Endangered and Threatened Wildlife and Plants; Proposed Reclassification of Certain Vicuna Populations From Endangered to Threatened and a Proposed Special Rule

Federal RegisterSep 8, 1999

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DEPARTMENT OF THE INTERIOR

Fish and Wildlife Service

50 CFR Part 17

RIN 1018-AE04

Endangered and Threatened Wildlife and Plants; Proposed

Reclassification of Certain Vicuna Populations From Endangered to

Threatened and a Proposed Special Rule

AGENCY: Fish and Wildlife Service, Interior.

ACTION: Proposed rule.

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SUMMARY: The U.S. Fish and Wildlife Service (Service) proposes to

reclassify vicuna (Vicugna vicugna) populations of Argentina, Bolivia,

Chile and Peru from endangered to threatened under the U.S. Endangered

Species Act (Act or ESA). The recently re-introduced population of

Ecuador, treated as a distinct population segment under the Act in

accordance with the Service's Policy on Distinct Vertebrate Population

Segments (61 FR 4722), will remain listed as endangered. The Service

also proposes to establish a special rule (under Section 4(d) of the

Act) allowing the importation into the United States of wool and legal

vicuna products produced with wool from vicuna populations listed both

as threatened under the Act and in Appendix II of the Convention on

International Trade in Endangered Species of Wild Fauna and Flora

(CITES), except that the Appendix II semi-captive populations of

Catamarca, Jujuy, La Rioja, Salta, and San Juan Provinces in Argentina

are specifically excluded from the special rule until such time as

their conservation benefit for wild vicuna populations has been

demonstrated adequately. It is proposed that importation into the

United States of wool and legal vicuna products made from wool that

originated from threatened and approved Appendix II populations will

require valid CITES export permits from the country of origin and also

the country of re-export, when applicable. Should the conservation or

management status of threatened vicuna populations change in one or

more range countries, the potential would remain to repeal the special

rule or reclassify the population as endangered, should that become

necessary for the conservation of the vicuna. The Service invites

information and comments on this proposed rule. The analysis of the

information and comments received could lead to a final decision that

would differ substantially from this proposal.

DATES: Comments must be received by December 7, 1999. Public hearing

requests must be received by October 25, 1999.

ADDRESSES: Comments and relevant information concerning this proposal

should be sent to the Chief, Office of Scientific Authority; mail stop:

Arlington Square, room 750, U.S. Fish and Wildlife Service; Washington,

DC 20240, or via E-mail to: [email protected]. Comments and materials

received will be available for public inspection by appointment, from 8

a.m. to 4 p.m., Monday through Friday, in Room 750, 4401 North Fairfax

Drive, Arlington, Virginia 22203.

FOR FURTHER INFORMATION CONTACT: Dr. Susan S. Lieberman, Chief, Office

of Scientific Authority, at the above address, or by phone (703-358-

1708), fax (703-358-2276), or E-mail ([email protected]).

SUPPLEMENTARY INFORMATION:

Background

The vicuna (Vicugna vicugna) was listed as endangered under the

U.S. Endangered Species Act on June 2, 1970. Among other things, the

effect of that listing was the prohibition of U.S. interstate or

international commerce in vicuna products. All populations of the

vicuna were included in Appendix I of the Convention on International

Trade in Endangered Species of Wild Fauna and Flora (CITES) on July 1,

1975 (the date of entry into force of the CITES Convention), which

thereby prohibited all primarily commercial, international trade in

vicuna products. Certain populations of vicuna in Chile and Peru were

subsequently transferred to CITES Appendix II at the sixth meeting of

the CITES Conference of the Parties (COP6) in 1987. The remaining

vicuna populations in Peru were transferred to Appendix II in 1994 at

CITES COP9, and certain populations in Argentina and Bolivia were

transferred to Appendix II in 1997 at CITES COP10. These transfers to

Appendix II, reflecting improved conservation status for specified

vicuna populations, allow the international trade under carefully

controlled conditions, of products manufactured from vicuna wool. This

international trade, however, is still excluded from the United States,

because of the species' listing under the Endangered Species Act. The

United States supported the CITES transfers of the populations to

Appendix II, based on the information received at the aforementioned

meetings of the Conference of the Parties, where the CITES Parties

voted to adopt the proposed transfers to Appendix II. The information

in the relevant CITES listing proposals is available on request from

the Office of Scientific Authority (see ADDRESSES Section).

We received a petition on October 5, 1995, from the President of

the International Vicuna Consortium, requesting that the vicuna be

removed from the U.S. list of endangered and threatened wildlife, or

reclassified with a special rule that would allow for a commercial

trade that would benefit the conservation of the species. The

petitioners cited the following as reasons for the requested ACTION:

(1) Improved management of vicuna populations, (2) improved enforcement

and trade controls, and (3) recognition that regulated commerce could

be beneficial to both rural communities that share landscapes with

vicunas and the vicunas themselves. The petitioners provided limited

supportive documentation.

Our 90-day finding on whether the petition presents substantial

scientific data is subsumed within this proposed rule, which finds

that: (1) Reclassification of the vicuna from endangered to threatened

is warranted for all range countries except Ecuador; and (2) that a

special rule (also referred to as a 4(d) rule) is warranted for all

Appendix II populations, with the exception of the Appendix II semi-

captive populations of Catamarca, Jujuy, La Rioja, Salta, and San Juan

Provinces

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in Argentina, which are specifically excluded until such time as their

conservation benefit for wild vicuna has been demonstrated adequately.

We base this finding and the proposed rule on information provided

in the submissions of the petitioner, other documents including those

submitted in support of the aforementioned CITES listing proposals, and

the Service's status review for the vicuna, which included interviews

with knowledgeable personnel from the vicuna range states, responses to

questions asked of each range country, and a 1997 on-site assessment of

vicuna populations and management in Argentina, Bolivia, Chile and Peru

by a contractor working for the National Fish and Wildlife Foundation

(Dr. Henry L. Short, Amherst, Massachusetts). All personal

communications and responses to questions asked of range countries

cited in the text were received by Dr. Short, unless otherwise noted

(see References Cited Section). The Service contracted with the

National Fish and Wildlife Foundation in 1997 to evaluate the

conservation and management status of vicuna populations, and to make

recommendations about the species' status, through a fact-finding

mission to vicuna range countries.

The vicuna produces a wool that is of very fine texture (about 12

microns in diameter) that can be woven into luxury garments. Raw wool

from vicuna has been legally auctioned at $500 per kg ($200 per lb) and

an average vicuna fleece provides about 0.2 kg (0.5 lbs) of fiber.

Individual vicuna in the high Andean plateaus of South America thus

have a fleece that is worth many times that of a sheep and several

times that of other species in the family Camelidae, such as alpacas

and llamas. This high value, in a resource-poor area, can represent

both a threat to the species and an opportunity if the species is

managed sustainably. The threat comes from illegal hunting if

protection and incentives for management are poor; the opportunity

exists if proceeds from the sale of vicuna wool from live-shorn animals

are substantially used to enhance the status of native people in the

Andean uplands and to encourage them to conserve and protect vicuna.

Summary of Factors Affecting the Species

Section 4(a)(1) of the Act and regulations implementing the listing

provisions of the Act (50 CFR part 424) set forth the procedures for

adding species to, changing the status of any listed species, or

deleting species from the list of endangered and threatened wildlife. A

species shall be listed or reclassified if the Secretary determines, on

the basis of the best scientific and commercial data available after

conducting a review of the species' status, that the species is

endangered or threatened because of any one or a combination of the

following factors: (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 human-made

factors affecting its continued existence.

We base this proposed rule on an assessment of the five listing

factors within the Act. The assessment considers the present biological

status of the vicuna within the range countries of Argentina, Bolivia,

Chile and Peru. No assessment of the status of the species is made for

the small population that has recently been reintroduced into Ecuador.

That is a protected population, that will not be exploited in the

foreseeable future. We do not propose to change that population's

endangered classification under the Act.

Some scientists recognize two subspecies of vicuna--V. v. mensalis

in the northern portion of the range and V. v. vicugna to the south.

These are putative subspecies in that they have been described on the

basis of slight differences in size and color, and the lack of a

prominent chest fringe in V. v. vicugna (Canedi and Pasini 1996),

rather than on distinct, measured genetic differences between the two.

Because the distribution of the vicuna is more or less continuous from

north to south within its range, it is possible that these two

subspecies simply represent the endpoints of a continuum of physical

and genetic variation within the species from north to south. As a

consequence, it would be very difficult to draw a definite boundary

between the two subspecies for purposes of management or listing under

the Act. Therefore, the subspecies are not differentiated in this rule

and the term vicuna, used herein, refers to populations of both

putative subspecies throughout their total range.

(A) The Present or Threatened Destruction, Modification, or Curtailment

of Its Habitat or Range

Approximately 190,000 vicuna are estimated to occur at varying

densities on approximately 20,500,000 ha of Andean highlands extending

in a rather narrow strip from central Peru through Bolivia, and into

northwest Argentina (between 8-30 degrees South latitude). The

historical range of the vicuna may have been twice the present

distributional area. A small, disjunct, recently-reintroduced

population also occurs in Ecuador.

Vicuna habitats occur in both the Altoandina and Puna Ecoregions.

The Altoandina Ecoregion comprises high Andean foothills, escarpments

and outcroppings and the Puna Ecoregion represents areas of high plains

or tablelands between mountain ranges. The habitats vary climatically

on both attitudinal and latitudinal scales but are generally arid and

cold, resulting in limited vegetation cover. The habitat of the vicuna

in the high Andean plateau region varies from 3,200 to 4,800 m above

sea level. This highland habitat has been somewhat degraded by humans

and their domesticated livestock, but still represents an extensive

habitat for vicuna. The low average density of 1 vicuna per 103 ha

reflects the limited carrying capacity of the high Andean habitats as

well as the fact that many vicuna habitats are understocked. National

Reserves, National Parks, Protected Areas, or Provincial Reserves where

vicuna are protected are scattered throughout vicuna habitat in each of

the four countries considered in this proposed rule.

Argentina

Vicuna distribution in Argentina includes portions of the

northwestern provinces of Jujuy, Salta, Catamarca, La Rioja, and San

Juan. Vicuna habitats in the Puna and Altoandina Ecoregions of

Argentina cover a surface area of about 10,000,000 ha (Canedi 1997,

pers. comm.). The area of available habitat has been reduced since the

arrival of Europeans in South America, because the species is no longer

present in the Patagonian regions of Argentina.

Vicuna habitat in Argentina is bounded to the west by the volcanic

chain of the Andean Cordillera in Chile, in the east by the eastern

Cordillera and the Sierra Pampeanas mountains, in the north by

contiguous vicuna habitat in Bolivia, and in the south, vicuna habitat

extends into the Province of San Juan. The general area is

characterized by blocks of uplifted mountains surrounding extensive

valleys featuring alkaline or saline flats and a rolling topography.

