds illegally traded, and birds domestically traded, factors that can potentially double the numbers, according to Cameron (2007, p. 163). ProFauna Indonesia, an animal protection nongovernmental organization, estimated that parrot smuggling in North Maluku, Indonesia, results in approximately 40 percent mortality (5 percent during glue trapping, 10 percent during transportation, and 25 percent during holding to sell in bird markets (due to malnutrition, disease, and stress)) (ProFauna Indonesia 2008, p. 5). Undocumented illegal trade (international and domestic) is difficult to quantify (Pain et al. 2006, p. 322; Thomsen et al. 1992, p. 3), and a listing in Appendix I of CITES does not totally stop illegal trade (Pain et al. 2006, p. 328). Seizures reported to the CITES Secretariat since 1990, however, are small—1 live bird seized in Austria in 1997; 25 live birds seized in the United Arab Emirates in 1998; and 4 live birds seized in Indonesia in 1999 (John Sellar 2009, pers. comm., p. 2). However, it should be noted that CITES Parties are not required to identify seizures in their annual reports, so actual seizure figures may be higher. Since 1999, the U.S. Fish and Wildlife Service, Office of Law Enforcement, has seized only two salmon-crested cockatoos for lack of proper permits (FWS 2009, p. 1).
While CITES reported a clear fall in trade after 1989, with an average annual worldwide import of 159 cockatoos (UNEP-WCMC 2009c, p. 5), illegal hunting and trade of salmon-crested cockatoos continues today, with high domestic consumption in Indonesia, despite this species also being protected under Indonesian laws (Republic of Indonesia Law No. 5, 1990, and Law No. 7, 1999), which include imprisonment and fines for violations (see Conservation Measures above). Extrapolating from figures obtained during interviews with parrot trappers in 1998, an estimated 4,000 salmon-crested cockatoos are trapped each year on Seram (BLI 2008k, p. 10; Cameron 2007, p. 164), which is approximately 6.4 percent of the population (Kinnaird et al., in litt., as cited in BLI 2001, p. 1666). Direct evidence of continuing illegal trade is the sighting of glue traps (Kinnaird 2000, p. 15). Poachers use glue traps by cutting a suitable perching branch out of a tree and replacing that branch with one that has been smeared with sticky glue. Then a tame decoy bird lures wild birds into the glue trap (ProFauna Indonesia 2008, p. 2). Birds are also captured using nylon fishing-line snares or by tracing adults to their nesting sites so that the young can be taken (ProFauna Indonesia 2004, p. 5; Juniper and Parr 1998, p. 218; Bowler 1988, p. 6). Metz (2005, p. 35) described local declines in the salmon-crested cockatoo, based on statements from trappers. When cockatoos became scarce on the western part of the island in 1991-92, poachers moved to the eastern and northern parts of the island.
Even with government controls, the commercial hunting of cockatoos (i.e., hunting by people to gain at least a temporary living from the activity) is relatively common on Seram (Ellen 1993, p. 199). Field research conducted in 2003-2005 in a small village (320 people, 60 households) located in the Manusela Valley led to the conclusion that collecting wild parrots, including the salmon-crested cockatoo, is a way for villagers to supplement their income during times of hardship (Sasaoka 2009, pers. comm., p. 1; Sasaoka 2008, p. 158). Most trapping was sporadic and the number of parrots caught was low. Traps are set in fruit trees such as durian (Durio spp.) and breadfruit (Artocarpus heterophyllus) from January to May, and traps are set in resting sites at any time of the year. In 2003, 21 salmon-crested cockatoos were trapped in the research site by 3 households; in 2004, 25 cockatoos by 5 households; and in 2005, 26 cockatoos by 10 households. Villagers sometimes kept the cockatoos for several months while waiting for the best price, but normally did not keep them as pets. Trappers received 70,000-100,000 IDR (7-10 USD) for an adult cockatoo and 200,000-250,000 IDR (20-25 USD) for a baby cockatoo, selling the birds to middlemen in coastal areas (Sasaoka 2009, pers. comm., pp. 1-2). In studying the forest peoples of Seram, social anthropologists have reported that parrot catching accounts for 25 to 30 percent of forest people's cash income, and that young men among the Halafara people of the Manusela Valley catch and sell parrots to raise their bride price (Badcock in litt. 1997 as cited in Snyder et al. 2000, p. 60).
The scope of the illegal trade in the salmon-crested cockatoo is unknown. After conducting an investigation from December 2003 to May 2004, ProFauna Indonesia reported that smuggling and trade in protected birds continues despite legislation that prohibits such activities. According to the report, at least 9,600 parrots, including salmon-crested cockatoos (numbers of birds by species not given in this article), are caught on Seram and sold to bird exporters in Jakarta via Ambon each year (ProFauna Indonesia 2006, p. 1; 2004, p. 6). The illegal practice involved Ambon's largest bird trader and Seram's most prominent bird collector and trader (Jakarta Post 2004, p. 2). A principal broker on Seram might have 20-50 salmon-crested cockatoos at any one time (Metz and Nursahid 2004, p. 8), even though legal trapping quotas are zero. A single trapper can capture up to 16 cockatoos each month within Manusela National Park (ProFauna Indonesia 2004, p. 4). However, finding Start Printed Page 30771and trapping birds have become harder, and the price paid to trappers has increased (Metz 2008, pp. 2-3).
Cockatoos are taken to the coast, sold, and transported to Ambon on boats in packed cages (Juniper and Parr 1998, p. 281) in hidden compartments surrounded by legally shipped lories and lorikeets (Metz and Nursahid 2004, p. 9; Profauna Indonesia 2004, p. 7) or by hiding birds in thermos bottles (Metz 2005, pp. 35-36; Metz and Nursahid 2004, p. 9; ProFauna Indonesia 2004, p. 9) or sections of bamboo (Cameron 2007, p. 164). Salmon-crested cockatoos may also be reported on shipping permits as white cockatoos (Cacatua alba), an unprotected species in Indonesia (ProFauna Indonesia 2004, p. 6). Some birds are flown to Jakarta and may receive a police escort to the market (Metz and Nursahid 2004, p. 9). Illegally exported cockatoos are reported from Indonesian markets in Medan and Sumatra or international markets in Singapore and Bangkok (Kinnaird 2000, p. 15), or they may pass through Singapore, China, Taiwan, and Malaysia, with Thailand a recent major importer (Metz n.d., p. 1). Cockatoos also may be smuggled directly out of Indonesia and sent by boat to the Philippines and Singapore, which act as distribution points for worldwide illegal trade (Cameron 2007, p. 164).
Most Indonesian towns have either a bird market or a stall selling birds within the main market (Shepherd et al. 2004, p. 2). Birds in Indonesian markets are most likely sold for domestic use, although some birds will go into international trade (Cameron 2007, p. 163). Metz (2007b, p. 2) estimated that 80 percent of illegally traded salmon-crested cockatoos remain in Indonesia. Some cockatoos remain as pets where they are trapped, but most are sold to homes in the cities in western Indonesia, where the salmon-crested cockatoo is a symbol of wealth and prestige (Metz n.d., p. 1). This cockatoo is still sold openly in the markets of Ambon and elsewhere in Indonesia. Cameron (2007, p. 163) noted that in 1998, Margaret Kinnaird and co-workers saw up to 40 salmon-crested cockatoos at any time in Ambon markets. In an analysis of the pet trade in Medan, Sumatra, between 1997 and 2001, Shepherd et al. (2004, p. 12) concluded that the salmon-crested cockatoo was common in trade in Medan, with 71 cockatoos being recorded in the markets. Most of the birds at the Medan market were sold as live pets (Shepherd et al. 2004, p. 24). In 2003, ProFauna Indonesia (2004, p. 8) found 50 salmon-crested cockatoos had been traded among three markets in Java known to sell hundreds of protected parrots: Bratang bird market in Surabaya, Pramuka bird market in Jakarta, and Pasar Turi in Surabaya. However, ProFauna Indonesia speculated that the real number must be higher than 50 because the number of parrots shipped from Seram to Jakarta within a month is at least 20 and estimated that a minimum of 240 salmon-crested cockatoos are illegally shipped to Jakarta in a year (ProFauna Indonesia 2004, pp. 10-11). In addition to being sold at markets in Jakarta, salmon-crested cockatoos are also sold to the people of Maluku, including soldiers of the National Indonesian Army returning to Java; shipments using military ships are difficult to control (ProFauna Indonesia 2004, p. 9).
