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Documenting Ecological Change in Time and Space: The San Joaquin Valley of California.

Mammalian Diversification:
From Chromosomes to Phylogeography
University of California, Berkeley
(pp. 57-78, In press)

Patrick A. Kelly, Scott E. Phillips, and Daniel F. Williams

California State University, Stanislaus
Endangered Species Recovery Program
Fresno, CA 93727

Contact for Correspondence:

Patrick Kelly
California State University, Stanislaus
Endangered Species Recovery Program

Abstract

The collections and journal archives of the Museum of Vertebrate Zoology (MVZ) at the University of California, Berkeley provide a unique historical database that can be effectively mined using new technologies in genetics and spatial analysis to address serious challenges to the conservation of biological diversity. Through direct reference to the journal entries of Joseph Grinnell and other MVZ biologists of the early 1900s and quantitative analyses of land use changes, we document the tempo and scale of land conversion through the 20th century in the San Joaquin Valley of California. We discuss the impacts of landscape level habitat changes to populations of selected mammal species, most notably the endemic San Joaquin kangaroo rat (Dipodomys nitratoides). Of the three described subspecies, two (Tipton, D. n. nitratoides; Fresno, D. n. exilis) are listed as endangered under the California and U.S. endangered species acts, and the third (short-nosed, D. n. brevinasus) is a California species of special concern. Despite intensive field surveys since 1992, we have been unable to locate a population of Fresno kangaroo rats. This is particularly troubling because analysis of cyt-b DNA sequences, which were developed from museum specimen tissue samples, has shown that the Fresno kangaroo rat is unique and strongly differentiated from the other two subspecies. As the population of California continues to grow, the assault on biological diversity will continue. Analyses of the unique historical data provided by the MVZ and other natural history museums, using the tools of modern molecular genetics and spatial analysis, are essential to addressing these threats and halting or reversing the decline of biological diversity.

Introduction

Since its establishment in 1908, the Museum of Vertebrate Zoology (MVZ) at the University of California, Berkeley has provided remarkable intellectual leadership in the ecology and evolution of terrestrial vertebrates, with emphasis on western North America. Most of this work has been in the realm of field biology. Joseph Grinnell set the example for museum scientists with his extensive field trips throughout California. Today, MVZ scientists continue to work in various ecosystems throughout the western United States, Central and South America, and elsewhere in the world. When they are not in the field, MVZ scientists are conducting genetic and other analyses in the laboratory to support their field studies. Few other institutions have amassed such a body of scholarship and knowledge about the natural world, or have worked as assiduously to promote field research as has the MVZ.

An appreciation for and desire to conserve the natural world has been a central theme in the MVZ’s long record of research and service, even if that appreciation was not always explicitly expressed in terms we might use today. The discipline we call conservation biology is the modern philosophical incarnation of a particular ecological worldview, one that evolved from economic zoology and more recently, from disciplines such as wildlife management, population ecology, behavioral ecology, and other fields (Hall 1939a, b, Grinnell 1940, Linsdale 1942). MVZ scientists have played a large role in conservation biology throughout the museum’s history. To understand this role, we provide a retrospective using extensive references to the work and writings of Joseph Grinnell and other principal figures in the early days of the museum.

Almost immediately upon his appointment as the first Director of the MVZ in 1908, Joseph Grinnell took a deep personal interest in Yosemite National Park (Runte 1990). Grinnell and other MVZ scientists conducted the key surveys that documented the vertebrate fauna of Yosemite. From this foundation of intensive field research, Grinnell played a critical role in the evolution of the management policies not only for Yosemite, but also for the National Park Service (Runte 1990). He wrote thousands of letters and memos to park officials (Runte 1990, p. 127). This dedication was not out of a sense of duty to assist in public administration. Rather, through his unfading commitment to science, Grinnell gently urged, prodded, and guided park officials towards more scientific management policies, directed primarily towards the conservation of native species (Runte 1990, p. 129). Through his commitment to public education, he also fostered and encouraged public support for science-based management principles and practices in the parks (Runte 1990, p. 111-112). Today, Yosemite is one of the crown jewels of the U.S. National Park System and is appreciated annually by millions of visitors from all over the world.