Aridity is a common and constant feature of the Puna. Many water

courses are temporary but there are occasional areas of damp ground

where surface water and green vegetation in the form of rushes, grasses

and a variety of succulent plants occur. Much of the thin vegetation

cover over most of the Puna consists of grasses and xerophilous half-

shrubs (Comision Regional de la Vicuna, 1994).

[[Page 48745]]

Temperatures are cold and frost can occur each day of the year. The

carrying capacity of the humid Puna may be as much as two vicuna per ha

but in the drier Puna habitats the carrying capacity may only be one

vicuna per 30 ha.

The Provinces of Jujuy, Salta, Catamarca, La Rioja, and San Juan

have created reserves and other protected areas for vicuna. In Jujuy

Province, Los Pozuelos Reserve was created in 1980 and consists of

308,000 ha. About 15,000 ha of this Reserve have been incorporated into

the UNESCO Man and Biosphere program as a natural area of international

significance. The vicuna population in the Reserve in 1997 was

estimated to be 2,750 (CITES 1997a). The Olaroz-Cauchari Flora and

Wildlife Reserve was created in 1981 to enhance vicuna populations and

consists of 543,300 ha. The vicuna population in the Reserve in 1994

was estimated to be 6,500 and growing (CITES 1997a). Other areas where

vicuna are protected in Jujuy Province include Vilama (97,000 ha),

Santa Victoria (54,600 ha), Palca de Aparzo (55,800 ha), Caballo Muerte

(18,500 ha), Casa Colorado (31,000 ha), Abra de Zenta (69,000 ha) and

Serranias del Chani (158,900 ha) (CITES 1997a; V. Lichtschein,

Management Authority of Argentina, pers. comm. with K. Johnson, Office

of Scientific Authority (OSA), 1999). These areas are not listed in the

WCMC Protected Areas Database, so we are unclear as to their actual

protective status (i.e., whether they are national, provincial, local

or private protected areas). The high altitude experimental station

(Campo Experimental de Altura or CEA) is located at Abra Pampa in Jujuy

Province. This experimental station of 3,000 ha is dedicated to the

development of appropriate management procedures to enhance fiber

production of vicuna, assure the survival of the species, and to

enhance the economic well-being of certain Puna ranchers. The human

population is very low throughout the Reserves and protected areas of

the Province.

In Salta Province, the Los Andes Wildlife Reserve of 1,440,000 ha

was created in 1980. The rigorous climate restricts the human

population to very low densities. Agriculture does not exist in this

area and the ranching of cattle, sheep, goats and llamas is

rudimentary. Although the carrying capacity for vicuna in the Reserve

is estimated to be one individual per 30 ha, a partial census in 1993

counted only 2,000 vicuna (CITES 1997a). In Catamarca Province, the

Laguna Blanca Wildlife Reserve was created in 1979 and enlarged in 1982

to 973,270 ha at which time it became recognized by the UNESCO Man and

Biosphere program as a natural area of international significance. The

human population is very sparse and scattered in the general area of

the Reserve. The 1993 vicuna population in Laguna Blanca Reserve was

estimated to be 3,505 (CITES 1997a). In La Rioja Province, the Laguna

Brava Reserve for Vicunas and the Protection of Ecosystems was created

in 1980 and consists of 405,000 ha. Human habitations do not exist in

the Reserve, which is contiguous with the San Guillermo Faunal Reserve

in San Juan Province. The 1996 vicuna population in the Reserve was

estimated to be 2,187 (CITES 1997a). San Guillermo Faunal Reserve was

created in 1972 and consists of 880,260 ha. In 1982 it became part of

the UNESCO Man and Biosphere program as a natural area of international

significance. This was the first Provincial Reserve dedicated primarily

to the protection of the vicuna. This area is devoid of human and

domestic animal populations. Although the area has a carrying capacity

estimated to be one vicuna per 7 ha of habitat, the 1992 vicuna

population in the Reserve was estimated to be only 7,100 (CITES 1997a).

We have virtually no quantitative information on the extent or

condition of vicuna habitats outside protected areas in Argentina.

Anecdotal information suggests that overgrazing by domestic livestock

(leading to soil compaction and desertification) and direct competition

for forage with domestic livestock may be important factors limiting

the growth of vicuna populations outside protected areas (CITES 1997a).

Other information indicates that some competition with domestic

herbivores occurs in the arid Puna where precipitation is <300 mm per

year but that competition is not as much of a problem in the humid Puna

where precipitation may exceed 500 mm per year. A program to combat

desertification has apparently been initiated in Jujuy Province (CITES

1997a).

The limited quantitative information presently available to us

indicates that vicuna populations throughout Argentina are not

endangered by the present or threatened destruction, modification, or

curtailment of habitat or range. However, they remain threatened by

this factor (especially overgrazing and direct competition with

domestic livestock) throughout Argentina. Through this proposed rule,

we seek additional, quantitative information on the status of vicuna

habitats throughout Argentina. We especially seek detailed information

on land use restrictions (for example, prohibitions on the grazing of

domestic livestock) and protective measures (for example, antipoaching

efforts) within protected areas, and on efforts to manage habitat

outside protected areas (including programs to combat desertification

and to reduce competition with domestic livestock).

Bolivia

Vicuna occur in western and southwestern Bolivia in the Departments

of La Paz, Oruro, Potosi, and Cochabamba (CITES 1997b). They have also

been reported from the Department of Tarija, but the reports have not

been confirmed (CITES 1997b). It has been suggested (DNCB 1997, pers.

comm.) that vicuna may once have ranged over 13,000,000 to 16,700,000

ha in the Puna and high plateau region of the Bolivian Andes, before

colonization by the Spaniards.

The Bolivian government has established Vicuna Conservation Units

(VCU) for administrative and management purposes (CNVB 1996). Eight

VCUs were originally established by the Instituto Nacional de Fomento

Lanero (INFOL 1985); a ninth unit was subsequently added as a result of

the National Vicuna Census of 1996 (CNVB 1996). These nine VCUs

encompass all of the vicuna's geographic range within Bolivia. The

National Vicuna Census of 1996 recorded vicuna populations in 76

``registered census areas'' totaling 3,428,356 ha within the nine VCUs.

These registered census areas are distributed throughout the Bolivian

highlands at an elevation range between 3,600 and 4,800 m. Thirty of

these registered census areas did not have any vicuna in the previous

national census (1986), indicating a significant increase in the

vicuna's distribution within Bolivia over a 10-year period. Sixty-nine

percent of the vicuna counted in 1996 (23,393 of 33,844) occurred in

the Conservation Units of Lipez-Chichas, Mauri-Desaguadero and Ulla

Ulla.

Vicuna are found in a number of protected areas in Bolivia. Within

the National System of Protected Areas (Sistema Nacional de Areas

Protegidas, or SNAP), vicuna occur in the Ulla Ulla National Fauna

Reserve (150,000), the Eduardo Avaroa National Andean Fauna Reserve

(714,000 ha), and Cerro Sajama National Park (100,230 ha) (information

from WCMC Protected Areas Database 1999). Other protected areas with

vicuna are the Huancaroma Vicuna Reserve (140,429 ha), Huancaroma

Wildlife Refuge (11,000 ha), Llica National Park (97,500 ha), Yura

National Fauna Reserve (96,853 ha), Altamachi Vicuna Reserve (100,000

ha), and the Incakasani-Altamachi Andean Fauna Reserve (23,000 ha)

[[Page 48746]]

(information from WCMC Protected Areas Database 1999).

The area where vicuna are presently found in Bolivia is expanding,

but will likely never equal the former distribution range because of

habitat changes caused by overgrazing by sheep and other domestic

livestock, and human-caused developments such as roads and cities.

Vicuna generally occur on communal property lands in Bolivia. In the

northern highlands vicuna share habitats mainly with alpacas, in the

central highlands with cattle, sheep, llamas, alpacas and agriculture,

and in the southern highlands with llamas (CITES 1997b). Overgrazing,

especially by sheep, has reduced range carrying capacity in many areas.

The limited quantitative information presently available to us

indicates that vicuna populations throughout Bolivia are not endangered

by the present or threatened destruction, modification, or curtailment

of habitat or range. However, overgrazing by domestic livestock and

direct competition for forage with domestic livestock are still

considered to threaten vicuna populations throughout Bolivia. Through

this proposed rule, we are seeking additional, quantitative information

on the status of vicuna habitats throughout Bolivia. We especially seek

detailed information on land use restrictions (for example,

prohibitions on the grazing of domestic livestock) and actual

protective measures (for example, antipoaching efforts) within

protected areas, on the status of development of Vicuna Management

Plans and Soil Use Plans in the three pilot areas of the National

Vicuna Conservation Program (Lipez-Chichas, Mauri Desauadero, and Ulla

Ulla), and on current efforts to manage habitat on lands which are not

within either the three aforementioned conservation units or

officially-designated protected areas. We also seek more information on

the National Program for the Fight Against Desertification and Drought.

Chile

The vicuna occurs in extreme northeastern Chile in the Regions of

Tarapaca, Antofagasta, and Atacama. Over 96 percent of the vicuna

(19,169 of 19,848) in Chile are found within the Caquena Management

Zone, Lauca National Park, and the Vicuna National Reserve within this

Province (Galaz 1997, pers. comm.). These areas have typical vicuna

habitats and limited human populations.

Most vicuna in Chile are found within protected areas. These

include the aforementioned Caquena Management Zone (90,146 ha), Lauca

National Park (137,883 ha) and the Vicuna National Reserve (209,131 ha)

within Parinacota Province. A few vicuna also occur in Salar de Surire

Natural Monument in Parinacota Province (11,298 ha), and Isluga Volcano

National Park in Iquique Province, Tarapaca Region (174,744 ha).

Information presently available to the Service indicates that

vicuna populations in Chile are probably not endangered by the present

or threatened destruction, modification, or curtailment of habitat or

range. This is because the overwhelming majority of vicuna in Chile

occur in protected areas where there is some measure of control over

domestic livestock grazing. However, overgrazing by domestic livestock

and direct competition for forage with domestic livestock may still

threaten vicuna populations in Chile. Through this proposed rule, we

seek additional, quantitative information on the status of vicuna

habitats throughout Chile. We especially seek detailed information on

land use restrictions (for example, prohibitions on the grazing of

domestic livestock) and protective measures (for example, antipoaching

efforts) within protected areas, and on effort to manage habitat

outside protected areas (including programs to combat desertification

and to reduce competition with domestic livestock).

Peru

Vicuna in Peru in 1997 were estimated to occur on about 6,361,000

ha throughout the 15,000,000 to 17,000,000 ha of suitable habitat in

the Peruvian high plains. Factors that could impact future areas of

vicuna habitat include increased urbanization, successful

reintroductions of vicuna into present areas of suitable but unoccupied

habitat, and the replacement of domestic livestock by vicuna. Vicuna

are better adapted to the rigorous climate and ecological conditions of

the Puna, than are many species of domestic livestock. Overgrazing by

domestic livestock remains the greatest threat to habitat conditions in

the Puna.

Vicuna occur in 782,186 ha of Peruvian protected areas, including

Huascaran National Park (340,000 ha), Pampa Galeras National Reserve

(75,250 ha) and the Salinas and Aguada Blanca National Reserve (366,936

ha) (Hoces R. 1997, pers. comm.).

