[Federal Register Volume 59, Number 163 (Wednesday, August 24, 1994)]
[Unknown Section]
[Page 0]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 94-20790]
[[Page Unknown]]
[Federal Register: August 24, 1994]
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DEPARTMENT OF THE INTERIOR
50 CFR Part 17
RIN 1018-AB73
Endangered and Threatened Wildlife and Plants; Five Plants From
the San Bernardino Mountains in Southern California Determined to be
Threatened or Endangered
AGENCY: Fish and Wildlife Service, Interior.
ACTION: Final rule.
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SUMMARY: The U.S. Fish and Wildlife Service (Service) determines
Erigeron parishii (Parish's daisy) to be threatened and Eriogonum
ovalifolium var. vineum (Cushenbury buckwheat), Astragalus albens
(Cushenbury milk-vetch), Lesquerella kingii ssp. bernardina (San
Bernardino Mountains bladderpod), and Oxytheca parishii var.
goodmaniana (Cushenbury oxytheca) to be endangered pursuant to the
Endangered Species Act of 1973, as amended (Act). These five plant
species are endemic to the carbonate deposits (limestone and dolomite)
of the San Bernardino Mountains, San Bernardino County, California.
Most of the carbonate deposits in this mountain range are within
actively used mining claims or mining claims that are being maintained
for their mineral resources. Limestone, ranging from cement grade to
pharmaceutical grade, is currently mined in the area; dolomite is not
currently mined. The open or terraced mining techniques that are used,
as well as associated overburden dumping and road construction, result
in destruction of the plants' habitat. Other threats to the plants
include off-highway vehicle use, urban development near the community
of Big Bear, expansion of a ski area, and energy development projects.
Several of the plants are also threatened with stochastic extinction
due to the small numbers of populations or total number of individuals.
This rule implements the Federal protection and recovery provisions
afforded by the Act for these five plants.
EFFECTIVE DATE: September 23, 1994.
ADDRESSES: The complete file for this rule is available for public
inspection, by appointment, during normal business hours at the U.S.
Fish and Wildlife Service, Ventura Field Office, 2140 Eastman Avenue,
Suite 100, Ventura, California 93003.
FOR FURTHER INFORMATION CONTACT: Carl Benz at the above address or at
(805) 644-1766.
SUPPLEMENTARY INFORMATION:
Background
The San Bernardino Mountains in southern California have been
recognized for supporting a wide diversity of natural habitats that
have resulted from their geographic position between desert and coastal
environments, elevational zonation, and uncommon substrates such as
limestone outcrops. The San Bernardino National Forest (Forest), which
encompasses most of the San Bernardino Mountains, constitutes less than
1 percent of the land area of the State, yet contains populations of
over 25 percent of all plant species that occur naturally in
California.
Outcrops of carbonate substrates, primarily limestone and dolomite,
occur in several bands running on an east-west axis along the desert-
facing slopes of the San Bernardino Mountains, with disjunct patches
occurring just to the south of Sugarlump Ridge and to the east as far
as the Sawtooth Hills. These outcrops are a remnant of an ancient
formation of sandstone, shale, and limestone, through which the
granitic core of the Transverse Ranges has emerged (Fife 1988).
The five taxa under discussion, Erigeron parishii (Parish's daisy),
Eriogonum ovalifolium var. vineum (Cushenbury buckwheat), Astragalus
albens (Cushenbury milk-vetch), Lesquerella kingii ssp. bernardina (San
Bernardino Mountains bladderpod), and Oxytheca parishii var.
goodmaniana (Cushenbury oxytheca), are restricted primarily to
carbonate deposits or soils derived from them. These taxa, and other
plants that occur on carbonate deposits, have commonly been referred to
as ``limestone endemics'' by botanists, whether they occur on limestone
or dolomite (Krantz 1990, Schoenherr 1992). Collectively, these five
taxa span a range approximately 56 kilometers (km) (35 miles) long,
ranging in elevation from 1,220 meters (4,000 feet (ft)) at the base of
the mountains to approximately 2,440 meters (8,000 ft), and occur as
components in the understory of a variety of plant communities,
including Jeffrey pine-western juniper woodland, pinyon-juniper
woodland, pinyon woodland, Joshua tree woodland, blackbrush scrub, and
desert wash.
Pinyon-juniper woodland communities dominate the desert-facing
slopes above 1,220 meters (4,000 ft) in elevation, and grade into a
Joshua tree woodland at lower elevations (Vasek and Thorne 1988).
Pinyon-juniper woodlands extend up to almost 2,100 meters (7,000 ft) in
elevation, where they intergrade with a Jeffrey pine woodland on drier
sites or mixed conifer forest on wetter sites. Open forests of
lodgepole pine and limber pine are found at the highest elevations. A
wide variation in the species composition exists within the pinyon-
juniper woodland. Pinus monophylla (pinyon pine) or Juniperus
osteosperma (Utah juniper), and more rarely Juniperus occidentalis
(western juniper) or Juniperus californica (California juniper), are
the structurally dominant species, occasionally occurring together.
Holland (1986) has referred to separate Mojavean pinyon woodland and
Mojavean juniper woodland and scrub communities. The understory varies
with slope and elevation, but typically includes species such as
Cercocarpus ledifolius (mountain mahogany), Ephedra viridis (Mormon
tea), Yucca schidigera (Mohave yucca), Yucca brevifolia (Joshua tree),
and Encelia virginensis (encelia). Patches of local dominance by
Coleogyne ramosissima (blackbrush) on lower elevation desert facing
slopes, or Arctostaphylos sp. (manzanita) on more interior canyons, are
common.
Erigeron parishii is a small perennial herb of the aster family
(Asteraceae) that reaches 1 to 3 decimeters (dm) (4 to 12 inches (in))
in height. The linear leaves are covered with soft, silvery hairs. Up
to 10 solitary flower heads are borne on cauline stalks; ray flowers
are deep rose to lavender, and heads have greyish green and glandular
phyllaries. E. parishii was first described by Asa Gray in 1884 based
on specimens collected by Samuel B. Parish in Cushenbury Canyon in
1881. E. parishii has sometimes been confused with E. utahensis, a
plant found on carbonate substrates in the mountains of the Mojave
Desert and in Utah, Colorado, and Arizona, but differs from the latter
in the structure of the pappus and its silvery-white rather than grey-
green stem.
Erigeron parishii is the most widely ranging of the five taxa
discussed herein, with a range 56 km (35 miles) long. The plant is
known from fewer than 25 occurrences, with the total population
numbering approximately 16,000 individuals. Fewer than a third of the
occurrences comprise more than 1,000 individuals each (Barrows 1988a).
From White Knob at the western terminus, populations occur primarily
along the belt of carbonaceous substrates, southeast to Pioneertown.
The plant is typically found associated with pinyon woodlands, pinyon-
juniper woodlands, and blackbrush scrub from 1,220 to 1,950 meters
(4,000 to 6,400 ft) in elevation. It is usually found on dry rocky
slopes, shallow drainages, and outwash plains on substrates derived
from limestone or dolomite. Some populations occur on a granite/
limestone interface, usually a granitic parent material overlain with
an outwash of limestone materials. Two small outlying populations at
the eastern edge of its range near Pioneertown occur on quartz
monzonite substrates. Historic occurrences were recorded from
Rattlesnake Canyon south of Old Woman Springs and from the Little San
Bernardino Mountains; these locations have not been surveyed in over 50
years and merit additional field surveys (Andy Sanders, University of
California, Riverside, pers. comm., 1992).
