+ All Categories
Home > Documents > Part I Introduction and Background

Part I Introduction and Background

Date post: 31-Dec-2021
Category:
Upload: others
View: 1 times
Download: 0 times
Share this document with a friend
26
Part I Introduction and Background
Transcript
Page 1: Part I Introduction and Background

Part I

Introduction and Background

Page 2: Part I Introduction and Background

Chapter 2

Importance ofBiological Diversity

Page 3: Part I Introduction and Background

CONTENTS

Highlights . . . . . . . . . . . . . . . . . . .Definition . . . . . . . . . . . . . . . . . . .Benefits to Ecological Processes

Ecosystem Diversity, .. ...,.,Species Diversity . . . . . . . . . . .Genetic Diversity . . . . . . . . . . .

Benefits to Research . . . . . . . . . .Ecosystem Diversity. . . . . . . . .Species Diversity . . . . . . . . . . .

● ✌ ☛ ✎ ✎ ✎ ☛ ● ☛ ☛ ✎ ☛ ☛ ✎ ✎ ✎ ✎ ✎ ✎ ✎ ✎ ✎ ✎ ✎ ☛ ✎ ✎ ☛ ✎ ✎ ☛ ✎ ☛ ☛ ✌ ✎ ✎ ✎

● ✌ ✎ ✎ ✎ ☛ ✌ ● 4 . . . . . . ● * . * , * * . . * , . ● . * * * * * . * . *

, * . * ● * * * * * . , ● * * * * * O ● . * * . * . * . . . . * * * * ● * ,

* , . * * * * ● * * * . * * , * * * , . , , . . . . . ● . * * * * * ● * , *

. * * . * * . ● . . * . , * * ● * * * . 6 * * , * * , ● , * . , . . , , * ,

, , , . , . . ● * . * * . * . . , * * . * , . . , . * . , * . * . , * * * *

* * * * . . * ● * * * * * * . * . * * * * * * * * ● . . * * * * * * ● * . *

,,..,., ● *,**,.* . . . . . . . . . . . . . . . . .,,*,**

, * * * . * * * * * , * * . * ● * * . * * . * ● * . . . . * . ● . . * * * ,

Gknetic Diversi~ . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .Benefits to Cultural Heritage ● ****** ,***.*** ● ******* ...,*,*, ,.,,..., . .

Ecosystem Diversity. . .**.*** ● ******* 9******* ***.**** ● ****,** ● *.,..Species Diversity . . . . . . . . . . . . . . . . . . . ● ***,9* ● **,**.* ● .****** ● ..*..*Genetic Diversity . . ● .*.*,, .*.**..* ..*,.*.. ● . . ***** . .* ,* . .* O** ,** . .

Benefits to Recreation and Tourism. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .Ecosystem Diversity. . . . . . . , * * . . * ● . * * * * . . ● . . , , ,** . .** .** , , , , . . . . . . ,Species Diversity ● **,*.. . . . . . .4. ● * .** .** , . , , . . . . . . . . * .** .****** . , .Genetic Diversity . . . . . ● **,*** ● *,.**.. ● ******* ..****** ● *,**.*. ● .**,

Benefits to Agriculture and Harvested Resources . . . . . . . . . . . . . . . . . . . . . . .Ecosystem Diversity. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .Species Diversity ● ****** ..,.**** ● ****.** ***.*..* ● .****** ● *..*.** . .Genetic Diversity . . . . . . . . ● ****** ● .*.*.** .,..*.** ● ****.** ..**,*., .*

Values and Evaluation of Biological Diversity .**,**. ● ***,.*. ● *****.* ● , *Economic Value . . . . . . .....;... . . . . . . .Intrinsic Value . . ;. . . . . . . . . . . . . . . . . . . .

Constituencies of Diversity . . . . . . . . . . . . . .Public Awareness. . . . . . . . . . . . . . . . . . . . .Balancing Interests and Perspectives . . . .

Chapter preferences . . . . . . . . . . . . . . . . . . .

TableTabie No.2-1. Examples of Benefits From Ecosystem,

and Genetic Diversity . . . . . . . . . . . . . . .

figure

Figure No.

● ☛ ☛ ☛ ☛ ☛ ☛ ● * * * * ’ * . ● * * * * * . * * . * * .

. * * * * * * ● ****O*. . . . . . , , , . , , . .

● . * * . * * . * . . . * * * . , . . . , 0 0 . . 0 . 0

● * * * * * . . * . . * * * * ● * . * , * * * . . . . .

● * * * . * . . * * * . * * * ● * * * . * . . ● * * * .

. . . . . . . ● . * * * * * * . . , . . , . . . . * * *

3737393941434343444546464647484849494949505153535454545555

Page

Species,, . . .0 . . ● . . * . * * , ● * . * , . * , ● * , , . 38

Page2-1. Krill:The Linchpin to the Antarctic Foodweb . . . . . . . . . . . . . . . . . . . . . . 42

B o x e sBOXNO. Page20A. Components of Biological Diversity ● ****** ● .****** ● ****.** ● .***.*. 38z-B. Scales of Ecosystem Diversity ● ● , . ● ● . . ● ● . ● . . . ● “* * # , ● , ● . . ● ● . , , , , , , ● ● 39

Page 4: Part I Introduction and Background

Chapter 2

Importance of Biological Diversity

Human welfare is inextricably linked to, anddependent on, biological diversity. Diversity isnecessary for several reasons: 1] to sustain andimprove agriculture, 2) to provide opportunitiesfor medical discoveries and industrial innova-tions, and 3) to preserve choices for address-ing unpredictable problems and opportunitiesof future generations. Actual and potential eco-

nomic uses range from subsistence foraging togenetic engineering. The essential services ofecosystems, such as moderating climate; con-centrating, fixing, and recycling nutrients; pro-ducing and preserving soils; and controllingpests and diseases are also dependent on bio-logical diversity. Finally, diversity has estheticand ethical vaIues.

Biological diversity refers to the variety andvariability among 1iving organisms and the eco-logical complexes in which they occur. Diver-sity can be defined as the number of differentkinds of items and their relative frequency ina set (97). Items are organized at many levels,ranging from complete ecosystems to the chem-ical structures that are the molecular basis ofheredity, Thus, the term encompasses the num-bers and relative abundance of different eco-systems, species, and genes. (Box 2-A describesmajor components of biological diversity.)

Species diversity, for example, decreaseswhen the number of species in an area is re-duced or when the same number exists but afew become more abundant while others be-come scarce. When a species no longer existsin an area, it is said to be locally eliminated.

The extreme effect of species diversity loss isextinction—when a species no longer existsanywhere.

Biological diversity is the basis of adaptationand evolution and is basic to all ecological proc-esses. It contributes to research and education,cultural heritage, recreation and tourism, thedevelopment of new and existing plant and ani-mal domesticates, and the supply of harvestedresources (table 2-1). The intrinsic importanceof biological diversity lies in the uniqueness ofall forms of life: each individual is different,as is each population, each species, and eachassociation of species. Major functional andutilitarian benefits of ecosystem, species, andgenetic diversity are described in the next fivesections; evaluation of diversity and the con-stituencies of diversity are discussed in the fi-nal sections.

37

Page 5: Part I Introduction and Background

38 ● Technologies To Maintain Biological Diversity

Table 2.1 .—Examples of Benefits From Ecosystem, Species, and Genetic Diversity

Agriculture andEcological Drocesses Research Cultural heritaae Recreation and tourism harvested resources

Ecosystem diversityMaintenance of produc-tivity; buffering environ-mental changes; watershedand coastal protection

Species diversityRole of plants and animalsin forest regenerat ion,grassland production, andmarine nutrient cycling;mobile links; natural fuelstations

Genetic diversityRaw material of evolutionrequired for survival andadaptation of species andpopulations

Natural research areas;sites for baseline monitor-ing (e.g., Serengeti NationalPark, Zambesi Teak Forest)

Models for research on hu-man diseases and drugsynthesis (e.g., bristleconepine, desert pupfish, me-dicinal leeches)

Fruit flies in genetics, cornin inheritance, and Nico-tiana in virus studies

SOURCE: Office of Technology Assessment, 19S6.

Sacred mountains andgroves; historic landmarksand landscapes (e. g.,Mount Fuji; Voyageurs Park,Minnesota)

National symbols (bald ea-gles); totems; objects ofcivic pride (e.g., port orfordcedar, bowhead whale, Fi-cus religiosa)

Breeds and cultivars ofceremonial, historic, es-thetic, or culinary value(e.g., Texas longhorn cattle,rice festivals (Nepal))

700 to 800 million visitorsper year to US. State andnational parks; 250,000 to500,000 visitors per year tomangrove forests in Ven-ezuela

95 million people feed, ob-serve, andlor photographwildlife each year; 54 mil-lion fish; 19 million hunt

100,000 visitors per year toRare Breeds Survival Trustin the United Kingdom

Rangeiands for livestock pro-duction (e.g., 34 in the U.S.);habitats for wild pollinatorsand pest enemies (e.g., sav-ing $40 to $80 per acre forgrape growers)

Commercial logging, fishing,and other harvesting indus-tries ($27 billion/year in U.S.);new crops (e.g., kiwi fruit, reddeer, catfish, and Ioblollypine)

Required to avoid negativeselection and enhancementprograms; pest and diseaseresistance alleles

Page 6: Part I Introduction and Background

Ch. 2—Importance of Biological Diversity ● 3 9

BENEFITS TO ECOLOGICAL PROCESSES

Ecological processes include—

regulation: monitoring the chemistry andclimate of the planet so it remains habitable;production: conversion of solar energy andnutrients into plant matter;consumption: conversion of plant matterinto animal matter;decomposition: breakdown of organicwastes and recycling of nutrients;protection processes: protection of soil bygrasslands and forests and protection ofcoastlines by coral reefs and mangroves,for example; andcontinuation of life: processes of feeding,breeding, and migrating.

