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    "Garden Hunting" in the American TropicsAuthor(s): Olga F. LinaresSource: Human Ecology, Vol. 4, No. 4 (Oct., 1976), pp. 331-349Published by: SpringerStable URL: http://www.jstor.org/stable/4602380.

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    Human

    Ecology, Vol. 4, No. 4, 1976

    "Garden

    Hunting"

    n the American

    Tropics

    Olga

    F.

    Linares1

    Using faunal analysis,

    this article outlines a coastal mammalian

    harvestingpat-

    tern

    involving

    a

    few

    terrestrialmammals whose

    biomass

    appears

    to have

    been

    greater when associated with

    man

    than

    under "natural" onditions.

    Archeologi-

    cal

    evidence

    suggests

    that these animals

    fed regularly

    on

    cultivated

    crops

    and

    were hunted

    in

    house

    gardens

    and

    cultivated

    ields. By

    concentrating

    he

    supply

    of both

    carbohydrates

    and

    animal

    protein, "gardenhunting" may

    have

    elimi-

    nated

    seasonality and schedulingproblems.

    And

    because

    it

    artificially

    ncreased

    the

    biomass

    of selected

    animals,

    it

    may

    have

    functioned

    as

    a

    substitute

    for

    animal

    domestication.

    KEY

    WORDS: hunting;

    tropics; faunal collections; coastal

    settlements; prehistoric

    hunting.

    INTRODUCTION

    Students

    of tropical South

    American cultures often draw a

    distinction

    between

    societies located

    near important

    rivers

    and societies

    occupying "mar-

    ginal" habitats away from

    the mainstreams Sauer, 1958;

    Cameiro,

    1964, 1970;

    Lathrap,

    1968, 1970; Morey, 1970;

    Meggers,1971).

    Nonriverinegroupsare con-

    sidered to be

    agriculturally

    mpoverished,as well as

    committed, in the absence

    of

    fishing possibilities, to

    the permanent

    quest for easily depleted

    terrestrial

    and

    arborealgame. Low

    population densities, small

    group size, settlement dis-

    persal, and

    constant

    movement are thought to result

    from this mode of life

    (Carneiro,

    1970).

    All

    nonriverine

    peoples were not, however,

    necessarilyequally restricted.

    NumerousIndiangroups

    were encounteredby the first

    Europeanexplorersalong

    both

    American seacoasts,

    but

    these have

    been

    discounted or ignored in the

    literature, possibly because

    these groups were rapidly

    decimated (see

    Sauer,

    1966).

    Yet

    archeologists

    have

    repeatedly

    shown

    that coastal settlements

    flou-

    Smithsonian

    Tropical Research Institute, P.O.

    Box 2072, Balboa, Panama Canal

    Zone.

    331

    i

    1976

    Plenum

    Publishing

    Corporation,

    227

    West

    17th

    Street,

    New

    York,

    N.Y.

    10011.

    No

    part

    of

    this

    publication

    may

    be

    reproduced,

    stored

    in

    a retrieval

    system,

    or

    transmitted,

    In

    any

    form or

    by any means, electronic,

    mechanical, photocopying, microfilming,

    recording,

    or

    otherwise,

    without written

    permission

    of

    the

    publisher.

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    332

    Linares

    rished in the tropics from at least 3000 B.C. onward.The subsistencesystem of

    these

    settlements must have been

    very different from those of inland groups. In

    fact, terrestrialhunting among these groupstended not toward a broad-spectrum

    "many species taken" adaptation

    but rather toward greaterspecialization and

    selectivity. A prehistoric example of selective hunting by otherwise maritime

    groups has been described by Coe and Flannery (1964), while Nietschmann

    (1973) has discussed hunting among the present-day turtle-fishing Miskito

    Indiansof coastal Nicaragua.

    The

    garden-hunting attern

    I

    describe here from a site called CerroBrujo

    in Bocas del Toro province,Panama, s also a specialized one and selectivity is

    indicated by the archeologicalremains. Rather than resembling ropical forest

    hunting, with its particular technology, its belief system, and male-oriented

    trekking activities(Siskind, 1973;

    Murphyand Murphy,1974), this game-procure-

    ment system was more akin to

    harvestingvegetable products and maritime re-

    sources.

    The

    contrast

    between

    animalbiomassunder naturalconditions and biomass

    under

    gardenhunting

    s

    marked.

    Shiftingcultivation, especially of cultivated root

    crops, affects the'biomassof

    terrestrialmammals

    hat are

    behaviorallypreadapted

    to

    becoming

    commensalsof man.

    As a kind of mammalian"tending pattern," garden hunting may have

    taken the

    place of

    animal

    domestication

    n

    parts

    of the New World

    ropics.

    Both

    patterns

    result in the

    substitution

    of

    culturally

    created for

    naturally existing

    mammalian

    biomasses.

    Even

    now, after

    the

    introduction of bamyard animals

    and

    cash

    crops, garden hunting

    remains

    a

    widespread

    and

    important practice.

    THE

    SETTING

    Bocas

    del

    Toro

    (hereafter designated

    as

    Bocas)

    is

    a

    long

    and

    narrow

    prov-

    ince located on the northwest

    sector of the Isthmus of

    Panama, facing

    the

    CaribbeanSea or Atlantic

    Ocean

    (Fig. 1). Climatically,

    Bocas

    is

    wet

    (The

    Af

    tropics

    in

    Koppen's

    classification),

    with two

    very short, relatively dry

    seasons.

    The mean annual rainfall

    averaged

    or

    5

    years

    is 3703

    mm

    (about

    148

    inches),

    with

    little seasonal variation and

    with most

    precipitation falling

    at

    night,

    thus

    limiting transpiration.

    Topographically,

    Bocas

    is

    characterized

    by low, rolling

    hills

    and

    ridges

    that extend to

    the water's

    edge.

    There

    are neither broad coastal

    plains

    nor

    many

    beaches.

    The

    archeological

    site of Cerro

    Brujo

    is found toward the

    tip

    of the

    small

    Aguacate Peninsula,away from majorriversbut accessibleto two lagoons (Fig.

    2).

    The

    "community pattern" represented

    is

    that

    of a

    dispersed

    hamlet

    con-

    sisting

    of

    four

    localities marked

    by

    shell-midden lusters.

    Within he

    hamlet

    unit,

    the localities

    nearest each other

    were 300 m

    apart;

    the

    two

    most

    distant

    were

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    "Garden Hunting" in the American Tropics 333

    T3

    cr

    96

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    C4

    'S E

    'S 0

    7 =

    E

    w

    < < M

    'IT

    Z

    3c

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    334

    Linares

    Fig.