Eriogonum ovalifolium var. vineum is a low, densely-matted
perennial of the buckwheat family (Polygonaceae). The flowers are
whitish-cream, darken to a reddish or purple color with age, and are
borne on flowering stalks reaching 1 dm (4 in) in height. The plant
flowers from May through June. The round to ovate leaves are white-
woolly on both surfaces and are 0.7 to 1.5 centimeters (cm) (0.3 to 0.6
in) long. The diameter of mats is typically 1.5 to 2.5 dm (6 to 10 in),
but may reach up to 5 dm (20 in) in particularly well-developed
individuals.
Eriogonum ovalifolium var. vineum was first collected by S.B.
Parish near Rose Mine, San Bernardino Mountains, in 1894, and was
described as E. vineum by John K. Small in 1898. In 1911, Aven Nelson
published the combination E. ovalifolium var. vineum. Jepson in his
manual used the combination of E. ovalifolium var. vineum in 1943. Munz
(1959) accepted the work of Stokes (1936), and recognized it as E.
ovalifolium ssp. vineum, in his flora of California. In 1968, Reveal
clarified the relationship of the plant to E. ovalifolium var. nivale,
with which it had been confused, and used the name E. ovalifolium var.
vineum (Reveal and Munz 1968). Three other varieties of E. ovalifolium
are distinguished on the basis of floral and leaf characteristics, but
none of them occur in the San Bernardino Mountains.
Eriogonum ovalifolium var. vineum is limited in distribution to the
belt of carbonate substrates of the north slopes of the San Bernardino
Mountains. The plant is currently known from approximately 20
occurrences over a distance of about 40 km (25 miles). Only a quarter
of those occurrences comprise more than 1,000 individuals each (Barrows
1988b), with the total population numbering approximately 13,000
individuals. E. ovalifolium var. vineum occurs from the White Knob area
east to Rattlesnake Canyon. Surveys by Barrows (1988b) resulted in a
slight range extension of the plant in the Rattlesnake Canyon drainage.
Since publication of the proposal, additional surveys by the Forest
staff located two previously unknown populations, one near Jacoby
Springs and one just north of Mineral Mountain (CNDDB 1992). Tierra
Madre Consultants (TMC) located a previously unknown population west of
White Knob (TMC 1992), which extends the known range of the plant west
by 1.6 km (1 mile). A dozen other extensions of existing occurrences
were reported by the Forest Service and TMC; all of these were within
the known range of the plant (CNDDB 1992, TMC 1992).
Eriogonum ovalifolium var. vineum occurs within openings of pinyon
woodland, pinyon-juniper woodland, Joshua tree woodland, and blackbrush
scrub communities between 1,400 and 2,400 meters (4,600 and 7,900 ft)
in elevation. Other habitat characteristics include open areas with
little accumulation of organic material, a canopy cover generally less
than 15 percent, and powdery fine soils with rock cover exceeding 50
percent. The plant typically occurs on moderate slopes, although a few
occurrences are on slopes over 60 percent. On milder, north-facing
slopes, it co-occurs with Astragalus albens.
Recent fieldwork by Howard Brown (Pluess-Staufer Inc., in litt.,
1992) has refined the information on the carbonate geology of the San
Bernardino Mountains. Eriogonum ovalifolium var. vineum clearly occurs
on limestone substrate in the White Knob area, and from Arctic/Bousic
Canyon west to Terrace Springs, south to Top Spring, and along the
north side of Lone Valley to Tip Top Mountain. However, E. ovalifolium
var. vineum occurs on dolomite in the Bertha Ridge area, north Holcomb
Valley, Jacoby Canyon, and along Nelson Ridge, according to Brown (in
litt., 1992). Additionally, a population just to the south of Mineral
Mountain is clearly on non-carbonate substrates; a population in
Furnace Canyon seems to be on a mixed lithology of granite, limestone,
and dolomite; and a population on Heartbreak Ridge is on carbonate
substrate.
Astragalus albens is a small silvery-white perennial herb in the
pea family (Fabaceae). The slender stems are decumbent, grow to 30 cm
(12 in) in length, and support leaves comprised of 5 to 9 small
leaflets. The purple flowers, which bloom from March to May, occur
toward the ends of the branches in 5-to 14-flowered racemes and develop
8- to 11-seeded pods. In 1885, A. albens was described by Edward L.
Greene based on a collection made by Parish and Parish 3 years earlier
(Greene 1885). In 1927, Per Axel Rydberg published the name Hamosa
albens (Rydberg 1927). In 1964, R.C. Barneby synonymized the genus
Hamosa and included the species in Astragalus (Barneby 1964). A.
leucolobus, a common associate on carbonate soils, is distinguished
from A. albens by its cobwebby pubescence on the leaflets, which are
strongly folded along the midrib, and differently shaped pods.
Astragalus albens is currently known from fewer than 20 occurrences
scattered throughout the eastern half of the carbonate belt, running
from Furnace Canyon southeast to the head of Lone Valley, a range of 24
km (15 miles). The proposal stated that the total number of individuals
was estimated at 2,000, but that this number is likely to be greater in
years of substantial rainfall. Several known populations comprised a
larger number of individuals during the 1992 field season than had
previously been reported. That may, in part, be due to favorable
rainfall during March 1992, which resulted in a large establishment of
seedlings, and in part to a more thorough survey effort. Of
significance is the extension of a population in the Top Spring-Smarts
Ranch Road area; several thousand individuals were found in this area,
making it the primary population center for the species. Population
estimates for 1992 place the total number of individuals between 5,000
and 10,000.
The plant is typically found on carbonate substrates along rocky
washes and gentle slopes within pinyon woodland, pinyon-juniper
woodland, Joshua tree woodland, and blackbrush scrub communities.
Erigeron parishii and Eriogonum ovalifolium var. vineum co-occur with
Astragalus albens at several locations. Most occurrences are found
between 1,500 and 2,000 meters (5,000 and 6,600 ft) in elevation on
soils derived directly from decomposing limestone bedrock. Three
occurrences are found below 1,500 meters (5,000 ft) in elevation in
rocky washes that have received limestone outwash from erosion higher
in the drainages. According to Brown (in litt., 1992), two populations
occur on granite substrates (Gordon Quarry and Granite Peaks), and one
occurs on granite and quartzite (Cactus Flat). Other habitat
characteristics include an open canopy cover with little accumulation
of organic material, rock cover exceeding 75 percent, and gentle to
moderate slopes (5 to 30 percent).
Lesquerella kingii ssp. bernardina is a silvery, short-lived
perennial member of the mustard family (Brassicaceae) reaching 1 to 2
dm (4 to 8 in) in height. The plant has yellow flowers located toward
the ends of the stems. The basal leaves are ovate and have long
petioles. The type material was collected by Frank W. Peirson at the
east end of Bear Valley in 1924. In 1932, Munz described this plant as
L. bernardina. In 1958, Munz combined L. bernardina with L. kingii, and
made the combination of L. kingii ssp. bernardina (Wilson and Bennett
1980). L. kingii ssp. kingii is found in the mountains of the eastern
Mojave Desert and the Inyo-White ranges extending into Nevada. It is
distinguished from L. kingii ssp. bernardina by its smaller petals and
styles.
Lesquerella kingii ssp. bernardina is currently known from two
areas, on either side of Bear Valley. One cluster of occurrences is on
the north side of the valley, near the east end of Bertha Ridge,
adjacent to the community of Big Bear, and is subject to impacts from
urbanization. The other cluster is centered on the north-facing slope
of Sugarlump Ridge to the south of the valley, approximately 10 km (6
miles) south of the Bertha Ridge occurrences. These latter occurrences
were discovered during spring 1990 on an existing downhill ski run, and
on and adjacent to proposed ski runs and lift lines within an existing
ski area (California Natural Diversity Data Base (CNDDB) 1990). The
estimate of total number of individuals in the Bertha Ridge occurrences
was 25,000 in 1980 and less than 10,000 in 1988; it is unclear whether
this was due to differences in sampling techniques or drought
conditions (Wilson and Bennett 1980, CNDDB 1990). In 1991, the
Sugarlump Ridge populations totalled approximately 10,000 individuals
(CNDDB 1991).