Information presently available to the Service indicates that

vicuna populations in Peru are not endangered by the present or

threatened destruction, modification, or curtailment of habitat or

range. This assessment is based on the overall size of Peru's vicuna

population, plus the large number of community-based management

programs there. Overgrazing by domestic livestock and direct

competition for forage with domestic livestock may still threaten

certain vicuna populations in Peru. Through this proposed rule, we are

seeking additional, quantitative information on the status of vicuna

habitats throughout Peru. We especially seek detailed information on

land use restrictions (for example, prohibitions on the grazing of

domestic livestock) and protective measures (for example, antipoaching

efforts) within protected areas, and on efforts to manage habitat

outside protected areas (including programs to combat desertification

and to reduce competition with domestic livestock).

(B) Overutilization for Commercial, Recreational, Scientific, or

Educational Purposes

Vicuna wool was valued by the Incas and estimates suggest there may

have been 1,000,000 to 1,500,000 vicunas in the region during the Incan

period. Although utilized by the Incas, there is no evidence that the

species was exploited at unsustainable levels. After destruction of the

Inca Empire by Europeans, vicunas were slaughtered in large numbers for

both their meat and wool. In the 1950's populations may still have

totaled 400,000, but hunting pressures and livestock competition may

have reduced the total population to about 6,000 individuals by 1965

(Nowak 1991). Other authors suggest somewhat different numbers but

similar trends.

Vicuna numbers in individual range countries have apparently

fluctuated as political and economic stability has fluctuated. For

example, vicuna numbers in Peru were low in 1965, gradually built to

high levels in 1990, were significantly reduced by illegal hunting

during the 1992-94 period of civil unrest, and have since recovered to

1990 levels. The major breakthroughs in the potential management of

vicuna in Peru were new laws transferring the custodianship of vicuna

to campesinos (peasants) and campesino communities, giving the

campesinos the responsibility to protect vicunas, the implementation of

protective measures, the determination that it was not necessary to

kill vicuna in order to obtain wool from their hides, and the

development of management techniques to herd, capture and shear living

vicuna (Wheeler and Hoces R. 1997). The key factor has been allowing

the benefits of vicuna management and utilization to accrue

collectively to campesino communities (rather than to middlemen

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or other individuals) (Wheeler and Hoces R. 1997).

The vicuna remains a potentially easily exploited resource. It has

great economic value and is a highly visible, diurnal occupant of open

landscape. Some poaching for skins or subsistence hunting for meat

probably still occurs, as does killing of vicunas because of perceived

competition with domestic livestock. This appears to be a source of

mortality that could potentially seriously impact vicuna numbers, as it

has done in the past.

Vicuna Population Status: Argentina

The vicuna population of Argentina is currently estimated to be

approximately 32,000 individuals and increasing, based on censuses

completed in various protected areas between 1992 and 1996 (CITES

1997a). Data appear to be most complete for Jujuy Province, where the

Olaroz-Cauchari Reserve has been surveyed regularly since 1973-74, and

estimates are available for a number of other areas where vicuna are

protected (CITES 1997a). The population of Jujuy Province was estimated

to be approximately 18,000 individuals in 1997 (CITES 1997a). A

population survey was recently completed in Salta Province (V.

Lichtschein, pers. comm. with K. Johnson, OSA, 1999), but the results

are not yet available to us. Data from other provinces are somewhat

dated and incomplete (CITES 1997a).

As previously mentioned, the vicuna population of Argentina is

believed to be increasing. Data from the Olaroz-Cauchari Reserve (where

numbers increased from about 330 individuals in 1973 to 6,500 in 1995)

Laguna Brava Reserve, and Laguna Blanca Reserve all show substantial

population increases over the past 10 to 20 years (CITES 1997a).

Possible causes for the population increases are the newly developed

support for vicuna by the campesino communities of the Puna, the

creation of protected areas and the control of illegal hunting

activities (Canedi 1997, pers. comm.). It is anticipated that some

transplanting will occur from certain areas if populations grow to

exceed carrying capacity.

Vicuna Utilization: Argentina

Poaching does not appear to be a major problem at present (V.

Lichtschein, pers. comm. with K. Johnson, OSA, 1999; E. Hoffman,

journalist, pers comm. with K. Johnson, OSA, 1999). Sport hunting of

vicuna is not permitted in Argentina and no permits have been issued

for the capture of wild vicuna for scientific or educational purposes.

The vicuna utilization scheme in Argentina consists of a developing

effort to sustainably use wild populations in Jujuy Province, and an

effort to develop semi-captive populations in the provinces of

Catamarca, Jujuy, La Rioja, Salta, and San Juan. This model has been

developed to be relevant to the conditions of the Argentine Puna where

lands are owned by individual ranchers, human populations are very

sparse and vast areas of potential habitat with limited vicuna

populations exist (CITES 1997a).

Experimental efforts to develop management programs under semi-

captive conditions are conducted at the National Institute of

Agriculture and Cattle Technology (INTA) at their High Altitude

Experiment Station (CEA) at Abra Pampa. Studies have emphasized

efficient fences to contain vicuna, the determination of the carrying

capacity of different range types, and the capturing and shearing of

vicuna and wool processing procedures.

The experimental results have direct applications because a limited

number of vicuna ranching operations have been established in Jujuy and

Salta Provinces. These ranch operations have used vicuna donated from

the Abra Pampa semi-captive herd and donated fencing materials. Vicuna

family units are placed into a fenced area. Individual ranchers who

have been trained in vicuna management have the responsibility to

protect and provide for the vicuna. Young vicuna, produced under these

semi-captive conditions, are either used as replacement stock or are

returned to CEA as compensation for the initial vicuna donation. The

semi-captive herds are sheared at two year intervals using the

techniques developed at CEA. At the time of shearing, representatives

of INTA, the Department of Renewable Natural Resources, the Gendarmes

(military police), a Doctor of Veterinary Medicine, and the wool buyer

are present to observe and/or supervise the operation. The wool buyer

in 1997 was an Argentine wool processing company that donated the

fencing materials. The wool purchase is used to retire the debt on the

fencing materials and to provide immediate payment to the individual

rancher. The wool, at the time of shearing, is weighed, bagged, marked,

sealed, recorded and stored in a sealed warehouse until all commercial

authorizations have been completed.

The production of vicuna wool under semi-captive conditions

benefits the individual campesino rancher and is a program growing in

popularity. It is claimed that this program enhances the status of

vicuna because the ranchers support the program and support the

presence of non-captive vicuna in the provinces, and it has enhanced

the gendarme-rancher relationship which has improved protective

measures for vicuna. However, we continue to have concerns over the

appropriateness and effectiveness of this approach as a conservation

tool for wild populations of vicuna. The captive population at Abra

Pampa has been developed from a limited number of founder animals (16

females and 6 males). As such, there is concern over the genetic

fitness of animals in this population. There is also concern about

possible genetic and disease consequences if vicuna from the Abra Pampa

population are translocated to different provinces and subsequently

escape to mingle with the wild population. We are concerned that semi-

captive populations may be established in the most favorable vicuna

habitat areas, thus potentially depriving wild vicuna populations of

important resources such as water or forage. Finally, we have no

information showing a demonstrable link between establishment of semi-

captive vicuna populations and improved conservation status of wild

populations (for example, a demonstrable reduction in poaching of wild

vicuna in areas with semi-captive populations, or a demonstrable

improvement in habitat conditions as a result of decreased domestic

livestock numbers in areas with semi-captive populations). The Appendix

II semi-captive populations of Catamarca, Jujuy, La Rioja, Salta, and

San Juan Provinces are specifically excluded from the proposed special

rule until their conservation benefit for wild vicuna is demonstrated

adequately. With this proposed rule, we seek substantive information

demonstrating the conservation value (for wild vicuna) of semi-captive

vicuna populations.

The vicuna is not considered to be endangered by previous or

current overutilization in Argentina. It is, however, considered to be

threatened by overutilization throughout Argentina, and will continue

to be threatened until appropriate conservation mechanisms are fully

implemented and the populations fully recover, based on successful

conservation and management. Through this proposed rule, we seek

additional information on the status of wild vicuna populations

throughout Argentina.

Vicuna Population Status: Bolivia

Vicuna populations in Bolivia were recorded as 33,844 in the

country-wide census of 1996 and current populations are estimated at

about 35,500 (DNCB 1997, pers. comm.). The population is

[[Page 48748]]

generally thought to be increasing, and perhaps has reached carrying

capacity in a few areas. Population data determined by direct and total

counts of individuals on selected habitat areas are best for the three

experimental pilot areas--Ulla Ulla, Mauri-Desaguadero and Lipez

Chichas whose populations were transferred to CITES Appendix II in

1997. Periodic censuses have occurred over a 30-year period for Ulla

Ulla, and over a 15-year period for the other two pilot areas. The

growth in the total vicuna population has been both in density within

well-known habitat areas and in the number of habitat areas with

vicuna. It is believed that the principal reason for the growth in the

general vicuna population is the protection provided by the campesino

communities, especially those that have government supported game

wardens.

Vicuna Utilization: Bolivia

Some campesino communities are hostile to vicunas because of crop

depredation or perceived competition with domestic livestock and the

fact that no economic benefits are presently realized from vicuna. This

may result in the killing of vicuna, although we have no substantive

information which directly supports this conclusion. The granting of

custodianship to the local communities and the delegation of monitoring

to the provincial governments is expected to provide the mechanism to

address this issue.

Poaching of vicuna is known to occur in Bolivia (CITES 1997b), and

may be at a level that is of concern. One individual was recently

arrested outside La Paz with 324 vicuna skins in his possession (E.

Hoffman, pers. comm. with K. Johnson, OSA, 1999). Vicuna products,

including rugs made from many skins, can be seen for sale in the San

Francisco Plaza in La Paz (E. Hoffman, pers. comm. with K. Johnson,

OSA, 1999). Local traditional authorities use vicuna ponchos, scarves

and blankets, especially at traditional celebrations (CITES 1997b). The

wool used in these products comes from animals killed illegally (CITES

1997b). Tour operators in remote areas claim to encounter skinned

vicuna carcasses on a regular basis (E. Hoffman, pers. comm. with K.

Johnson, OSA, 1999).

Vicuna are not captured in Bolivia for educational or scientific

purposes. There is no intent to have commercial meat operations as the

only authorized commerce will be in wool and wool products from live-

shorn vicunas from wild populations. At present, there is no trade in

wool as Bolivia has a zero quota under CITES.

Bolivia, as well as the other signatory countries to the Conveno

para la Conservacion y Manejo de la Vicuna (Convention for the

Conservation and Management of the Vicuna, or the Vicuna Convention),

has agreed not to export fertile specimens of vicuna. The sole

exception has been a 1993 export of 100 vicunas to the Republic of

Ecuador to aid in their vicuna recovery efforts. This was accomplished

within the multilateral frameworks of both the Vicuna Convention and

the CITES Convention.