    2.

    Looking

    into

    Almirante

    Bay

    from a

    ridge

    on the

    Aguacate

    Peninsula.

    800 m

    apart.

    We

    have calculated

    the adult residential

    population

    at Cerro

    Brujo

    as

    approximately

    25

    persons

    (Linares

    and

    Ranere, 1971;

    Linares,

    1970).

    The

    principal

    biotopes

    utilized

    by

    the Cerro

    Brujo

    and other

    Aguacate

    inhabitants

    an be listed as

    follows:

    1.

    Terrestrial

    biotopes: (1) Ridgetops

    between the 80

    and

    140 m

    contours

    were used for

    habitation

    and

    possibly

    for small kitchen

    gardens

    and

    tree

    crops.

    (b)

    The

    40 and

    80 m

    contour was

    probably

    used for

    swidden

    fields.

    (c)

    Streams

    flowingthrough

    the

    base of the

    ridgesprovided

    the

    only sourceof freshwaterand wereprobablyfavoritespots for garden-

    ing

    and

    hunting. (d) Low-lying

    swamps

    are

    used

    nowadays

    to collect

    crabs and to

    gatherpalmproducts.

    These are difficult

    areas o

    traverse.

    2.

    Littoral or marine

    biotopes:

    (a)

    Mangrove tands and mud flats

    fringing

    the shore were

    used for

    gathering

    wo

    species

    of

    Ostrea,

    two

    species

    of

    Arca,

    and a

    species

    of

    d7ama.

    This

    is

    also

    the

    natural

    habitatof

    the

    caiman,

    which was

    occasionally

    hunted.

    (b)

    From shoreline to

    about

    2

    fathoms,

    or

    approximately

    4

    m,

    are

    coral

    outcrops,

    barrier

    eefs,and

    other habitats where most inshore

    fishing

    took

    place.

    (c)

    Offshore

    beyond

    2

    fathoms

    are

    found

    largerpelagic

    fish,

    most of

    which were

    not

    taken, suggestingthat the open sea was mostly used for green turtle

    fishing

    and for

    transportation.

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    "Garden

    Hunting" n the AmericanTropics

    335

    The bulk of the cultural materials excavated at Cerro Brujo came from

    two main

    midden clusters

    (Fig. 3), representinga brief

    occupation.

    Five

    radio-

    carbon

    estimates

    fall

    between A.D.

    960 and A.D. 985.

    A

    20-30

    year occupa-

    tion accordswell with the time

    span

    of a

    contemporaryGuaymi

    hamlet.

    Close similaritiesexist between the

    oldest of the

    CerroBrujoartifacts

    and

    those

    from a number of sites in the

    neighboringhighlands

    of

    Chiriquiprovince

    (see Linareset al.,

    1975).

    I

    have suggested

    elsewhere

    Linares,

    n

    press)

    that the

    Cerro Brujo

    inhabitantsmigrated to their

    peninsular

    setting

    from landlocked

    interiorhabitats.This

    hypothesis

    is

    corroboratedby

    the absence of molluscs

    in

    the

    oldest

    levels, as

    well

    as by the close

    chronological

    and

    spatial overlaps.

    A thorough surveyof the Aguacate Peninsula n 1973 revealedonly three

    additional archeological

    sites. These resemble Cerro

    Brujo

    in

    size, layout, and

    chronology

    (Fig. 4).

    Each

    site

    was made

    up

    of

    several

    dwelling ocalities,marked

    by shell-midden

    efuse

    deposits,

    found within an area

    1.5-2

    km in

    diameter.

    Since

    each

    loose

    cluster

    of

    localities was separated rom

    similar

    units

    by tractsof un-

    inhabited

    territory, I am assuming hat

    eachcorresponded o a

    dispersedhamlet

    (what

    Young, 1971, calls

    a caseri'o

    among the modernGuaymi

    who inhabit this

    area).

    These

    ancient

    hamlets

    were

    usually located on the highest

    ridges of the

    Aguacate

    Peninsula,at spots with both

    lagoons in view. Population

    densities over

    the

    entire

    peninsula at

    A.D. 900 can

    be roughly estimated as no

    more than 3

    personspersquarekilometer.

    Fig. 3.

    Aerial

    photograph

    of

    the

    principal

    Cerro

    Brujo

    shell-midden cluster in process of

    excavation.

    (Lower

    trench is 10

    by

    6.5

    m.)

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    336

    Linares

    (CA-1,-2, -4).

    Except for

    a

    deforested zone along the only major alluvial areas n

    Bocas

    (the Changuinola-Sixaola n the west and the Cricamolaon the east), the prov-

    ince presentsa mosaic of small clearings n the midst of extensive forested

    tracts.

    The vegetation

    is typically a "dense growth of large, predominantlybroad-leaf

    evergreen, rees" (Gordon, 1969: 5) mixed with a few deciduousspecies. Before

    proceeding, we must consider in some detail whether the ecology of the

    area

    today is similar to that of late pre-Columbian imes. (For places referred o in

    this discussion,see Fig. 1.)

    Scholars have argued quite persuasively that much of the New

    World

    tropics was heavily populated and extensively cultivated in late prehistoric

    times (Gordon, 1957; Sauer, 1966; Dobyns, 1966; Bennett, 1964;

    Lathrap,

    1970). Some areas, however, were not, and the interfiuvial zone

    bordering

    AlmiranteBay, including the Aguacate

    Peninsula, eems to have been one of the

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    "Garden

    Hunting"

    in the American

    Tropics

    337

    relatively undisturbed regions.2 Given the limitations of the early Spanish des-

    criptions of Panama (Howe, 1974:

    12-18; Young, 1970), we must

    turn

    to

    archeology for evidence

    of

    population

    distribution and

    man-inducedvegeta-

    tional changes

    at the time of occupation

    of

    the

    Bocas sites.

    The shell mounds of Almirante

    Bay

    and

    Chiriqui Lagoon

    were first

    de-

    scribed by

    Gordon

    (1961),

    who

    concludes,

    in a later

    publication,

    that the

    "shell

    collectors must have

    been

    numerous

    .

    ."