The habitat for Lesquerella kingii ssp. bernardina is characterized
by carbonate substrates, either brown sandy soils with white carbonate
rocks or outcrops of large carbonate rock. According to geologic
information supplied by Brown (in litt., 1992), all populations of L.
kingii ssp. bernardina both in the Bertha Ridge and the Sugarlump Ridge
areas occur on dolomite. Slopes are typically gentle to moderate and
are both north- and south-facing between 2,100 and 2,700 meters (6,800
and 8,800 ft) in elevation. Within Jeffrey pine-western juniper
woodlands, as well as white fir forest in some locations, the
subspecies is found in open areas with little accumulation of organic
material. The plant seems to be tolerant of slight disturbance;
scattered plants were found growing on old roads, undeveloped lots, and
undeveloped yards within the Whispering Forest housing tract (Myers and
Barrows 1988). However, the plant is conspicuously absent from heavily
graded and mulched ski runs in the Bear Mountain ski area.
The carbonate substrates that support Lesquerella kingii ssp.
bernardina lie south and west of those that support most of the
populations of the other four taxa under discussion. However, near the
east end of Bertha Ridge, the southernmost population of Eriogonum
ovalifolium var. vineum occurs in close proximity to one colony of
Lesquerella kingii ssp. bernardina.
Oxytheca parishii var. goodmaniana is a small wiry annual of the
buckwheat family (Polygonaceae). The type material was collected by
Parish and Parish in 1882 near Cushenbury Spring. For a number of
years, historical collections were mistakenly identified as O. parishii
var. abramsii or O. watsonii. Barbara Ertter (1980) described the
variety in honor of George J. Goodman, who was the first to recognize
both the distinctiveness of the variety and its close relationship to
O. parishii. O. parishii var. goodmaniana stands 0.5 to 3 dm (2 to 12
in) tall with a basal rosette of leaves 1 to 3 cm (0.4 to 1.2 in) long
and stems with bracts at the nodes. The flowers consist of 6 small
white to rose or greenish-yellow petals; clusters of 3 to 12 flowers
are subtended by a distinct involucral bract. O. parishii var.
goodmaniana is separated from the other three varieties of O. parishii
by the presence of only four to five awns on the bracts, rather than
seven or more.
Oxytheca parishii var. goodmaniana is the most restricted of the
carbonate endemic species of the San Bernardino Mountains. Forest
Service surveys in 1992 located three additional populations, bringing
the total number of known occurrences to seven (CNDDB 1992). One
location near Cushenbury Spring is located near an active limestone
mine; two more occurrences are located near the abandoned Green Lead
gold mine, one of which is bisected by a road; the fourth occurrence is
located near the north side of Holcomb Valley. The three newly
discovered populations are located along the Helendale Fault in the
vicinity of Tip Top Mountain, Mineral Mountain, and Rose Mine. This
represents a significant extension of approximately 19 km (12 miles) to
the southeast from the previously known range of the plant. Given the
availability of potentially suitable habitat between the newly
discovered and the previously known populations, other sites supporting
this taxon may be found with additional surveys.
With the exception of the north Holcomb Valley population, which
occurs on dolomite, all populations of Oxytheca parishii var.
goodmaniana occur on limestone or a mixed lithology of limestone and
dolomite (TMC 1992). In 1990, the total known population consisted of
fewer than 3,000 individuals. With discovery of the new populations,
however, current estimates have been doubled. Since it is an annual
species, the number of individuals might be higher in years with winter
and spring rainfall and temperatures favorable to seed germination and
seedling establishment. The low number of occurrences, however, as well
as individuals, also subjects the species to the possibility of
stochastic extinction.
Previous Federal Action
Federal action on three of the five plants began when the Secretary
of the Smithsonian Institution, as directed by section 12 of the Act,
prepared a report on those native U.S. plants considered to be
endangered, threatened, or extinct in the United States. This report
(House Document No. 94-51), which included Erigeron parishii and
Lesquerella kingii ssp. bernardina as threatened and Eriogonum
ovalifolium var. vineum as endangered, was presented to Congress on
January 9, 1975. On July 1, 1975, the Service published a notice in the
Federal Register (40 FR 27823) accepting the report as a petition
within the context of section 4(c)(2) (now section 4(b)(3)) of the Act
and of the Service's intention thereby to review the status of the
plant taxa named therein, including Erigeron parishii, Eriogonum
ovalifolium var. vineum, and Lesquerella kingii ssp. bernardina.
The Service published an updated notice of review for plants on
December 15, 1980 (45 FR 82480). This notice included Eriogonum
ovalifolium var. vineum and Lesquerella kingii ssp. bernardina as
category 1 candidates (species for which the Service has substantial
information on biological vulnerability and threat to support proposals
for listing) and Erigeron parishii as a category 2 candidate (species
for which data in the Service's possession indicate listing is possibly
appropriate, but for which substantial information on biological
vulnerability and threats is not currently available to support
proposals for listing).
On February 15, 1983 (48 FR 6752), the Service published a notice
of its prior finding that the listing of Eriogonum ovalifolium var.
vineum and Lesquerella kingii ssp. bernardina is warranted but
precluded in accordance with section 4(b)(3)(B)(iii) of the Act, as
amended in 1982. Pursuant to section 4(b)(3)(C)(i) of the Act, the
finding must be recycled on an annual basis, until the species is
either proposed for listing or the petitioned action is found to be not
warranted. In October 1983, 1984, 1985, 1986, 1987, 1988, 1989, and
1990, further findings were made that the listing of Eriogonum
ovalifolium var. vineum and Lesquerella kingii ssp. bernardina was
warranted, but that the listing of these species was precluded by other
pending proposals of higher priority. In the September 27, 1985 (50 FR
39526), and February 21, 1990 (55 FR 6184), plant notices of review,
Eriogonum ovalifolium var. vineum and Lesquerella kingii ssp.
bernardina were again included as category 1 candidates, and Erigeron
parishii as a category 2 candidate. The February 21, 1990, notice also
included Astragalus albens in category 1 and Oxytheca parishii var.
goodmaniana in category 2. Since publication of that notice, additional
survey work was completed for Oxytheca parishii var. goodmaniana,
providing new information on the status of that species. Similarly, the
Service was made aware of increased threats to Erigeron parishii, in
the form of two new pending mining operations that would likely
adversely impact this species. As a result, on November 19, 1991 (56 FR
58332), the Service published a proposed rule in the Federal Register
to list the five plants as endangered.
Summary of Comments and Recommendations
In the November 19, 1991, proposed rule and associated
notifications, all interested parties were requested to submit factual
reports or information relevant to a final decision on the listing
proposal. Appropriate State agencies, county governments, Federal
agencies, scientific organizations, and other interested parties were
contacted and requested to comment. Requests for a public hearing were
received from eight parties, primarily mining industry representatives,
but also including the National Inholders Association and the Bear
Mountain Ski Resort. As a result, on May 15, 1992, and again on May 26,
1992, the Service published notices in the Federal Register (57 FR
20805 Bernardino Sun and the Barstow Desert Dispatch. Requests for a
public hearing were received from eight parties, primarily mining
industry representatives, but also including the National Inholders
Association and the Bear Mountain Ski Resort. As a result, the Service
conducted a hearing on June 3, 1992, at the San Bernardino County
Government Center in San Bernardino. Testimony was taken from 1 p.m. to
4 p.m., and from 6 p.m. to 8 p.m., with 21 parties presenting
testimony.