Stopping illegal trade is complicated by the vast size of Indonesia's coastline and government officials with limited resources and knowledge to deal with the illegal pet trade and corruption (Metz 2007c, p. 2). ProFauna Indonesia claimed that illegal traders exploited the religious conflict between Muslims and Christians in the Maluku Islands in May of 2004, flooding the markets in Jakarta with salmon-crested cockatoos. Animal activist and Chairman of the Balikpapan Orangutan Survival Foundation, Willie Smith, suggested that it would be difficult to stop the illegal trade in cockatoos because much of the smuggling was backed or carried out by the Indonesian military and because the departments responsible for protecting natural resources were hampered by conflicts of interest and a lack of willingness to take action (Jakarta Post 2004, pp. 3, 4). Until recently, the wildlife protection laws have not been vigorously enforced, but this may be changing. For example, in September 2004, National Park Officers arrested a long-term bird buyer and confiscated nine salmon-crested cockatoos. The buyer was sentenced to two months' jail time and given a fine (Metz n.d., p. 1).
To combat the illegal wildlife trade, Southeast Asian countries, including Indonesia, formed the Association of South East Asian Nations-Wildlife Enforcement Network (ASEAN-WEN) in 2005 to protect the region's biodiversity (Gulf Times 2008, p. 1). ASEAN uses a cooperative approach to law enforcement (Cameron 2007, p. 164). It focuses on the gathering and sharing of intelligence, capacity building, and better cooperation in anti-smuggling and Customs controls across Southeast Asia (Lin 2005, p. 192). For example, in 2008, Indonesian police officers and forestry and Customs officers participated in an intensive Wildlife Crime Investigation Course to help the government tackle poaching and smuggling (Wildlife Alliance 2008, p. 2).
Assessing the effects of trade on wild populations of parrots, such as the salmon-crested cockatoo, is difficult because the threats of habitat loss and trade operate in concert (Snyder et al. 2000, pp. 2, 68). For example, the loss of habitat due to logging, conversion of forests to agriculture and plantations, increased human settlement, oil exploration, and infrastructure development leads to more exposure to bird trapping. Thus, it is difficult to distinguish between the effects of habitat loss and trade on the cockatoo. In addition, little information is available on the number and age of birds being taken from the wild and when and where the birds are being trapped. For example, the trapping of large numbers of breeding-age adults from a population is apt to have a larger overall adverse impact than the removal of a similar number of juveniles (Thomsen et al. 1992, p. 10). Coates and Bishop (1997, pp. 39-41) reported that trapping the salmon-crested cockatoo for international and domestic Indonesian markets, in combination with ongoing destruction of lowland forests, was having a major negative impact on wild populations. They concluded that, despite the protection given to the cockatoo by Manusela National Park, this cockatoo was being trapped to extinction.
Recreational, Scientific, or Educational Purposes
While conducting research in one village in central Seram, Dr. Sasaoka (pers. comm. 2009, p. 2) wrote that hunting with air guns for food started in 2000. Although the use of air guns was not common in his research site, about 10 villagers were using air guns to hunt Columbidae species (pigeons and doves). If a hunter encountered a salmon-crested cockatoo in the forest or garden by chance, the hunter would shoot it for food. Based on Dr. Sasaoka's unpublished field data, about 40 salmon-crested cockatoos were shot and killed by air gun hunting in 2003. This information raises questions on the use of air guns on Seram. Without additional data, however, we are unable to assess the possible impact air gun hunting may be having or will have on the survival of salmon-crested cockatoos. We are not aware of any overutilization of the salmon-crested cockatoo for recreational, scientific, or educational purposes that is a threat to the species now or in the foreseeable future.Start Printed Page 30772
Release of Confiscated Cockatoos
In recent years, small numbers of confiscated salmon-crested cockatoos have been rehabilitated and released into the wild. In 2005, the Kembali Bebas Avian Center for the rescue and rehabilitation of Indonesian parrots was established on Northern Seram (IPP (Indonesian Parrot Project) 2008c, p. 1; Price 2008, p. 2). In March 2006, three illegally trapped salmon-crested cockatoos, which had been confiscated from local trappers by forestry officials in 2004, were released on Seram. The birds were tested for diseases, observed for wild behaviors, fitted with a leg band, and tagged with a microchip to allow for long-term monitoring (IPP 2008a, p. 2). In January 2008, six more salmon-crested cockatoos were released, and in February 2008, seven more were released. The project provides the government a means of dealing with confiscated parrots. It also gives local villagers pride in their native birds and teaches them the principles of conservation (ireport 2008, pp. 2-3). Although the Center uses the IUCN and CITES guidelines when releasing birds due to the risk of introducing diseases into wild populations (Metz 2007c, p. 7), some parrot experts find the release of confiscated birds generally the least favorable conservation option and should be avoided because of the risk of introducing diseases into wild populations (Snyder et al. 2000, pp. 22-24). However, we found no information indicating this action as a threat to the salmon-crested cockatoos.
Indonesia is a culturally diverse country and the values and perceptions of many Indonesians may differ from those of western conservationists. Many rural villagers are unaware that birds have restricted distributions and do not understand the concept of extinction. Thus, they may think that, when a population declines, the birds moved into the hills or are getting smarter and, therefore, harder to catch (Snyder et al. 2000, pp. 60-61). In addition, using and trading natural resources is a basic part of Indonesian culture and economy (Snyder et al. 2000, pp. 60-61). As a result, one of the most important components of successful conservation programs is local education that promotes optimism, cooperation, and collaboration and helps people discover and understand the underlying causes of environmental problems (Snyder et al. 2000, pp. 14-15).
Others also have recognized the need for a strong awareness campaign concerning the legal and conservation status of the salmon-crested cockatoo (BLI 2001, p. 1668; Metz 1998, p. 11). The IPP is a nonprofit organization dedicated to the conservation of wild Indonesian parrots, with goals to teach the principles and value of conservation, replace trapping of parrots with sustainable economic alternatives, work with the Indonesian authorities to rehabilitate and release confiscated parrots back into the wild, conduct scientific research, and provide information (Metz 2007c, p. 6). IPP started a Conservation-Awareness-Pride (CAP) program to reach adults and children in the villages where the birds are trapped and in the cities where the birds are most often shipped for sale (Metz 2007a, p. 1). The program is using the salmon-crested cockatoo as a flagship species for conservation to familiarize the people, especially the children, of Maluku Province with the image of its unique endemic parrots (IPP 2008b, p. 1). In 2007, IPP reported that almost 4,500 students have participated in the CAP program, which was showing progress (Metz 2007a, p. 1-2). A new nongovernmental organization was formed to help carry out this work (IPP 2008b, p. 2).
Other anti-poaching programs of the IPP include providing sustainable income for local villagers to reduce trapping and smuggling (IPP 2008c, p. 2). Former parrot poachers earn a living by providing the day-to-day care of rescued parrots at the Kembali Bebas Avian Center for the rescue and rehabilitation of Indonesian parrots. Villagers also are employed to collect and process the nuts of the kenari tree (Canarium spp.), which are part of the diet of larger cockatoos. The nuts are sold to parrot owners outside of Indonesia and all proceeds are used to pay workers (Metz 2007c, p. 13).