    (Gordon,

    1969:

    67). Although

    Gordon'sdescriptionof the Bocas environment

    s

    invaluable,his archeological

    interpretationsmay be misleading.Most of the

    shell-middensdescribed

    Gordon,

    1961: map 2;

    1969: map 4, p. 68) are very small. They are not to be taken as

    archeological "sites" (i.e., hamlet

    clusters

    in

    this

    context),

    but

    as

    dwelling

    localities or garbagedumps, to be exact-some of them

    associatedwith at most

    a

    single house. (Thus, while Gordon's

    map

    indicates nine "sites" in

    Aguacate

    Peninsula, our

    survey shows only four

    dispersed hamlets.) Furthermore, hese

    localities were

    probablyoccupied only for

    a

    short time. Incidentally, n the

    years

    between our

    excavations

    of

    Cerro Brujo and

    a

    systematic survey

    of

    Aguacate

    Peninsula, the

    Guaymi Indian family

    living

    in

    the vicinity of our site, much in

    the manner of

    their ancestors (Linares, 1970),

    has

    shifted residence

    twice,

    abandoningan old

    house and building two

    new

    structures.

    All

    this has

    taken

    place in 3 years, within a radius of less than 1 km, and is a normalprocedure

    in the

    developmental cycle of the Guaymi

    domestic group (Young, 1971).

    There is

    little evidence, then, that

    in

    the

    late

    prehistoricperiod

    Almirante

    Bay or its

    immediate vicinity was much

    more heavily populated or disturbed

    by

    man than

    it

    is

    now.

    This

    impression

    is

    strengthenedby

    the

    palynological

    record.

    None of

    the

    18

    samples prepared or

    analysis

    rom one of the

    two cores

    collected

    from

    freshwater

    bogs

    about

    100 m from

    the Cerro

    Brujo

    hamlet con-

    tained pollen of

    agriculturalplants:

    "Pollens

    which may indicate

    disturbance,

    cheno-ams,

    composites, Cecropia sp.

    and

    grasses

    are rare in the

    samples

    ex-

    amined ....

    With a cursory look such as this it appears that there is

    no record

    of forest disturbanceby man in the CoreCBII" (West, n.d.: 1), or at least no

    record of major

    disturbances ver a long period of time.

    THE

    CERRO

    BRUJO

    FAUNA: SOMECULTURAL NFERENCES

    Over 6000 mammal bones

    were

    recovered

    from

    the

    shell-containing

    (i.e., more recent) of the two occupations

    at

    the Cerro

    Brujo site. These, plus

    other

    animal

    bones,

    make

    up

    15,000

    specimens altogether. Grayson

    (1973)

    has

    2A

    careful reading of Fernando Colon's

    account of

    his

    father's

    fourth

    voyage in

    1502 (re-

    produced

    in

    Lothrop,

    1950: 3-7) conflrms

    this point. Although

    he mentions

    encounter-

    ing Indians in

    Almirante Bay, the only

    places where

    he

    talks about

    towns and many

    peoples

    are in

    Catiba, Zobrare, etc.

    These places are

    about 200 km to

    the

    east

    of Almirante

    Bay,

    in

    northern

    Veraguas province.

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    338

    Linares

    classified the mammals nto 1437 identifiablespecimensbelongingto 14 species

    (excluding man) and then calculated

    the "minimumnumbers of individuals"of

    each species. Keeping in mind that

    there are difficulties with this method,3 we

    can pi ceed with our analysis.

    Table

    I

    suggests

    that the Cerro

    Brujo nhabitants

    had strong hunting preferences

    for

    certain species. Agouti (Dasyprocta punc-

    tata), paca (Cuniculus paca),

    and nine-banded armadillo

    (Dasypus

    novem-

    cintus) together constitute 80.9%

    of all

    animals aken. Four argespecies-collared

    peccary

    (Tayassu

    tajacu), white-lipped

    peccary

    (Tayassu

    pecari),

    white-tailed

    deer

    (Odocoileus virginianus),

    brocket

    deer

    (Mazama mericana)-are less impor-

    tant, amounting o 10.1%of the total. The rats (Sigmodon,Oryzomys,Hoplomys)

    and the

    opossums (Caluromys,

    Marmosa)together add up to only 6.8% of the

    total

    number

    of minimum

    individual

    mammals.The manatee (Trichechus

    man-

    atus), an aquaticmammal, s only 1.9%of the total.4

    Table

    I

    may convey

    the

    impression

    that

    small

    mammalswere

    the

    only im-

    portant components of the Cerro

    Brujo diet; however, any such impression s

    dispelled

    if

    we convert

    these

    values

    to

    butchered

    weights (Table II) and

    add up

    the

    values for

    the

    samespecies

    as

    grouped

    above.Conversion o butcheredweights

    changes

    the

    percentages

    onsiderably,

    and

    t is

    obvious

    that in

    reckoning

    "cultural

    importance"both measuresare

    needed to drawconclusions.5 The two methods

    become more disparatewhen the smaller (or the larger)animalsare compared.

    This

    is

    exaggerated

    n

    the case

    of

    agoutisand manatees.

    Both of these animals

    were

    probably equal in importance:

    the

    caviomorph

    rodents

    (agouti

    and

    paca)

    were

    important

    for

    regular

    consumption

    and the manatee for intermittentcon-

    sumption.

    Whether

    heir

    combined

    presence

    is

    calculated

    in

    individual

    numbers

    'The

    minimum

    numbers

    method

    (MNI

    for short) determines

    the

    necessary

    number

    of

    in-

    dividuals

    of a

    species

    accounting

    for all

    identical

    bone

    elements

    found

    in a

    given

    collec-

    tion.

    Using

    the Cerro

    Brujo

    fauna, Grayson (1973)

    demonstrated

    that

    the

    MNIs

    vary

    significantly

    depending

    on the

    analytic units

    used

    for

    the calculations.

    He

    compared

    MNIs

    calculated

    on the basis

    of single excavation

    strata

    with

    MNIs

    calculated

    on the

    basis

    of

    the

    whole site. Neither of these alternatives is entirely satisfactory. Therefore, White (n.d.),

    at my

    request,

    reanalyzed

    the Cerro

    Brujo fauna

    and calculated

    MNIs

    on the basis

    of

    nine

    "features"

    representing

    activity loci

    within

    a dwelling locality.

    As expected,

    he came

    out

    with

    more

    accurate

    values,

    halfway

    between

    those

    obtained

    by Grayson.

    Nonetheless,

    since both

    methods

    yielded

    a

    similar rank

    order

    for

    the most

    important

    species,

    I

    have

    used Grayson's

    MNI

    figures

    based

    on the

    single

    strata distinctions

    because

    these

    figures

    are

    published,

    and because

    I

    consider

    them to be the less distorting

    of

    the alternatives

    he

    presents.

    Skeptics

    should keep

    in mind

    that differential

    bone

    preservation,

    distribution,

    and

    destruction,

    to say

    nothing

    about differences

    in

    cultural practices

    (hunting

    techniques,

    taboos,

    food

    preferences),

    necessarily

    affect a-ll

    faunal analysis-as

    indeed they

    affect

    all

    kinds

    of prehistoric

    reconstructions.