Knowledge of the relationship between di-versity and ecological processes is fragmentary,but it is clear that diversity is crucial to the func-tioning of all major life processes, for diversityhelps maintain productivity and buffers eco-systems against environmental change. Diversitywithin ecosystems is essential for protective,productive, and economic benefits. Speciesdiversity is necessary for a stable food web. Anddiversity of genetic material allows species toadapt to changing environmental conditions.

Ecosystem Diversity

Ecosystems are systems of plants, animals,and micro-organisms, together with the non-living components of their environment (45).It can be recognized on many scales, frombiome—the largest ecological unit—to micro-habitat (box 2-B). Ecosystem diversity refers tothe variety that occurs within a larger land-scape. Loss of ecosystem diversity can resultin both the loss of species and genetic resourcesand in the impairment of ecological processes.

In eastern and southern Africa, for instance,the mosaic of ephemeral ponds, flood plains,and riparian woodlands enable antelope, ele-phant, and zebra to survive long cycles of wetand dry years (16,23). On the American conti-nent, many animal species cope with oscilla-tions in weather and climate by migrating be-tween biomes—spending the rainy season in

Box 2-B.—Scales of Ecosytem Diversity

Several ways exist to classify the manyscales of ecosystem diversity. An exampleusing the Pacific Northwest to illustrate fourlevels of ecosystems is shown below. Animalspecies characteristic of each level are noted.

1. Biome: temperate coniferous forest–Rufous hummingbird-Mountain beaver

Z. Zone: western hemlock-Coho salmon–Oregon slender salamander

3. Habitat: old growth forest–Vaux’s swift–Spotted owl

~. Microhabitat: fallen tree–Clouded salamander—California red-backed vole

The fallen tree component of old growth andmature forests illustrates the contribution ofecosystem diversity to ecological processes.Fallen trees provide a rooting medium forwestern hemlock and other plants that is moistenough for growth to continue during the sum-mer drought, a reserve of nitrogen and othernutrients, and a source of food and shelter foranimals and micro-organisms that play keyroles in redistributing and returning the nti-trients to the regenerating forest. For exam-ple, the rotten wood provides habitat for truf-fles, and the truffles are eaten by the Californiared-backed vole, which spreads the trufflespores, so helping the growth of Douglas firtrees, which require mycorrhizal fungi (suchas truffles) for uptake of nutrients (56).

the tropical dry forest and the dry season inthe rain forest, that is, summer in temperateforest and winter in tropical forest. Others usedifferent habitats within the same biome; forexample, leaf-eating primates and flower-pol-linating bats move from dry sites in the rainyseason to evergreen riparian trees in the dryseason (32,48).

Several types of ecosystems are closely asso-ciated with protective and productive processesof direct economic benefit. Cloud forests, for

Page 7: Part I Introduction and Background

40 . Technologies TO Maintain Biological Diversity

example, increase precipitation, often substan-tially (38). Watershed forests generally reducesoil erosion and thereby help protect down-stream reservoirs, irrigation systems, harbors,and waterways from siltation (45). Coral reefsare productive oases in otherwise unproductivetropical waters. Algae living inside coral polypsenable the corals to build the reefs (8,49). Thereefs, in turn, support local fisheries and pro-tect coastlines.

Wetlands are another example of an ecosys-tem with protective processes linked to eco-nomic output. Millions of waterfowl and otherbirds of great economic value depend on thediverse North American wetlands—coastal tun-dra wetlands, inland freshwater marshes, prai-rie potholes, coastal saltwater marshes, andmangrove swamps—for breeding, feeding, mi-grating, and overwintering.

These wetlands also support most commer-cial and recreational fisheries in the UnitedStates. About two-thirds of the major U.S.commercial fish, crustacean, and mollusk spe-cies depend on estuaries and salt marshes forspawning and nursery habitat (88,90). Otherwetland services include water purification (byremoving nutrients, processing organic wastes,and reducing sediment loads), riverbank andshoreline protection, and flood assimilation,Wetlands temporarily store flood waters, reduc-ing flow rates and protecting people and prop-erty downstream from flood and storm damage.

For example, the U.S. Army Corps of Engi-neers chose protection of 8,500 acres of wet-lands over construction of a reservoir or ex-tensive walls and dikes as the least-cost solutionto flooding problems in the Charles River ba-sin in Massachusetts, It was estimated that loss

Page 8: Part I Introduction and Background

Ch. 2—Importance of Biological Diversity ● 4 1

of the Charles River wetlands would have re-sulted in an average of $17 million per year inflood damage (80,88,90), (Data on wetlands eco-system losses are given in chapter 3.)

Species Diversity

Some species play such an important role inparticular ecosystems that the ecosystems arenamed after them. Zambezi Teak Forest andLongleaf-Slash Pine Forest are examples. Butthe ecological processes that maintain domi-nant species often depend on other species. Forexample, elephants and buffaloes make a cru-cial contribution to regeneration of Zambeziteak by burying seeds, providing manure, anddestroying competing thicket species (72),

Depletion of species can have a devastatingimpact higher up the food chain. For example,catches of common carp in the Illinois Riverare one-tenth of what they were in the early1950s. This decrease appears to be the resultof pollution-caused die-off in the 1950s of fin-

gernail clams, may fly larvae, and other river-bottom macro-invertebrates. These macro-inver-tebrates are still scarce, for river-bottom sedi-ment is slow to recover from pollution, muchslower than water quality, for example (44).

Certain species have a greater effect on pro-ductive processes than is indicated by their po-sition in a food web (figure 2-1). Earthworms,for instance, improve the mixing of soil, in-crease the amount of mineralized nitrogenavailable for plant growth, aerate the soil, andimprove its water-holding capacity (98). Antsalso contribute to soil formation in temperateregions and the tropics. They contribute to theaeration, drainage, humidification, and enrich-ment of both forest and grassland soils (99).

In East Africa, species diversity increases theproductivity of grasslands. For example, graz-ing by wildebeest promotes the lush regrowtheaten by gazelles (59,60). Similar interactionshave been observed in North American grass-lands between prairie dogs and bison. Althoughthe standing crop of grass in prairie dog towns

A Se / /o

Cave National Park, South Dakota, contains a variety of wildlife elk, prairie dogs, prong horn. anddeer Interactions between species such as dogs and bison increase the productivity of grasslands,

Page 9: Part I Introduction and Background

42 . Technologies To Maintain Biological Diversity

Figure The Linchpin to the Antarctic Foodweb

Antarctic waters are among the most product ive in t he world. The main link in this food web is the small 11, shrimp-like uresthat feed on plankton. in turn, support seabirds, fish, and squid, which are the mainstay of seals and whales.

Page 10: Part I Introduction and Background

is half that of grass outside, protein levels anddigestibility are significantly higher. In WindCave National Park, prairie dog towns occupyless than 5 percent of the area, but bison spend65 percent of their time per unit area in thetowns, mostly feeding (28).

Some species have an unusually prominentposition in food webs, being major predatorsof species on lower levels of the food chain andmajor prey of species on higher levels. Arcticcod, for example, feed on herbivorous and car-nivorous zooplankton (amphipods, copepods,and decapods). Cod, in turn, is an importantfood of many bird and marine mammal spe-cies including gulls, narwhals, belugas, andharp seals (25),

Genetic Diversity

Intraspecific genetic diversity allows speciesto adapt to changing conditions, thus sustain-ing ecosystem and species diversity; it alsohelps produce plants and animals that will sup-port more productive agriculture and forestry,Genetic diversity is distributed unevenly among

Ch. Z—Importance of Biological

and within species. Somepear to be more variable

Diversity ● 4 3

groups of species ap-than others: reptile,

bird, and mammal species have less than halfthe genetic variation found in invertebrate spe-cies and less than a quarter of that found inmany insects and marine invertebrates (34),

The greater the amount of genetic variationin a population, the faster its potential rate ofevolution (7). Certain genes are directly impor-tant for survival (e. g., genes conferring diseaseresistance), In addition, genetic diversity ena-bles species to adapt to a wide range of physi-cal, climatic, and soil conditions and to changesin those conditions. Genetic diversity is posi-tively correlated with fitness, vigor, and repro-ductive success (7,85).

Among marine animals, and probably amongterrestrial animals as well, high genetic varia-bility is associated with high species diversity,which in turn is associated with a number ofspatially different microhabitats (e. g., tropicaland deep sea environments). It seems likely thatthe high genetic variability y provides the flexibil-ity to make finely tuned adjustments to micro-habitats.