Bolivia's National Program for the Conservation of Vicuna is in

very early stages of implementation. Bolivia is developing pilot

programs for harvesting and marketing wool from live-shorn vicuna that

borrow significantly on the successful management program in Peru. The

initial step of the National Vicuna Conservation Program was to

transfer three substantial vicuna populations in areas where campesino

interest and commitments were high (Ulla Ulla, Mauri-Desaguadero, Lipez

Chichas) from CITES Appendix I to II, so that pilot management and

shearing programs could be perfected prior to expanding the management

programs to other vicuna habitats. The second step has been the

development of an agreement between the Programma Quinua Potosi

(PROQUIPO) and the DNCB to operate the Pilot Center of Sud Lipez to

actually develop and demonstrate those management and shearing programs

to enable the sustainable use of the vicuna through live shearing to be

realized eventually.

Vicuna population trends throughout Bolivia are encouraging, and

populations appear to have recovered to the extent that they are no

longer endangered by previous and current overutilization. We consider

that the vicuna is threatened by overutilization throughout Bolivia,

and will continue to be threatened until appropriate conservation

mechanisms are fully implemented and the populations fully recover,

based on successful conservation and management. Through this proposed

rule, we seek additional information on the status of wild vicuna

populations throughout Bolivia. We especially seek information on the

magnitude of poaching.

Vicuna Population Status: Chile

Over 96 percent of the vicuna (19,200 of 19,850) in Chile occur in

Parinacota Province in the extreme northeastern portion of the country.

The populations in the Caquena Management Zone (3,700 vicuna on 101,380

ha) and in the National Vicuna Reserve (8,050 vicuna on 288,970 ha) in

this Province were transferred to CITES Appendix II in 1987, and would

be the only populations utilized commercially should a program to

capture and shear live vicuna be instigated (Galaz 1997, pers. comm.).

The adjacent population in Lauca National Park (7,410 vicuna on 153,380

ha) was retained on Appendix I to provide further control over vicuna

in this protected natural area. The vicuna population in Parinacota

Province is believed to be at or near carrying capacity in typical

vicuna habitat. The remaining four percent of Chile's vicunas occur

elsewhere in the upper Andean tablelands in northeastern Chile. About

650 vicuna are believed to occur in small scattered groups over about

215,000 ha elsewhere in the Tarapaca Region and in the neighboring

Antofagasta and Atacama Regions.

Vicuna Utilization: Chile

The hunting, capture and sale of vicuna and vicuna products is

unlawful in Chile and, at present, there is no national or

international trade in vicuna fiber, no exports of living vicuna and no

known illegal trade in vicuna products. Poaching is not considered to

be a problem in Chile (E. Hoffman, pers. comm. with K. Johnson, OSA,

1999). In summary, protected areas have been established in locations

with a high density of vicunas, a conservation and management plan has

been developed for vicuna, legal provisions have been developed to

protect the species and adequate protection is being provided for the

species, especially in Lauca National Park and the National Vicuna

Reserve.

The vicuna is not considered to be endangered by previous or

current overutilization in Chile. However, as a vicuna wool industry

could potentially be approved in Chile, overutilization is still

considered to threaten the Chilean population until such time as

control mechanisms for harvest and commercialization are demonstrated

to be adequate.

Vicuna Population Status: Peru

The 1997 census in Peru estimated a population of 103,650 vicuna on

6,361,000 ha of habitat (Hoces R. 1997, pers. comm.) in the high Andean

tablelands of the departments of Ancash, Apurimac, Arequipa, Ayacucho,

Cajamarca, Cusco, Huancavelica, Huanuco, Junin, La Libertad, Lima,

Moquegua, Pasco, Puno and Tacna. Vicuna populations have been

increasing since 1994. This is believed to be due to the increased

efforts to control vicuna poaching and

[[Page 48749]]

the development of a vicuna wool utilization program. Several campesino

communities now participate in the protection, management and

utilization of vicuna in cooperation with the National Council of South

American Camelids (CONACS) and the National Institute of Natural

Resources (INRENA), which is the designated CITES Management Authority

for Peru.

Vicuna Utilization: Peru

As mentioned previously, vicuna numbers in Peru have fluctuated

greatly in recent years as a result of political and economic

instability. Vicuna numbers were low in 1965, gradually built to high

levels in 1990, were significantly reduced by illegal hunting during

the 1992-94 period of civil unrest, and have since recovered to 1990

levels.

At present, legislation in Peru permits the taking of vicuna if

properly authorized and technically supported. Some culling of vicunas

(about 1,000 per year) did occur from 1977 to 1983 but no quotas have

been declared and little if any legal take has occurred since that

date. Any take for scientific studies is rare and, when authorized, is

tightly controlled. There is no legal utilization of vicuna for meat or

parts.

Commercialization of vicuna wool products will likely not result in

overutilization of vicuna because of the system of controls that exist

in monitoring wool collections, governmental supervision by CONACS and

INRENA, and the involvement of local campesino communities. CONACS and

INRENA have the responsibility to protect and monitor vicunas within

protected areas such as Huascaran National Park, Pampa Galeras National

Reserve and the Salinas and Aguada Blanca National Reserve. The

protection and monitoring of vicunas in the rural communities is a

major responsibility of participating campesino communities in

coordination with CONACS and INRENA.

CONACS has developed techniques, at Pampa Galeras, for capturing

and harvesting wool from living wild vicuna. Capture methods are based

on the traditional ``chaku, a surround technique used by the Incas to

capture and shear vicunas (Wheeler and Hoces R. 1997). CONACS has

taught and supervised campesino communities in this technique and other

aspects of vicuna management. At Pampa Galeras and in other areas of

the Peruvian Puna, vicunas occur on communal lands and campesinos

represent an abundant and important work force.

The process used to capture and shear vicunas was observed in

August 1997 by Dr. Short (on behalf of the National Fish and Wildlife

Foundation). Vicunas to be shorn were slowly herded across a wide

habitat area and ``pushed'' into a V-shaped funnel trap. The vicuna

were eventually crowded into a corral where they were sorted by hand to

identify adults with adequate fleeces; this is a consideration because

it takes about 18 months to grow a fleece that will yield shorn fibers

that are 2 cm (0.78 in) long. All animals were ear-tagged, identified,

weighed and cursorily examined for general condition. Each animal to be

clipped was restrained and the fleece along the back and flanks was

removed in a single mass, using electric clippers. That portion of the

fleece was placed in a plastic bag. The shoulder, rump and leg wool was

then clipped and placed in a separate bag. Both bags of wool from an

individual animal were tagged, sealed, weighed and recorded at the

field location immediately after clipping was completed. Belly and

chest hair were left intact on the animal in the belief that it would

subsequently insulate the animal when it was resting on cold ground.

The capture, handling, clipping and the securing of the vicuna fleece

was accomplished by campesinos under the supervision of personnel from

CONACS and the Sociedad Nacional de la Vicuna (SNV). Upon the

completion of the clipping effort the shorn animal was released.

Clipping took about two minutes per animal. No significant injuries

were observed from the capture, handling or clipping of the live wild

vicunas under these observed conditions.

Cleaning of guard hairs and dirt from vicuna fleeces is usually

accomplished by women from the campesino communities. Such cleaning

takes about 2-3 woman-days per 250-gram (9 ounce) fleece. Up to 100

women from the Lucanas campesino community near Pampa Galeras may be

employed during the time period required to process an annual harvest

of up to 2,000 fleeces. Careful weights are kept as fleeces are

unsealed, cleaned, re-bagged and resealed prior to auction. A single

auction supervised by CONACS serves all campesino communities producing

vicuna wool.

Vicuna management essentially provides full-time employment for

many members of the Lucanas community--building fences, obtaining and

cleaning fleeces, providing protection to vicuna and providing

instruction to other communities wishing to establish a vicuna

industry. It was reported that as part of the arrangement between the

Lucanas community and the government, 500 vicunas are used to restock

vicuna habitats in neighboring communities, in exchange for both a

hydro-electric project and other economic assistance.

The Pampa Galeras experience is the model for other campesino

communities in Peru and will likely be the model for similar efforts in

Bolivia. Campesino communities in both countries benefit by having some

initial funds to develop a vicuna management infrastructure--either

from the national government, as in Peru, or the European Community in

aid to Bolivia.

Efforts are apparently underway in Peru to develop ranching of

vicuna (i.e., fencing of natural areas to produce semi-captive

populations) (Wheeler and Hoces R. 1997). Although translocation of

animals does not appear to be involved in this case, we still have many

of the same concerns as previously expressed for the semi-captive

populations in Argentina. We reiterate our desire to receive

substantive information demonstrating the conservation value (for wild

vicuna) of semi-captive vicuna populations.

The vicuna is not considered to be endangered by previous or

current overutilization in Peru. It is, however, considered to be

threatened by overutilization, and will continue to be threatened until

appropriate conservation mechanisms are fully implemented and the

populations fully recover, based on successful conservation and

management.

(C) Disease or Predation

Vicunas, like most mammals, suffer from a variety of endo-and ecto-

parasites. Mange caused by parasitic mites can result in skin lesions

and loss of hair, especially in those populations that coexist with

domestic livestock, especially during drought conditions. Drought

conditions or extremely degraded ranges adversely impact vicuna by

causing movements to new habitats with the possible dissolution of some

family groups and reductions in reproductive rates and successes, and

perhaps increased mortalities. Major predators on vicuna include the

puma (Felis concolor), the Andean fox or zorro (Dusicyon culpaeus) and

perhaps the Andean condor (Vultur gryphus), which may kill newborn and

very sick animals.

Vicuna populations in the four range countries are not believed to

be endangered from the impacts of disease or predation, in part because

the numbers of individuals within each population are considered to be

increasing. Likewise the vicuna populations are not likely to be

threatened by these factors if the benefits from the commercialization

of vicuna wool products are used to

[[Page 48750]]

enhance the standard of living in campesino communities, with

concomitant effective protection and enforcement. We remain concerned

about the potential for disease transmission from animals that are

translocated for the development of semi-captive populations or for

release to the wild to supplement wild populations, and seek additional

information on this issue.

(D) The Inadequacy of Existing Regulatory Mechanisms

The regulatory mechanisms in place vary significantly among the

four range countries. Those in Peru are very substantive and involve

the establishment of new governmental agencies, new mechanisms to

enhance inter-community coordination, enhanced vicuna management

procedures and a regulated and active vicuna wool industry that

currently returns economic benefits to campesino communities. Argentina

has also developed regulatory mechanisms to allow the development of a

vicuna wool industry that currently benefits a small number of local

ranchers. Bolivia is currently developing mechanisms to develop a wool

industry and is building on many of the procedures that are apparently

successful in Peru. Chile has no current plans for developing a wool

industry but has conceptualized how such an industry might be

successfully managed.

Regulatory Mechanisms: Argentina

In Argentina, the First Interprovincial Technical Conference on the

Conservation of the Vicuna met in 1972 and agreed to develop methods to

capture, transport and recolonize vicuna habitats and develop a plan

for the management, shearing and the manufacture of handicrafts from

vicuna fiber. Additional meetings integrated the provincial vicuna

programs, established a national program, and established the ``Vicuna

Regional Commission'' as a mechanism to attain national coordination on

the vicuna management program (Comision Regional de la Vicuna, 1994).