    4R. White (n.d.)

    recalculated

    the

    percentages

    for

    each of these species

    clusters

    as (a) 7

    3.8%;

    (b)

    16.8%;

    (c)

    7.4%; (d)

    0.9%.

    He

    is also

    of

    the

    opinion

    that, of the two,

    only

    the collared

    peccary was present in the Cerro Brujo fauna. This strengthens the thesis of this article.

    5White

    (n.d.)

    would

    rank

    the

    most important

    species

    by

    butchered

    weight in

    the

    following

    order

    of

    decreasing

    mportance:

    Tayassu,

    Odocoileus,

    Cuniculus,

    Trichechus,

    Dasyprocta,

    and Dasypus.

    This rank

    order strengthens

    the argument

    that

    small mammals

    were

    not the

    only

    ones

    taken

    by

    the

    Cerro Brujo group.

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    "Garden Hunting" in the American Tropics

    339

    Table I. List

    of

    Mammals Hunted by

    the

    Prehistoric Cerro Brujo Inhabitantsa

    Number of Minimum

    Species English name specimens

    numbers Percent

    Dasyproctapunctata Agouti

    822

    204 43.8

    Cuniculus aca Paca

    224

    104 22.3

    Dasypusnovemcintus

    Nine-banded armadillo

    186

    69 14.8

    Tayassu ajacu Collared peccary

    94

    27 05.8

    Sigmodon Cotton rat

    28

    16 03.4

    Odocoileusvirginianus

    White-tailed

    deer

    20

    14

    03.0

    Oryzomys

    Rice rat 16 11 02.4

    Tayassu

    ecari

    White-lipped peccary 15 4 00.9

    Hoplomys Armored rat

    8

    3 00.6

    Didelphis narsupialis Opossum

    5

    1 00.2

    Mazama mericana

    Brocket deer

    3 2

    00.4

    Caluromys Woolly opossum

    2

    1

    00.2

    Marmosa Mouse opossum 1 1 00.2

    Trichechusmanatus Manatee 13 9 01.9

    Total 1437 466

    aAdapted

    from

    Grayson (1973:

    Table

    2, p. 436).

    Table

    II.

    Comparison

    of the Minimum Number

    of

    Individualsa

    with the Butchered

    Weight

    of the

    Most

    Important

    Mammals

    at Cerro

    Brujo

    Minimum

    Butchered

    weights

    number

    of

    Species

    individualsb

    Kilograms

    Pounds

    Percent

    of

    total

    Agouti

    43.8 556

    1224

    16.7

    Paca 22.3 709 1560 21.3

    Nine-banded armadillo

    14.8 219 483 06.6

    Collared

    peccary

    5.8 490 1080

    14.8

    Cotton rat

    3.4 4.09 9 0.12

    White-tailed

    deer 3.0

    382 840

    11.5

    Rice rat

    2.4 1

    2.4

    0.06

    White-lipped peccary

    0.9 91

    200

    2.73

    Opossum

    0.2 9

    90 0.27

    Woolly opossum

    0.2

    3.6

    8

    0.10

    Mouse

    opossum

    0.2

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    340

    Linares

    Table

    III.

    Comparison

    of the Butchered

    Weights (i.e., meat

    without bones) of the

    Terrestrial Fauna

    Hunted

    by

    the Cerro

    Brujo

    Inhabitantsa with the

    Fauna

    Hunted

    by

    the Miskito Indians

    of

    Nicaraguab

    and the

    Bayano

    Cuna Indians of

    PanamaC

    Cerro Brujo Miskito area

    Bayano Cuna

    Species

    hunted

    (20-year span) (1-year sample) (14-day sample)

    Agouti 16.7 Insignificant

    Agouti

    Nine-banded

    armadillo 06.6 Not mentioned

    Insignificant

    Paca 21.3 Insignificant Paca

    Manatee 24.6 1.5%

    (Not here)

    Collared peccary 14.8 0.61% Collared peccary

    White-tailed deer 11.50 45.0% Not important

    White-lipped peccary 2.73 50.0%

    White-lipped peccary

    Brocket deer

    1.09

    0.30% Brocket deer

    Tapir

    None

    2.0%

    Tapir, plus

    two kinds

    of

    monkeys, coati,

    tree

    squirrels

    aValues

    expressed

    as

    percentage

    of

    total butchered

    weights

    of

    all minimum

    number

    of

    individuals

    of

    all

    species

    in

    the

    collection.

    bData

    adapted

    from Nietschmann

    (1973:

    Tables

    1

    and

    2).

    CData adapted from

    Bennett

    (1962: Table 6, p. 42).

    (1.3%) or in butchered weights (3.9%), deep-forest

    species such as the brocket

    deer and the

    white-lippedpeccary

    are seen

    to have been

    insignificant.

    A

    further

    comparison

    can be

    made

    (Table III)

    between the butchered

    weights

    in the

    Cerro

    Brujo

    mammal

    sample

    and the

    butchered

    weights given

    for the same

    species

    hunted

    by

    the

    coastal

    Tasbapauni

    Miskito

    Indiansof eastern

    Nicaragua (Nietschmann, 1973;

    I

    have

    extrapolated

    the

    information from his

    Tables 21 and

    22).

    The

    last column

    in

    Table

    III of this

    article

    simply

    lists the

    terrestrialmammals

    hunted

    by

    the

    mainland,noncoastal,

    Bayano

    Cuna of

    eastern

    Panama Bennett, 1962: Table 6, p. 42). Although few hard

    and fast

    conclusions

    can be drawn from Table III, the comparativedata do support the idea that

    Cerro

    Brujo

    inhabitants

    harvested a different

    proportion

    of

    a faunal

    community

    than

    did

    the other

    groups.

    The abundant

    species

    at

    Cerro

    Brujo

    are of

    little

    im-

    portance

    to

    the

    Miskito

    Indians.In

    turn,

    the

    Bayano

    Cuna

    regularly

    hunt

    a

    num-

    ber of additionalmammalian

    pecies.

    To

    summarize,hunting among

    each

    of

    these three

    peoples,

    the

    Bayano

    Cuna,

    the

    Miskito

    Indians,

    and the

    prehistoric

    Cerro

    Brujo group,

    differs

    greatly.

    The

    Bayano

    Cuna

    exploit

    the

    high canopy,

    as well as the

    deep forest,

    for

    game.