Ecotourism can provide economic benefits to local communities and lead them to value and protect species and ecosystems (Snyder et al. 2000, p. 16). The development of tourism is one of the priorities of Maluku Province. In 1981, Smiet and Siallagan (1981, p. 18) wrote that the scenic beauty and colorful wildlife of Seram would be great tourist attractions. The Proposed Manusela National Park Management Plan 1982-1987 suggested that tourist accommodations be developed in the Manusela Valley of the park (Smiet and Siallagan 1981, p. 32). However, Edwards (1993, p. 11) suggested that the irregular and difficult means of transportation and lack of infrastructure and facilities for tourists are unlikely to encourage large numbers of visitors. Despite these difficulties, in 2001, Project Bird Watch led its first eco-tour of Seram (St. Joan 2005, p. 24), followed by additional tours (IPP 2009, p. 1). These tours provide ex-trappers and other villagers income by acting as bird guides, porters, and cooks. The local people see that their birds can attract people from others parts of the world, providing money and hopefully instilling pride in Indonesian birds (Metz 2007c, p. 12). Other ecotourism has developed on a small scale. In 2008, a few Internet sites advertised or reported on bird watching tours to Seram (Bird Tour Asia 2008, pp. 1-3; Eco-Adventure in Indonesia 2008, p. 1; King Bird Tours 2007, pp. 1-6).
Summary of Factor B
Keeping pet birds, especially parrots, plays an important role in Indonesian culture, creating a massive demand for parrots internationally and domestically. By the 1980s, uncontrolled trapping of salmon-crested cockatoos for the pet bird trade was adversely impacting the species. Based on CITES records, 74,838 specimens of salmon-crested cockatoos were exported from Indonesia between 1981 and 1990, with international imports (from all exporting countries) averaging 8,393 annually. Because trade was having a detrimental effect on wild populations, the CITES countries voted to transfer the species from CITES Appendix II to CITES Appendix I, effective January 18, 1990.
An Appendix-I listing generally precludes commercial trade in wild-caught birds, but it is difficult to quantify undocumented illegal international and domestic trade. Illegal trapping and trade in wild-caught salmon-crested cockatoos continues today, with high domestic consumption in Indonesia. Hunting of parrots by people to supplement their income is relatively common on Seram. Interviews in villages suggested that perhaps as many as 4,000 salmon-crested cockatoos (approximately 6.4 percent of the population) are captured annually, with an estimated 80 percent sold within Indonesia and 20 percent put in international trade. The salmon-crested cockatoo is still sold openly in the markets of Ambon and elsewhere in Indonesia. Generally, little is known about how the domestic trade in birds in Indonesia is affecting wild populations. Little information is available on the number and age of birds being taken from the wild and when and where the birds are being trapped. In addition, it is difficult to assess the effects of trade on wild populations because the impacts from trade operate in combinations with the loss of the species' habitat.Start Printed Page 30773
Illegal trade is difficult to control because Indonesia has a vast coastline; government officials have limited resources and knowledge to deal with the illegal pet trade, have conflicts of interest, and lack a willingness to take action; and there is widespread corruption. Indonesia is a member of ASEAN-WEN and has made an effort to train some of their police, forestry, and Customs officers in methods to tackle poaching and smuggling. However, outside of a recent sting operation involving the salmon-crested cockatoo, the wildlife protection laws have not been vigorously enforced for this species.
Recent information that hunters from one small village in central Seram used air guns to kill 40 salmon-crested cockatoos for food in one year is of concern. Without additional information, however, we are unable to assess the possible impact air gun hunting may be having or will have on the survival of the salmon-crested cockatoo.
In recent years, several programs—rehabilitation and release of confiscated parrots, public awareness program, economic incentive program, and ecotourism—were established on Seram to support the conservation of the salmon-crested cockatoo. It is too soon to assess if these programs have been successful in gaining local support and reducing poaching. At this time, poaching of the salmon-crested cockatoo for the commercial pet trade and use of wild-caught salmon-crested cockatoos as pets in Indonesia continues.
In summary, although the recent use of air guns to hunt salmon-crested cockatoos for food is of concern, based on the best available information, we find that overutilization of the cockatoo for recreational, scientific, or education purposes is not a threat to the continued existence of this species. However, we find that uncontrolled, illegal domestic and international trade of salmon-crested cockatoos as pets is a threat to the continued existence of this species.
Factor C. Disease or Predation
One of the most serious diseases found in cockatoo species is beak and feather disease. All cockatoo species are likely susceptible to this disease. The disease affects wild and captive birds, with chronic infections resulting in feather loss and deformities of beak and feathers. Birds usually become infected in the nest by ingesting or inhaling virus particles. Birds either develop immunity, die within a couple of weeks, or become chronically infected. No vaccine exists to immunize populations (Cameron 2007, p. 82). In Indonesia's Kembali Bebas Rescue and Rehabilitation Center on Seram, 50 cockatoos have been screened for beak and feather disease. None of the birds was found to be positive for the virus, but a number had positive antibodies to the virus (Metz 2007b, p. 3).
Another serious disease that has been reported to infect cockatoos is proventricular dilatation disease (PDD). It is a fatal disease that poses a serious threat to domesticated and wild parrots worldwide, particularly those with very small populations (Kistler et al. 2008, p. 1; Waugh 1996, p. 112). This contagious disease causes damage to the nerves of the upper digestive tract, so that food digestion and absorption are negatively affected. The disease has a 100 percent mortality rate. In 2008, researchers discovered a genetically diverse set of novel avian bornaviruses that are thought to be the causative agents, and developed diagnostic tests, methods of treating or preventing bornavirus infection, and methods for screening for the anti-bornaviral compounds (University of California at San Francisco 2008, p. 1). We are unaware of any reports that this disease occurs in salmon-crested cockatoos in the wild.
Wild birds, especially waterfowl and shorebirds, are natural reservoirs of avian influenza. Most viral strains have low pathogenicity and cause few clinical signs in infected birds. However, strains can mutate into highly pathogenic forms, which is what happened in 1997 when highly pathogenic avian influenza H5N1 first appeared in Hong Kong (USDA et al. 2006, pp. 1-2). The H5N1 virus is mainly propagated by commercial poultry living in close quarters with humans. The role of migratory birds is less clear (Metz 2006a, p. 24). Scientists increasingly believe that at least some migratory waterfowl carry the H5N1 virus, sometimes over long distances, and introduce the virus to poultry flocks (WHO 2006, p. 2). The H5N1 virus has infected and caused death in domestic poultry, people, and some wild birds in Asia, Europe, and Africa. About half of the people infected die from the disease (FWS 2006, p. 1). As of September 10, 2008, Indonesia confirmed its 136th human case (WHO 2008, p. 26). As of December 2006, avian influenza was not present in fowl in the Maluku Province (Metz 2006b, p. 42).
There has been only one documented case of avian influenza H5N1 in parrots—a parrot held in quarantine in the United Kingdom was diagnosed with the disease. However, from 2004-2006 (Metz 2006a, pp. 24-25), fears of the avian influenza H5N1's risk to human health resulted in the culling of wild and pet birds in Asia and Europe, including the salmon-crested cockatoo. In the Philippines, 339 smuggled parrots were euthanized following confiscation. In Taiwan, 28 palm and salmon-crested cockatoos were euthanized at the airport out of fear that they might harbor the disease. In Indonesia, agriculture officials announced that all birds, including pet birds, within a given radius of chickens infected with avian influenza would be culled. However, when avian influenza struck Ragunan Zoo in Jakarta, parrots and cockatoos were not euthanized unless testing showed they had the disease (IPP 2006, p. 1).
Man probably introduced rats, mice, pigs (Sus celebensis), deer (Cervus timorensis), civet (Paradoxurus hermaphroditus), and oriental civet (Viverra tangalunga) to Seram (Smiet and Siallagan 1981, p. 8). Goats, horses, cows, and water buffalo (Bubalus bubalis) also have been introduced. Although the deer as grazers have some adverse effect on low forest brush (Ellen 1993, pp. 193, 201), we are unaware of an adverse effect from these mammals to the salmon-crested cockatoo's habitat. The cockatoo has natural predators, such as snakes and monitor lizards that raid the nest for eggs and chicks (Metz et al. 2007, p. 37).