Argentina ratified the CITES Convention in 1981. In 1988 Argentina

signed the Vicuna Convention and has since carried out its programs

within the context of this agreement. Argentine National Law for the

Conservation of Wildlife 22.421 and its Regulatory Decree No. 691,

provides for vicuna protection. The Constitution of Argentina, reformed

in 1994, assures the rights of the provinces over their respective

natural resources, assures the rights of indigenous people to use these

natural resources in traditional ways, and embraces the conservation of

biological diversity and the sustainable development of natural

resources.

Several laws and decrees within the various Provinces list the

vicuna as a protected species, establish protected areas for the

species, prohibit hunting, and prohibit commercialization,

transportation, or manufacturing of parts or products from hunted

animals, regardless of origin. Laws and decrees also allow the

installation of captive breeding operations and the commercialization

and industrialization of products from captive-bred animals (Canedi

1997, pers. comm.).

The Departments of Renewable Natural Resources for Jujuy, Salta,

Catamarca and La Rioja Provinces have signed agreements with the

Secretariat of Natural Resources and Human Environment and the National

Gendarmes, a Federal Law Enforcement group, to enforce provisions of

Provincial and National laws that prohibit illegal hunting and

smuggling. The Gendarmes conduct extensive patrols in rural areas and

on the borders, and have officers at the ports, airports and borders.

They are capable of conducting inspections and investigations involving

the illegal trafficking of vicuna wool. They also have an environmental

division which meets with campesinos and tries to promote the vicuna

program. Although both the Department of Renewable Natural Resources

and the Gendarmes may not have adequate resources at their disposal,

they are thought to be working effectively with the campesino

communities of the Puna as evinced in the increase of vicuna

populations of the Puna (Canedi 1997, pers. comm).

The only legal wool at the present time is that obtained from the

shearing of live vicuna at the officially authorized semi-captive

population facilities. We understand that a registry of authorized

semi-captive populations is maintained by the national Direccion de

Fauna y Flora Silvestres (V. Lichtschein, pers. comm. with K. Johnson,

OSA, 1999). Wool from shorn fleeces is bagged, tagged, weighed, sealed,

recorded, and the government agency that supervised the shearing is

identified on the bag. Wool from officially authorized breeders

(ranchers) can be directly auctioned for direct export, or the ranchers

(if artisans) can retain the wool, and make and sell cloth. Either the

wool buyer or the rancher-artisan would need a transport permit and

that transport permit would need to be presented when the CITES export

permit is requested. Fabric or products manufactured by rancher-

artisans will need to be marked with the official seals or stamps. Such

fabrics or products, expected to be limited in numbers, can only be

sold to licensed outlets recognized and approved by the government. The

check on whether fabrics or products are made from legal vicuna wool is

determined by comparing weights of fleeces harvested under supervised

shearing operations, the weight of raw wool that is retained by the

authorized rancher-artisan and the weights of woolen products produced

by that artisan. At present it is not clear to us which government

agency supervises shearing, which approves licensed outlets for vicuna

products, and which conducts checks of producers to ensure that only

legal wool is used in artesanal products. There is apparently no

national legislation that covers all aspects relating to the trade in

vicuna or the administrative aspects relating to this trade (CITES

1997a).

Wild populations of vicuna in the Province of Jujuy and semi-

captive populations of vicuna in the Provinces of Jujuy, Salta,

Catamarca, La Rioja and San Juan were transferred from CITES Appendix I

to Appendix II at CITES COP10, effective September 18, 1997. Exports

are limited to wool shorn from live animals, cloth and articles made

from that cloth, luxury handicrafts and knitted articles. The reverse

side of cloth and cloth products must bear the logo adopted by

countries signatory to the Vicuna Convention and the words ``VICUNA-

ARGENTINA-ARTESANIA.'' All specimens not meeting the above conditions

are subject to the prohibition against primarily commercial trade.

Articles bought by a foreign tourist at a government authorized store

will be exportable as personal accompanying baggage only after a CITES

export permit has been obtained. The only apparent control of artisan

goods sold to residents of Argentina and later resold to foreign

tourists is the requirement that the tourist have a CITES export permit

upon his/her return to his/her country of origin. This is a requirement

for importation of any personal effects or personal accompanying

baggage by U.S. residents, under the conditions of the special rule

accompanying this petition finding. If the wool from an authorized

captive breeder is sold at auction, the buyer, presumably a wool

processing company, would get a permit from the Provincial Natural

Resources Department which the buyer would present to the National

Secretary for Natural Resources and Human Environment to obtain the

required CITES permit for export.

The National Police (Gendarmes) are expected to aid provincial

authorities in the control of poaching, illegal trade and

[[Page 48751]]

transport of unauthorized products within the country and the routine

inspection of products of legal origin to certify their origin.

Collaboration will also be provided by the National Aeronautical Police

at the country's airports to intensify inspections of commercial

products and passengers.

The vicuna does not appear to be endangered by inadequate

regulatory mechanisms in Argentina. The species, however, is considered

to be threatened by this factor because many of the regulatory

mechanisms are in early stages of implementation, and we are still

unclear about several aspects related to the control of trade in raw

vicuna wool and artesanal products. The vicuna will remain threatened

by this factor until appropriate conservation mechanisms are fully

implemented and the populations fully recover. Through this proposed

rule, we seek detailed information on the control of trade in vicuna

wool and wool products in Argentina, and on the status of national

legislation to control trade.

Regulatory Mechanisms: Bolivia

Bolivia's National Program for the Conservation of Vicuna is in

very early stages of implementation. Bolivia is developing pilot

programs for harvesting and marketing wool from live-shorn vicuna that

borrow significantly on the successful management program in Peru. The

Ministry of Sustainable Development and the Environment is the

organization responsible for planning and coordinating the conservation

of natural resources with the major plans for national development. The

DNCB (Direccion Nacional de Conservacion de la Biodiversidad Unidad de

Vida Silvestre) is located within this Ministry and is the technical

body whose objective is the conservation and sustainable use of

biological resources. The wildlife unit with responsibilities for

executing the National Vicuna Conservation Program is located within

the DNCB.

Several laws and decrees are relevant to vicuna management in

Bolivia. Bolivia and Peru signed the Treaty of La Paz in 1969 to

provide a measure of international protection for vicuna and this

treaty was a precursor to what is presently known as the Vicuna

Convention. Bolivia has also been a signatory to CITES since 1979. The

Agrarian Reform Act of 1953 enabled some rural communities to have

private lands and other rural communities to have unfenced communal

lands which are advantageous to free-roaming vicunas. Law 1654

decentralized executive power to regional departments. Law 1715, passed

in 1996, created the National Institute for Agrarian Reform and

promoted the sustainable use of land, the promotion of practices

favoring conservation and the protection of biodiversity, and the

concept that lands where conservation is practiced would not be subject

to expropriation. Other laws legalized traditional social

organizations, authorized rights for using renewable natural resources

and authorized the establishment of the Secretariat for Sustainable

Development in each Bolivian Department to enhance vicuna management at

regional levels.

Supreme Decree 24529 passed in March 1997, authorized regulations

for the protection and management of vicunas in Bolivia. The Decree

grants custodianship of vicuna populations to the rural communities and

gives the rural communities the exclusive rights to use vicuna fibers,

subject to the listed regulations (DNCB 1997, pers. comm.). Regulations

promulgated under this Decree will affect all activities dealing with

the management, protection, capture, shearing and the commercialization

of vicuna products (as described in subsequent paragraphs). The

regulations are similar to existing legislation in the other countries

that also signed the Vicuna Convention. At present, we are unclear if

these regulations have been approved and fully implemented, although we

were previously told that the DNCB had begun implementation of

regulations by holding workshops in campesino communities to explain

the regulations, by publishing print media guides describing the

regulations and by helping campesino communities begin their compliance

with the regulations (DNCB 1997, pers. comm.). We were also told that

the DNCB had begun coordinating with the National Police and military

to help curb illegal activities dealing with vicuna and their products.

The National Program for Vicuna Conservation emphasizes the management

of wild free-ranging populations of vicuna and emphasizes a desire to

improve habitat quality.

Any vicuna wool presently in commerce in Bolivia is considered

illegal wool. Under the regulations, all existing vicuna wool products

including those in the domestic market are to be inventoried and

registered and all new products or wool fibers will also be registered.

Any non-registered vicuna products will in the future be considered

illegal. The only wool that will be allowed for commercial purposes

will be that obtained from live-shorn vicuna that have been captured

according to regulations. Only raw wool for the manufacture of cloth

will be exported. Bolivia does not have a textile industry with the

capability to manufacture vicuna wool cloth (DNCB 1997, pers. comm.).

Under the regulations, the harvesting of vicuna wool will only be

allowed in organized campesino communities which (1) have the rights to

capture and shear vicuna and utilize vicuna wool and (2) have delegated

authority to work with government authorities in the management and

conservation of the vicuna. These campesino communities are the only

legal benefactors of the sale of vicuna wool. The National Vicuna

Conservation Program will be carried out in these communities and will

contain habitat and vicuna management plans and vicuna census and

distribution data. This information will be basic to decisions to

conduct vicuna drives, and in the conduct of capture and shearing

operations. Monitoring information will be provided by game guards and

recommendations for management actions will be produced in the

campesino communities. Government authorities will be present when

vicuna capturing and shearing occurs. The authorities will register the

number of vicuna captured, the number shorn, the weights of fleeces,

etc., and supervise the bagging, weighing, marking and sealing of

vicuna wool. This information is provided to the CITES authorities for

reference purposes and information later provided in support of export

permit applications must correspond to the on-site records. The

Netherlands government has provided financial support to underwrite

initial efforts to implement the National Vicuna Conservation Program.

The initial effort of the National Vicuna Conservation Program will

be at the Pilot Center of Sud Lipez and its objective will be to

demonstrate the potential worth of the vicuna. The pilot project will

include the capture and shearing of live vicunas and the manufacture of

fabric and eventually the sale of vicuna fiber for the manufacture of

textiles to demonstrate the potential economic benefit to campesino

communities. The vicuna populations of the Conservation Units of Mauri-

Desaguadero, Ulla Ulla and Lipez Chichas were transferred from CITES

Appendix I to Appendix II at COP10, effective September 18, 1997. A

zero annual export quota presently exists. Future exports will be

limited to wool shorn from live animals and to cloth and articles made

from such cloth, including luxury handicrafts and knitted articles. The

reverse side of cloth and cloth products must bear the

[[Page 48752]]

logo adopted by countries signatory to the Vicuna Convention and the

words ``VICUNA-BOLIVIA-ARTESANIA.'' All specimens not meeting any of

the above conditions will be deemed to be subject to the prohibition

against primarily-commercial trade.