    On

    the

    other

    hand,

    the

    coastal

    Tasbapauni Miskito are maritime

    exploiters,

    partly

    as a result of

    the

    commercial

    demand

    for turtles.

    Although they

    hunt

    a number

    of

    other

    species, they

    focus

    on

    only

    two

    large

    terrestrialmammals

    (the white-lipped peccary

    and the

    white-tailed deer),

    which they track inland

    during

    a

    specified

    season. In

    the

    Cerro

    Brujo case,

    a

    considerable

    amount of

    game

    was

    provided by

    six

    species (Table III),

    but

    only

    three

    species

    were

    regu-

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    "Garden

    Hunting

    in the American

    Tropics

    341

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    342

    Linares

    larly caught

    (see Table I). An idea of just how

    much terrestrialgame was being

    taken is provided

    by the next comparison.

    Faunal

    assemblages rom archeological

    sites are assumed by faunal ana-

    lysts to represent

    the products of cultural selection

    -

    samples that are biased

    under human hunting pressures.

    Rarely, however, has anyone

    attempted to

    measure just

    how far a cultural faunal assemblage

    departs from

    "normal" spe-

    cies

    distributions

    n

    undisturbedhabitats.

    In the

    present case,

    we

    can rearrange

    the data on

    Table I and calculate

    the biomassof the terrestrial

    animals in the

    Cerro Brujo collection.6 This

    procedure may

    facilitate comparisonbetween

    a

    "cultural faunal assemblage"and the same assemblage n two "natural," i.e.,

    undisturbed,

    habitats(Table IV).

    Table

    IV

    suggests

    that

    the

    biomass

    for

    every species represented

    in the

    collection

    is

    significantlyhigher

    in

    our site than

    is their

    biomass in

    nature. The

    propositionmay be entertained

    that the product of 20 years

    of casual hunting

    is somehow equivalent to having

    recovered

    a complete sample of

    all

    the indi-

    vidual animals

    of a certain species

    found in each of two "natural"

    habitats at

    any one point

    in time. This proposition

    is

    obviously very difficult

    to test. None-

    theless, Table

    IV givesus some relative dea of

    "cultural"vs. "natural"biomass:

    (1) The percentage biomasses

    of

    the three

    most common species

    in our Cerro

    Brujo collection (agouti, paca, and armadillo) together amount to 52.9% of

    the

    total.

    In

    the

    Surinam

    situation,

    the

    figure

    for the same

    species

    is

    12.7%.

    In

    BarroColorado Island (BCI) it

    is

    19.4%,

    assuming hat

    the

    biomass

    for

    Dasypus

    is

    more

    or

    less

    the same as

    in

    Surinam.

    (2)

    The

    collared

    peccary

    alone

    accounts

    for

    21.68%

    of the Cerro Brujo biomass,

    while it

    is

    only 3.5%

    of

    the total

    in

    Surinam and

    3.5%

    in

    BCI. (3)

    The

    biomass

    of white-tailed

    deer at Cerro

    Brujo

    was much higher

    than at

    BCI

    (compare

    19.5

    5%

    with

    0.6%).

    If

    we

    now take into consideration

    the full data

    presented

    by Eisenberg

    and

    Thorington

    (1973)

    for all

    terrestrialand

    arborealmammalian

    species (the

    bats

    excepted)

    in Surinam

    and

    BCI,

    and

    compare

    these with those

    for our

    faunal

    collection

    of

    mammals,

    we see that

    at those two

    localities

    not one of

    the

    most dominant mammals

    in

    terms

    of

    biomass) appears

    n our

    collections.

    This

    suggests

    that

    the Cerro

    Brujopeople

    were

    being extremely selective,

    or that

    they

    did not

    develop appropriatehunting techniques.

    They

    seem

    to

    have been

    ignor-

    ing many

    of tl'e

    following

    common

    animals:

    (1)

    the two-toed sloth

    (Choleopus

    sp.)

    and

    the three-toed

    sloth

    (Bradypus sp.); (2) monkeys

    of

    several

    genera

    (Cebus,Ateles, Alouatta,

    etc.); (3) tapir (Tapirus sp.); (4)

    the

    spiny

    rat

    (Pro-

    echimys sp.),

    one

    of the most

    abundant

    of the New World

    tropical

    rodents

    'I have used

    Eisenberg

    and Thorington's 1973) method for calculatingbiomass. This in-

    volved multiplying the numbersof individualanimalsby the live weight of an "average"

    adult specimen and

    then

    calculating he percentage

    biomass of each

    species

    in

    the

    Cerro

    Brujo collection. The difficulties with using average-weights re illustratedby

    the

    fact

    that Eisenbergand Thorington(1973: Table 1, p. 152) and Nietschmann 1973: Table

    20, p. 165) presentslightlydifferent ive weightsfor the samespecies.

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    "Garden

    Hunting"

    in

    the

    American

    Tropics

    343

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    344 Linares

    (Gliwicz, 1973); (5)

    the

    coati (Nasua sp.),

    as

    well as

    squirrels Sciuridae)

    and

    raccoon (Procyon).

    The absence of these

    animals n our collection cannot be due

    to

    simple

    deforestation or

    game depletion. As

    I

    have

    indicated,

    one

    must

    assume

    that the land was at least as

    forested

    then as it is

    now. Furthermore, ome

    of

    these animals,e.g., coatis, would

    have

    flourished n

    second growth.

    By compiling

    a

    list of

    the main

    behavioral

    traits of terrestrial

    mammals

    appearing n our

    Cerro Brujo collection (Table V), and consideringthe

    habits

    and

    habitats

    of

    the

    mammals

    that

    do

    not

    appear n the refuse

    of

    this site, we

    can see two

    things.

    The most

    abundant animals

    present

    are either smallish

    ani-

    mals that live in the underbrushor in burrows, often in the vicinity of encamp-

    ments or

    recently cleared

    fields

    (the caviomorphrodent and armadillo),or

    larger

    forms

    that

    are not too

    shy

    and live

    -

    or

    can

    live

    -

    in

    forest-edgeconditions (the

    collared

    peccary

    and the white-tailed

    deer).

    The mammals

    missingaltogether

    or

    poorly represented

    are

    either

    those that inhabit

    the

    high canopy (monkeys,

    sloths)

    or

    those

    that

    are fast

    climbers coatis,

    squirrels)

    or

    those

    that

    are

    veryshy

    and

    live in forested conditions

    away

    from man

    (the brocket

    deer and

    the

    tapir).

    In short, althoughlargeforest tractsmust have existed

    in Bocas

    at that

    time, the

    Table

    VI.