When Joseph Grinnell passed away prematurely in 1939, his legacy was measured by more than the prodigious numbers of study skins, journal pages, and publications he produced during his 21-year tenure as director; his commitment to conservation had become woven into the fabric of the MVZ. Over the past century, MVZ scientists and students have continued to follow Grinnell’s philosophy. Through their profound commitment to preserving as well as understanding the natural world. This commitment is needed more today than ever before.

It is probable that “Californians Incorporated,” a commercial agency whose efforts are expended vigorously toward securing congestion of human population in the San Francisco Bay region, is right now the greatest single enemy of wild animal life in west-central California. The slogan “where life is better” is a curious perversion: it has sinister portents for even man himself.

Joseph Grinnell (1928)

When Joseph Grinnell wrote these prophetic words, California had a human population of less than 6,000,000. By 2000, more than 33,000,000 persons called California home. This more than five-fold increase in population has resulted in very serious consequences for biological diversity throughout California. Further losses in biological diversity, sometimes referred to as natural capital (UNEP-WCMC 2001), are inevitable. The State of California is expected to have a population of about 46,000,000 people by 2020 (California Department of Finance 2001). The impacts of this high rate of population growth are being felt throughout California but they have been most profound in four of the State’s ten bioregions: South Coast, Central Coast, Bay Delta, and San Joaquin Valley (California Biodiversity Council 1992). In this analysis, we report on landscape change in the San Joaquin Valley over the past century and describe the consequences of these changes for biological diversity in this region. MVZ scientists have worked in the San Joaquin Valley since 1911. Their collections and journal archives provide a unique historical database that can be effectively mined using new technologies in genetics and spatial analysis to address significant challenges to the conservation of biological diversity in the San Joaquin Valley. We report on an initial exploration of this body of work and make recommendations for future study.

The San Joaquin Valley: A Century of Change

March 1911 saw the arrival of the first MVZ expedition in the San Joaquin Valley (Grinnell 1911). Joseph Grinnell, Harry Swarth and other MVZ biologists spent much of March, April, and May, 1911, collecting at various localities throughout the San Joaquin Valley and the Carrizo Plain. This was followed by much more work by Grinnell, Swarth, Joseph Dixon, Ward Russell, Seth Benson and many others in 1912 and subsequent years. The extensive journal notes from the MVZ expeditions not only describe the fauna of the region but also paint a detailed and graphic picture of a changing landscape:

The surrounding country is flat and mostly farmed (wheat and orchards); unless it has been graded the surface shows the queer hummocky condition know locally as hog-wallow land [vernal pool ecosystem] of clayey, “hard pan”.

Joseph Grinnell, Lane Bridge,
10 mi. N Fresno, Fresno Co., 6 April 1911.

Proceeding to Goshen this afternoon, the country is observed from the train. Practically every rod from Berenda [Madera Co.] to Selma [Fresno Co.] is under close cultivation in grain, alfalfa, raisins, and orchards.

Joseph Grinnell, Goshen, Fresno Co., 23 April 1911.

To the north and northwest the county is pretty closely farmed, up to the Tule River; but a belt through Tipton and to the south and east, is largely grazing land yet tho there are pumps being put in and it is only a matter of a few years until every rod of ground in under cultivation.

Joseph Grinnell, Tipton, Tulare Co., 24 April 1911

Left Berkeley at 8:00 A.M., catching the 8:53 train at Oakland, which reached Bakersfield at 8 P.M. I had thus a good chance to see the whole length of the San Joaquin Valley, on the east side. It appears to be nearly all under cultivation, or else used as pasturage, and open tracts are evidently changing rapidly, being divided into smaller holdings and more intensively cultivated.

Harry Swarth, traveling from Oakland to
Bakersfield by train, 5 May 1911.

Left Bakersfield on the 8:15 A.M. train (which pulled out at 9:30) reaching McKittrick at 11:30. The stretch of country between the two places is not cultivated as I expected to see it. Outside of Bakersfield were long stretches of brush land, and then miles of bottom land, with ditches and sloughs, pretty well grown up with cotton woods and willows. Around Buttonwillow there was a good deal of alfalfa and other hay fields, but from there to McKittrick it was all brush land, much of it quite sandy.

Harry Swarth, traveling from Bakersfield to
McKittick (western Kern Co.) by train, 17 May 1911.