BENEFITS TO RESEARCH

Research may hold answers to many of thequestions facing this complex world. The re-sults of research on the patterns and processesof temperate forests have provided methods forsustainable management of those ecosystems,Knowledge of tropical rain forests will resultin similar strategies. Without diversity of spe-cies, researchers would not have the neededplant material to develop many vaccines, in-travenous fluid, or other medicines, The poten-tial for further advancement has not been fullyrealized, yet a loss of species diversity will ad-versely affect future research. Protection ofgenetic diversity is equally essential, becausematerials from plants and animals have pro-vided valuable knowledge on viruses, immu-nology, and disease resistance.

Ecosystem Diversity

Many contributions of ecosystem diversityto global ecological processes, e.g., the role ofwetlands in the Earth’s oxygen balance, haveyet to be demonstrated quantitatively, But theresearch required to develop and test these hy-potheses depends on the full range of diversity.By studying natural ecosystems, scientists arebetter able to understand how the Earth works.

Knowledge of the role of ecosystem diversityin ecological processes is substantial and grow-ing, largely because of the availability of natu-ral research areas such as the Olympic NationalPark and the H.J, Andrews Experimental Eco-logical Reserve in Willamette National Forest(42,81). Relatively undisturbed grasslands in the

Page 11: Part I Introduction and Background

44 ● Technologies TO Maintain Biological Diversity

Serengeti National Park (Tanzania) and WindCave National Park (South Dakota) provide re-search significant for range management. Re-search includes, for example, studies of the ex-tent to which grazing intensity increasesprimary production and the protein content anddigestibility of grasses (28). Research on spe-cies and natural gene pools also requires eco-system maintenance.

Representative examples of major ecosystemsare used as reference sites for baseline moni-toring on productivity, regeneration, and adap-tation to environmental change. In addition,evaluation of development projects to ensurethey are both economical and sustainable callsfor assessment of, among other things, theirenvironmental effects measured against un-altered sites with similar vegetation, soils, andclimate.

The Zambezi Teak Forest ecosystem, for ex-ample, which yields Zambia’s most valuabletimber, is declining rapidly, due to excessivelogging, fire, and shifting cultivation. If presenttrends continue, this forest would effectivelydisappear in 50 years. Attempts at artificialregeneration have met with little success. Toimprove understanding of natural regeneration,an undisturbed tract of the forest in Kafue Na-tional Park is being studied. Continued moni-toring of the Kafue tract will provide dataneeded for assessing costs and benefits of anysilviculture system for the Zambezi Teak For-est (72,74).

Ecosystems are also living classrooms. TheUniversity of California’s Natural Land andWater Reserves System includes 26 reservesrepresenting 106 of the 178 habitat types iden-tified for the State. The reserves are used forinstruction and research in botany, geology,ecology, archeology, ethology, paleontology,wildlife management, genetics, zoology, pop-ulation biology, and entomology (52). Enablingchildren and adults to experience different eco-systems is an effective way to teach ecologicalprocesses, genetic variation, community com-position and dynamics, and human relationswith the natural world.

Species Diversity

Species diversity is the basis for many fieldsof scientific research and education. The ar-ray of invertebrates used in research illustratesthe importance of diversity to the advancementof science. The 100 or so species of Hawaiianpicture-winged fruit flies are the organisms ofchoice for basic research on genetics, evolu-tionary biology, and medicine. Tree snails ofHawaii and the Society Islands provide idealmaterial for research on evolution and geneticvariation and differentiation (57).

Bristlecone pines, the oldest known livingorganisms and found only in the U.S. South-west, are used to calibrate radiocarbon datesand hence, are important for archeology, pre-history, and climatology (62). Contributions ofplant and animal species to biomedical researchand drug synthesis abound (63,71). Examplesinclude:

Desert pupfishes, found only in the South-west, tolerate salinity twice that of salt-water and are valuable models for researchon human kidney disease (63).Sea urchin eggs are used extensively in ex-perimental embryology, in studies of cellstructure and fertilization, and in tests onthe teratological effects of drugs (98).Medicinal leeches are important in neu-rophysiology and research on blood clot-ting (98).An extract of horseshoe crabs provides thequickest and most sensitive test of vaccinesand intravenous fluids for contaminationwith bacterial endotoxins (98).Butterfly species are used in research oncancers, anemias, and viral diseases (82).The study of sponges is making substan-tial contributions to structural chemistry,pharmaceutical chemistry, and develop-mental biology and has also resulted in thediscovery of novel chemical compoundsand activities. D-arabinosyl cytosine, an im-portant synthetic antiviral agent, owes itsdevelopment to the discovery of spongouri-dine, which was isolated from a Jamaican

Page 12: Part I Introduction and Background

Ch. 2—Importance of Biological Diversity ● 45

Cohen Z o o

The armadillo is one of only two animal species known to contract leprosy.These animals now serve as research models to find a cure.

sponge. Three derivatives of this com-pound have been patented as antiviral andanticancer drugs (10).

Genetic Diversity

Genetic variability is one of the characteris-tics of fruit flies, tree snails, and butterflies thatmakes them so useful for research. The unusualrange of diversity among the races, varieties,and lines of corn contributes to its enormousvalue for basic biological research. One exam-ple is the discovery and analysis of regulatorysystems that control gene expression, whichadded a new dimension to the study of in-heritance (21).

The genus Nicotiana has also been usedwidely in genetic and botanical research largely

because of the great variation among its spe-cies (84). The varied reactions to specific virusescharacteristic of many Nicotiana species pro-vide a potential tool for separating and iden-tifying viruses, Nicotiana species have beeninvolved in numerous discoveries of virus re-search (e. g., virus transmissibility, purification,and mutability) (35),

Special genetic stocks are essential researchtools. For example, inbred lines of chickens de-veloped at the University of California at Davisare used worldwide for research on immunol-ogy and disease resistance of chickens. Mutantstocks of chickens also serve as genetic modelsfor scoliosis (lateral curvature of the spine) andmuscular dystrophy in humans (58).

Page 13: Part I Introduction and Background

46 ● Technologies TO Maintain Biological Diversity

BENEFITS TO CULTURAL HERITA6E

Throughout history, societies have put greatvalue on physical features of their environment.In developed and developing countries, a diver-sity of ecosystems is a source of esthetic, his-toric, religious, and ritualistic values. Speciesdiversity assures people of national and statesymbols, and many such symbols are protected.Genetic diversity continues in part because ofthe cultural value of plants and animals. Gar-deners around the world share seed materialensuring genetic survival.

Ecosystem Diversity

Natural ecosystems have great cultural (in-cluding religious, esthetic, and historic) impor-tance for many people. Mountains are the focusof religious celebrations and rituals through-out the world: Mount Kenya, Mount Everest,Mount Fuji, Mount Taishan in China, and BlackMesa in Arizona. Forests also have great spir-itual value: probably the only surviving exam-ples of primary forest in southwestern Indiaare sacred groves—ancient natural sanctuarieswhere all living creatures are protected by thedeity to which the grove is dedicated. Remov-ing even a twig from the grove is taboo (36).

People who lead subsistence-based lives iden-tify closely with the ecosystems on which theydepend. Two examples are the Guarao peoplein the mangrove swamps and savannas of Vene-zuela’s Orinoco Delta (39) and the Inuit peoplein the tundra of the North American Arctic(9,24). The economic, social, and spiritual ele-ments of the relationship between such peoplesand the ecosystems that support them are in-separable.

Ecosystems define and symbolize relation-ships between human beings and the naturalworld and express cultural and national iden-tity, In the United States, the landscapes pro-tected in wilderness areas, national parks, mon-uments, and preserves are full of historicalmeaning and show the close ties between Amer-ica the nation and America the land. Examplesof these are pre-Columbian Indian habitationsat Mesa Verde in Colorado; symbols of the

opening of the Midwest and West at VoyageursPark in Minnesota; and combinations of wilder-ness preservation and human occupation in-cluding current subsistence-use at Kobuk Val-ley in Alaska (66,94).

Species Diversity

Whereas the Continenta] Congress in 1782adopted the bald eagle as a national symbol; and

Whereas the bald eagle thus became the sym-bolic representation of a new nation under anew government in a new world; and

Whereas by that act of Congress and by tra-dition and custom during the life of this Na-tion, the bald eagle is no longer a mere bird ofbiological interest but a symbol of the Amer-ican ideals of freedom . . .

–Bald and Golden Eagle Protection Act of 1940

.

National Federation

Cultural value of species is exemplified by the baldeagle, adopted by the Continental Congress as a

symbol of the United States.

Page 14: Part I Introduction and Background

Ch. 2—lmporfance of Biological Diversity ● 47

When Congress adopted the bald eagle as anational symbol, it was responding to an an-cient human need to identify with other spe-cies, All over the world and throughout history,people have adopted animals and plants as em-blems, icons, symbols, and totems and investedthem with ideals and values, adopted them asrepresentations of particular characteristics oftheir culture and society, sought the power andauthority they stand for, or venerated them asembodiments of fruitfulness and life itself.