    List

    of

    Fish, Amphibians, and

    Reptiles from Cerro Brujoa

    Minimum

    Species Colloquial name numbers Percentage

    Megalops-Albula Tarpon 6 2.2

    Belonidae Needlefish

    7 2.6

    Centropomus

    Snook

    53 19.3

    Serranidae

    Grouper (sea bass)

    53 19.3

    Carangidae

    Jack

    21

    7.7

    Lutjanus

    Snapper 38

    13.9

    Haemulon Grunt

    10 3.6

    Sparidae Porgies

    3

    1.1

    Sciaenidae Drums (corvina) 1 0.4

    Sparus

    sp.

    Parrotfish

    4

    1.5

    Eleotridae Gobies 3

    1.1

    Kyphosus

    Rudderfish 1

    0.4

    Sphyraena

    Barracuda 6 2.2

    Diodontidae

    Porcupine

    fish

    16

    5.8

    Rays Rays

    5

    1.8

    Sharks Sharks

    2

    0.7

    Anuran

    Frogs

    7

    2.6

    Crocodilian Caiman

    5

    1.8

    Geoemyda Forest turtle 1 0.4

    Chelonidae

    Sea turtle 19

    6.9

    aAdapted

    from a list

    by Wing (n.d.).

    The minimum number of in-

    dividuals

    is

    given only

    for the

    most recent of

    the

    two

    occupations.

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    "Garden Hunting" in the

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    CerroBrujo inhabitants were concentrating on species that live in forest-edge

    conditions

    and

    readily nvademan-made

    learings.

    Evidence

    supporting he idea

    that

    this

    specializationwas

    facilitatedby the

    presence of alternativeprotein sources from

    the sea

    is

    given in Table VI.

    The

    total

    minimum

    number

    of individual

    ish, reptiles,

    and

    amphibians

    n Table

    VI,

    having

    been

    calculated

    on

    a

    differentbasis from

    that of

    Grayson

    1973), although

    on

    the same basis as that of

    White

    (see

    footnote

    4), appears

    o be smaller

    han

    that

    of mammals.But marine

    fishing

    may

    have been

    even

    more

    important

    han

    terrestrialhunting (White and

    Wing, personal

    communications).

    In

    fact, Cerro

    Brujo people were capable of

    taking

    in

    large, and sometimes

    dangerous,

    aquatic

    organisms.Themost common ediblespeciesin TableVI (Centropomus, erranid,

    carangid,

    Lutianus) also grow very

    large. Missing

    from

    the collection are

    the

    open-water

    pelagic

    fish that

    swim

    rapidly,

    such

    as

    the

    tuna

    and the

    mackerel.

    The

    mostcommon

    fish

    species

    n

    the collection occur nshore

    and can be

    harvested

    with traps and

    spears. Such harvesting

    accords well

    with the absence of all fish-

    hooks and net

    weights

    in

    the Cerro

    Brujo deposits.

    If

    trapsand

    spearswere

    the

    most

    common

    fishing gear employed

    (WingandRubinoff,

    personalcommunica-

    tions),

    then the

    techniquesemployed for

    getting

    protein

    on land and

    in

    the

    sea

    were

    probably

    much the same. It is

    also important to note the

    scarcity of

    birds

    in

    our

    collection (less than

    20 bones; Grayson,

    personal

    communication)and

    the

    total

    absence

    of

    arboreal

    reptiles

    such

    as

    iguanas

    and lizards

    (Rand, personal

    communication).

    CONCLUSIONS

    For

    inferringman-induced

    vegetational

    changes in the areas

    around the

    Cerro Brujo encampment, and

    reconstructing

    huntingpractices,

    we

    can contrast

    mammalian

    pairs

    ound

    in

    our collection

    (see Fig.

    5).

    In

    the

    tropics,

    as

    elsewhere,

    speciesof the samefamily haveevolvedcontrastingmorphologiesand/orbehavior

    and

    occupy

    different ecological

    niches.

    Comparing

    the

    popularity

    of related

    species n the

    collections

    is

    a usefulmethod

    for

    inferringpast

    conditions:

    1.

    The

    white-lipped vs. the collared

    peccary:

    The

    first does not

    occur

    (White, personal

    communication),

    or

    occurs

    in

    very

    small numbers

    (Grayson, 1973),

    in our collection.

    The reason for this

    may be

    that

    the

    white-lipped(although

    it travels

    in

    huge

    packs)

    is also

    more

    dangerous,

    especially

    to

    hunters

    without

    guns,

    and

    cannot be

    caught

    in

    traps.

    Further, a pack

    needs a largehome range

    andprobablya large

    forest.

    In

    contrast, the

    collared peccary

    travels

    n small

    packs,

    is more

    peaceful,

    needs

    smaller

    territories,

    and

    is

    used to

    living

    n

    disturbedconditions. It

    readily

    eats

    cultivated

    crops.

    Collared

    peccariesalso do well

    as semi-

    domesticates

    of man.

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    346

    Linares

    B

    G

    Fig.

    5. Most

    important

    mammal

    ter-

    restrial

    species

    at

    Cerro

    Brujo.

    (A)

    Mazama

    americana

    (brocket

    deer);

    (B)

    Dasyproctapunctata

    agouti);

    (C)

    Cuniculus

    paca

    (paca);

    (D)

    Dasypus

    novemcintus

    nine-banded

    armadillo);

    (E)

    Tayassu ajacu

    collared peccary);

    (F)

    Tayassu

    ecani

    (white-lipped

    pec-

    cary);

    (G)

    Odocoileus

    virginianus

    (white-tailed deer).

    Drawings

    by

    M.

    H.

    Moynihan.

    F

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    "Garden Hunting" in the

    American

    Tropics

    347

    2. White-tailed

    deer vs. the brocket deer:

    The open brush and grassland

    species (Odocoileus)

    was almost

    seven

    timesmore

    popular

    at CerroBrujo

    than the small, crepuscular,

    olitary, shy, forest-dwelling

    brocket

    deer

    (Mazama).Because

    the white-taileddeer

    can withstand

    heavy harvesting

    by man,

    it

    was probably

    one of the

    few

    large species

    that could

    be

    hunted

    near home,

    in

    cleared

    and

    cultivated

    fields.

    3.

    The

    agouti and

    the paca

    were hunted

    in CerroBrujo

    in

    numbers dis-

    proportionate

    to their natural biomass

    (Table IV).

    As

    N.

    Smythehas

    observed (personal

    communication),

    the ratio of one

    species

    to the

    other in our collections (roughlyfour times as many agoutisas pacas)

    conforms to their

    natural

    densities;

    he

    agouti,

    however,

    s more diurnal.