During the comment periods, the Service received written and oral
comments from 51 parties. Multiple comments were received from mining
industry representatives, both during and after the closure of the
comment periods. The California Department of Fish and Game, The Nature
Conservancy, California Native Plant Society, Audubon Society, Sierra
Club, Natural Heritage Foundation, Center for Plant Conservation,
Rancho Santa Ana Botanic Garden, University of California Natural
Reserve System, and the Forest Service were 10 of 36 commenters
expressing support for the listing proposal. Eleven commenters,
including seven mining industry representatives, two multiple-use
groups, and one assemblyman opposed the listing. The Bureau of Mines
initially opposed the listing during the public comment period.
However, oral testimony at the public hearing by a Bureau of Mines
representative indicated a more neutral stance and an offer to assist
in data analysis to be used in the development of a Forest Service
habitat management guide for the five taxa. Most of those opposed to
the listing also asked for a 6-month extension to the rulemaking
process to allow results of additional surveys completed during the
1992 field season to be included in the final determination. Four
commenters were neutral, including a Congressman, one county
supervisor, and the Big Bear Chamber of Commerce. In addition, results
of additional surveys for the plants (CNDDB 1992, TMC 1992) and
additional biological information that was submitted to the Service
since publication of the proposal have been incorporated into this
final rule. Opposing comments and other comments questioning the rule
have been organized into specific issues. These issues and the
Service's response to each are summarized as follows:
Issue 1: Numerous comments were received concerning the Service's
reference to the five plants as ``limestone endemics'' in the proposal.
This reference appears to be of great concern to the mining industry
because a number of populations occur on dolomite, quartz monzonite,
granite, or mixed lithologies of these substrates, and not solely on
limestone, in the strict sense. Other commenters focused on the
Service's use of inaccurate geologic maps that indicated that
substrates at particular plant locations were limestone, while maps
currently being revised by the U.S. Geological Survey (USGS) will
indicate that substrates in those locations may actually consist of
dolomite or other rock types. Many of these commenters believe that
more accurate geologic data would disprove the hypothesis that these
plants are ``limestone endemics.''
Service Response: According to the Dictionary of Geologic Terms,
one definition of ``limestone'' is given as ``(A) general term for that
class of rocks that contain at least 80 per cent of the carbonates of
calcium or magnesium'' (American Geologic Institute 1976). Apparently
in keeping with this definition, the USGS map for the Lucerne Valley
quadrangle (7.5 minute series) referred to the Furnace Limestone unit
as being comprised of white carbonate rocks, grey carbonate rocks,
quartzite, and phyllite--metasedimentary rocks of Paleozoic age (USGS
1964). Similarly, the California Division of Mines and Geology map for
the San Bernardino quadrangle (1:250,000) refers to the same units as
upper Paleozoic limestone and marble, and Cambrian and uppermost
Precambrian crystalline limestone (California Division of Mines and
Geology 1986). These maps represent the best information available to
the Service. The colloquial use of the term ``limestone endemic'' to
refer to the five taxa under discussion is based, in part, on the
generic use of the term ``limestone'' by geologists and botanists.
While intending to use ``limestone'' as a generic term, the Service
erred in the proposal by referring to such substrates as calcium
carbonate deposits, rather than simply carbonate deposits. The term
calcium carbonate, or limestone in the more technical sense, refers to
carbonate with a high percent of calcium, as differentiated from
dolomite, which is carbonate with a high percent of magnesium. The
Service has used more precise descriptions of substrate type in this
rule and generally refers to these species as ``carbonate endemics.''
The Service looks forward to any additional information that the
revised USGS maps will provide.
Issue 2: Numerous commenters contended that the plants are not
endemic to the 35-mile range of the north slope of the San Bernardino
Mountains but are also found to the east and west of that range and in
mountain ranges of the Mojave Desert. Several commenters indicated that
geologists had observed several of the taxa in the New York Mountains.
Service Response: The record of botanical collections and surveys
from the San Bernardino Mountains and the Mojave Desert ranges is more
than adequate to establish general ranges of the plants. Additional
surveys were conducted in 1992 in four mountain ranges in the east
Mojave Desert, in the San Bernardino Mountains, and in the San Gabriel
Mountains to determine any range extensions for the five taxa. Only one
of the four new populations of Erigeron ovalifolium var. vineum was
located outside of the known range and this was within a mile of known
locations. The Forest Service also conducted additional surveys in 1991
and 1992 for all five taxa, which resulted in a significant range
extension for Oxytheca parishii var. goodmaniana. However, with the
exception of the range extension for Oxytheca parishii var.
goodmaniana, the newly located populations do not represent significant
new biological or distributional data affecting the status of the
remaining four plants. Although the new range extension for Oxytheca
parishii var. goodmaniana is considered significant, the taxon is still
so limited in distribution that listing as endangered is still
appropriate. In addition, no unthreatened populations were discovered.
Issue 3: Numerous commenters contended that surveys for the plants
were not adequate or up-to-date, that the plants have only been found
on limestone because only limestone substrates were targeted for
surveys, and that the discovery of additional populations with each new
survey indicates that the plants are more widespread than previously
thought. Some commenters stated that the surveys were performed by
``biased individuals'' whose unpublished reports had not been subject
to peer review, and that information on which the proposal was based
constituted ``junk science.'' Other commenters stated that the existing
knowledge of the plants was more than adequate to proceed with listing,
and that a 6-month extension for the purpose of collecting additional
information on the range and distribution of the plants, as requested
by the mining industry, was unnecessary.
Service Response: Botanists have been collecting plants in southern
California for scientific study for over 150 years; all five plants
were originally collected at least 100 years ago. Carbonate substrates
in particular have been the focus of numerous surveys because botanists
have recognized that these nutrient-deficient substrates often support
unique taxa. As early as 1979, the Forest Service performed rangewide
surveys of three of the taxa (Erigeron parishii, Eriogonum ovalifolium
var. vineum, and Lesquerella kingii ssp. bernardina). Moreover, since
1979, the Forest Service has conducted surveys of almost all ground-
disturbing projects on the San Bernardino National Forest to determine
project impacts to species considered to be sensitive and has performed
botanical investigations of at least 25 taxa. The surveys have been
conducted on numerous substrates and throughout the geographic range of
the San Bernardino and adjacent National Forests, including the San
Bernardino, San Gabriel, and San Jacinto Mountains. While the Service
recognizes that new occurrences may be discovered through additional
surveys, the body of information is adequate to proceed with this
listing. The Service accepts the reliability of the surveys performed
and considered this information the best scientific information
available.
Issue 4: Several commenters charged that the Service ignored
results of propagation studies on Erigeron parishii and Eriogonum
ovalifolium var. vineum performed by Rancho Santa Ana Botanic Garden
that indicate that 1) the two plants do not require limestone, and 2)
the plants are easy to propagate from seeds and cuttings. The industry
believes these results show a potential for successful reclamation
after mining.
Service Response: The Service is fully aware of the propagation
efforts for two of the species (Erigeron parishii and Eriogonum
ovalifolium var. vineum) by Rancho Santa Ana Botanic Garden researchers
(Mistretta 1991). However, germination or survival under horticultural
conditions does not accurately represent conditions required for long-
term survival in the wild. Other efforts to propagate Erigeron parishii
from seed have met with less success (Forest Service 1992). The results
of these studies are preliminary and inconclusive, and the long-term
viability of species under cultivation is questionable. In addition,
the normal life histories and other habitat characteristics of
substrate endemics typically are not maintained in horticultural
settings.