The MVZ journal archives again and again reveal the commitment to detail exhibited by Grinnell and his field teams. They not only surveyed the landscape and collected examples of the fauna, but they also reported on numerous conversations and interviews with local residents, especially ‘old-timers.’ Grinnell’s journal entries in particular are peppered with references to local observations on the presence, or, more usually, absence of kit foxes (Vulpes macrotis), “chipmunks” (antelope ground squirrels, Ammospermophilus nelsoni), kangaroo rats (Dipodomys spp.), bighorn sheep (Ovis canadensis), grizzly bears (Ursus arctos) and other mammals that were declining in numbers or losing significant amounts of habitat to land conversion by the early 1900s:

One man interviewed said there were “Kangaroo rats” in his place six years ago when he first plowed but that he had seen none since. Several have told us that 20 years or more ago “rattlesnakes and kangaroo rats” abounded in certain places in the vicinity of Fresno. Evidently the mammal and reptile fauna of the region have been as profoundly modified by human settlement as the birds.

Joseph Grinnell, Clovis, Fresno Co., 11 April 1911

It would seem that this chipmunk [antelope ground squirrel] is retreating in range from the east side of the Tulare Valley, as the country settles up (either cultivated or pastured closely) and as the ground squirrel (C. beecheyi) comes in. We are repeatedly told that the latter has only recently come into this belt, and that it is becoming more numerous all the while.

Joseph Grinnell, Earlimart, Tulare Co., 1 May 1911

Mr. J.S. Douglas is the superintendent of the ranch here. He has been in the country since the 70’s, and is absolutely trustworthy. He tells me as follows: He personally knows of sheep [bighorn sheep] in the Sespe Country, where the last one was killed in 1900. On the San Emigdio ranch, there were many sheep in the steep hills in the 70’s and early 80’s. Many were shot. In 1888 there were fully 150 sheep in 3 flocks.

Joseph Grinnell, San Emigdio Ranch (Wind Wolves Preserve today), Kern Co., 22 April 1912

The landscape that Grinnell and Swarth described on the east side of the San Joaquin Valley differed significantly from that of the west side in the early 1900s. The great water projects–the Central Valley Project and the State Water Project–had not yet been undertaken and much of the west side was still open rangeland characterized by a mix of grassland, alkali sink scrub, and salt bush scrub (Kahrl 1978, Reisner 1987, Thelander 1994, USFWS 1998, Hundley 2001). Between 1915 and 1923, Joseph Dixon spent a considerable amount of time in the San Joaquin Valley, much of it on the “plains” on the west side of the valley. There, he documented the detrimental effects of human activity on native fauna such as pronghorn antelope (Antilocapra americana) and the kit fox:

Serious inroads have been made into the population of kit foxes in the San Joaquin Valley, comprising the subspecies mutica. Large numbers of the animals have been caught there for fur in recent years. For instance, in 1919 Arthur Oliver caught 100 foxes in one week on an area 20 miles long and 2 miles wide, on the plains on the west side of the San Joaquin Valley, in Fresno County. (See fig. 162.) On December 3, 1920, 37 steel traps set in that region caught 5 kit foxes in one night.

Grinnell, Dixon, and Linsdale (1937 p. 418).

Far more significant inroads than those provided by fur trappers were in store for kit foxes however. The MVZ photography archive records the impact of agricultural activity in this region between 1920 and 1937 (Figure 1a, from Grinnell, Dixon, and Linsdale 1937, p. 419). For this study, on June 3, 2001 one of us (PAK) took a photograph at the same location as Dixon’s 1920 photograph (Figure 1b). This location (36.67738 North, 120.62191 West, Datum WGS 84) is 25.1 km southwest (bearing 216º) of Firebaugh, Fresno Co. This point is about 5 km from the base of the foothills and, unlike in 1920, is now completely cultivated. Today, most of the west side plains of the San Joaquin Valley are cultivated to the base of foothills.

figure1a

Figure 1a. Western Fresno Co. kit fox habitat in 1920. (Derived from photograph by Joseph Dixon, Archives, Museum of Vertebrate Zoology, University of California, Berkeley).

figure1b

Figure 1b. The same location in 2001. (CSU Stanislaus, Endangered Species Recovery Program).