The endangered bowhead whale plays a piv-otal cultural role in several Yupik and InupiatEskimo villages in northern Alaska, Bowheadwhale hunting is the first and most importantactivity in the subsistence cycle. It is a majorsocial unifier, providing community identityand continuity with the past, The division, dis-tribution, and sharing of bowhead whale meatand skin involve the entire community, strength-ening kinship and communal bonds. Importantceremonies, celebrations, and feasts accom-pany the harvest of a bowhead whale and thedistribution and sharing of its meat (4,5).

Port Or ford Cedar (Chamaecyparis lawsoni-ance), prized for its cultural and economicvalues, has become the focus of a recent con-troversy. It grows only in a small area of south-ern Oregon and northern California, where itproduces some of the area’s highest priced tim-ber. Top quality may cost as much as $3,000per 1,000 board-feet. This price reflects demandfrom Japan, where it is used in homes and tem-ples as a substitute for the no longer availableJapanese Hinoki cypress. It also has great cul-tural importance for Native Americans of theHupa, Yurok, and Karok tribes in northwesternCalifornia, who regard it as sacred and use thewood in homes and religious ceremonies, Man-agement of remaining stands of the cedar hasbecome controversial, because mature trees arein short supply and threatened by a tree-killingroot-rot disease, spread partly by logging oper-ations (22).

Native Americans seek to reserve all the PortOrford Cedar growing on formal tribal land–now administered by the U.S. Forest Service—for ceremonial purposes. Other citizens’ groups

seek a management plan that would control log-ging operations and restrict loggers’ access tosome areas to reduce the spread of the fungus.Scientists at the Forest Service and OregonState University are exploring the genetic diver-sity of the species in an effort to develop strainsresistant to the fungus (22),

In South and Southeast Asia, trees, Asianelephants, monkeys, cobras, and birds figureprominently in tribal religions and have beentaken into the pantheons of Hinduism and Bud-dhism. Certain tree species, such as F i cusreligiosa, are sacrosanct and may not be cutdown (2,20); political authorities often invokethe sanction of animals to win popular support(61). Interspecific loyalties persist; the hornbill,central figure of the Gawai Kenya-lang or Horn-bill Festival of the Iban people in Sarawak,Malaysia, is also the official emblem of the state(50).

In urban North America, species also expresscommunity identity. Inwood, Manitoba, pro-claims itself the garter snake capital of theworld (after the mass matings of red-sided gar-ter snakes that occur nearby) (67], and PacificGrove, California, dubs itself Butterfly Town,USA (after the spectacular colonies of Monarchbutterflies that overwinter there) (98). Theseactions are partly commercial acumen—thephenomena are tourist attractions—but theyalso reflect civic pride and perhaps somethingdeeper as well,

Many crop varieties and livestock breeds per-sist because they are culturally valuable todifferent societies, This group includes plantsand animals with religious and ceremonial sig-nificance—such as the festival rices of Nepaland Mithan cattle in northern Burma and north-eastern India (40)—as well as varieties valuedfor their contribution to the traditional diet.Farmers in the Peruvian Andes commonlyplant their potato fields with many varieties(often 30 or more), producing a mixture ofcolors, shapes, textures, and flavors to enhancethe diet (14), In northwestern Spain, a mosaic

Page 15: Part I Introduction and Background

48 . Technologies TO Maintain Biological Diversity

.

credit. G.

of local varieties of beans and other legumesis grown, each variety intended for a particu-lar dish in the traditional cuisine (3).

A growing number of Americans value tradi-tional cuhivars and breeds for their history andfor their esthetic and culinary qualities. NativeAmericans, helped by grassroots organizations,continue to grow traditional varieties of corn,chiles, beans, and squash (91). Hispanic-Ameri-can farmers in the Southwest prefer native cornfor its texture, flavor, and color, even thoughits yield is only one-third to one-fourth of hy-brid corn (64), The cultural value of rare live-stock breeds is exemplified by Texas Longhorncattle (which have a prominent place in Amer-ican history) and Navaho sheep (whose fleeceis important to Navaho weaving).

Gardeners have organized national and re-gional networks to conserve some plant vari-eties because they have better taste, have linkswith national, local, and ethnic history; are suit-able for the home garden; and because of theabundance of colors and forms found amongold and local varieties of potatoes, corn, beans,and other crops (33,43,47,64,91).

Hopi Indian garden of mixed crops illustrates ancienthorticultural traditions that persist on this continent.

BENEFITS TO RECREATION AND TOURISM

Millions of people worldwide derive benefits Ecosystem Diversityfrom recreation and tourism provided by bio-logical diversity. Without diverse ecosystems, State and National parks in the United Statescountries would lose tremendous amounts of attract 700 to 800 million visitors per yearforeign exchange. Without wilderness areas, (73,74), and National Forests receive some 200national parks, or national forests, city dwellers million visitors per year (93). One reason forwould have no place to “escape” the daily pres- these visits—indeed, some surveys suggest thesures. Species diversity is essential to the mil- main reason—is to enjoy the variety of land-Iions of wildlife photographers, bird lovers, and scapes the parks and forests protect (83), Sight-plant and animal watchers. And without ge- seeing accounts for more recreation-visitornetic diversity, horticulturists, gardeners, ani- days (52 million) in National Forests than anymal breeders, and anglers would find little en- other recreation activity except camping (60joyment in their avocations. million) (93).

Page 16: Part I Introduction and Background

———

Ecosystem diversity is a significant recrea-tional asset in developing countries as well. InVenezuela, the mangrove forests of MorrocoyNational Park attract 250,000 to 500,000 visi-tors per year (39); in Nepal, mountain land-scapes, rhododendron forests, and fauna bringin foreign exchange (55),

Species Diversity

About 95 million Americans a year partici-pate in nonconsumptive recreational uses ofwildlife (observing, feeding, or photographingwild plants and animals); each year 54 millionAmericans fish and 19 million Americans huntfor sport. In the process they spend $32.4 bil-lion per year (95).

Surveys of American recreational uses ofwildlife reveal that a number of different spe-cies interest people. Recreational hunters inNorth America pursue some 90 species (73,74).Millions of Americans take time to observe notonly birds and mammals, but also amphibians,reptiles, butterflies, spiders, beetles, and otherarthropods (95),

Ch. Z—Importance of Biological Diversity “ 49

Little data exist on wildlife recreational useby people in developing countries, but for sev-eral nations wildlife-based tourism is big busi-ness. The spectacular wild animals of east andsouthern Africa are the resource base of a tour-ist industry that brings millions of dollars inforeign exchange. In 1985, Kenya netted about$300 million from almost 500,000 visitors, mak-ing wildlife tourism the country’s biggest earnerof foreign exchange (l).

Genetic Diversity

Millions of home gardeners and members ofhorticultural and animal breed associations de-rive recreational benefit from genetic diversity.So, too, do millions of anglers who take advan-tage of stocking and enhancement programs.Tourism associated with genetic diversity in-volves fewer people, although the Rare BreedsSurvival Trust in the United Kingdom receives100,000 visitors a year. In North America, atleast 10 million people visit the some 200 liv-ing historical farms—open-air museums that re-create and interpret agricultural and otheractivities of a particular point in history (91).

BENEFITS TO AGRICULTURE AND HARVESTED RESOURCES

In agriculture, a diversity of ecosystems, spe-cies, and genetic material provides increasedamounts and quality of yields. In a world wherepopulation is rapidly increasing, assuring a con-tinued increase in harvested resources is es-sential. Diversity in an agroecosystem provideshabitat for predators of crop pests and breed-ing sites for pollinators. Diversity of species canbe a buffer against economic failure and canalso play an important role in pest management.Further, the use of genetic materials by breed-ers has attributed to at least 50 percent of theincrease in agriculture yields and quality.

Ecosystem Diversity

Both diversity and isolation affect the abilityof pests to invade a crop. They also affect thesupply of pests’ enemies, Uncultivated habitatsnext to croplands contain wildflowers, which

contain important nutrients for the adult stagesof predatory and parasitic insects (37). Wild-flowers also support essential alternate hostsfor parasites, especially in seasons when peststhey prey on are not present, In California, forinstance, wild brambles (Rubus) provide an off-season reservoir of prey for wasps, which con-trol a major grape pest, This arrangement savesgrape growers $40 to $60 per acre in reducedpesticide costs (6,54).

A variety of wild habitats also provides food,cover, and breeding sites for pollinators. Wildpollinators (chiefly insects) make major contri-butions to the production of at least 34 cropsgrown or imported by the United States, witha combined annual average value of more than$1 billion. They are the main pollinating agentsin the production of cranberry and cacao, thepropagation of red clover, and the production

Page 17: Part I Introduction and Background

50 Technologies to Maintain Biological Diversity

and propagation of cashew and squash. Theyare also significant pollinators for such cropsas coconut, apple, sunflower, and carrot. Theabundance of wild pollinators is largely deter-mined by the availability of ecosystem diver-sity (woods, scrub, bare ground, moist areas,patches of flowers) within flight range of thecrops to be pollinated (73,74).

permanent pastures and rangelands occupyone-fourth of the Earth’s land surface (31). Be-cause they support most of the world’s 3 bil-lion head of domesticated grazing animals (45),rangelands can be considered harvested eco-systems, where the nutrients and solar energyof marginal lands are converted into meat, milk,wood, and other goods,

In the United States, 34 rangelands are in-volved and include plains, prairie, mountaingrassland, and Texas savanna (93). Pastoralnomadism and migrations by wild herbivoresare traditional ways of using these resources.Modern ways include hauling sheep betweensummer and winter ranges, which may be 300to 400 kilometers apart in the intermountainregion (12).