The success rate for salvage of Eriogonum ovalifolium var. vineum
from the Gordon Quarry was less than 50 percent (Forest Service 1992).
Although some potential for reclamation with these species after mining
may exist, the purpose of the Act is to conserve ecosystems upon which
listed species depend. Reintroduction is a potentially important
recovery tool, but it has not been shown to restore mine sites to pre-
disturbance conditions that would ensure the long-term survival of such
plants and, therefore, does not preclude the need to list the species.
Issue 5: Several commenters were concerned that important
information concerning the potential for reclamation of mined sites was
not included in the proposal. They claim that three of the plants
(Astragalus albens, Erigeron parishii, and Eriogonum ovalifolium var.
vineum) are opportunistic, weedy intruders, or invaders. As evidence,
they cited the Barrows surveys that document populations occurring on
roadbeds, roadcuts, and quarry benches. They also state that
accompanying notes indicate populations in these disturbed habitats are
more vigorous or more dense than those on adjacent pristine areas, and
the plants appear to tolerate light disturbances. Some commenters
indicated that old roadbeds, roadcuts, and old quarry benches
constituted more than ``lightly disturbed'' habitat, and that the
plants in fact can recolonize heavily disturbed sites. One commenter
stated that ``the effects of mining as a possible positive influence''
had not been considered.
Service Response: The Service did not reference Astragalus albens,
Erigeron parishii, and Eriogonum ovalifolium var. vineum growing on old
roadbeds, roadcuts, and quarry benches because, in most cases, these
plants did not constitute independent self-perpetuating populations,
but rather scattered individuals that had dispersed into disturbed
habitat from adjacent populations on undisturbed habitat. The Forest
Service has noted that Eriogonum ovalifolium var. vineum and Erigeron
parishii have colonized infrequently used roads at three sites, and
small quarries at two sites, each of which is less than 1 hectare (2
acres) in size, have been abandoned for 20 to 25 years, and had small
patches of native vegetation left within them at the time of mining. In
contrast, no colonization by any of the five plants has been observed
in the larger quarries. Furthermore, Forest Service surveys at the
Right Star site for Astragalus albens indicate that the mean density of
individuals in disturbed areas is significantly lower than that in
adjacent undisturbed areas (137 versus 679 per acre) (Forest Service,
in litt., 1992).
Initial flushes of recolonization by plants may occur in response
to light and very intermittent disturbance. The mechanism under which
recolonization occurs and its role in the long-term survival of the
five species is unknown. Research on recolonization may indicate that
the species can recolonize areas to aid in their long-term survival.
However, data do not indicate that these plants have extensive
recolonization capabilities. Heavily disturbed sites, (i.e., those
stripped to bedrock with little residual fine-textured substrates, and
with no nearby islands of native vegetation from which plants can
recolonize) do not show any levels of successful recolonization.
Several recent reports document Erigeron parishii occurring on
tailing slopes (Brown, in litt., 1992). Recent observations by an
interagency reclamation review team that visited all four current
quarry operations on the north slope of the San Bernardino Mountains
found that Salsola sp. (Russian thistle) was the most prevalent plant
on tailing slopes and road berms (Forest Service 1992). Erigeron
parishii or the other taxa under discussion on even ``lightly
disturbed'' sites may or may not represent independent self-
perpetuating populations.
Issue 6: Several commenters stated that a lack of understanding of
mining operations has led to a premature conclusion about the impact of
mining on plant habitat. One commenter noted that a block of mining
claims does not represent the actual area that would be disturbed
during mining operations. Brown (in litt., 1992), who recently remapped
the geology of the San Bernardino quadrangle in collaboration with
USGS, stated that about 2 percent of the limestone in the San
Bernardino Mountains is of commercial value and would be subject to
mining within the next 75 years. The remaining limestone will not be
mined, though virtually all of it is under claim.
Service Response: The impact of mining on plant habitat is not
restricted to the quarry site itself, but includes loss of habitat
through overburden (materials that need to be removed to reach the
underlying limestone, as well as the low-grade limestone that is
currently not being marketed) dumping, tailing dumping, road
construction (including sidecasting), and exploratory mining activity,
which may constitute a surface disturbance several times the size of
the quarry. Additional biological values of the habitat may be lost
through habitat fragmentation, alteration of hydrology, and an increase
in airborne particulates that may depress pollinator success.
Aside from whether the extent of primary and secondary impacts of
mining on plant habitat are being accurately assessed, the threat that
exists to plant habitat from the mere presence of mining claims must be
considered. According to the Mining Law of 1872 (30 U.S.C. 22 et seq.),
a claimholder must have a sincere intent to mine; in fact, a claim can
be legally seized by another party if the original claimholder is shown
not to meet this requirement. No mechanisms are currently available to
Federal land management agencies making regulatory decisions to protect
sensitive natural resources on lands that are under claim. This
situation is discussed more thoroughly under Factor D below.
Issue 7: A few commenters stated that the Endangered Species Act
addresses species, and not varieties or subspecies. Therefore, if the
range of the three species (Eriogonum ovalifolium, Lesquerella kingii,
and Oxytheca parishii), which includes the Sierra Nevada Mountains, the
desert mountain ranges, Oregon, and Nevada, is considered, none of the
varieties or subspecies of these three plants could be considered
endangered under the Act.
Service Response: Section 3(15) of the Act states that ``The term
``species'' includes any subspecies of fish or wildlife or plants. * *
*'' In response to concerns from the Smithsonian Institution that the
definition included subspecies but not varieties, the Service published
regulations on April 26, 1978 (43 FR 17912) that discussed common use
of both terms by botanists and recognized plant ``varieties'' as
equivalent to ``subspecies'' and, therefore, ``species,'' as defined by
the Act.
Issue 8: A few commenters thought that the five taxa do not meet
the definition of ``endangered'' according to the Act. Similar comments
stated that the taxa are so ``regenerative'' and so common they could
never be endangered, farmers in Lucerne Valley have been trying to
eradicate Astragalus albens for years without success, the California
Department of Fish and Game has not listed these taxa as rare, and the
only reason the taxa were being proposed for listing was to satisfy the
California Native Plant Society lawsuit agreement.
Service Response: Although additional survey data and information
on threats posed to the five plant taxa by mining were presented to the
Service, none of the information contradicted the Service's contention
that the five taxa are threatened by mining and other potential impacts
in the San Bernardino Mountains (see Factor A in Summary of Factors
Affecting the Species). In fact, a report submitted on behalf of the
mining industry (TMC 1992) confirmed the limited distribution of these
five taxa. For example, in the TMC report, the greatest increase in
population size for any of the five taxa surveyed amounted to less than
2 percent for Eriogonum ovalifolium var. vineum and occurred primarily
within the currently known range of the plant. Thus, the Service has
concluded that the distribution of the five species was sufficiently
well known prior to the proposed listing, and has not significantly
changed with additional survey results. The comment concerning the
commonness of Astragalus albens in Lucerne Valley is evidently a case
of mistaken identity; A. albens has never been recorded from the
Valley.
The procedures for designating species as threatened or endangered
are outlined in section 4(a)(1) of the Act and promulgated regulations
(50 CFR part 424). As discussed earlier in this rule, Federal action on
several of these taxa began as early as 1975. While the California
Native Plant Society lawsuit settlement may have accelerated the rate
at which California plant species have been proposed for listing, the
suit does not change the standards by which species are evaluated for
potential listing. Moreover, preparation of the proposal was
essentially completed prior to the California Native Plant Society
settlement agreement. Although the State has not pursued listing any of
these taxa, the California Department of Fish and Game has clearly
stated its support for the listing of all five taxa and has provided a
substantial amount of information to the Service that was used in
preparation of this final rule.