Summary of Factor C
Disease and predation associated with salmon-crested cockatoos in the wild are not well documented. Although some serious diseases—such as beak and feather disease and PDD—occur in cockatoos in the wild, we found no information that these diseases occur in salmon-crested cockatoos in the wild. Cases of avian influenza H5N1 are continuing to occur in Indonesia; however, parrots generally are not considered to be natural reservoirs of this disease. While there is the potential for captive-held salmon-crested cockatoos to be euthanized, especially smuggled ones that have been seized at ports, the number of birds euthanized is small and not a threat to the species.
A number of introduced mammals occur on Seram, but we are unaware of any predation on the salmon-crested cockatoo from these introduced mammals. The salmon-crested cockatoo has natural predators, but we were unable to find information that these natural predators are having any significant negative impact on the Start Printed Page 30774productivity of this species. Thus, we find that neither disease nor predation is a threat to the salmon-crested cockatoo in any portion of its range now or in the foreseeable future.
Factor D. The Inadequacy of Existing Regulatory Mechanisms
As described below, Indonesia has laws and regulations in place to conserve biodiversity, manage forest, regulate trade, provide species protection, and develop and manage protected areas.
The Indonesian Government has passed legislation to control activities that have an adverse impact on the environment and to conserve biodiversity. In 1991, it drafted the Biodiversity Action Plan (BAP), which became a comprehensive framework for biodiversity conservation, advocating a wide range of policy and institutional reforms to slow the rate of biodiversity loss. In 1997, the government produced Agenda 21-Indonesia, a National Strategy for Sustainable Development. These two documents recognize a complex mix of problems, including increasing population, poor implementation of regulations, conversion of forests to agricultural lands, transmigration projects, disregard of land tenure, breakdown of traditional community management, unsustainable logging, and poaching.
The main objectives of the BAP are to slow the loss of primary forests and other habitats, expand data on Indonesia's biodiversity, and foster sustainable use of biological resources. Agenda 21-Indonesia broadly develops the BAP. For example, in situ conservation would include establishing an integrated protected area system, gaining local support for protected areas, developing sustainable means of funding for protected areas, and supporting donor activities to maximize conservation efforts (Murdoch University 2000, pp. 1-2).
The U.S. Agency for International Development (USAID) assessed the status of biodiversity in Indonesia under the Foreign Assistance Act (22 U.S.C. 2151 et seq.) and concluded that threats to biodiversity had worsened since 1998 and decentralization had led to increased exploitation of biodiversity (Rhee et al. 2004, p. xvii). Most managers at the district level are generally unaware or uncaring of biodiversity issues (Jepson et al. 2001, pp. 859-860).
The Indonesian government has laws and regulations in place to support sustainable forest management. The primary law is the Basic Forestry Law (Law No. 41). It provides for the management of forest conservation, protection, and production; defines main forest functions; and deals with forest management, planning, research, development, education, training, and enforcement (FAOLEX 2008b, p. 1; Rhee et al. 2004, chap. 2 p. 3; Law No. 41 1999, pp. 11-14). Presidential Instruction No. 4/2005 describes the duties of the different responsible government entities and addresses the eradication of illegal logging by taking action against anyone who harvests or collects timber forest without a license; receives, buys, or sells timber collected illegally; or carries, controls, or has timber without a certificate of legitimacy (FAOLEX 2009, p. 1; Indonesia 2005, pp. 1-3).
Agenda 21-Indonesia identifies the major shortcomings in the management of production forests to include current concession policies and logging practices (Murdoch University 2000, p. 1). A major threat to Indonesia's forest resources is conflict: (1) Among local communities and between local communities and concessions over management and extraction rights; and (2) between different levels of government over licensing and regulation of timber extraction and forest conversion (Rhee et al. 2004, chap. 6 p. 9). Land tenure and access in forests are contentious issues. The Indonesian government has jurisdiction over all resources, but has often ignored the land use or ownership claims of local peoples (Rhee et al. 2004, chap. 2 pp. 21-22).
In addition, the laws and regulations are frequently ignored, in part because of widespread corruption (BLI 2008k, p. 7). The Indonesian economic crisis that led to the downfall of the Suharto regime resulted in the government instituting a rapid and far-reaching decentralization that gave local government greater autonomy (Down to Earth 2000, p. 1). Decentralization resulted in confusion of roles and responsibilities, and implementation of decentralization has been slow and uncertain because of conflicting interpretation of policies and priorities and the lack of capacity or experience of local governments to manage (Rhee et al. 2004, chap. 2 p. 20).
USAID also assessed the status of forests in Indonesia under the Foreign Assistance Act and concluded that threats to forests had worsened since 1998 and decentralization had led to worse forestry practices and increased conflict over land tenure (Rhee et al. 2004, p. xvii). The responsibility for the management of forests was placed at the district level within provinces, but criteria and standards were still set by the central government. Most districts do not have the capacity for planning for sustainable development and have limited capacity to govern. Today, Indonesia is torn apart by economic and political crises, and the gap between sustainable forest management and the reality of current mismanagement is wide (Jepson et al. 2001, pp. 859-860).
In 2008, the Indonesian Government reported to the Commission on Crime Prevention and Criminal Justice on its strategic plan on forestry, outlining its priorities of fighting illegal logging, controlling forest fires, restructuring the forestry sector, rehabilitating and conserving forest resources, and decentralizing forest management. The Government said it was committed to intensifying the fight against illegal logging by implementing a forest crime case tracking system, prosecuting forest crimes, and enhancing collaboration by sharing information on forest crime and illegal timber shipments (Commission on Crime Prevention and Criminal Justice 2008, p. 4).
International Wildlife Trade
Indonesia has been a member of CITES since December 28, 1978. It has designated Management, Scientific, and Enforcement authorities to implement the treaty (CITES 2008b, p. 1) and has played an active role in CITES meetings.
The salmon-crested cockatoo is listed in Appendix I of CITES. CITES, an international treaty with 175 member nations, including Indonesia and the United States, entered into force in 1975. In the United States, CITES is implemented through the U.S. Endangered Species Act of 1973, as amended (Act). The Secretary of the Interior has delegated the Department's responsibility for CITES to the Director of the Service and established the CITES Scientific and Management Authorities to implement the treaty. Under this treaty, member countries work together to ensure that international trade in animal and plant species is not detrimental to the survival of wild populations by regulating the import, export, and reexport of CITES-listed animal and plant species (USFWS 2010, unpaginated). Although CITES reports indicate a drastic fall in international trade of salmon-crested cockatoos after the species was transferred to Appendix I in January 1999, illegal hunting and trade of this species continue today, Start Printed Page 30775with high domestic consumption within Indonesia, as discussed above under Factor B.
Species Protection and Management Plans
The salmon-crested cockatoo is on the Indonesian Government's list of protected species (Rhee et al. 2004, chap. 5 pp. 2, App. VIII) and is protected by Indonesian Law 5/1990, Conservation of Biodiversity and Ecosystems (see Conservation Status above), which establishes the basic principles and general rules for the management, conservation, and use of biological resources, natural habitats, and protected areas. Protected species may not be captured, collected, displaced, killed, destroyed, transported, or traded except for the purposes of research, science, and safeguarding the plants or animals. People that violate the law are subject to fines and punishment (Law No. 5 1990, pp. 1-44; FAOLEX 2008a, p. 1).
While laws to protect species are in place, enforcement often is severely lacking (Shepherd et al. 2004, p. 4) or difficult, given the thousands of islands that make up Indonesia (Nichols et al. 1991, p. 1) and considering that illegal activities remain socially acceptable at the local level. Thus, the law is generally disregarded and only sporadically enforced (Kinnaird 2000, p. 14). Few enforcement officers are trained in species identification, and the enforcement agency lacks capacity and incentive. Illegal trade has been reported to the Natural Resource Conservation Agency, which is responsible for enforcing the law, but that agency is “powerless” when confronted with the situation (ProFauna Indonesia 2004, p. 8). To further complicate enforcement, some bird dealers claim that members of the Department of Forest Protection and Nature Conservation are involved in the trade (Shepherd et al. 2004, p. 4) (see Factor B above for a discussion of the problems relating to stopping illegal trade in salmon-crested cockatoos).