The regulations also establish the System for the Protection of the

Vicuna (SVV) which provides for the development of an inter-community

network for the management and protection of the species. These persons

will have direct control over activities such as wool sales, and will

also have responsibilities for determining status and trends in vicuna

populations. The SVV will be composed of game guards who will be

responsible for the protection and control of vicuna in each

conservation unit, made up of local vicuna protection officers and Park

Rangers who are the enforcement officers within protected areas such as

National Parks. Protection and control efforts will also be supported

by special units of the National Police. The military will also assist

in patrols, inspections and the seizures of illegal products. Customs

will assist in the control of the export and import of wool at the

ports of entry, border posts and airports to assure that CITES

requirements are fulfilled. The Secretariat for Natural Resources and

the Environment (SNRNMA) will regulate and coordinate the activities

and participants within the SVV.

The vicuna does not appear to be endangered by inadequate

regulatory mechanisms in Bolivia. The species, however, should be

considered threatened by this factor because many of the regulatory

mechanisms are in early stages of implementation, and we are still

unclear about the status of proposed regulations dealing with the

management, protection, capture and shearing of vicuna, and the

commercialization of vicuna products. The vicuna will remain threatened

by this factor until appropriate conservation mechanisms are fully

implemented and the populations fully recover. Through this proposed

rule, the Service seeks information on the status of proposed

regulations and the implementation of other regulatory mechanisms, such

as SVV, within Bolivia.

Regulatory Mechanisms: Chile

The existing regulatory mechanisms in Chile are presently dedicated

to the protection of vicuna. Chile has not yet authorized the capture

of vicunas to develop a vicuna wool industry and the only exports of

raw wool have been to obtain analyses of the wool's physical

properties. It is illegal to possess vicuna parts and products so no

mechanisms have been developed for registering or identifying raw wool,

or for establishing warehouses for storing wool (SAG 1997, pers.

comm.).

Law No. 4.601 passed in 1929, modified by law No. 19.473 passed in

1996, indefinitely closed the hunting season for vicuna throughout the

Republic of Chile. The hunting, capturing and selling of vicuna (and

vicuna parts) is outlawed. Persons possessing, transporting or involved

in commercial operations with vicuna products need to prove their

actions are authorized by these laws. The Servicio Agricola y Ganadero

(SAG) of the Ministry of Agriculture is the CITES Management Authority,

and has a Department for the Protection of Renewable Natural Resources

and a Wildlife Division. Authorized customs officers (uniformed

police), accredited officials from SAG, and representatives of the

National Forest Corporation provide protection to vicunas within the

National System of Protected Wild Areas.

Preliminary plans, should a vicuna wool industry become authorized,

indicate that the responsible party would need to provide an

application to SAG indicating, among other things, the likely number of

animals to be captured and sheared, the expected yield of the wool

harvest, the logistics of the capture and shearing operation, where and

how the wool would be stored and its eventual destination. SAG, should

they approve the application, would oversee the capture process,

register the quantity of harvested wool, and seal the warehouse where

the wool is stored. SAG would also provide the necessary export

permits, after determining that the quantities for export correspond to

quantities authorized and actually harvested. Preliminary plans also

suggest that a mechanism would be established to deal with the

production and sale of luxury handicrafts and knitted articles. That

organization would be responsible for receiving the wool, registering

and offering the wool products for sale, for recording the sale of

registered craft items and providing an accounting of the sale of

registered craft items (SAG 1997, pers. comm.).

Chile has succeeded in having certain vicuna populations in the

Paranicota Province, Region of Tarapaca (specifically, the populations

in the Caquena Management Zone and the Vicuna National Reserve)

transferred from CITES Appendix I to Appendix II in 1987 (at COP6). Any

future export of vicuna products would be limited to wool sheared from

live animals in Appendix II populations and to cloth and items made

from that cloth including luxury handicrafts, and knitted articles. The

reverse side of cloth and cloth products would need to bear the logo

adopted by countries signatory to the Vicuna Convention and the words

``VICUNA-CHILE-ARTESANIA.'' All specimens not meeting any of the above

conditions would be deemed to be subject to the prohibition against

primarily-commercial trade.

The vicuna is not considered to be endangered by inadequate

regulatory mechanisms in Chile. However, as a vicuna wool industry

could potentially be approved in Chile, the vicuna remains threatened

by this factor until such time as regulatory mechanisms for harvest and

commercialization are demonstrated to be adequate.

Regulatory Mechanisms: Peru

A complex regulatory mechanism exists for Peru and it controls

commerce in vicuna wool products. The infrastructure promoting vicuna

management includes the National Council of South American Camelids

(CONACS) which is a public decentralized organization of the Ministry

of Agriculture in charge of the promotion, standardization, and control

of activities with the South American camelids. CONACS has offices in

Lima and throughout the vicuna range, and is the proprietor of the

trademarks ``VICUNA-PERU'' and ``VICUNA-PERU-ARTESANIA.'' The Institute

of Natural Resources (INRENA) is also a public decentralized

organization of the Ministry of Agriculture, and is in control of all

renewable natural resources in Peru, and is the CITES Management

Authority for Peru. The National Society of the Vicuna (SNV) is a

private organization which represents the 660 campesino communities and

coordinates vicuna management within and between campesino communities

(``Communal Committees of the Vicuna'') and with CONACS at both

regional and national levels (Hoces R. 1997, pers comm.).

Several national laws protect vicuna and regulate its management.

Law 26496 is especially important as it promotes protection and

provides penalties for the illegal hunting of vicuna, gives the

custodianship of vicuna herds that occupy campesino community lands to

those campesino communities and allows the campesinos to be responsible

for the conservation, management and the utilization of the species.

The law also establishes the Official Registry of the Vicuna which

provides a record keeping process that

[[Page 48753]]

controls and tracks volumes of wool from the time of vicuna shearing in

the field to the time that fiber is sold as cloth or merchandise on the

international market. Other laws recognize the Vicuna Convention and

the CITES Convention.

Pertinent laws are implemented through the 660 ``Communal

Committees of the Vicuna'' which form the basis for the National System

of Conservation. There is a system of park rangers shared by groups of

communities and these park rangers can access the National Ecological

Police and Peruvian Army units to help control the illegal killing of

vicuna. CONACS and INRENA authorize and control management activities,

including vicuna capture; since 1996 they manage a limited captive

breeding program where enclosures of approximately 1,000 ha (``Modules

of Sustainable Use''), each with about 250 vicuna, are developed or are

to be developed within individual campesino communities.

The shearing, collecting, processing and commercialization of

vicuna wool from wild vicunas or from groups contained within the

permanent enclosures, is controlled by CONACS and INRENA. The

processing and commercialization of the wool is done by a single

company that obtained that right through a competitive bidding process

at a supervised auction. A cooperative agreement exists between the SNV

and the company winning the competitive bid, apparently to ensure that

campesino communities will be correctly represented in the distribution

of monies from the sale of vicuna wool and wool products. There is an

authorized season for shearing and the act of shearing is supervised by

personnel representing CONACS, SNV and INRENA. Pertinent information is

gathered at the time of shearing and a report describing the shearing

operation (numbers of animals, wool weights per animal, etc.) signed by

representative of the Communal Committee and CONACS, becomes part of

the record at the Official Registry of the Vicuna. A second source of

legal wool is from vicuna that die from natural causes or are found or

obtained by campesinos or park rangers, or from skins that are seized

in successful anti-poaching operations. Such specimens, to become

legal, must be declared to SNV and CONACS and entered into the vicuna

registry. Legal wool is gathered and stored in private warehouses

belonging to the campesino communities, registered in the vicuna

registry, and is under the control of CONACS. Illegal wool is prevented

from entering commerce because it is not registered with the vicuna

registry, and consequently not included in the wool stores represented

in the single legal auction. The vicuna registry records weights of

wool sheared or collected, carded or cleaned, and these weights are

used by CONACS and SNV throughout the processing and commercialization

process to indicate whether final products likely only contain legal

wool. The CITES Management Authority controls commerce by requiring

records of wool weights and opinions from CONACS before any products

(fiber, cloth or articles) can be legally either imported or exported

from Peru.

The processing of vicuna fiber and the commercialization of vicuna

products involves a joint venture ``Association in Participation''

between SNV and the consortium that won the auction for vicuna wool.

The SNV provides the wool to the consortium which includes a Peruvian

company that fabricates cloth from the vicuna fibers, which is then

sent to an Italian manufacturing plant where luxury clothing items are

produced. A second Italian firm then handles the promotion and

marketing of the finished vicuna products (Hoces R. 1997, pers. comm.).

CONACS supervises production to guarantee that all articles will

contain 100 percent vicuna wool. This process is designed to maximize

the financial returns from the vicuna fibers; the profits from the

final sales are distributed, under the supervision of CONACS and

INRENA, to the campesino participants. Raw vicuna wool currently sells

for $500/kg of fiber and additionally a percentage of the final sale

price on the completed product goes to the campesino communities.

The vicuna populations of Pampa Galeras National Reserve and

Nuclear Zone, Pedregal, Oscconta and Sawacocha (Province of Lucanas),

Sais Picotani (Province of Azangaro), Sais Tupac Amaru (Province of

Junin), and Salinas Aguada Blanca National Reserve (Provinces of

Arequipa and Cailloma) were transferred from CITES Appendix I to

Appendix II in 1987 (at COP6). All remaining Peruvian vicuna

populations were transferred to Appendix II in 1994 (COP9), effective

February 16, 1995. All exports are limited to cloth fabricated from the

3,294 kg (7,260 lbs) of stored wool present in November 1994 or from

the wool stores obtained from the recent authorized shearing of live

animals or from dead animals listed in the vicuna registry, and items

made from that cloth and to certain luxury handicrafts and knitted

articles produced in Peru. The reverse side of cloth and cloth products

must bear the logo adopted by countries signatory to the Vicuna

Convention and the words ``VICUNA-PERU-ARTESANIA.'' This trademark will

also occur on all luxury artisan products and knitted articles of

vicuna wool. Peru also plans to add to the produced articles, a seal or

identification tag with codes indicating the origin of the product, the

assigned trademark or label and the CITES permit number. All specimens

not meeting any of the above conditions will be subject to the

prohibition against primarily commercial trade.

The vicuna is not considered to be endangered by inadequate

regulatory mechanisms in Peru. The species is, however, considered to

be threatened by this factor, and will continue to be threatened until

appropriate conservation mechanisms are fully implemented and the

populations fully recover.

E. Other Natural or Human-Made Factors Affecting Its Continued

Existence

The great potential threat to the vicuna is that pelts can be

easily obtained from poached animals and that the wool industry may

actually prefer the longer fibers that can be obtained by soaking and

pulling hairs from pelts, rather than the clipped hairs from legal

fleeces (Canedi 1997, pers. comm). The vulnerability of the vicuna to

political instability is well documented. For example, vicuna

populations in Peru were estimated at about 60,000 in 1980 and 1981 but

were overexploited and in 1982 populations were reduced to about

25,000. A slow recovery was observed until 1988 when populations were

again estimated at about 60,000. Vicuna populations were again reduced

to low levels from 1989 to 1993 when vicuna wool from poached animals

was used to help finance guerilla activities in some countries.