With the progressive construction of water storage and delivery projects over the past century—notably the massive Central Valley and State Water projects (1935 to 1970)—great tracts of formerly uncultivated or rarely cultivated land were converted to intensive agricultural use (Kahrl 1978, Reisner 1987, Thelander 1994, Hundley 2001). The natural landscape became increasingly fragmented as grasslands, wetlands, shrublands, woodlands and forests were converted for cultivation (Figures 2a-d). The fragmented mosaic of natural and cultivated land described by Grinnell and Swarth in 1911 and 1912 gave way over time to the vast cultivated landscape evident today (USFWS 1998).

figure2

Figure 2. Agricultural land conversion in the San Joaquin Valley, pre-European settlement to 2000.

Effects On Native Mammals

The scale of land conversion in the San Joaquin Valley over the past 100 to 150 years is staggering (Figure 3, Table 1). We estimate that there has been a loss of more than 29,000 km2 of natural communities in the San Joaquin Valley. About 64% of grasslands, 91% of water and wetlands, 97% of riparian forest/oak woodland, and 67% of shrublands have been converted to agricultural use (Table 1). The resulting losses in biological diversity are almost incalculable. If we were to assume conservatively that valley grasslands had an average annual small mammal biomass of 0.300 kg/ha (i.e., low density and low diversity situation of 5-10 kangaroo rats or 15-20 ‘mice’ per hectare), the loss of grasslands represented in Table 1 would translate to an annual loss of 542.85 metric tonnes of small mammals. When we consider the interrelated population dynamics of small mammals and the many predatory species that largely depend on them (e.g, carnivores, raptors, owls, snakes), this loss in biodiversity is compounded significantly.

figure3

Figure 3. Percent change in natural community cover in the San Joaquin Valley, pre-European settlement to 2000.

Table 1. Estimated area changes (km2) by major land cover category in the San Joaquin Valley, pre-European settlement to 2000.

Land Cover CategoryPre-European2000ChangePercent
Developed or degraded 0 29,228 29,228
Grasslands 28,400 10,304 -18,095 -63.7
Open water and Wetlands 5,146 463 -4,683 -91.0
Riparian/Valley oak woodland 2,893 94 -2,799 -96.8
San Joaquin Valley shrublands 5,553 1,929 -3,624 -65.3

Mammals that have larger area requirements (e.g., tule elk (Cervus elaphus), pronghorn, and kit foxes) were quickly impacted by the settlement and development of the San Joaquin Valley. Perhaps less evident were effects on species with seemingly smaller area requirements. Work by MVZ researchers, however, indicates that these species also appear to be very susceptible to habitat fragmentation and degradation. We have already noted Grinnell’s 1911 observations that kangaroo rats and antelope ground squirrels appeared to be declining in the face of land settlement. Extensive field research throughout the San Joaquin Valley since 1992 by biologists with the California State University, Stanislaus, Endangered Species Recovery Program (ESRP) confirmed Grinnell’s fears that kangaroo rats are susceptible to habitat fragmentation (USFWS 1998, Uptain et al. 1999). A review of the MVZ collections and journal archives helps reveal the extent of the impact to kangaroo rat populations from land conversion.

Between 1911 and 1960, MVZ expeditions collected San Joaquin kangaroo rats (Dipodomys nitratoides) at 20 localities throughout the San Joaquin Valley (Figure 4). We estimate that D. nitratoides is currently extant at probably no more than nine of these locations, seven of which are in the band of largely uncultivated rangeland that remains around the margins of the San Joaquin Valley. The remaining two locations are in Tulare County, in the vicinity of the Pixley National Wildlife Refuge and the California Department of Fish and Game’s Allensworth Ecological Reserve. These two public land holdings are still occupied by D. nitratoides, at least on some land parcels, but most of the valley floor locations trapped by Grinnell and other MVZ researchers have given way to cultivation. Where uncultivated lands remain on the valley floor, they are usually privately owned and often closed to trapping surveys.

figure4

Figure 4. MVZ collection localities for San Joaquin kangaroo rats, 1911 to 1960.