Species Diversity

Diversity of harvestable species acts as abuffer that allows people in fluctuating envi-ronments to cope with extremes. For instance,in Botswana, five wild plant species are exten-sively used by pastoralists and river people, butan additional 50 or more species are resortedto in times of drought (17).

Harvested species provide much of the sub-sistence of indigenous peoples and rural com-munities throughout the world. Wild beardedpig and deer contribute about 36,000 tons ofmeat a year to rural diets in Sarawak, Malay-sia. This amount of meat from domestic ani-mals would cost about $138 million. (15). Percapita consumption of harvested food by Inuitin the North American Arctic averages annu-ally from 229 kg (504 lb) to 346 kg (761 lb). Theper capita cost of buying substitute food (usu-ally of lower nutritional and cultural value) wasestimated to be $2,1OO per year (1981 figures)(4,101).

The commercial timber, fishery, and fur in-dustries obtain most of their resources by har-vesting wild species, Harvested resources arealso major contributors to the pharmaceuticalindustry, and to many other industries as well.The average annual value of the wild resourcesproduced and imported by the United Statesbetween 1976 and 1980 was about $27,4 billion,of which $23 billion was timber (73,74).

Many species are involved, but most of themare economically significant only to the trades-men involved. Even so, the number of harvestedspecies might run up to more than a hundred.For example, it takes on average 70 species tomake up 90 percent of the annual value of U.S.commercial fishery landings (74).

In agriculture, two types of diversity are use-ful in pest management programs: crop diver-sity and pest enemy diversity, Crop diversity(multiple cropping) can promote the activity ofbeneficial insects. For example, to attractLycosa wolf spiders, the main predators of cornborers in Indonesia, farmers interplant the cornwith peanuts (46). In California, lygus bugs, oneof the main pests of cotton, are controlled some-what by strip-planting alfalfa, which the bugsprefer to cotton (11). Pest enemy diversity in-cludes introduced as well as native enemies.The Florida citrus industry saves $35 millionper year by using three parasitic insect speciesthat were imported and established at a costof $35,000. Some 200 foreign insect pests in theUnited States are controlled by introduced par-asites and predators (63).

A long-standing use of wild species diversityis as a source of new domesticates. In theUnited States, the combined farm sales and im-port value of domesticated wild species is wellover $1 billion per year. The domestication oftwo major groups of resources—timber treesand aquatic animals—has only begun and is atabout the same stage that agricultural domes-tications were some 5,000 years ago. But agri-cultural and horticultural domestications arestill occurring.

Among the successful new food crops devel-oped this century are kiwifruit, highbush blue-berry, and wild rice (most of the wild rice

Page 18: Part I Introduction and Background

Ch. 2—lmportnce of Biological Diversity ● 5 1

Two intercropping systems —fava beans and sprouts, and wild mustard and sprouts—demonstratethe benefits of diversity to agriculture. Both systems benefit the sprouts crop: wild mustard acts as a trap c r o p

of flea beetles, and fava beans fix nitrogen with possible benefits to sprouts yields.

produced in the United States is domesticated).New and incipient forage crops include Bahiagrass, desmodium, and several of the wheat-grasses, Red deer and aquiculture species suchas catfish, hardshell clam, and the giant fresh-water prawn, are among the newly domesti-cated livestock. Loblolly pine, slash pine,parana pine, and balsa are some of the new tim-ber domesticates (73,74).

Domestication of wild species increases theeconomic benefits of wild species by improvingproduct quality and by raising yields. It can alsomake a valuable contribution to rural develop-ment in areas that are marginal for conven-tional crops and livestock. Nepal’s Departmentof Medicinal Plants has organized the farmingof two native species IRauvolfia serpentine and

VaZeriana wallichii) for example, and it is in-vestigating propagation of several other wildspecies that are sources of drugs, perfumes, andflavors for export, Scientists in Zambia and Bot-swana are working on the domestication ofmungongo tree, whose fruits are used for foodand oil and whose wood is valued for carvings(74),

Genetic Diversity

Health and long-term productivity of wild re-source species—from game animals to timbertrees to food and sport fish—depend on geneticdiversity within and among the harvested pop-ulations, If the best individuals (biggest animals,tallest trees) are harvested before they repro-

Page 19: Part I Introduction and Background

52 ● Technologies To Maintain Biological Diversity

credit M

Medicine from nature: sp., known as “sangrede grade” in the Peruvian Amazon. This tree produces

a sap used for a variety of medicinal purposes.

duce, then the productivity and adaptability ofthe population will progressively decline.

In addition, certain populations are betteradapted to particular locations than others. Forexample, chinook, coho, and sockeye salmonfrom different rivers are genetically distinct;these distinctions reflect differences in thephysical and chemical characteristics of thestreams in which they originated (69,70). Diver-sity needs to be maintained so that any restock-ing to compensate for overharvesting or habi-tat degradation can use populations that areadapted to the specific environmental con-ditions.

In agriculture, genetic diversity in the formof readily available genes reduces a crop’s vul-nerability to pests and pathogens. Resistancegenes can be introduced as long as a high de-gree of genetic diversity is maintained in off-site collections, onsite reserves, and agroeco-systems. U.S. plant breeders keep a substantialsupply of diversity in cultivars, parental lines,synthetic populations, and other breeders’ stocksready for use (13,26),

The genetic variation in domesticated plantsand animals and in their wild relatives is theraw material with which breeders increaseyields and improve the quality of crops and live-

stock. Use of genetic resources during this cen-tury has revolutionized agricultural produc-tivity. In the United States from 1930 to 1980,yields per unit area of rice, barley, and soybeansdoubled; wheat, cotton, and sugarcane yieldsmore than doubled; fresh-market tomato yieldstripled; corn, sorghum, and potato yields morethan quadrupled; and processing-tomato yieldsquintupled (65,92).

At least half of these increases have been at-tributed to plant breeders’ use of genetic diver-sity. The gain due to breeding is estimated tobe 1 percent per year for corn, sorghum, wheat,and soybeans, due mainly to improvements ingrain-to-straw ratio, standability, drought re-sistance, tolerance of environmentaI stress, and

Nat/ens—/d

Plant breeders’ use of genetic diversity has significantlyincreased the productivity of crops such as wheat.

Page 20: Part I Introduction and Background

Ch. 2—Importance of Biological Diversity ● 5 3

pest and disease resistance (18,27,79). Similarly,the average milk yield of cows in the UnitedStates has more than doubled during the past30 years; about one-fourth of this increase isdue to genetic improvement (89).

Developing countries have also achieved in-creased production of major crops. The GreenRevolution that has transformed heavily popu-lated Asian countries is founded on use of par-ticular genes. High-yielding varieties of rice,for example, rely on a gene from a traditionalvariety for the “dwarf” stature that enables theplant to channel nutrients from fertilizers intograin production without getting top-heavy andfalling over before harvest time. Although thedwarfing trait is effective in many locations,the high-yielding varieties need other geneticcharacteristics from many different varieties,The rice variety IR36, used in many countriesto sustain yield gains, was derived by cross-breeding 13 parents from 6 countries (19,87).

progress in tomato improvement in the UnitedStates has followed the use of exotic germplasm(traditional cultivars, wild forms of the domes-ticated species, and exclusively wild species).Fruit quality (color, sugar content, solids con-tent); adaptations for mechanized harvesting;and resistance to 15 serious diseases have beentransferred to the tomato from its wild relatives.One researcher noted:

Resistance to some of these diseases is man-datory for economic production of the crop inCalifornia, and it is doubtful whether the State’stomato industry would exist without these andother desired traits derived from exotics (77).

Rice and tomato illustrate the importance ofmaintaining as much of the genetic variationremaining within the domesticates and their

wild relatives as possible, because both cropshave benefited from genes occurring in a sin-gle population and nowhere else, Asian rice cul-tivars get their resistance to grassy stunt virus,a disease that in one year destroyed 116,000hectares (287,000 acres), from one collectionof Oryza nivara (53). The gene for a jointlessfruit-stalk (a trait that assists mechanized har-vesting and is worth millions of dollars per year)in tomato is found in a single population of awild relative (Lycopersicon cheesmanii) uniqueto the Galapagos Islands (78),

A variety of genetic resources is being usedin the breeding of livestock, particularly cattleand sheep. Crossbreeding Brahman cattle withHereford, Angus, Charolais, and Shorthornbreeds has had a major impact on commercialbeef production in North America (30). A num-ber of African cattle breeds are notable sourcesof disease and pest resistance (West AfricanShorthorn to trypanosomiasis, N’dama and Ba-ole to dermatitis, Zebu to ticks) (34), The Finn-ish landrace of sheep was almost lost beforeits high level of reproductive efficiency was dis-covered, It has now been incorporated intocommercial mating lines in the United King-dom and North America (30).