The vicuna represents one of the most significant economic

resources available in many Andean highlands that have limited human

populations with limited economic resources at their disposal.

Indigenous people fully realize that a poached vicuna can be used once

but that the managed, live-sheared vicuna can be used repeatedly

(Wheeler and Hoces R. 1997). Assigning the responsibility of vicuna

management to campesino ranchers and/or campesino communities and

granting those people the opportunity to legally realize economic gains

from their management and protection efforts represents a significant

bio-political decision. It is also significant that governments in four

range countries have cooperated in the development of a vicuna wool

industry and that scarce resources have been

[[Page 48754]]

devoted to the management of this species. Vicuna management, as

described herein, is one of the better examples of the economic gains

to be realized from the sustainable use of a biological resource.

Distinct Vertebrate Population Segment

The definition of ``species'' in section 3(16) of the Act includes

``any distinct population segment of any species of vertebrate fish or

wildlife which interbreeds when mature.'' Distinct vertebrate

population segments for purposes of listing under the Act are defined

in the Service's February 7, 1996, Policy Regarding the Recognition of

Distinct Vertebrate Population Segments (61 FR 4722). For a population

to be listed under the Act as a distinct vertebrate population segment,

three elements are considered: (1) The discreteness of the population

segment in relation to the remainder of the species to which it

belongs; (2) the significance of the population segment to the species

to which it belongs; and (3) the population segment's conservation

status in relation to the Act's standards for listing (i.e., is the

population segment, when treated as if it were a species, endangered or

threatened?). International borders may be used to delineate discrete

population segments where there are significant differences in: (1) The

control of exploitation; (2) management of habitat; (3) conservation

status; or (4) regulatory mechanisms on each side of the border (61 FR

4722). Discrete population segments can also be defined by marked

physical, physiological, ecological, or behavioral separation from

other populations of the same taxon.

We recognize the vicuna population of Ecuador as a distinct

vertebrate population segment for purposes of listing under the ESA.

The vicuna population of Ecuador is geographically isolated and

separate from other vicuna in Argentina, Bolivia, Chile, and Peru.

Historically, the vicuna was eliminated from Ecuador. A small, disjunct

population has been recently reintroduced to Ecuador. The population

was established from 100 animals exported from Bolivia in 1993. This

was accomplished within the multilateral frameworks of both the Conveno

para la Conservacion y Manejo de la Vicuna (Convention for the

Conservation and Management of the Vicuna, or the Vicuna Convention)

and the CITES Convention. It should be noted that Ecuador is also a

Party to the Vicuna Convention. Ecuador's population remains listed in

CITES Appendix I, and there is no plan to commercially utilize the

species in the near future. Furthermore, the Parties to the Vicuna

Convention view this as a separate population, worthy of special

recovery efforts. Although the countries of the region that are Parties

to the Vicuna Convention view this as an ``experimental'' population,

that should not be seen in the domestic U.S. context of experimental

populations under the Act, where criteria and definitions differ. For

these reasons, the Ecuadoran population of vicuna satisfies the

discreteness and significance criteria of the DVPS Policy, and,

therefore, merits treatment as a distinct population segment under the

ESA.

In contrast to the rather strict requirements for listing entities

(species, subspecies, or distinct vertebrate population segments) under

the ESA, CITES has retained a degree of flexibility in the listing

process through the use of annotations. There is no specific

requirement that populations be delimited by national borders or marked

biological differences. CITES Article I defines a species as ``any

species, subspecies, or geographically separate population thereof'',

and different populations of a species can be listed in different CITES

Appendices. Thus, it has been possible to transfer sub-national

populations of vicuna in Argentina, Bolivia, and Chile from Appendix I

to Appendix II. This accounts for the lack of perfect symmetry between

populations proposed for threatened status and those currently listed

in Appendix II of CITES.

Summary of Findings

The Service finds that the vicuna is a highly vulnerable species

whose populations are generally increasing over a large area of very

specific habitat--the high Andean tablelands of Argentina, Bolivia,

Chile and Peru. The current status of the vicuna and its future

potential seems directly attributable to recent bio-political decisions

made in the range countries to turn over the custodianship of the

species to the native people sharing these landscapes. Laws, decrees

and infrastructures have been or are being developed to help the

campesinos manage and protect the species. In return the campesinos are

or are likely to receive critical financial benefits from that

management that will benefit both individuals and their communities.

The management and protection accorded to the vicunas, by campesinos in

cooperation with governmental entities, provides the best opportunity

for the vicuna to survive as a species and as a very important part of

the Puna and Altoandina ecosystems.

Specifically, we find that the vicuna is threatened by the (1)

present or threatened destruction, modification, or curtailment of its

habitat or range, (2) previous or current overutilization, and (3) the

possibility of inadequately controlled illegal harvest pressures

including poaching, in Argentina, Bolivia, Chile, and Peru. A

reclassification of the vicuna from endangered to threatened under the

Act will, with the attendant special rule, allow carefully regulated

commerce of vicuna products into the United States. Funds generated by

opening the United States market will help provide the resources

necessary to further manage the species.

In response to the petition submitted by the International Vicuna

Consortium, we find that: (1) Reclassification of the vicuna from

endangered to threatened is warranted for all range countries except

Ecuador; and (2) that a special rule is warranted for all Appendix II

populations, with the exception of the Appendix II semi-captive

populations of Catamarca, Jujuy, La Rioja, Salta, and San Juan

Provinces in Argentina, which are specifically excluded until such time

as their conservation benefit for wild vicuna is demonstrated

adequately. The present publication provides a 12-month finding on that

petition and includes a proposed special rule.

Description of the Proposed Special Rule

The intent of the proposed special rule is to enhance the

conservation of the vicuna through support for properly designed and

implemented programs for vicuna conservation throughout their native

range. The proposed special rule is intended to support the

conservation efforts of the four range states of Argentina, Bolivia,

Chile, and Peru, by acknowledging and deferring to certain of their

management programs that allow utilization of vicuna wool from wild,

live-sheared animals, with benefits accruing to indigenous communities.

The proposed special rule clarifies that only properly identified

vicuna products can be imported into the United States. The vicuna

products that can be imported are only those items of either raw

(unprocessed) vicuna wool or cloth, or items made from that wool,

including luxury handicrafts and knitted articles, that are properly

identified, and have accompanying valid, legal CITES Appendix II export

permits or re-export certificates. Under the proposed special rule, an

endangered or threatened species permit for individual shipments would

not be required under 50 CFR part 17. To be

[[Page 48755]]

imported, vicuna products must originate in populations that are listed

both as threatened under the Act and in Appendix II of CITES, with the

exception that Appendix II semi-captive populations in Catamarca,

Jujuy, La Rioja, Salta, and San Juan Provinces in Argentina are

excluded from the proposed special rule until such time as their

conservation benefit for wild vicuna populations is demonstrated

adequately. If adequate information is presented during the public

comment period, these populations may be included under the final

special rule.

We are aware that there have been poaching and illegal trade

problems with this highly valuable species in the past, and any loss of

control would seriously undermine the conservation programs of these

countries, thereby potentially jeopardizing vicuna populations.

Therefore, we propose not to allow the import of vicuna products from

threatened and approved Appendix II populations if the countries of

origin or the countries of manufacture or re-export have been

determined by the CITES Conference of the Parties or the CITES Standing

Committee to be not effectively implementing the Convention.

Specifically, the proposed special rule would prohibit importation from

countries of export or re-export that have either failed to designate a

Management Authority or Scientific Authority, or have been identified

by the Conference of the Parties to the Convention, the Convention's

Standing Committee or in a Notification from the Secretariat as a

country from which Parties should not accept CITES permits.

Commerce with the United States in vicuna products, if the proposed

special rule is adopted as final at the conclusion of the regulatory

process, will only be allowed with countries that have both designated

CITES Management and Scientific Authorities, and that are not subject

to a Schedule III Notice of Information for all wildlife or all CITES-

listed species. In the case where vicuna products are exported to a

second country, for manufacturing purposes, and the finished products

are re-exported to the United States, then neither the country of

origin nor the country of re-export can be subject to Schedule III

Notice of Information based on the criteria described in the special

rule if imports are to be allowed. The U.S. Management Authority will

provide on request the list of those countries subject to a Schedule

III Notice of Information to those manufacturers in the country of re-

export and to importers so that they may be advised of restrictions on

vicuna products. At present, no countries are subject to a Schedule III

Notice of Information for all wildlife or all CITES-listed species.

For vicuna and vicuna products, there is no personal effects

exemption in the proposed special rule. That is, items purchased by

travelers overseas or personal items owned by people moving to the

United States will require appropriate CITES export documents (permits

or re-export certificates) to be imported legally into the United

States. This is based on analysis of the annotation for the vicuna in

the official CITES Secretariat list of the CITES Appendices, and

dialogue with the CITES Secretariat in Geneva. The vicuna annotations

in the CITES Appendices are unique, and require that only certain

products be exported from the range countries, under very strict

conditions. For Peru, for example, the only products that can be

exported (even non-commercially) are those manufactured from the

stockpile held at the time of the ninth meeting of the Conference of

the Parties, in November 1994, and they all require CITES Appendix II

export permits. In Argentina, for example, articles bought by a foreign

tourist at a government authorized store can be exported as personal

accompanying baggage only after a CITES export permit has been

obtained. In countries of re-export as well, very strict controls are

required. The items manufactured from vicuna wool are very expensive

luxury articles, and illegal trade poses a serious risk to the species

and the conservation programs of the range states. Furthermore, all

range countries require CITES permits for export of vicuna products,

and do not recognize any personal effects exemption. It would be

inappropriate and unfair to require export documents from range

countries but not from countries of manufacture (re-export). Therefore,

in this proposal, tourist souvenirs or other personal items require a

CITES export document from the country of export or re-export in order

to be legally imported into the United States.

All products must comply with all product annotations as described

in the CITES Secretariat's official annotated list of the CITES

Appendices. If those product annotations change at a future meeting of

the Conference of the Parties (COP) to CITES, the Service will have to

re-evaluate its 4(d) finding. The criteria for determining if a vicuna

product is properly identified are drawn from the CITES Appendices, and

the product annotations for vicuna contained therein. For cloth and

cloth products, the only products that can be imported are those where

the reverse side of cloth and cloth products bear the logo adopted by

countries signatory to the Conveno para la Conservacion y Manejo de la

Vicuna (Vicuna Convention), and the words ``VICUNA--(Country of

Origin)--ARTESANIA'' (country of origin is the name of the original

exporting country where the vicuna wool in the products originated,

either Argentina, Bolivia, Chile, or Peru). For finished vicuna

products (including luxury handicrafts and knitted articles) and any

bulk shipments of raw wool, the product or shipment must have a seal or

identification tag with codes describing the origin of the vicuna

product, the trademark or label (``VICUNA--(Country of Origin)--

ARTESANIA'') and the CITES export permit number. This proposed special

rule, and these criteria for properly identified vicuna products, are

derived from the CITES Appendices themselves. The product annotations

were proposed by the range countries and adopted by the CITES

Conference of the Parties. Therefore, we are proposing to align U.S.

importation practices with those approved by the CITES Parties, in

order to facilitate effective conservation of the vicuna in range

countries. In our judgment the protective regulations set out in the

proposed rule contain all of the measures that are necessary and

advisable to provide for the conservation of the vicuna in Argentina,

Bolivia, Chile, and Peru.