    Smythe's suggestion that

    the Cerro Brujoinhabitantsmust

    have been

    using snares

    and traps, which

    are effective

    day

    or

    night,

    conformsvery

    well to hunting practices

    as reconstructed

    from

    artifactual

    evidence.

    Furthermore,

    hese caviomorph

    odentseat all sorts

    of cultivatedplants,

    including rootcrops

    and fruits. They

    live

    under

    tree trunks and

    inside

    rotten logs (Smythe,

    1970).

    The

    perfect

    environment or them

    is the

    sort found,

    for example,

    in the slashed and mulched

    fields

    of the

    Guaymi of Bocas;because

    of the constant rains,these

    fields are burned

    but

    infrequently.

    For

    additional inferences on

    hunting practices,

    we have noted the

    total

    absence

    in

    our collection

    of

    monkeys, sloths,

    and climbing species (such as

    squirrels

    and coatis). The likelihood

    that the

    Cerro Brujo group did

    not use

    projectile

    weapons (blowguns,

    arrows, etc.) with

    which

    to

    fell animals in

    the

    higher

    canopy

    is

    increasedby

    the

    fact that these items are missing

    in

    our

    ex-

    cavations.

    But such

    negative

    evidence

    is

    inconclusive, especially

    since the hunt-

    ing gear

    employed today by a tropical

    forest

    group is normallymade

    entirely

    of

    perishable

    materials.

    As I have previously suggested,the CerroBrujo people probablyorigi-

    nated

    inland.

    Two

    main shifts

    in

    hunting

    were

    made

    once these groupsmigrated

    to

    the

    coast. Onewas

    to

    a smallrange

    of terrestrial nimals, he other to marine

    ani-

    mals.

    The new terrestrialhunting

    adaptation that

    was devisedand is represented

    at Cerro

    Brujo

    s

    what

    I

    have called

    "garden

    hunting" because

    in all likelihood

    it took

    place

    in and near cultivated

    fields and

    house gardens.7In this dual

    sys-

    tem, animal protein

    and carbohydratesare

    spatially concentrated and

    their

    Gardenhunting

    s

    still the predominant

    orm of

    huntingamong

    many nland South Amer-

    ican groups,

    including the Guaymi

    and Cuna Indians of Panama.The Chiriqui

    Guaymi

    until recently pole-fencedtheir root crops,and built hutsin theirmaize-bean ields, where

    they stayed

    overnight

    o hunt (J. Bort, personal ommunication).

    Among

    the islandCuna,

    who hunt on the mainland,

    guarding rops

    is such an important unction

    of the hunt that

    a man can

    freely kill animals n another

    man's field (Gonzilez, personal

    ommunication),

    while he

    cannot even touch

    the other man's crops

    without complying with

    elaborate

    accessrules(Howe and Sherzer,

    1975).

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    348

    Linares

    abundance

    vis a vis each

    other

    is

    regulated.By

    reducingseasonalityand schedul-

    ing problems, gardenhunting

    was analogous to,

    and

    may

    have

    even

    substituted

    for, actual animal

    domestication.

    ACKNOWLEDGMENTS

    The Cerro Brujo excavations

    were financed by a grant

    from the National

    Science Foundation (NSF-Gr-2846).

    Besides myself as

    principal nvestigator,a

    number of colleaguesand students participatedin the project. Among them I

    should

    like

    to

    mention Dr. Anthony

    J.

    Ra-nere archeologist),

    Dr.

    Philip Young

    (ethnographer),and MissE. Jane

    Rosenthal,Miss reneBorgono, and Mr. M'aximo

    Miranda,all graduate students now.

    Special thanks

    are owed to

    Dr.

    DonaldK.

    Grayson, who

    did

    the initial

    mammalian dentifications, and

    to Mr. Richard S.

    White, Jr., who reanalyzed the data.

    Dr. Elizabeth

    Wing identified the fish,

    reptiles, and amphibians,

    and

    Mr. James West analyzedsome of the palyno-

    logical cores.

    I should like to thank Wing, White, and

    West for permission to

    refer

    to theirunpublishedreports.

    This

    article

    has been

    enriched

    by

    the comments of

    my colleagues

    at the

    Smithsonian TropicalResearch Institute, namely Drs. MartinH. Moynihan,A.

    Stanley Rand,Ira Rubinoff,

    Neal G. Smith, and most specially

    Nicholas Smythe.

    Data on the modern Guaymi have

    been kindly provided by

    Mr. John Bort and

    on

    the San Blas Cuna

    by

    the

    second

    chief

    of

    Niatuppu-Tikantikki,

    Mr.

    Gonzalez.

    REFERENCES

    Bennett, C.

    F. (1962). The Bayano Cuna

    Indians, Panama: An ecological

    study of liveli-

    hood

    and diet. Annals of

    the

    Association

    of American Geographers

    2(1): 32-50.

    Bennett, C. F. (1964). Human

    Influences

    on the

    Zoogeography f Panama. bero-Ameri-

    cana,

    Vol. 51. University of California Press, Berkeley, 112 pp.

    Carneiro, R.

    L. (1964). Shifting cultivation

    among the Amahuaca

    of

    eastern Peru. Volker-

    kundliche

    Abhandlungen

    Hanover)

    1: 9-18.

    Carneiro, R. L. (1970).

    Hunting

    and

    hunting magic among

    the

    Amahuaca

    of

    the

    Peruvian

    montala. Ethnology

    IX(4):

    3

    31-34

    1.

    Coe, M. D., and Flannery, K.

    V. (1964).

    Microenvironments and Mesoamerican

    prehistory.

    Science

    143:

    650-654.

    Colon, F.

    (1502).

    Vida del

    Almirante

    Don

    Cistobal

    Col6n,

    escrita

    por

    su

    hijo,

    Hernando

    Colon (see Lothrop,

    1950).

    Dobyns, H.

    F. (1966).

    Estimating aboriginal American

    population: An appraisal of tech-

    niques with a New

    Hemispheric

    estimate. Current

    Anthropology 7(4): 395-416.

    Eisenberg, J.

    F., and Thorington, R. W.

    (1973). A preliminary analysis of a

    neotropical

    mammal fauna. Biotropica 5(3):

    150-161.

    Gliwi-ez, J. (1973). Characteristics of a population of

    Proechimys semispinosus

    (Tomes,

    1860)

    -

    A

    rodent

    species

    of

    the

    tropical

    rainforest.

    Bulletin de l'Academie

    Polonaise

    des Sciences Cl. 1.XXI-6:

    413-418.

    Goldman, E. A. (1920).