Yield and quality improvements can continueto be made and defended against pests and path-ogens, provided plant and animal breeding con-tinues to be supported and the genetic diversitythat breeders draw on is maintained, Indeed,there is no option but to go on improving cropsand livestock if world agriculture is to respondsuccessfully to economic and environmentalchanges and to the new strains of pests and dis-eases that evolve to overcome existing re-sistance.

VALUES AND EVALUATION OF BIOLOGICAL DIVERSITY

Biological diversity benefits everyone, is val-ued by many (in a variety of ways), but is ownedby no one. Thus, its evaluation is fraught withcomplexity. There are two broad classes ofvalue: economic and intrinsic.

Economic Value

Economic evaluation potentially covers allfunctional benefits described in this chapter,ranging from tangible benefits from harvested

Page 21: Part I Introduction and Background

54 “ Technologies To Maintain Biological Diversity

resources and breeding materials to spiritualand other cultural benefits. The ability to cal-culate these values varies, however. In the caseswhere markets exist, calculations are easily de-termined (at least $27,4 billion per year in theUnited States for commercially harvested wildspecies, as noted earlier). In other cases, valuesare more difficult to calculate, and “shadowprices” may be used to approximate values forsuch benefits as ecological processes and recre-ation, For cultural and esthetic values, eco-nomic valuation may be impossible,

If humans interacted in a system with limitedresources, then markets would allow equilib-rium prices to emerge for all commodities, serv-ices, amenities and resources. These priceswould reflect the relative values (including so-cial values) of each item. The essential prem-ises for economic valuation are utility and scar-city (75).

But for most benefits of biological diversity,free market principles do not apply. Mainte-nance of biological diversity is a “nonrival”good (it benefits everybody), and it is a “nonex-clusive” good (no person can be excluded fromthe satisfaction of knowing a species exists),as are many of its benefits (research and edu-cation, cultural heritage, nonconsumptive rec-reation, use of genetic resources). And it is notclear that market-oriented logic is adequate todeal with two cardinal features of biologicaldiversity: its potential for indefinite renewabil-ity (long-time horizon) and for extinction (ir-reversibility) (75).

CONSTITUENCIES

Biological diversity benefits a variety of in-terest groups, so its constituency is enormousbut fragmented by the interests of particulargroups. Each group may appear small com-pared with the Nation as a whole. Collectively,however, these groups and their combined con-cern amount to the national interest in main-taining biological diversity.

Intrinsic Value

Intrinsic evaluation acknowledges that othercreatures have value independent of humanrecognition and estimation of their worth. Theconcept is both ancient and universal. Aspokesperson of the San people of Botswanaput it this way:

Once upon a time, humans, animals, plants,and the wind, sun, and stars were all able totalk together. God changed this, but we are stilla part of a wider community. we have the rightto live, as do the plants, animals, wind, sun,and stars; but we have no right to jeopardizetheir existence (16).

This preceding statement might be supportedby Americans who believe in “existence values”—values that are defined independently of hu-man uses (68). This belief implies a human obli-gation not to eradicate species or habitats, evenif doing so harms no human. A 3-year studyof American attitudes toward wildlife foundthat the majority seemed willing to make sub-stantial social and economic sacrifices to pro-tect wildlife and its habitats (51). Advocates ofwildlife protection maintain that “it makes mefeel better to know there are bears in the area,even though I’d just as soon never run into one”(76). Proponents of biological diversity arguethat even if diversity is functionally redundantor has no utilitarian worth, it should be main-tained just “because it is there. ”

OF

A

DIVERSITY

Public Awareness

major obstacle to promoting effective andlong-term maintenance of biological diversityis the lack of awareness on the part of the gen-eral public of the importance of diversity (inthe broader sense). It is easy to understand whythe loss of biological diversity has difficulty cap-

Page 22: Part I Introduction and Background

turing public attention. First, the concept iscomplex to grasp. For this reason, efforts to so-licit support have appealed to emotionalismassociated with the loss of particularly appeal-ing species or spectacular habitats (86), Al-though effective in many cases, this approachhas the effect of limiting the constituency andthe boundaries of the problem. A second reasonis that the more pervasive threats to diversity,such as habitat loss or narrowing of agricul-tural crop genetic bases, are not dramatic eventsthat occur quickly. The difficulty is one of re-sponding to a potentially critical problem that,for the average person, seems to lack immediacy.

Finally, promoting the case for biologicaldiversity maintenance is also difficult becauseof the proliferation of environmental problemsbrought to public attention in the last decadeor two, including acid rain, ozone depletion,the greenhouse effect, and loss of topsoil. “Allthese environmental problems have the apoca-lyptic potential to destroy, yet in every case thecause, imminence, and scope of that power aresubject to polarizing (and eventually paralyz-ing) interpretation” (29).

Notwithstanding these difficulties, the envi-ronmental movement of the 1970s elevatedenvironmental quality to a major public policyconcern. Although the momentum of public at-tention may have slowed in the 1980s, it is clearthat concern for the environment remainsfirmly entrenched in the collective conscious-ness of the American public. A 1985 Harris poll,for example, indicated that 63 percent of Ameri-cans place greater priority on environmentalcleanup than on economic growth (41).

Ch. 2—importance of Biological Diversity 55

Balancing Interests andPerspectives

In assessing the level of public resources tobe directed toward maintaining biologicaldiversity, it is important to maintain a frameof reference of how, when, and for whom bio-logical diversity is important. Such a perspec-tive should consider:

1. varying perceptions on the value of biologi-cal diversity and threats to it;

2. an awareness that only some diversity canbe or probably will be saved; and

3. a recognition that resources available toaddress efforts are limited.

As mentioned earlier, biological diversity isnot at present a pervasive concern for manypeople, or at least there is no consensus thatas much diversity must be conserved as possi-ble. While earlier sections of this chapter iden-tified large constituencies that value biologi-cal diversity, some elements of society remainapathetic to the issue, and others support ef-forts to eliminate various components of diver-sity. For example, considerable resources aredirected to reducing populations or even elim-inating entire species of pests, pathogens, orpredators that threaten agriculture and humanhealth. In terms of public policy, such effortsimply a need to recognize that in some casesdiversity maintenance and other human inter-ests can conflict. It should be noted, however,that conflicts stem less from the existence ofdiversity than from the altered abundance ofparticular species.

CHAPTER 2 REFERENCES

1. Achiron, M., and Wilkinson, R., “Africa: TheLast Safari?” Newsweek, Aug. 18, 1986,

2. Agrawal, S, R., “Trees, Flowers and Fruits inIndian Folk Songs, Folk Proverbs, and FolkTales, ” Glimpses of Indian Ethnobotany, S.K.Jain (cd.) (New Delhi, Bombay, Calcutta, India:Oxford and IBH Publishing Co,, 1981).

3. Alaman Castro, M. C., Casanova Pena, C., andBueno Perez, M. A., “La Recognida de Germo-

plasma por el Noroeste de Espana, ” Plant Ge-netic Resources Newsletter 53:41-43, 1983.

4. Alaska Consultants and Stephen Braund &Associates, Subsistence Study of Alaska Es-kimo WhaZing ViZZages (Washington, DC: U.S.Department of the Interior, 1984).

5. Alaska Eskimo Whaling Commission, AlaskaEskimo Whaling (Barrow, AK: 1985).

6. AliNiazee, M. T., and Oatman, E. R., “Pest Man-

Page 23: Part I Introduction and Background

56 ● Technologies To Maintain Biological Diversity

agement Programs, ” Biological Control and In-sect Pest Management, D.W. Davis, et al. (eds.)(Oakland, CA: University of California, Divi-sion of Agricultural Sciences, 1979).

7. Ayala, F. J., “The Mechanisms of Evolution, ”Scientific American 239(3):56-69, 1978.

8. Basson, P. W., Burchard, Jr., J. E., Hardy, J. T,,and Price, A. R. G., Biotopes of the Western Ara-bian Gulf.” Marine Life and Environments ofSaudi Arabia, Aramco Department of Loss Pre-vention and Environmental Affairs (Dhahran:1977).

9. Berger, T. R., Village Journey: The Report ofthe Alaska Native Review Commission (NewYork: Hill & Wang, 1985).

10. Berquist, P. R., “Sponge Chemistry—A Re-v iew, Colloques Internationaux du C N R S291:383-392, 1978,

11. Bishop, G. W., Davis, D. W., and Watson, T. F.,“Cultural Practices in Pest Control,” Biologi-cal Control and Insect Pest Management, D.W.Davis, et al, (eds.) (Oakland, CA: University ofCalifornia, Division of Agricultural Sciences,1979).

12. Box, T. W., “Potential of Arid and Semi-AridRangelands,” Potential of the WorZd’s Foragesfor Ruminant Animal Production, 2d cd., R.D.Child and E.K. Byington (eds.) (Morrilton, AR:Winrock International Livestock Research andTraining Center, 1981).

13, Brown, W. L., “Genetic Diversity and GeneticVulnerability—An Appraisal, ” Economic Bot-any 37(1):4-12, 1983.