As discussed under Factor B, protection under Indonesian law has not stopped trapping and trade of salmon-crested cockatoos. There is some evidence that the actions of Indonesian government agencies and the military are changing; however, if penalties are not enforced for illegal trade, trapping from the wild will continue (ProFauna Indonesia 2004, pp. 9-11).
In 1982, Indonesia used the best principles of conservation biology to plan a national protected area system, with the development of a national conservation plan (NCP) (Jepson et al. 2002, p. 40). Large areas were proposed as conservation areas. Subsequently, forests were also allocated for production, watershed protection, or conservation, and Indonesia endorsed the principles of sustainable forest management. However, these principles were never fully reconciled with national policy and practice (Jepson et al. 2001, p. 859). As a result, reserves generally have not been added to the proposed network of the NCP, and existing reserves have not been managed effectively (Whitten et al. 2001, p. 1). Agenda 21-Indonesia identifies problems faced in managing protected areas, including the “lack of public participation, lack of management framework, the need for regional income, insufficient funding and lack of law enforcement” (Murdoch University 2000, pp. 1-2).
In reviewing the efficacy of the protected area system of East Kalimantan Province, Indonesia, Jepson et al. (2002, pp. 31, 39-40) found that key reserves either had not been established or were degraded (i.e., moderate and widespread habitat modification or populations of key fauna significantly reduced). They concluded that turning reserve planning into practice had failed because of local-level sociopolitical realities. The ability of the Indonesian government to manage and protect reserves or to establish reserves that were proposed in the NCP in East Kalimantan, and in Indonesia as a whole, had been severely constrained by problems, including insufficient funding, workforce shortages, weak penalties, a general lack of support for conservation in society, corruption, and the aggressive use of resources by migrants.
We are unaware of any review of the efficacy of protected areas in Seram, but find that the general conclusion of the East Kalimantan study applies. Wai Bula, an area in the northeastern part of Seram (Kinnaird et al. 2003. p. 230), illustrates the inability of the Indonesian government to implement the NCP. Wai Bula, proposed as a nature reserve in 1981, was never officially designated and has a low probability of future protection (Kinnaird et al. 2003, p. 231). It has been identified as an IBA (see Important Bird Areas above) with primary lowland and lower montane forests and a current population of cockatoos (BLI 2008f, p. 1). It was proposed as a nature reserve, but 93 percent is also under logging concessions (Kinnaird et al. 2003, p. 231). Resolution of these conflicting land use designations would have a considerable impact on the amount of protected habitat available for the salmon-crested cockatoo (Kinnaird et al. 2003, p. 231).
The unique wildlife and plants of Seram are somewhat protected by Manusela National Park, an area of 2,323.2 km2 (896.8 mi2) in the center of the country, and Gunung Sahuwai Nature Reserve, an area of 122.8 km2 (47.4 mi2) on the western peninsula. Under Act No. 5 of 1990, the use of biological resources and their ecosystems in protected areas is to be sustainable, and plants and animals are to be managed with consideration of their long-term survival and maintenance of their diversity. Research, education, improvement of the species, and recreational activities are permitted, but other activities are prohibited (FAOLEX 2008a, pp. 1-2).
Although 14 percent of the forests on Seram are in protected areas, 15 percent of Manusela National Park is under logging concessions and 4.6 percent has been converted to other land uses. A road has been built through the park, which increases the risk of logging and human encroachment. Five villages of indigenous people, who mainly work as dry land farmers and hunt and collect forest products (including parrots), exist in the park. In 1980, 999 people lived within the park boundaries, and 19,102 people lived within 10 km (6 mi) of its boundaries. We are unaware of logging concessions in Gunung Sahuai Nature Reserve, and it has experienced less (3.1 percent) land conversion and human encroachment (Kinnaird et al. 2003, pp. 230-231).
The regulations and management of the protected areas are ineffective at reducing the threats of habitat destruction (see Factor A above) and poaching for the pet trade (see Factor B above). Reserve management is at the national level—the responsibility of the Directorate General of Forest Protection and Nature Conservation. Effective reserve management is hampered by a shortage of staff, expertise, and money, and the remoteness of protected areas. The recent civil unrest forced a reduction in conservation programs, with some protected areas virtually unsupervised (BLI 2008k, p. 9).
Summary of Factor D
While Indonesia has a good legal framework to manage wildlife and their habitats, implementation of its laws and regulatory mechanisms has been inadequate to reduce the threats to the salmon-crested cockatoo. As discussed under Factor A above, we found that logging and conversion of forests to agriculture and plantations are primary Start Printed Page 30776threats to the habitat of the salmon-crested cockatoo. Laws and regulations are frequently ignored, and illegal logging is considered a leading cause of forest degradation in Indonesia. The decentralization of government has led to unsustainable forestry practices, increased exploitation of resources, and increased conflict over land tenure. Current concession policies and logging practices hamper sustainable forestry. Because nearly 50 percent of Seram's forests are held under logging concessions, with more than 75 percent within the salmon-crested cockatoo's favored lowland habitat, the proper management of these logging concessions could determine the survival of this species.
The salmon-crested cockatoo is listed in Appendix I of CITES (see discussion under Conservation Status above), which requires CITES Parties to ensure controlled legal international trade. However, as discussed under Factor B above, uncontrolled illegal domestic and international trade continues to adversely impact the salmon-crested cockatoo. The species is on Indonesia's list of protected species, and the law provides prohibitions, including capture and trade, and lays out fines and punishment. However, the law is generally ignored and only sporadically enforced.
Manusela National Park and Gunung Sahuwai Nature Reserve provide some protection to the salmon-crested cockatoo. Management of these protected areas, however, is hampered by staff shortages, lack of expertise and money, and remoteness of the areas. Another Important Bird Area, Wai Bula, was proposed as a nature reserve in 1981, but was never officially designated. Resolution of its designation would increase the amount of protected habitat available for the salmon-crested cockatoo, but the delay in making such a designation reflects the inability of the Indonesian government to implement the national conservation plan.
In summary, we find that the existing regulatory mechanisms, as implemented, are inadequate to reduce or remove the current threats to the salmon-crested cockatoo. There is no information available to suggest these regulatory mechanisms will change in the foreseeable future.
Factor E. Other Natural or Manmade Factors Affecting the Continued Existence of the Species
Fires in tropical forests are becoming increasingly common (Cochrane 2003, p. 913; Kinnaird and O'Brien 1998, p. 954; Uhl & Kauffman 1990, p. 437; Woods 1989, p. 290). For example, in 1983, disastrous, large-scale El Niño wildfires occurred in the tropical forests of Borneo, although severe droughts had occurred previously without causing extensive fires. Woods (1989, p. 290) concluded that the extensive fires were the result of forests becoming more fire-prone due to logging, road building, and cultivation. He also found that potential recovery of forest structure is not good in logged forests, especially if further burning occurs. The 1997-98 El Niño fires in Indonesia devastated vast tracts of forest, especially on the islands of Sumatra and Kalimantan (islands to the far west of Seram) and Irian Jaya (a neighboring island to the east of Seram) (Kinnaird and O'Brien 1998, p. 954). The forest fires were mainly caused by poor logging practices, burning of agriculture land, and land clearing for plantations (Grimmett and Sumarauw 2000, pp. 6, 8; Kinnaird and O'Brien 1998, p. 954).