There are some small populations of D. nitratoides at other locations, especially in the southern San Joaquin Valley, that are not represented in the MVZ collections. San Joaquin kangaroo rats however, have largely disappeared from the valley floor. Populations seem to be in a continuing decline, probably due to the combined effects of habitat conversion, fragmentation, degradation, and other factors (Chesemore and Rhodehamel 1992, Williams and Kilburn 1992, Williams and Germano 1993, Goldingay et al. 1997, USFWS 1998, Uptain et al. 1999, Kelly 2000). Populations in the more or less continuous band of grassland around the valley periphery are doing better but, even there, San Joaquin kangaroo rats are difficult to find.

The Tools of Conservation Ecology.

Joseph Grinnell was a visionary scientist and conservationist. At the very outset of his MVZ career, he recognized that the true value of the museum would not be gained from the simple accumulation of vertebrate specimens.

It is quite probable that the facts of distribution, life history, and economic status may finally prove to be of more far-reaching value, than whatever information is obtainable exclusively from the specimens themselves.

At this point I wish to emphasize what I believe will ultimately prove to be the greatest value of our museum. This value will not, however, be realized until the lapse of many years, possibly a century, assuming that our material is safely preserved. And this is that the student of the future will have access to the original record of faunal conditions in California and the west wherever we now work. He will know the proportional constituency of our faunae by species, the relative numbers of each species and the extent of the ranges of species as they exist to-day.

Perhaps the most impressive fact brought home to the student of geographical distribution, as he carries on his studies, is the profound change that is constantly going on in the faunal make-up of our country. Right now are probably beginning changes to be wrought in the next few years vastly more conspicuous than those that have occurred in ten times that length of time preceding. The effects of deforestation, of tree-planting on the prairies, of the irrigation and cultivation of the deserts, all mean the rapid shifting of faunal boundaries, the extension of ranges of some animals, restriction in the ranges of others, and, with no doubt whatever, the complete extermination of many others, as in a few cases already on record.

Joseph Grinnell (1910)

The tools that Grinnell employed in his work were his scientific intellect, exceptional observational skills, the thousands of scientific specimens he and his colleagues so painstakingly collected, and, above all else, the detailed journal notes that he accumulated during his surveys of the western United States. A century later, the MVZ has powerful tools that were unavailable to Grinnell. The rapid development of new techniques in genetics, spatial analysis, and landscape ecology that have been pioneered or rapidly adopted by MVZ scientists, have provided fresh insights into not only evolutionary questions, but also our most pressing conservation concerns.

Genetics

This application of new technology is exemplified by the work of James Patton (in litt.), who on the basis of cyt-b DNA sequences, has shown that the Fresno kangaroo rat (D. n. exilis) is unique and strongly differentiated from the other two subspecies of the San Joaquin kangaroo rat, the Tipton and short-nosed kangaroo rats (D.n. nitratoides and D.n. brevinasus,respectively). This finding is noteworthy because both the Fresno and Tipton subspecies are listed as endangered by the State and Federal governments. Despite intensive surveys and trapping efforts conducted throughout its former range, not a single Fresno kangaroo rat has been captured since 1992. One individual was captured on the California Department of Fish and Game’s Alkali Sink Ecological Reserve on two occasions in Nov. 1992 by one of us (DFW, ESRP data), and Patton’s analyses of D. n. exilis had to be completed using tissue biopsies taken from study skins in collections at the MVZ and California State University, Fresno. On the basis of this new genetic information, if extant populations of the Fresno kangaroo rat can be located, they are likely to be given the highest priority for conservation by government agencies.

Spatial Analysis

As with technological developments in genetic analysis, there have been tremendous developments in recent years in computer and database technology. In particular, rapid growth in computer and satellite technologies now provide powerful tools for spatial analyses; in particular, geographic information systems (GIS) and global positioning systems (GPS). GIS technology allows a user to create databases that store both spatial and tabular information. Spatial data registered to a common map coordinate system can then be compared based on location. Historical map and descriptive data can be combined with current information to assess spatial changes over time. This enhances a user's ability to query database records based on their location relative to other geographic features. GPS provides researchers with greater ability to remotely collect and retrieve spatial information . Compact and inexpensive GPS receivers provide the ability to geo-reference field locations in the field, rather than after the fact. This can be very valuable for relating locations to external spatial data derived from a GIS.