14, Brush, S. B., Carney, H. J., and Huaman, Z.,“Dynamics of Andean Potato Agriculture, ”Economic Botany 35(1):70-88, 1981,

15. Caldecott, J., and Nyaoi, A., “Hunting inSarawak,” report prepared for the Ad hoc Sub-committee on Mammals and Birds of the Sara-wak State Legislative Assembly Special SelectCommittee on Flora and Fauna, Sarawak For-est Department, Kuching, Malaysia, 1985.

16. Campbell, A. C., “Traditional Wildlife Popula-tions and Their Utilization, ” Which Way Bot-swana WiZdZife? proceedings of the Sympo-sium of the Kalahari Conservation Society,Gaborone, Botswana, Apr. 15-16, 1983.

17. Campbell, A. C., The Use of Wild Food Plantsand Drought in Botswana (Gaborone, Bot-swana: National Museum, no date).

18, Castleberry, R, M,, Crum, C. W., and Krull, C. F.,“Genetic Yield Improvement of U.S. MaizeCultivars Under Varying Fertility and ClimaticEnvironments,” Crop Science 24(1):33-36,1984.

19, Chang, T, T., Adair, C. R., and Johnston, T. H,,

“The Conservation and Use of Rice Genetic Re-sources,” Advances in Agronomy 35:37-9I,1982.

20. Chaudhuri, R. H. N., and Pal, D. C., “Plants inFolk Religion and Mythology, ” GZimpses of In-dian Etlmobotany, S.K. Jain (cd.) (New Delhi,Bombay, Calcutta, India: Oxford and IBH Pub-lishing Co., 1981),

21. Coe, E, H., and Neuffer, M. G., “The Geneticsof Corn, ” Corn and Corn Improvement, 2d cd.,Monograph 18, G.F. Sprague (cd.) (Madison,WI: American Society of Agronomy, 1977).

22. Cohn, L., “The Port Orford Cedar, ” AmericanForests, July 1986, pp. 16-19.

23. Cooke, H. J., “The Kalahari Today: A Case ofConflict Over Resource Use, ” The Geographi-cal Journal 151(1):75-85, 1985.

24. Damas, D. (cd.), Arctic, Volume 5: Handbookof North American Indians (Washington, DC:Smithsonian Institution, 1984).

25. Davis, R. A., Finley, K. J., and Richardson, W. J,,The Present Status and Future Managementof Arctic Marine Mammals in Canada (Govern-ment of Northwest Territories, Yellowknife:Science Advisory Board, 1980).

26. Duvick, D. N., “Genetic Diversity in MajorFarm Crops on the Farm and in Reserve,” Eco-nomic Botany 38(2):161-178, 1984.

27, Duvick, D. N., “Plant Breeding: Past Achieve-ments and Expectations for the Future, ” Eco-nomic Botany 40(3):289-297’, 1986.

28, Dyer, M. I., Detling, J. K., Coleman, D. C., andHilbert, D. W., “The Role of Herbivores inGrasslands,” Grasses and Grasslands: Sys-tematic and Ecology, J,R. Estes, R.J. Tyrl, andJ.N. Brunken (eds,) (Norman, OK: Universityof Oklahoma Press, 1982).

29, Ebisch, R., “A Layman’s Guide to ModernMenaces, ” TWA Ambassador, 18(10):49-58,October 1985.

30, Fitzhugh, H. A., Getz, W,, and Baker, F. H., “Sta-tus and Trends of Domesticated Animals, ”OTA commissioned paper, 1985.

31. Food and Agriculture Organization (FAO) ofthe United Nations, 1984 FAO ProductionYearbook, FAO Statistics Series 38 (Rome:1985).

32. Foster, R. B,, “Heterogeneity and Disturbancein Tropical Forest Vegetation, ” ConservationBiolog: An Evolutionary-Ecological Perspec-tive, M.E. Soulb and B.A. Wilcox (eds.) (Sunder-land, MA: Sinauer Associates, 1980).

33. Fowler, G., “Report on Grassroots GeneticConservation Efforts,” OTA commissioned pa-per, 1985.

34, Frankel, O. H., and SOU16, M, E., Conservation

Page 24: Part I Introduction and Background

35

36<

37.

38

39.

40.

41

42.

43.

44,

45.

and Evolution (Cambridge, MA: CambridgeUniversity Press, 1981).Fulton, R. W., “Nicotianas as Experimental Vi-rus IIosts, ” ,\’icotiana: Procedures for Experi-mental Use, Technical Bulletin 1586, R.D. Dur-bin (cd. ) (Washington, DC: U.S. Department ofAgriculture, 1979).Gadgil, M., and Vartak, V. D., “Sacred Gro\resof Maharashtra: An Inventory, Glimpses of[ndian Ethnobotan~, S.K. Jain (cd.) (IXew Delhi,Bombay, Calcutta, India: Oxford and IBH Pub-lishing Co,, 1981).Hagen, K. S., and Bishop, G. W., “Use of Sup-plemental Foods and Behavioral Chemicals toIncrease the Effectiveness of Natural Ene-mies, ” l?io]ogica] control and Insect Pest .Vlan-agement, D,W, []avis, et a], (eds) (Oakland, CA:University of California, Division of Agricul-tural Sciences, 1979).Hamilton, L. S., and King, P. N., Tropical ~or-ested Watersheds: HtiVdrologic and Soils Re-sponse to Major Uses or Conversions (Boulder,CO: Westview Press, 1983),Hamilton, 1.. S., and Snedaker, S.C. (eds.),Handbook for ,blangro~~e Area Management(Honolulu, HI: East-West Center, 1984).Harlan, J, R., crops and Man (Madison, WI:American Society of Agronomy, 1975),Harris, I.., “Current Public Perceptions, Atti-tudes, and Desires on Natural Resources Man-agement, ’ Transactions of the 50th NorthAmerican Wild]ife and Natura] Resources Con-ference [Washington, DC: Wildlife Manage-ment Institute, 1985), pp. 68-71.Harris, 1,. D., The Fragmented Forest: IslandBiogeographic Theory and the Preser~’ation ofBiotic Di~ersit~ (Chicago, IL, and London:Universit~r of Chicago Press, 1984).Henson, E. L., “An Assessment of the Conser-\’ation of Animal Genetic Diversity at theGrassroots Level, ” OTA commissioned paper,1985.Illinois Natural History Survey, “Slow Growthand Short I,ife Spans of Illinois River Carp, ”The Illinois .%ratural History Survey Reports257, 1986.International Union for Conservation of Na-ture and Natural Resources (IUCN], WorldConser~ation Strateg~: Living Resource Con-servation for Sustainable Development (Glandand Nairobi: International Union for Conser-vation of Nature and Natural Resources-UnitedNations Environmental Program-World Wild-life Fund, 1980).

46.

47.

48.

49

50

51.

52.

53.

54.

55

56.

Ch. 2—importance of Biological Diversify ● 5 7

IRRI Cropping Systems Program, 1973 AnnualReport (Los Banes, Philippines: The Interna-tional Rice Research Institute, 1973),Jabs, C., The Heirloom Gardener (San Fran-cisco, CA: Sierra Club Books, 1984).Janzen, D. H., “Guanacaste National Park:Tropical Ecological and Cultural Restoration, ”project report to Servicio de Parques Nacion-ales de Costa Rica, Fundacion de Parques Na-cionales de Costa Rica, Fundacion N’eotropica,Nature Conservancy International Program.Department of Biology, University of Pennsyl-vania, Philadelphia, 1986,Kaplan, E. H., A Field Guide to Coral Reefs ofthe Caribbean and Florida Including Bermudaand the Bahamas (Boston, MA: Houghton Mif-flin, 1982).Kavanagh, M., “Planning Considerations fora System of ~National Parks and Wildlife Sanc-tuaries in Sarawak, ” Sara~ak Gazet/e 61 :15-29, 1985.Kellert, S. R., “Americans’ Attitudes andKnowledge of Animals, ” Transactions of the45th North American Wildlife and Natural Re-sources Conference, 1980 (Washington, DC:Wildlife Management Institute, 1980].Kennedy, J. A., “Protected Areas for Teachingand Research: The Universit~’ of California Ex-perience, ” National Parks, Conservation, andDe\’elopment: The Role of Protected Areas inSustaining Society, J.A. McNeely and K.R.Miller (eds.) (Washington, DC: Smithsonian In-stitution Press, 1984).Khush, G, S., Ling, K. C., Aquino, R.(; ., andAguiero, V. M., “Breeding for Resistance toGrassy Stunt in Rice, Plant Breeding Papersl(4b):3-9, 1977.Kido, H., Flaherty, D, L,, Bosch, D. F., andValero, K. A., “Biological Control of GrapeLeafhopper, California Agriculture 37:4-6,1983,Lucas, P. H. C., “How Protected Areas Can HelpMeet Society’s Evolving Needs, ” NationalParks, Conservation, and De~elopment: 7’heRole of Protected Areas in Sustaining Societ~’,J.A. McNeely and K.R. Miller (eds.] (Washing-ton, DC: Smithsonian Institution Press, 1984).Maser, C,, and Trappe, J.M. (eds. ), The Seenand Unseen World of the Fa]]en Tree, GeneralTechnical Report PNW-164 (portland, OR: U.S.Department of Agriculture, Forest Service, Pa-cific Northwest Forest and Range ExperimentStation, 1984).