Forest fires are often part of El Niño events, which are expected to increase in number and severity due to global climate change. Using a global climate model that had successfully predicted the 1997-98 El Niño, Timmermann et al. (1999, pp. 694-696) looked at the effect of future greenhouse warming on El Niño frequency. They concluded that, if emissions of greenhouse gases continue to increase, events typical of El Niño will become more frequent and variations may become more extreme. Because more tropical forests are becoming disturbed and because the number of El Niño events is predicted to increase and be more severe, serious fires in Indonesia, including Seram and other areas of the tropics, are likely to remain a critical conservation concern (Adeney et al. 2006, p. 292).
Fires can lead to the long-term decline of the rain forest, with destruction of leaf litter and the seedling-sapling layer, increased invasion of exotic plants, increased tree mortality, and changes in the soil. Although many animals have the ability to escape direct mortality from fire, they also may be negatively affected by loss of food, shelter, and territory. For example, the number of frugivorous and omnivorous birds declined after the 1997-98 El Nino fire in Indonesia, with helmeted and rhinoceros hornbills (Buceros rhinoceros and B. vigil) declining by 50 percent in one study area (Kinnaird and O'Brien 1998, p. 955).
At the current time, high impact fires are not adversely affecting the habitat of the salmon-crested cockatoo. In 1985, Ellen (1985, p. 567) wrote that fires seldom get out of hand on Seram when land is cleared for agriculture. In addition, the 1997-98 El Niño fires in Indonesia are said to have not affected Seram (Metz 1998, p. 11). However, because devastating El Niño fires have been shown to occur more frequently in logged or disturbed forests and Seram has extensive logging planned and ongoing clearing of land for plantations and agriculture, El Niño-related fires will likely have a severe impact on Seram in the future (Kinnaird et al. 2003, p. 234).
Unlike the rest of Indonesia, which is 90 percent Muslim, the Moluccas have equal numbers of Christian and Islamic followers. Under the Suharto government, primarily Muslim transmigrants moved to Seram, and the government assigned officials, police, and military from outside the region. Rioting between Muslim and Christian citizens became an ongoing problem on Seram. In 1999 and 2001, as Indonesia plunged into a deep economic crisis, resentments erupted and thousands of people were killed (Javaman 2009, p. 1). It is unknown if the civil unrest affected the salmon-crested cockatoo, but the violence temporarily stopped development. On the other hand, many birds were sold to soldiers; thus a heavy military presence led to a rise in cockatoo trade (ProFauna Indonesia 2004, p. 9; Kinnaird 2000, p. 15).
In 1864, Wallace (1864, p. 279) reported that the salmon-crested cockatoo was considered a harmful pest in coconut palms around villages on Seram. The cockatoos gnawed through shells of young coconuts to reach the pulp and water inside.
Historically, the cockatoo was persecuted (BLI 2004, p. 2; Metz 1998, p. 10), but BLI (2008b, p. 2) reports this persecution is in the past and unlikely to be a threat in the future.
Summary of Factor E
Forest fires negatively impact birds through direct mortality or the loss of food, shelter, and territory. Research has shown that frugivorous and omnivorous birds may decline by 50 percent as a result of fires in areas of disturbed tropical rain forests. Forest fires are becoming more common in tropical rain forests, and occurring more frequently in logged or disturbed areas. As discussed under Factor A above, logging and conversion of land to agriculture and plantations is ongoing and will likely increase in the future on Seram. Approximately 75 percent (8,271 km2 (3,193 mi2)) of the lowland habitat Start Printed Page 30777favored by the salmon-crested cockatoo is under logging concession. Approximately 44 percent (6,220 km2 (2,401 mi2)) of Seram's lowland forest is slated for conversion and, by 2028, most of this land will be converted to agriculture or plantations. Therefore, we find that, even though fires are not currently adversely affecting the salmon-crested cockatoo, fires will be a threat to this species throughout all of its range in the foreseeable future due to the extensive planned logging and clearing of land for agriculture and plantations and predicted increase in number and severity of El Niño events due to global climate change.
Civil unrest is an ongoing problem on Seram, but we are unaware that it has adversely impacted the salmon-crested cockatoo other than a possible increase in sporadic illegal trade, which is discussed under Factor B above. The persecution of salmon-crested cockatoo as pests in coconut palm groves does not appear to be a problem today. Thus, we find that neither civil unrest nor persecution is a threat to the salmon-crested cockatoo in any portion of its range now or in the foreseeable future.
Status Determination for the Salmon-Crested Cockatoo
We have carefully assessed the best available scientific and commercial information regarding the past, present, and potential future threats faced by the salmon-crested cockatoo. The species is likely to become in danger of extinction within the foreseeable future throughout all of its range primarily due to extensive logging and conversion of lowland forests to agricultural lands and plantations (Factor A) and uncontrolled, illegal trapping for the domestic and international pet trade within Indonesia (Factor B). Also, existing regulatory mechanisms, as implemented, are inadequate to mitigate the current threats to the salmon-crested cockatoo (Factor D). Although El Niño forest fires are not currently adversely affecting the salmon-crested cockatoo, fires will be a threat in the foreseeable future due to the extensive planned logging and clearing of land and predicted increase in number and severity of El Niño events due to global climate change (Factor E).
The salmon-crested cockatoo is endemic to the island of Seram, with records from three small adjacent islands. Current populations are estimated at 62,400 individuals, with a decreasing population trend. The cockatoo is largely a resident of lowland rain forests, predominately between 100-600 m (328-1,968 ft), with the highest densities of birds occurring in little-disturbed forests. It requires large, mature trees for nesting.
Logging and conversion of forests to agriculture and plantations are primary threats to the habitat of the salmon-crested cockatoo in the foreseeable future. By 2001, about 20 percent of the original forest cover had been cleared. Nearly 50 percent of the island's forests are held under logging concessions, of which 75 percent are held within lowland forests, prime salmon-crested cockatoo habitat. Unsustainable logging practices destroy the forest canopy and dramatically reduce habitat available for cockatoos, especially if large nest trees and strangling figs are harvested. Between 1980 and 1990, an estimated 1,200 km2 (463 mi2) of the salmon-crested cockatoo's habitat was lost. In addition, about 44 percent of lowland forest is designated as conversion forest. Researchers predict that by 2028, up to 50 percent of the current salmon-crested cockatoo population (at least 31,000 cockatoos) may be lost as a result of conversion of forests to agriculture and plantations. Although about 14 percent of the forests are within protected areas, logging concessions are held in 15 percent of these areas, and small-scale illegal logging and human encroachment also occur there. By 2028, extensive logging and conversion of lowland forests to agriculture and plantations, combined with transmigratory human resettlement, oil exploration, and infrastructure development, are likely to destroy much of the salmon-crested cockatoo's habitat.
Illegal trapping of the salmon-crested cockatoo for the pet trade is widespread. Pet birds are an important part of Indonesian culture, with large numbers of wild-caught parrots traded domestically and internationally. In the late 1970s, the salmon-crested cockatoo was extensively trapped for the pet bird trade. By the 1980s, the pet bird trade was adversely impacting the species. Between 1981 and 1990, 74,838 specimens of salmon-crested cockatoos were exported from Indonesia, and international imports (from all exporting countries) averaged 8,393 annually. Although the salmon-crested cockatoo was transferred to Appendix I of CITES, trappers reportedly remain active, and wild-caught birds are openly sold in domestic markets within Indonesia. Interviews in villages suggest that perhaps as many as 4,000 birds, or 6.4 percent of the current estimated population, are still being captured annually, with 80 percent of these 4,000 birds illegally traded domestically and 20 percent illegally exported from Indonesia. Ending illegal trade is hampered by Indonesia's large coastline, officials with limited resources and knowledge, and corruption. The continuing illegal trade of the salmon-crested cockatoo is a threat to the survival of the species in the foreseeable future.