Based upon information the Service has received regarding the
status and distribution of these five species, including data from the
Forest Service, The Nature Conservancy, local botanists, private
consultants, and mining industry, the Service believes that the listing
of these plants is warranted. The Service finds that Astragalus albens,
Eriogonum ovalifolium var. vineum, Lesquerella kingii ssp. bernardina,
and Oxytheca parishii var. goodmaniana are in danger of extinction
throughout all or a significant portion of their ranges and, therefore,
fit the definition of endangered as defined in the Act. Erigeron
parishii has the widest range and largest number of populations of the
species proposed herein for listing; moreover, several populations are
known to occur on non-carbonate substrates that are not under claim.
However, a large portion of its range is under mining claims, and only
the population at the Burns Reserve currently has any permanent
protection. Therefore, it is likely to become endangered in the
foreseeable future and fits the definition of threatened as defined in
the Act.
Issue 9: Several commenters stated that the effects of drought on
the plants had not been considered in the proposal, implying that the
plants would not be considered rare if surveys were performed during
non-drought years when the species were more abundant. One commenter
felt that the effects of drought should be studied and quoted Rupert
Barneby who, when describing Astragalus albens, wrote ``* * * in years
of low rainfall, * * * the populations become decimated or even
annihilated except for dormant seeds. In the first spring after a
drought of several seasons duration, whole colonies of young plants can
be found in prolific flower * * *'' (Barneby 1964).
Service Response: It is well known that drought will reduce both
vigor and abundance of annual as well as short-lived or herbaceous
perennial species. In the same sentence that was quoted above, Rupert
Barneby wrote that ``* * * the plants flower precociously; and a good
proportion of them are probably monocarpic, especially in years of low
rainfall * * *'' (Barneby 1964). Monocarpic plants, those which flower
and fruit once and then die, may be particularly subject to the
vagaries of climate, especially in regions that are typically arid.
Seed for these plants may persist in the soil for years before
favorably climatic conditions allow for successful seedling germination
and establishment. This habit points out the need to maintain
undisturbed habitat for the plants to accommodate the ``boom and bust''
cycles in population sizes. While the Service agrees that it would be
interesting to study the effects of drought on the fluctuations in
plant population sizes, the ranges of all five plants under discussion
are small and their habitat currently receives little protection.
Reference to the effects of drought on Astragalus albens and
Lesquerella kingii ssp. bernardina is included in this rule in the
Background section and under Factor E in the Summary of Factors
Affecting the Species.
Summary of Factors Affecting the Species
Section 4 of the Endangered Species Act (16 U.S.C. 1533) and
regulations (50 CFR part 424) promulgated to implement the listing
provisions of the Act set forth the procedures for adding species to
the Federal Lists. A species may be determined to be an endangered or
threatened species due to one or more of the five factors described in
section 4(a)(1). These factors and their application to Erigeron
parishii Gray (Parish's daisy), Eriogonum ovalifolium Nuttall var.
vineum (Small) A. Nelson (Cushenbury buckwheat), Astragalus albens
Greene (Cushenbury milk-vetch), Lesquerella kingii Wats. ssp.
bernardina (Munz) Munz (San Bernardino Mountains bladderpod), and
Oxytheca parishii var. goodmaniana Ertter (Cushenbury oxytheca) are as
follows:
A. The present or threatened destruction, modification, or
curtailment of its habitat or range. All five species proposed for
listing are restricted primarily to carbonate and adjacent carbonate/
granitic substrates occupied by pinyon-juniper woodland on the northern
side of the San Bernardino Mountains. The imminent and primary threat
facing these species is the ongoing destruction of the carbonate
substrates on which they grow by activities associated with limestone
mining, including direct removal of mined materials, disposal of
overburden on adjacent unmined habitat, and road construction.
Additional threats to their habitat include off-highway vehicle use,
urban development near the community of Big Bear, development of a ski
run, and energy development projects.
The first burst of mining activity in the San Bernardino Mountains
occurred in the 1860s with the discovery of gold in Holcomb Valley.
Historically, gold was extracted both by underground mining and by
placer mining. Only small-scale and weekend prospecting for gold
continues today. However, gold-bearing alluvium in Holcomb Valley has a
low to medium potential for development in the future, and a good
potential exists for a large gold extraction operation in the Blackhawk
area (Forest Service 1988). Several silver mines were also in operation
during the late 1800s in Cushenbury Canyon and near Blackhawk Mountain.
Limestone is considered a locatable mineral, as are gold and
silver, and, therefore, is open to claim under the 1872 mining law.
Virtually all of the approximately 13,210 hectares (32,620 acres) of
carbonate substrates within the San Bernardino Mountains are currently
under claim. Recent calculations by Brown (in litt., 1992) break down
the 13,210 hectares (32,620 acres) into component substrates as
follows: 4,040 hectares (9,980 acres) of dolomite (30.6 percent), 7,910
hectares (19,530 acres) of limestone (59.9 percent); and 1,260 hectares
(3,110 acres) mixed limestone and dolomite (9.5 percent).
Most of the currently mined limestone is being processed by four
operations that are located along the base of the north slope of the
mountains. Because of the limited availability of limestone in the
western United States, those claims currently not under production are
still being maintained either in anticipation of a future market, as a
means of keeping claims from being mined by competing companies, or in
anticipation of leasing out claims for the extraction of other valuable
minerals.
In the surrounding Lucerne Valley mining district, the first
limestone mines started operation in the 1940s; the current annual
production of limestone is approximately 3.3 million tons (Forest
Service 1988). Annual production, however, typically represents only
the fraction of material that is trucked off the mine site as product.
The ratio of disturbed material to product material may range from 1:1
up to more than 5:1. Forest Service records indicate that ratios at
Riverside Cement (Partin) between 1972 and 1977 ranged from 4.9:1 to
13:1, and averaged 7.1:1. A 1988 calculation for the same operator
placed the ratio at 6.7:1 (Forest Service 1988). Thus, based on the
1988 production of 3.3 million tons of limestone and a 5:1 ratio of
disturbed material to limestone, 16.5 million tons of waste material
would be generated. A typical mine site consists of an open pit or
terraced pit, haul roads for hauling the blasted rock to a processing
plant, and the processing plant itself, which sorts and crushes the
material. The overburden is redistributed in piles on site. In the
future, less low-grade limestone will be left onsite as the market for
limestone products changes. The direct impacts to four of the five
plants from limestone mining include the removal and destruction of
individuals and habitat from mining, the construction of haul roads,
and the deposition of overburden piles on top of currently occupied
habitat. Certain operations targeting pharmaceutical grade limestone
tend to create a higher ratio of exploratory roads and access roads
relative to the size of the quarry operations since those deposits are
smaller.
Aside from impacts associated with gold and limestone mining,
several species are potentially threatened by destruction of habitat by
other activities. Sand and gravel is currently being mined, and a new
operation has been proposed for several washes on the lower desert-
facing slopes that may impact at least one occurrence of Erigeron
parishii (TMC 1989). Urban development has encroached upon several
occurrences of Lesquerella kingii ssp. bernardina near Big Bear City
and threatens to encroach upon an occurrence of Erigeron parishii near
Pioneertown. The proposed addition of a downhill ski run to the ski
area on the north side of Sugarlump Ridge may eliminate portions of an
occurrence of Lesquerella kingii ssp. bernardina.