To investigate the patterns of habitat loss noted by Grinnell and others in the San Joaquin Valley, we used GIS to combine historical and modern map sources for developed lands. We combined developed lands data with historical vegetation data to map and quantify the level of habitat loss at different time intervals.

We estimated the extent of historical vegetation types using wetland features from 1885 irrigation maps (Hall 1890) and GIS data derived from a map of potential vegetation of California (ESRP and USBR MPGIS 1999). We scanned the source maps and used image processing software to align the images to a common map coordinate system.

To normalize the classification differences between sources, we reclassified map features to four general habitat types: grasslands; shrub lands; riparian/Valley oak woodland; and open water/wetlands. We digitized the reclassified map information to a GIS database to quantify the area of each habitat type within our study area.

Using scanned irrigation and land cover maps and GIS data, we estimated the extent of developed land in 1885, 1912, 1940, and 2000 (Hall 1890, USDA 1912, USBR MPGIS 1996, USGS 1990, CSUS/ESRP 2001). We used the GIS to combine historical vegetation and developed land data for each time interval. We next calculated the area of habitat lost in each category between each time interval. Table 1 lists changes in habitat categories between pre-European settlement and 2000.

Recently the MVZ has been adding geo-referenced location data to museum specimen records (Wieczorek 2001). The availability of these geo-referenced data provides an ability to easily map record locations. More importantly, it provides researchers with the ability to relate information associated with record locations to external spatial data. Where specimen collection locations coincide with areas of lost habitat, we can gain further insights into the dynamics of landscape change from journal entries, genetic data, and other associated information.

The Challenge.

As Joseph Grinnell predicted in 1910, the MVZ collections and journals are needed now more than ever. The persistent growth of the human population of California continues to erode the tremendous, and in many ways unique, biological diversity of the State.

Many of the species that Grinnell inquired about when interviewing local residents of the San Joaquin Valley in 1911 and 1912 are now either extinct, rare, or are listed as sensitive, threatened, or endangered by the State and Federal governments. Ecosystems throughout California are threatened by urbanization, resource extraction, recreation, and other anthropogenic activities.

The vernal pool ecosystems (“hog-wallow land”) that Grinnell commented on in 1911 have been greatly reduced and will likely become further degraded in the coming years. For example, ground-breaking for the University of California’s 10th campus occurred on Oct. 25, 2002 near the city of Merced, immediately adjacent to the largest remaining expanse of vernal pools in the San Joaquin Valley.

Proposed housing, commercial, highway, and other infrastructure developments present a more routine and pervasive threat to biodiversity. Agency biologists are required daily to provide their professional judgment on the likely impacts of such developments on sensitive species and ecosystems, usually with an incomplete knowledge of the distribution, abundance, and natural history of the affected species, and nearly always with no phlyogeographic information for key species.

The pressures on the remaining natural land in California continue to intensify, suggesting that the decline of ecosystems and their constituent flora and fauna will continue. MVZ scientists and students have at their disposal the tools needed to address these increasingly serious conservation challenges. In particular, they have the opportunity and tools to identify and provide a better understanding of major phylogeographic boundaries in California. It is our fervent hope that the MVZ will continue its strong leadership role in addressing these conservation challenges in the years ahead.

Acknowledgements.

The authors would like to extend their sincere gratitude to Jim Patton for his friendship, scholarship, advice, and support over many years of professional and personal interaction. If Joseph Grinnell were alive today, he would be very pleased to know that Jim has so closely followed in his footsteps.

Our institution is a repository of facts; and no matter what may be said to the contrary by those who undervalue the efforts of the hoarder of facts, it must always be the mass of carefully ascertained facts upon which the valid generalization rests.

Joseph Grinnell (1910)

Jim’s accumulation of facts about the ecology and evolution of small mammals throughout the New World has been nothing short of astonishing. Those of us who have had the privilege to work with Jim over the years also know that he has contributed many “valid generalizations” as well.

The biological surveys, genetic studies, and GIS analyses referenced in this chapter were largely supported by the Bureau of Reclamation, the U.S. Fish and Wildlife Service, and the California Department of Fish and Game. We are grateful for their support. The opinions expressed are those of the authors, not necessarily the opinions of the sponsoring agencies.

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