Indonesia has a good legal framework to manage wildlife and their habitats, but implementation of its laws and regulatory mechanisms has been inadequate to address the threats to the salmon-crested cockatoo. Logging laws and policies are frequently ignored and rarely enforced, and illegal logging is rampant, even occurring in national parks and nature reserves. Current concession policies and logging practices hamper sustainable forestry. The salmon-crested cockatoo is a protected species in Indonesia, and the law prohibits capture and trade and also provides for fines and punishment. Again, the law is generally ignored and only sporadically enforced. Illegal bird trade is socially acceptable, making it difficult to enforce laws. Public awareness programs, economic incentive programs, and ecotourism are in their infancy, and it is too early to tell if they are helping to control poaching on the island. The illegal trade of the salmon-crested cockatoo for the domestic trade, and to a smaller extent international trade, continues to occur.
Fires are becoming more common in tropical rain forests where logging, road building, and clearing of land for agriculture occur. Fires can lead to the long-term decline of the rain forest, and many animals may be negatively affected by loss of food, shelter, and territory. Currently, high impact fires are not adversely affecting the habitat of the salmon-crested cockatoo, but due to future planned extensive logging and clearing of land for agriculture and plantations and a predicted increase in the number and severity of El Niño events, fires will be a threat to this species in the foreseeable future.
Section 3 of the Act defines an “endangered species” as “any species which is in danger of extinction throughout all or a significant portion of its range” and a “threatened species” as “any species which is likely to become an endangered species within the foreseeable future throughout all or a significant portion of its range.” The salmon-crested cockatoo population estimate is approximately 62,400, and the threats of habitat loss and trade are not at a level to consider the species to be in danger of extinction at this time. However, based on the analysis of the five factors discussed above, we determine that the salmon-crested cockatoo is likely to become an endangered species within the Start Printed Page 30778foreseeable future throughout all of its range.
Significant Portion of the Range Analysis
Having determined that the salmon-crested cockatoo meets the definition of threatened under the Act, we considered whether there is a significant portion of the range of the species that meets the definition of endangered. The Act defines an endangered species as one “in danger of extinction throughout all or a significant portion of its range,” and a threatened species as one “likely to become an endangered species within the foreseeable future throughout all or a significant portion of its range.” For purposes of this finding, a significant portion of a species' range is an area that is important to the conservation of the species because it contributes meaningfully to the representation, resiliency, or redundancy of the species. The contribution must be at a level such that its loss would result in a decrease in the ability to conserve the species.
The salmon-crested cockatoo is endemic to Seram and the three small, neighboring Indonesian islands of Ambon, Haruku, and Saparua. Very limited information is available on the status of the species on Ambon, Haruku, and Saparua. Whether this species is native or introduced to Ambon is uncertain, and a very small number of cockatoos (sightings of six to eight birds) are thought to occur in remaining natural forests in the more remote regions of the island. The status of the salmon-crested cockatoo is unknown on Haruku and Saparua. For Haruku, there is one unspecified locality and observation reported in 1934; for Saparua, there is one specimen recorded for 1923. Even less information is available on the habitat and the threats to the species on these islands. The relatively larger population size in high-quality habitat on Seram suggests that this area may be a significant portion of the range. The salmon-crested cockatoo primarily occurs in lowland forests throughout the island of Seram; its current population is estimated to be approximately 62,400 birds; and the species persists in high densities in primary and disturbed primary forests on Seram. After a review of the best scientific and commercial data, we determined that there is no significant portion of the range in which the salmon-crested cockatoo is currently in danger of extinction.
We have carefully assessed the best scientific and commercial information available regarding the past, present, and future threats to this species. Under our five-factor analysis above, we determined that the species is threatened by logging and conversion of forests to agriculture and plantations, illegal trapping for the pet trade, inadequacy of regulatory mechanisms, and fires resulting from El Niño events throughout its entire range. The species is threatened by each of these factors uniformly throughout Seram. There is no significant portion of the range in which the salmon-crested cockatoo is currently in danger of extinction. There is no information to suggest that the species is currently in danger of extinction because of the reasonably large population size of the species on the island and its occurrence throughout the lowland forests of Seram in primary and disturbed primary forest habitat, as well as secondary forest habitat. Although we do not believe that the species is currently endangered, we believe it is likely that the salmon-crested cockatoo will become endangered throughout its range in the foreseeable future. Thus, we list the salmon-crested cockatoo as a threatened species throughout all of its range under the Act.
Available Conservation Measures
Conservation measures provided to species listed as endangered or threatened under the Act include recognition, requirements for Federal protection, and prohibitions against certain practices. Recognition through listing results in public awareness, and encourages and results in conservation actions by Federal and State governments, private agencies and groups, and individuals.
Section 7(a) of the Act, as amended, and as implemented by regulations at 50 CFR part 402, requires Federal agencies to evaluate their actions within the United States or on the high seas with respect to any species that is proposed or listed as endangered or threatened and with respect to its critical habitat, if any is being designated. However, given that the salmon-crested cockatoo is not native to the United States, we are not designating critical habitat for this species under section 4 of the Act.
Section 8(a) of the Act authorizes the provision of limited financial assistance for the development and management of programs that the Secretary of the Interior determines to be necessary or useful for the conservation of endangered and threatened species in foreign countries. Sections 8(b) and 8(c) of the Act authorize the Secretary to encourage conservation programs for foreign endangered species and to provide assistance for such programs in the form of personnel and the training of personnel.
The Act and its implementing regulations set forth a series of general prohibitions and exceptions that apply to all endangered and threatened wildlife. These prohibitions, at 50 CFR 17.21 and 17.31, in part, make it illegal for any person subject to the jurisdiction of the United States to “take” (take includes harass, harm, pursue, hunt, shoot, wound, kill, trap, capture, collect, or to attempt any of these) within the United States or upon the high seas; import or export; deliver, receive, carry, transport, or ship in interstate or foreign commerce in the course of commercial activity; or sell or offer for sale in interstate or foreign commerce any endangered wildlife species. It also is illegal to possess, sell, deliver, carry, transport, or ship any such wildlife that has been taken in violation of the Act. Certain exceptions apply to agents of the Service and State conservation agencies.
Permits may be issued to carry out otherwise prohibited activities involving endangered and threatened wildlife species under certain circumstances. Regulations governing permits are codified at 50 CFR 17.22 for endangered species and 17.32 for threatened species. For endangered wildlife, a permit may be issued for scientific purposes, to enhance the propagation or survival of the species, and for incidental take in connection with otherwise lawful activities. For threatened species, a permit may be issued for the same activities, as well as zoological exhibition, education, and special purposes consistent with the Act.
Section 4(d) of the Act states that the Secretary of the Interior (Secretary) may, by regulation, extend to threatened species prohibitions provided for endangered species under section 9. Our implementing regulations for threatened wildlife (50 CFR 17.31) incorporate the section 9 prohibitions for endangered wildlife, except when a special rule is promulgated. For threatened species, section 4(d) of the Act gives the Secretary discretion to specify the prohibitions and any exceptions to those prohibitions that are appropriate for the species, provided that those prohibitions and exceptions are necessary and advisable to provide for the conservation of the species. A special rule allows us to include provisions that are tailored to the specific conservation needs of the threatened species and which may be more or less restrictive than the general provisions at 50 CFR 17.31.Start Printed Page 30779
Under the special rule, all prohibitions and provisions of 50 CFR 17.31 and 17.32 apply to the salmon-crested cockatoo, except that import and export of certain salmon-crested cockatoos into and from the United States and interstate commerce are allowed without a permit under the Act, as explained below.
Import and Export
We assessed the conservation needs of the salmon-crested cockatoo in light of the broad protections provided to the species under CITES and the WBCA. The salmon-crested cockatoo is listed as Appendix I under CITES, a treaty which contributes to the conservation of this species by ensuring that trade in specimens of the species is not detrimental to its survival and is not for commercial purposes (see Conservation Status). The purpose of the WBCA is to promote the conservation of exotic birds and to ensure that imports of exotic birds into the United States does not harm them (see Conservation Status).