Other impacts include the destruction of individuals and habitat
through increased off-highway vehicle and other recreational use that
departs from roads built for mining assessment work as well as
abandoned mine roads. The Forest Service has proposed construction of
two new sections of the integrated off-highway vehicle system; these
will potentially impact populations of all taxa except Lesquerella
kingii ssp. bernardina.
Since publication of the proposal to list the five taxa, initial
proposals for two energy developments have been received by the Forest
Service. A proposed hydroelectric generation plant, which includes the
use of an old mine quarry to hold water and new ground disturbance for
construction of water delivery pipelines, would likely negatively
affect populations of all five taxa except Lesquerella kingii ssp.
bernardina. A 115-kilovolt powerline proposed for construction through
Cushenbury Canyon may affect Erigeron parishii, Eriogonum ovalifolium
var. vineum, Astragalus albens, and Oxytheca parishii var. goodmaniana.
Because the location of the five plants is tied primarily to the
location of carbonate deposits, it is useful to discuss threats
relative to the primary plant population centers. A description of the
primary population centers of the five plants and the threats in each
area follows.
The westernmost occurrences of two of the plants under discussion
(Erigeron parishii and Eriogonum ovalifolium var. vineum) are in the
vicinity of White Mountain, an outcrop that rises to 2,100 meters
(6,900 ft) in elevation above the desert community of Lucerne Valley.
The third largest of the limestone mines is located here, with an
annual production of approximately 500,000 tons. The proximity of
occurrences of Erigeron parishii and Eriogonum ovalifolium var. vineum
to current mining operations indicates that these plants occurred on
the mining site, but have been extirpated from it. The westernmost
populations of these two species will soon be eliminated under a
recently approved mining plan of operations. As compensation for this
impact, the County of San Bernardino has directed the mining company to
sponsor horticultural studies and experimental reseeding on reclaimed
portions of the mine site.
Approximately 7.5 km (6 miles) to the east of White Mountain, the
north side of Holcomb Valley drops off abruptly into Furnace Canyon.
Habitat for Erigeron parishii and Eriogonum ovalifolium var. vineum was
removed by quarry operations, including the construction of haul roads
and the dumping of overburden at these quarry sites, which were
primarily abandoned prior to 1974. In the areas adjacent to the quarry
sites, populations of Erigeron parishii, Eriogonum ovalifolium var.
vineum, and Astragalus albens, portions of which have been eliminated,
are still found. A proposed hydroelectric generation plant would use
one of the abandoned quarries. If the proposed hydroelectric plant is
approved, new disturbance associated with the project would likely
disturb habitat for Erigeron parishii, Eriogonum ovalifolium var.
vineum, Astragalus albens, and Oxytheca parishii var. goodmaniana.
The second largest operating limestone mine, with an annual
production of 800,000 tons, is operating in the vicinity of Marble
Canyon, a few miles east of Furnace Canyon. A recent expansion of one
overburden pile is eliminating a sizable population of Astragalus
albens.
Six kilometers (4 miles) to the east of Furnace Creek is the deeply
incised Cushenbury Canyon. The mining operation located at this site
has an annual production of 2,000,000 tons of limestone, the largest of
the four currently operating limestone mines. Erigeron parishii,
Eriogonum ovalifolium var. vineum, and Astragalus albens are found on
the rocky slopes surrounding Cushenbury Canyon. A number of populations
have already been negatively affected by mining and road construction.
Up until several years ago, dust from the crushing operation was
settling on the slopes downwind from the operation. The resultant and
still present crust that formed on the slopes is thought to have
inhibited the growth and survival of a number of plant species,
including populations of Erigeron parishii, Eriogonum ovalifolium var.
vineum, and Astragalus albens. A population of Oxytheca parishii var.
goodmaniana, one of the most restricted of the five taxa under
discussion, was also rediscovered in this area in 1978. The species was
not searched for in a 1990 survey at this location due to continuing
drought conditions. A few populations of Erigeron parishii are found on
alluvial substrates below the mouth of Cushenbury Canyon. A recent
proposal to mine these alluvia for sand and gravel would threaten these
populations.
Erigeron parishii, Eriogonum ovalifolium var. vineum, and
Astragalus albens occur 3.2 km (2 miles) to the east of Cushenbury
Canyon on Blackhawk Mountain, which rises to an elevation of 2,000
meters (6,700 ft). Historically, gold and silver were mined near
Blackhawk Mountain. New gold mining activity using cyanide heap-leach
methods has been proposed for the north slope of Blackhawk Mountain,
although to date only exploratory drilling has been done. Blackhawk
Mountain currently supports one of the best assemblages of the
carbonate endemic species. Old roads bisect the habitat, but the lack
of limestone mining has left much of the landscape intact. Creek
drainage, another dozen occurrences of these three species are
scattered along Nelson Ridge and an unnamed ridge that flank Long
Valley for a distance of approximately 6.4 km (4 miles). No active
mining is currently found along the Helendale Fault, though historic
mining may have affected certain occurrences, and some assessment work
is currently being done.
Above Lone Valley, the main fork of Arrastre Creek slowly climbs
for another 6.4 km (4 miles) towards the Rose Mine Valley-Tip Top
Mountain area. Scattered occurrences of Eriogonum ovalifolium var.
vineum are found along this stretch. Some of the densest stands of
Eriogonum ovalifolium var. vineum have been bisected by motorcycle and
jeep trails near Rose Mine Valley (Krantz 1979b); such use of the area
continues.
Farther south and east, the tributaries of Arrastre Creek run off
the north and west slopes of Tip Top Mountain, which rises to an
elevation of 2,000 meters (6,700 ft). On the south and east side of Tip
Top Mountain, tributaries flow into the Rattlesnake Canyon drainage.
Along this drainage is another cluster of occurrences of Erigeron
parishii and Eriogonum ovalifolium var. vineum. Significant new
populations of Oxytheca parishii var. goodmaniana were located by
Forest Service surveys in 1992 near Tip Top Mountain and nearby Mineral
Mountain. The easternmost occurrences for Oxytheca parishii var.
goodmaniana and Eriogonum ovalifolium var. vineum occur a few miles
east of Tip Top Mountain. Historic mining has affected Erigeron
parishii and Eriogonum ovalifolium var. vineum; Krantz (1979b) noted
that a dirt road leading to an abandoned quarry had bisected habitat
for both plants. Erigeron parishii may be able to tolerate some
disturbance, as evidenced by its occurrence along roadsides, while
Eriogonum ovalifolium var. vineum remains absent from roadsides in this
area (Krantz 1979a, 1979b). Off-road vehicle traffic currently
adversely impacts plants in this area.
About 24 km (15 miles) south and east of Tip Top Mountain, the
mountains give way to the broad alluvial fans of the upper desert. Near
Burns Reserve and Pioneertown, a few disjunct occurrences of Erigeron
parishii are found. The Burns Reserve is protected by the State of
California through the auspices of the Natural Reserve System of the
University of California. The Pioneertown site has been proposed for
urban development. The Nature Conservancy has secured a voluntary
agreement with the landowner to protect the Erigeron parishii at this
site.
Scattered patches of carbonate substrate occur outside the main
belt that traverses the San Bernardino Mountains. On the east end of
Bertha Ridge, north of Bear Valley, several small patches of
Lesquerella kingii ssp. bernardina and Eriogonum ovalifolium var.
vineum occur. These populations are adjacent to the community of Big
Bear and are subject to impacts associated with urban development.
Surveys by Myers and Barrows (1988) indicated that several occurrences
of Lesquerella kingii ssp. bernardina have been reduced in size since
the previous surveys were performed in 1980 (Wilson and Bennett 1980).