Public Comments Solicited

We intend that any action resulting from this proposal be as

effective as possible. Therefore, we are soliciting any comments or

suggestions from the public, other concerned governmental agencies, the

scientific community, the trade industry, or any other interested party

concerning any aspect of this proposal. We are particularly seeking

comments concerning biological or commercial trade impacts on any

vicuna population, or other relevant data concerning any threat (or

lack thereof) to the wild populations of vicuna in South America.

Final action on the proposed reclassification of the vicuna, and

the promulgation of the special rule will take into consideration the

comments and any additional information we receive. Such communications

may lead to adoption of final regulations that differ from those in the

proposed rule.

National Environmental Policy Act

We have determined that Environmental Assessments and Environmental

Impact Statements, as defined under the authority of the National

Environmental Policy Act of

[[Page 48756]]

1969, need not be prepared in connection with regulations adopted

pursuant to section 4(a) of the Endangered Species Act of 1973, as

amended. A notice outlining our reasons for this determination was

published in the Federal Register on October 25, 1983 (48 FR 49244).

Paperwork Reduction Act of 1995

This rule does not contain any new information collection

requirements under the Paperwork Reduction Act of 1995. The existing

OMB information collection control number is 1018-0012. An Agency may

not conduct or sponsor, and a person is not required to respond to a

collection of information unless it displays a currently valid OMB

control number. This rule does not alter that information collection

requirement.

Required Determinations

We invite comments on the anticipated direct and indirect costs and

benefits or cost savings associated with this proposed special rule,

for vicuna. In particular, we are interested in obtaining information

on any significant economic impact of the proposed special rule on

small public and private entities. Once we have reviewed the available

information, we will determine whether we need to prepare an initial

regulatory flexibility analysis for the special rule. We will make any

such analysis or determination available for public review. Then, we

will revise, as appropriate, and incorporate the information in the

final rule preamble and in the record of compliance (ROC) certifying

that the special rule complies with the various applicable statutory,

Executive Order, and Departmental Manual requirements. Under the

criteria in Executive Order 12866, the proposed special rule is not a

significant regulatory action subject to review by the Office of

Management and Budget.

References Cited

All personal communications mentioned below were received by Dr. Henry

L. Short, Amherst, Massachusetts, a contractor working for the National

Fish and Wildlife Foundation.

Canedi, A. A. 1997. pers. comm. Argentina responses to questions.

August 25, 1997.

Canedi, A. A. and P. S. Pasini. 1996. Repoblamiento y bioecologia de la

vicuna silvestre en la Provincia de Jujuy, Argentina. pp. 7-24 in

Animal Genetic Resources Information. United Nations Environment

Programme. Food and Agriculture Organization of the United Nations.

Rome.

CITES. 1997a. Proposal: Transfer of the vicuna (Vicugna vicugna)

population in the province of Jujuy (21 47'S-24 38'S; 64 80'W-67 19'W)

from Appendix I to Appendix II and of the populations in semi-captivity

in the provinces of Jujuy, Salta, Catamarca, La Rioja, and San Juan,

with the sole purpose of permitting international trade in wool fibre

from live vicuna, in cloth and manufactured products, under the

trademark ``VICUNA-ARGENTINA.'' Republic of Argentina.

CITES. 1997b. Proposal: Transfer of the populations (Vicugna vicugna)

of the Conservation Units: Mauri-Desaguadero (17 30'S-18 30'S and 68

30'W-69 30'W), Ulla Ulla (14 45'S-15 25''S and 69 00'W-69 20'W) and

Lipez-Chichas (21 30'S-23 00'S and 66 20'W-68 10''W) from CITES

Appendix I to Appendix II for the sole purpose of allowing

international trade of fabrics made with fiber from the shearing of

live animals under the trademark ``VICUNA-BOLIVIA.'' Republic of

Bolivia.

CNVB. 1996. Censo Nacional de la Vicuna en Bolivia: Gestion 1996.

Direccion Nacional de Conservacion de la Biodiversidad.

Comision Regional de la Vicuna. 1994. Acciones de las Provincias

Argentinas para su Conservacion y Uso Sustentable. Republica Argentina,

Salta. 25pp.

DNCB (Direccion Nacional de Conservacion de la Biodiversidad, Unidad de

Vida Silvestre). 1997. pers. comm. Bolivia responses to questions.

August 1997.

Galaz, J. 1997. pers. comm. August 1997.

Hoces, R.D. 1997. pers. comm. Peru responses to questions. September

1997.

INFOL. 1985. Memoria VI Reunion Ordinaria de la Comision Tecnico

Administradora del Convenio para la Conservacion de la Vicuna. La Paz,

Bolivia.

Nowak, R. N. 1991. Vicuna. pp. 1353-1357 in Walker's Mammals of the

World. Fifth edition. Volume II. The Johns Hopkins University Press.

Baltimore and London.

SAG (Servicio Agricola y Ganadero). 1997. pers. comm. Chile responses

to questions. August 22, 1997.

Wheeler, J.C., and D. Hoces R. 1997. Community participation,

sustainable use, and vicuna conservation in Peru. Mountain Research and

Development 17(3): 283-287.

List of Subjects in 50 CFR Part 17

Endangered and threatened species, Exports, Imports, Reporting and

recordkeeping requirements, Transportation.

Regulations Promulgation

Accordingly, the Service hereby proposes to amend part 17,

subchapter B of chapter I, title 50 of the Code of Federal Regulations,

as set forth below:

PART 17--[AMENDED]

1. The authority citation for part 17 continues to read as follows:

Authority: 16 U.S.C. 1361-1407; 16 U.S.C. 1531-1544; 16 U.S.C.

4201-4245; Pub. L. 99-625, 100 Stat. 3500, unless otherwise noted.

2. Section 17.11(h) is amended by revising the entry for the

vicuna, under ``Mammals'', on the list of Endangered and Threatened

Wildlife to read as follows:

Sec. 17.11 Endangered and threatened wildlife.

* * * * *

(h) * * *

--------------------------------------------------------------------------------------------------------------------------------------------------------

Species Vertebrate

-------------------------------------------------------- population where Critical Special

Historic range endangered or Status When listed habitat rules

Common name Scientific name threatened

--------------------------------------------------------------------------------------------------------------------------------------------------------

Mammals

* * * * * * *

Vicuna........................... Vicugna vicugna..... Argentina, Bolivia, Entire, except T 3, ____ NA 17.40 (k)

Chile, Ecuador, Ecuador.

Peru.

Do ......do ......do Ecuador............ E 3, ____ NA NA

* * * * * * *

--------------------------------------------------------------------------------------------------------------------------------------------------------

[[Page 48757]]

3. Paragraph (k) is added to Sec. 17.40 and reads as follows:

Sec. 17.40 Special rules--mammals.

* * * * *

(k) Vicuna (Vicugna vicugna)--(1) Prohibitions. All provisions of

Sec. 17.31 (a) and (b) and Sec. 17.32 of this part shall apply to

vicuna and vicuna products from both populations listed in Appendix I

of the Convention on International Trade in Endangered Species of Wild

Fauna and Flora (CITES) and the Appendix II semi-captive populations of

Catamarca, Jujuy, La Rioja, Salta, and San Juan Provinces in Argentina.

Except as provided in paragraph (k)(2) of this section, it is unlawful

for any person to commit, attempt to commit, solicit to commit, or

cause to be committed any acts described in paragraphs (k)(1)(i)-(ii)

of this section with vicuna from all other populations listed in

Appendix II of CITES:

(i) Import, export, and re-export.

(ii) Sell or offer for sale, deliver, receive, carry, transport, or

ship in interstate or foreign commerce in the course of a commercial

activity.

(2) Exceptions. The import, export, or re-export of, or interstate

or foreign commerce in vicuna products, consisting of either raw wool

or items and cloth made, or partially made, from vicuna wool, may be

allowed without a threatened species permit issued pursuant to 50 CFR

17.32 when the provisions in parts 13, 14, and 23 and the applicable

paragraphs set out below have been met:

(i) The vicuna product must comply with all CITES product

annotations as given in the CITES Secretariat's official list of the

CITES Appendices and found at 50 CFR 23.23, and be identified as

follows:

(A) Cloth and cloth products: The reverse side of cloth and cloth

products must bear the logo adopted by countries signatory to the

``Conveno para la Conservacion y Manejo de la Vicuna'', and the words

``VICUNA-(Country of Origin)-ARTESANIA'', where country of origin is

the name of the original exporting country where the vicuna wool in the

products originated.

(B) Finished vicuna products (including luxury handicrafts and

knitted articles) and any bulk shipments of raw wool: The product or

shipment must have a seal or identification tag with codes describing

the origin of the vicuna product, the trademark or label (``VICUNA-

(Country of Origin)-ARTESANIA'') and the CITES export permit number,

where country of origin is the name of the original exporting country

where the vicuna wool in the products originated.

(ii) The accompanying CITES permit or certificate must contain the

following information:

(A) The country of origin, its export permit number, and date of

issuance.

(B) If re-export, the country of re-export, its certificate number,

and date of issuance.

(C) If applicable, the country of last re-export, its certificate

number, and date of issuance.

(iii) At the time of import, for each shipment covered by this

exception, the country of origin and each country of re-export involved

in the trade of a particular shipment must not be subject to a Schedule

III Notice of Information pertaining to all wildlife or to all CITES-

listed wildlife that may prohibit or restrict imports. A listing of all

countries that are subject to such a Schedule III Notice of Information

will be available by writing: The Office of Management Authority, ARLSQ

Room 700, 4401 N. Fairfax Drive, U.S. Fish and Wildlife Service,

Arlington, Virginia, 22203.

(3) Notice of Information. Except in rare cases involving

extenuating circumstances that do not adversely affect the conservation

of the species, the Service will issue a Schedule III Notice of

Information that identifies a restriction on trade in specimens of

vicuna addressed in this paragraph (k) if any of the following criteria

are met:

(i) The country is listed in a Notification to the Parties by the

CITES Secretariat as lacking both designated Management and Scientific

Authorities that issue CITES documents or their equivalent.

(ii) The country is identified in any action adopted by the

Conference of the Parties to the Convention, the Convention's Standing

Committee, or in a Notification issued by the CITES Secretariat,

whereby Parties are asked to not accept shipments of specimens of any

CITES-listed species from the country in question.

Dated: August 23, 1999.

Donald J. Barry,

Assistant Secretary for Fish and Wildlife and Parks.

[FR Doc. 99-23333 Filed 9-7-99; 8:45 am]

BILLING CODE 4310-55-P

This is a copy of a public record, reproduced as it was published. It is not legal advice, and it may not be the version a court would rely on. Check the official source before you cite it.

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