International trade of the salmon-crested cockatoo has been drastically reduced since the listing of the species in Appendix I of CITES and the protection of the species under the WBCA. A review of the CITES data shows that in the 19 years between 1991 and 2009, 334 live salmon-crested cockatoos were imported into the United States. Many of these birds are personal pets that owners took with them when traveling from and returning to the United States. None of these birds were imported from Indonesia. The best available commercial data indicate that the current threat to the salmon-crested cockatoo stems from illegal trade in the domestic and international markets of Indonesia and surrounding countries. Thus, the general prohibitions on import and export contained in 50 CFR 17.31, which only extend within the jurisdiction of the United States, would not regulate such activities. Thus, we find that the prohibitions and authorizations contained within this special rule provide all the necessary and advisable conservation measures that are needed for this species.
The special rule applies to all commercial and noncommercial international shipments of live salmon-crested cockatoos and parts and products, including the import and export of personal pets and research samples. In most instances, the special rule adopts the existing conservation regulatory requirements of CITES and the WBCA as the appropriate regulatory provisions for the import and export of certain captive salmon-crested cockatoos. The import and export of birds into and from the United States, taken from the wild on or after January 18, 1990; conducting an activity that could take or incidentally take salmon-crested cockatoos; and foreign commerce will need to meet the requirements of 50 CFR 17.31 and 17.32, including obtaining a permit under the Act. However, the special rule allows a person to import or export either: (1) A specimen held in captivity prior to January 18, 1990 (the date the species was transferred to CITES Appendix I), even if taken from the wild prior to that date; or (2) a captive-bred specimen, without a permit issued under the Act, provided the export is authorized under CITES and the import is authorized under CITES and the WBCA. If the specimen was taken from the wild and held in captivity prior to January 18, 1990, the importer or exporter will need to provide documentation to support that status, such as a copy of the original CITES permit indicating when the bird was removed from the wild or museum specimen reports. For captive-bred birds, the importer would need to provide either a valid CITES export/re-export document issued by a foreign Management Authority that indicates that the specimen was captive-bred by using a source code on the face of the permit of either “C”, “D” or “F”. For exporters of captive-bred birds, a signed and dated statement from the breeder of the bird, along with documentation on the source of their breeding stock, would document the captive-bred status of U.S. birds.
The special rule applies to birds captive-bred in the United States and abroad. The terms “captive-bred” and “captivity” used in this special rule are defined in the regulations at 50 CFR 17.3 and refer to wildlife produced in a controlled environment that is intensively manipulated by man, from parents that mated or otherwise transferred gametes in captivity. Although the special rule requires a permit under the Act to “take” (harm and harass) a salmon-crested cockatoo, “take” does not include generally accepted animal husbandry practices, breeding procedures, or provisions of veterinary care for confining, tranquilizing, or anesthetizing, when such practices, procedures, or provisions are not likely to result in injury to the wildlife when applied in captive wildlife.
Although we do not have current data, we believe there are a large number of salmon-crested cockatoos in the United States. Current ISIS (International Species Information System) information shows 123 salmon-crested cockatoos are held in U.S. zoos (ISIS 2008, p. 4). This number is an underestimate as some zoos do not enter data into the ISIS database. In addition, CITES annual report data shows that 58,484 live salmon-crested cockatoos were imported into the United States between 1981 and 1989, before the species was added to CITES Appendix I (UNEP-WCMC 2009b, p. 2). We believe that a number of these birds are still held in captivity in the United States. In 1990 and 1991, surveys of captive breeding by U.S. aviculturists showed 820 and 625 salmon-crested cockatoos were held by 239 and 194 survey respondents, respectively (Allen and Johnson 1991, p. 17; Johnson 1992, p. 46). We have no information to suggest that interstate commerce activities are associated with threats to the salmon-crested cockatoo in the wild or will negatively affect any efforts aimed at the recovery of wild populations of the species. Furthermore, allowing interstate commerce of birds captive-bred and reared in the United States will preclude the U.S. demand for salmon-crested cockatoos obtained from international markets, which would otherwise contribute to the illegal capture and trade of wild birds. Therefore, because interstate commerce within the United States has not been found to threaten the salmon-crested cockatoo, the species is otherwise protected in the course of interstate commercial activities under the incidental take provisions contained in 50 CFR 17.31, and international trade of this species for primarily commercial purposes is prohibited under CITES, we find this special rule contains all the prohibitions and authorizations necessary and advisable for the conservation of the salmon-crested cockatoo.
Under the special rule, a person may deliver, receive, carry, transport, ship, sell, offer to sell, purchase, or offer to purchase a salmon-crested cockatoo in interstate commerce without a permit under the Act. At the same time, the prohibitions on take under 50 CFR 17.31 would apply under this special rule and any interstate commerce activities that could incidentally take cockatoos would require a permit under 50 CFR 17.32.
National Environmental Policy Act (NEPA)
We have determined that environmental assessments and environmental impact statements, as defined under the authority of the National Environmental Policy Act of Start Printed Page 307801969 (42 U.S.C. 4321 et seq.), need not be prepared in connection with regulations adopted under section 4(a) of the Act. We published a notice outlining our reasons for this determination in the Federal Register on October 25, 1983 (48 FR 49244).
A complete list of all references cited in this final rule is available on the Internet at http://www.regulations.gov or upon request from the Endangered Species Program, U.S. Fish and Wildlife Service (see the FOR FURTHER INFORMATION CONTACT section).
The primary authors of this final rule are the staff members of the Branch of Foreign Species, Endangered Species Program, U.S. Fish and Wildlife Service, 4401 N. Fairfax Drive, Arlington, VA 22203.Start List of Subjects
List of Subjects in 50 CFR Part 17
- Endangered and threatened species
- Reporting and recordkeeping requirements
Accordingly, we amend part 17, subchapter B of chapter I, title 50 of the Code of Federal Regulations, as follows:Start Part
PART 17—[AMENDED]End Part Start Amendment Part
1. The authority citation for part 17 continues to read as follows:End Amendment Part Start Amendment Part
2. Amend § 17.11(h) by adding new entry for “Cockatoo, salmon-crested” in alphabetical order under BIRDS to the List of Endangered and Threatened Wildlife, as follows:End Amendment Part
(h) * * *
|Species||Historic range||Vertebrate population where endangered or threatened||Status||When listed||Critical habitat||Special rules|
|Common name||Scientific name|
|* * * * * * *|
|* * * * * * *|
|Cockatoo, salmon-crested||Cacatua moluccensis||Seram, Haruku, Saparua, and Ambon, Indonesia||Entire||T||779||NA||17.41(c)|
|* * * * * * *|
3. Amend § 17.41 by adding paragraph (c) to read as follows:End Amendment Part
(c) Salmon-crested cockatoo (Cacatua moluccensis). (1) Except as noted in paragraphs (c)(2) and (c)(3) of this section, all prohibitions and provisions of §§ 17.31 and 17.32 of this part apply to the salmon-crested cockatoo.
(2) Import and export. You may import or export a specimen without a permit issued under section 17.32 of this part only when the provisions of parts 13, 14, 15, and 23 of this chapter have been met and you meet the following requirements:
(i) Captive-bred specimens: The source code on the Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES) document accompanying the specimen must be “F” (captive-bred), “C” (bred in captivity), or “D” (bred in captivity for commercial purposes)(see 50 CFR 23.24); or
(ii) Specimens held in captivity prior to January 18, 1990: You must provide documentation to demonstrate that the specimen was held in captivity prior to January 18, 1990. Such documentation may include copies of receipts, accession or veterinary records, CITES documents, or wildlife declaration forms, which must be dated prior to January 18, 1990.
(3) Interstate commerce. Except where use after import is restricted under § 23.55 of this chapter, you may deliver, receive, carry, transport, ship, sell, offer to sell, purchase, or offer to purchase in interstate commerce a live salmon-crested cockatoo.
Dated: May 9, 2011.
Acting Director, U.S. Fish and Wildlife Service.
[FR Doc. 2011-12928 Filed 5-25-11; 8:45 am]
BILLING CODE 4310-55-P