57. ,Ntayr, E., The Gro\~’th of Biological Thought:

Page 25: Part I Introduction and Background

58 ● Technologies To Maintain Biological Diversity—

Diversity, Evolution, and Inheritance (Cam-bridge, MA, and London: Belknap Press ofHarvard University Press, 1982).

58, McGuire, P. E., and Qualset, C.O. (eds.), Pro-ceedings of a Symposium and Workshop onGenetic Resources Conservation for California,Napa, Apr. 5-7, 1984.

59. McNaughton, S. J., “Serengeti Migratory Wilde-beest: Facilitation of Energy Flow by Graz-ing, ” Science 191:92-94, 1976.

60. McNaughton, S. J., “Grazing as an Optimiza-tion Process: Grass-Ungulate Relationships inthe Serengeti, ” American Naturalist 113:691-703, 1979.

61. McNeely, J. A., and Wachtel, P. S., Power, Pol-itics, Religion, Nature, and Animals: How theCoalition Has Worked in Southeast Asia(Gland, Switzerland: International Union forConservation of Nature and Natural Resourcesand World Wildlife Fund, 1986).

62, Mirov, N. T., and Hasbrouck, J., The Story ofPines (Bloomington, IN: Indiana UniversityPress, 1976].

63. Myers, N,, A Wealth of Wild Species: Store-house for Human Welfare (Boulder, CO: West-view Press, 1983).

64. Nabhan, G., and Dahl, K., “Role of GrassrootsActivities in the Maintenance of BiologicalDiversity: Living Plant Collections of NorthAmerican Genetic Resources, ” OTA commis-sioned paper, 1985.

65. National Plant Genetic Resources Board, PlantGenetic Resources: Conservation and Use(Washington, DC: U.S. Department of Agricul-ture, 1979).

66. The Nature Conservancy, Preserving Our Nat-ural Heritage, Volume I: Federal Activities(Washington, DC: U.S. Department of the In-terior, National Park Service, 1977).

67, Nikiforuk, A., “Secrets in a Snake Pit, ” A4ac-]ean’s, May 28, 1984.

68, Norton, B., “Value and Biological Diversity, ”OTA commissioned paper, 1985.

69, Okazaki, T., “Genetic Study on PopulationStructure in Chum Salmon (OncorhynchusKeta), ” Bulletin of Far Seas Fisheries ResearchLaboratory 19:25-116, 1982.

70. Okazaki, T., “Genetic Structure of ChumSalmon (Oncorhynchus Keta) River Popula-tions,” BuZZetin of the Japanese Society of Sci-entific Fisheries 49(2):189-196, 1983.

71. Oldfield, M, L., The VaZue of Conserving Ge-netic Resources (Washington, DC: U.S. Depart-ment of the Interior, National Park Service,1984).

72, Piearce, G. D., “The Zambezi Teak Forests: ACase Study of the Decline and Rehabilitationof a Tropical Forest Ecosystem, ” prepared forthe 12th Commonwealth Forestry Conference,Victoria, BC, Canada, Division of Forest Re-search, Kitwe, September 1985.

73. Prescott-Allen, C., and Prescott-Allen, R., TheFirst Resource: Wild Species in the NorthAmerican Economy (New Haven, CT, andLondon: Yale University Press, 1986).

74. Prescott-Allen, R., “National ConservationStrategies and Biological Diversity, ” a reportto International Union of Conservation of Na-ture and Natural Resources, Conservation forDevelopment Centre (Gland, Switzerland: Sep-tember 1986),

75, Randall, A,, “An Economic Perspective on theValuation of Biological Diversity, ” OTA com-missioned paper, 1985.

76. Randall, A., “Human Preference, Economics,and the Preservation of Species, ” The Preser-vation of Species, B. Norton (cd. ) (Princeton,NJ: Princeton University Press, 1986].

77. Rick, C. M., “Collection, Preservation, and Useof Exotic Tomato Genetic Resources, ” Pro-ceedings of a Symposium and Workshop onGenetic Resources Conservation for California,Napa, P.E, McGuire and C,O, Qualset (eds.],Apr. 5-7, 1984.

78. Rick, C. M,, and Fobes, J. F., “Allozymes of Ga-lapagos Tomatoes: Polymorphism, GeographicDistribution, and Affinities, ” Evolution 29:443-457, 1975.

79. Russell, W. A,, “Dedication: George F. Sprague,Corn Breeder and Geneticist ,“ PZant BreedingReviews. Volume Z, J. Janick [cd.) (Westport,CT: AVI Publishing Co., 1984).

80. Saenger, P., Hegerl, E. J,, and Davie, J. D. S.,Global Status of Mangrove Ecosystems, Com-mission on Ecology Papers 3 (Gland, Switzer-land: International Union for Conservation ofNature and Natural Resources, 1983).

81, Sedell, J. R., Bisson, P. A., June, J. A., andSpeaker, R. W., “Ecology and Habitat Require-ments of Fish Populations in South Fork HohRiver, Olympic National Park, ” EcoZogicaZ Re-search in National Parks of the Pacific North-west: Proceedings, Zd Conference on ScientificResearch in the NationaZ Parks, 1979, E.E. Star-key, J,F, Franklin, and J.W. Matthews (eds.),Oregon State University, Forest Research Lab-oratory, Corvallis, 1982.

82. Smart, P., The Illustrated Encyclopedia of theButterfly World (London: Salamander Books,1976).

Page 26: Part I Introduction and Background

83. Smith, G. C., and Alderdice, D., “Public Re-sponses to National Park Environmental Pol-icy, ” Envjronrnent and ~ehat~or 11(3)329-350,1979.

84, Smith, H. H., “The Genus as a Genetic Re-

85<

86,

87.

88.

89

90.

91.

92.

source, Nicotiana: Procedures for Experi-mental Use, Technical Bulletin 1586, R.D. Dur-bin (cd.) (Washington, DC: U.S. Department ofAgriculture, 1979).Soul;, M. E., “Thresholds for Survival: Main-taining Fitness and Evolutionary Potential, ”Conser~ation Biolog: An Evolutionary-Ecolog-ica] Perspective, M. E. Soule and B.A. Wilcox(eds.) (Sunderland, MA: Sinauer Associates,1980).Stanfield, R. L., “In the Same Boat, ” National~ourna~, Aug. 16, 1986, pp. 1992-1997.Swaminathan, M. S., “Rice, Scientific Amer-ican January 1984, pp. 81-93.Tiner, R. W., Wetlands of the United States:Current Status and Recent Trends (Washing-ton, DC: U.S. Department of the Interior, Fishand Wildlife Service, 1984].U.S. Congress, Office of Technology Assess-ment, Impacts of Applied Genetics: Micro-organisms, Plants, and Animals, OTA-HR-132(Washington, DC: U.S. Government PrintingOffice, April 1981).U.S. Congress, Office of Technology Assess-ment, Wetlands: Their Use and Regulation,OTA-O-206 (Washington, DC: U.S. Govern-ment Printing Office, March 1984).U.S. Congress, Office of Technology Assess-ment, Grassroots Conservation of BiologicalDiversit~ in the United States—Background Pa-per ,#1, OTA-BP-F-38 (Washington, DC: U.S.Government Printing Office, February 1986).U.S. Department of Agriculture, AgriculturalStatistics 1981 (Washington, DC: U.S. Govern-ment Printing Office, 1981).

Ch. 2—/mportance of Biological Diversity ● 5 9

93<

94,

95,

96.

97

98

99,

100.

101

U.S. Department of Agriculture, Forest Serv-ice, An Assessment of the Forest and RangeLand Situation in the United States, Forest Re-source Report 22 (Washington, DC: 1981).U.S. Department of the Interior, National ParkService, Index: National Park System and Re-lated Areas as ofJune 1, 1982 (Washington, DC:1982).U.S. Department of the Interior and U.S. De-partment of Commerce, U.S. Fish and Wild-life Service and U.S. Bureau of the Census,1980 National Survey of Fishing, Hunting, andWildlife-Associated Recreation (Washington,DC: 1982).Vartak, V. D., and Gadgil, M., “Studies on Sa-cred Groves Along the Western Ghats FromMaharashtra to Goa: Role of Beliefs and Folk-lores, ” Glimpses of Indian Ethnobotan~r, S.K.Jain (cd.) (New Delhi, Bombay, Calcutta, India:Oxford and IBH Publishing Co., 1981).Webb, M,, Environmental Affairs Office,World Bank, Washington, DC, personal com-munication, June 1986.Wells, S. M., Pyle, R. M., and Collins, N. M., TheIUCN Invertebrate Red Data Book (Gland,Switzerland: International Union for Conser-vation of Nature and Natural Resources, 1983).Wilson, E. O., The Insect Societies (Cambridge,MA: Belknap Press of Harvard UniversityPress, 1971].World Resources Institute/International Insti-tute for Environment and Development, WorldResources 1986 (New York: Basic Books, Inc.,1986).Worrall, D., A Baffin Region Economic Base-line Study: Economic De~’elopment and Tour-ism (Yellowknife: Government of the North-west Territories, Department of EconomicDevelopment and Tourism, 1984).


Recommended