    Mammals of Panama. Smithsonian

    Miscellaneous

    Collections

    69(5).

    This content downloaded from 132.248.9.8 on Fri, 16 May 2014 11:48:26 AMAll use subject to JSTOR Terms and Conditions

    http://www.jstor.org/page/info/about/policies/terms.jsphttp://www.jstor.org/page/info/about/policies/terms.jsphttp://www.jstor.org/page/info/about/policies/terms.jsp
  • 8/11/2019 garden hunting.pdf

    20/20

    "Garden

    Hunting" in

    the

    American Tropics

    349

    Gordon,B.

    L. (1957). Human

    Geography

    nd

    Ecology

    in

    the

    Sinu

    Countryof Colombia.

    Ibero-Americana,

    Vol. 39.

    University

    of

    California

    Press, Berkeley,

    117

    pp.

    Gordon,

    B. L. (1961). Notes

    on the

    Chiriqui' Lagoon

    District and

    adjacent

    regions

    of

    Pan-

    ama

    II.

    Mimeographed

    report, Department

    of

    Geography,

    University

    of

    California,

    Berkeley,

    28

    pp.

    Gordon,

    B. L. (1969).

    Anthropogeography

    and

    rainforest

    ecology

    in

    Bocas

    del Toro

    pro-

    vince,

    Panama.

    Mimeographed

    report,

    Department

    of

    Geography,

    University

    of

    California,

    Berkeley,

    99

    pp.

    Grayson, D. K.

    (1973). On the

    methodology

    of faunal

    analysis.

    American

    Antiquity 38(4):

    432-438.

    Howe, J. (1974).

    Village political

    organization

    among

    the

    San Blas Cuna.

    Ph.D. disserta-

    tion,

    University

    of

    Pennsylvania.

    Xerox,

    University

    Microfilms,

    Ann

    Arbor, Mich.,

    442

    pp.

    Howe, J.,

    and Sherzer,

    J. (1975).

    Take and tell:

    A

    practical

    classification from the San

    Blas

    Cuna.

    American

    Ethnologist2(3):

    435-460.

    Lathrap,

    D. W.

    (1968). The

    "hunting"

    economics of

    the

    tropical

    forest zone of

    South

    America:

    An

    attempt at

    historical

    perspective. In

    Lee, R. B.,

    and De

    Vore, I. (eds.),

    Man, the

    Hunter,

    Aldine,

    Chicago, pp.

    23-29.

    Lathrap, D.

    W. (1970).

    The

    UpperAmazon.

    Praeger,

    New York.

    Linares, 0. F.

    (1971).

    Cerro

    Brujo,

    a

    tiny

    Guayml

    hamlet of the

    past.

    Bulletin of the

    Uni-

    versityof

    Pennsylvania

    Museum13: 27-35.

    Linares, 0.

    F. (in

    press).

    Adaptive strategies

    in Western

    Panama.

    Paper

    presented at the

    Smith-

    sonian

    Institution

    Conference on

    Biogeographic

    Approaches to

    Archeology, May

    1974,

    Washington, D.C. World

    Archaeology.

    Linares, 0.

    F., and

    Ranere, A.

    J. (1971).

    Human

    adaptations

    to the

    tropical forest of

    wes-

    tern

    Panama.

    Archaeology

    24(4): 346-355.

    Linares, 0. F.,

    Sheets, P.,

    and

    Rosenthal, E. J.

    (1975).

    Prehistoric

    agriculture

    in tropical

    highlands.

    Science

    187:

    137-145.

    Lothrop, S.

    K. (1950).

    Archaeology of Southern

    Veraguas,

    anama.

    Memoirs

    of

    the

    Pea-

    body Museum

    of

    Archaeology

    and

    Ethnology,

    Harvard

    University, IX(2):

    4-7.

    Mendez, E.

    (1970).

    Los

    Principales Mamiferos Silvestres de

    Panama.

    Imprenta

    Barcenas,

    Panama City.

    Meggers, B.

    J. (1971). Amazonia: Man

    and

    Culture

    in a

    Counterfeit

    Paradise.

    Aldine, Chicago.

    Morey, R. V.

    (1970).

    Ecology and culture

    change among

    the

    Colombian

    Guahibo. Ph.D.

    dissertation,

    University of

    Pittsburgh.

    Xerox,

    University

    Microfilms, Ann

    Arbor,

    Mich.

    1973.

    Murphy,

    Y.,

    and

    Murpihy, R.

    F. (1974). Women

    of

    the

    Forest.

    Columbia

    University

    Press,

    New

    York.

    Nietschmann,B. (1973).

    Between

    Land and Water:

    The

    Subsistence

    Ecology of the

    Miskito

    Indians, Eastern Nicaragua. Seminar Press, New York.

    Sauer, C.

    0. (1958).

    Man in

    the ecology

    of

    tropical

    America.

    Proceedings

    of

    the

    Ninth Paci-

    fic Science

    Congress, 1957, 20:

    105-110.

    Sauer, C.

    0.

    (1966).

    The

    Early Spanish

    Main.

    University

    of

    California

    Press,

    Berkeley.

    Siskind, J.

    (1973). To

    Hunt

    in the

    Morning.

    Oxford

    University Press,

    New

    York.

    Smythe,

    N.

    (1970).

    Ecology

    and behavior of

    the

    agouti

    (Dasyprocta

    punctata)

    and

    related

    species

    on

    Barro Colorado

    Island. Ph.D.

    dissertation,

    University

    of

    Maryland.

    Walker,

    E.

    P.

    (1968).

    Mammals

    of

    the

    World, Vols.

    I

    and II. Johns

    Hopkins Press,

    Baltimore.

    West, J. (n.d.)

    Progress report

    of pollen

    analysis of

    core CBII

    from Cerro

    Brujo, Bocas

    del

    Toro,

    Panama.

    Typescript,

    3

    pp.

    White, R.

    (n.d.) Notes on a

    re-analysis of

    the Cerro Brujo

    Fauna. Typescript,

    20 pp.

    Wing,

    E.

    (n.d.)

    Use

    of

    aquatic

    resources at Cerro

    Brujo (CA-3).

    Typescript,

    9 pp.

    Young, P. D.

    (1970). Notes

    on the

    ethnohistorical evidence

    for

    structural

    continuity in

    Guaymf society. Ethnohistory 17(1-2): 11-29.

    Young,

    P.

    D. (1971).

    Ngawbe:

    Tradition nd

    Change

    Among the

    Modern

    Guaymiof Wes-

    tern

    Panama.

    University of

    Illinois

    Studies in

    Anthropology,

    No. 7, Urbana.