At the northern edge of Holcomb Valley, Oxytheca parishii var.
goodmaniana is found near an old gold mine site. A low to moderate
potential exists for the reactivation of mining activity in this area
in the future, depending on the price of gold (Forest Service 1988).
On the north-facing slope of Sugarlump Ridge on the south side of
Bear Valley, several large populations of Lesquerella kingii ssp.
bernardina were recently discovered. Several of these populations may
be affected by the proposed expansion of a downhill ski area (Michael
Brandman & Associates 1990).
In summary, virtually all of the carbonate substrates where these
five species occur are under claim and subject to being mined or are
threatened by other disturbance. The only sizable carbonate substrates
not under claim are located on the south side of Bear Valley near
Sugarlump Ridge. Those claims that are not currently being mined are
being maintained either in anticipation of expanding operations once
current quarry supplies are depleted (as a means of keeping competing
companies from mining the claims) or in anticipation of leasing the
claims for the mining of other valuable minerals.
All five taxa, except Erigeron parishii, are limited mainly in
distribution to carbonate substrates within a 40-km (25-mile) range
along the primarily northern slopes of the San Bernardino Mountains.
The range of the five taxa overlap for the most part, but Erigeron
parishii extends to the southeast another 16 km (10 miles). Although
Erigeron parishii is found primarily on carbonate substrates, several
occurrences are on non-carbonate substrates. The five species occur on
lands under mining claim or on lands that have been patented, which
subjects them to habitat destruction. Other activities, such as off-
highway vehicle recreation, urbanization, development of a ski run, and
energy development projects, threaten to alter or destroy habitat for,
as well as the limited number of occurrences of, these five species.
B. Overutilization for commercial, recreational, scientific, or
educational purposes. Although these species are not presently sought
after by collectors, they are vulnerable to taking because of their
limited distribution. Some plant taxa have become vulnerable to
collecting by curiosity seekers as a result of increased publicity
following listing. The increased public attention could potentially
increase their desirability, thereby increasing the threat of
collection.
C. Disease or predation. No data exist to substantiate whether or
not disease threatens any of the plants. The seed capsules of
Lesquerella kingii ssp. bernardina were observed to have been broken
open by unknown seed predators at one of the Big Bear occurrences (C.
Rutherford, U.S. Fish and Wildlife Service, and M. Lardner, U.S. Forest
Service, pers. obs., 1990). It is unknown whether seed predation would
affect the viability of the species. In the vicinity of Round Mountain,
several occurrences of Astragalus albens are known to occur within a
grazing allotment administered by the Bureau of Land Management (BLM).
The effects of cattle grazing on this species have not yet been
investigated.
D. The inadequacy of existing regulatory mechanisms. All five
plants are on List 1B of the California Native Plant Society,
indicating that, in accordance with chapter 10, sec. 1901 of the
California Department of Fish and Game Code, they are eligible for
State listing. If State listing were pursued, the Native Plant
Protection Act and the California Endangered Species Act would prohibit
the ``take'' of State-listed plants (Fish and Game Code chapter 10,
sec. 1908, and chapter 1.5, sec. 2080), but would not protect the
plants from taking via habitat modification or land use change by the
landowner. After the California Department of Fish and Game notifies a
landowner that a State-listed plant grows on his or her property, State
law requires only that the landowner notify the agency ``at least 10
days in advance of changing the land use to allow salvage of such
plant'' (chapter 10, sec. 1913). Although these State laws provide a
measure of protection to the species, they are not adequate to protect
the species in all cases. Numerous activities do not fall under the
purview of this legislation, such as certain projects proposed by the
Federal government and projects falling under State statutory
exemptions. Where overriding social and economic considerations can be
demonstrated, these laws allow project proposals to go forward, even in
cases where the continued existence of the species may be jeopardized
or where adverse impacts are not mitigated to the point of
insignificance.
About 20 to 25 percent of the occurrences of Erigeron parishii and
15 to 20 percent of the occurrences of Eriogonum ovalifolium var.
vineum occur on private land. The mining of limestone on private land
is under the jurisdiction of the county of San Bernardino, which is
responsible for administering regulations in accordance with the
California Environmental Quality Act and the California Endangered
Species Act. The county has included terms and conditions in the
granting of certain operating permits that have directed the applicants
to undertake efforts to restore the habitat and reintroduce Erigeron
parishii and Eriogonum ovalifolium var. vineum to the site. Recently,
the county included a permit condition for the expansion of an
overburden pile that required the applicant to designate preserve areas
with the concurrence of the California Department of Fish and Game and
the Service. One population of Erigeron parishii occurs on land owned
by the University of California at the Burns Pinyon Reserve; no
activities are currently planned that would affect the population. The
remaining occurrences of these two species, as well as almost all the
occurrences of the other three species are primarily on lands managed
by the Forest Service and, to a lesser degree, by BLM.
Several laws enacted by Congress and regulations promulgated to
implement them address surface management of Federal lands, including
mining, but they provide limited protection for natural resources. For
instance, the Federal Land Policy and Management Act (FLPMA) of 1976
(43 U.S.C. 1701 et seq.), as amended, was passed to provide policy for
``the management, protection, development, and enhancement'' of public
lands managed by BLM. Section 302 of FLPMA, which addresses management
of use, occupancy, and development of public lands, states ``* * * the
Secretary shall, by regulation or otherwise, take any action necessary
to prevent unnecessary or undue degradation of the lands'' (43 U.S.C.
1732 (b)). Unnecessary or undue degradation is defined to mean surface
disturbance greater than that which would normally result by a prudent
operator taking into account the effects of mining operations on other
resources (43 CFR 3809.0-5(k)). The policy of FLPMA as expressed by
regulation is that a person has a statutory right to mine certain
Federal lands (43 CFR 3809.0-6). Mining operations that exceed 5 acres
in extent and certain other defined operations require a plan of
operations that must be approved by BLM (43 CFR 3809.1-4, 1-6).
However, prior to approval of the plan, BLM must evaluate the action
with respect to any species that is proposed or listed as endangered or
threatened and with respect to its critical habitat if any.
Federal agencies, such as BLM, are required to (1) confer
informally with the Service on any action that is likely to jeopardize
the continued existence of a proposed species or result in destruction
or adverse modification of proposed critical habitat, or (2) enter into
formal consultation with the Service on any action that is likely to
jeopardize the continued existence of a listed species or result in
destruction or adverse modification of critical habitat. However,
Federal agencies are not required to implement Service recommendations
for proposed species or proposed critical habitat. Therefore, although
FLPMA affords some general protection in that resources other than
mining interests must be considered by an operator, the protections
afforded listed species pursuant to section 7 of the Endangered Species
Act are not required to be implemented unless listing takes place.
Thus, listing affords additional protection to these particular
species.
Additionally, section 601 of FLPMA specifically addresses
management of public lands within the California Desert Conservation
Area, which includes all BLM lands where four of the five plants occur
(except Lesquerella kingii ssp. bernardina) (43 U.S.C. 1781). The
purpose of this section is ``to provide for the immediate and future
protection and administration of the public lands in the California
desert within the framework of a program of multiple use and sustained
yield, and the maintenance of environmental quality'' (43 U.S.C. 1781).
Multiple use is defined, in part, to mean ``the management of the
public lands and their various resource values so that they are
utilized in the combination that will best meet the present and future
needs of the American people . . .'' (43 U.S.C. 1702(c)). The concept
of multiple use includes the ``harmonious and coordinated management of
the various resources without permanent impairment of the . . . quality
of the environment with consideration being given to the relative
values of the resources . . .'' (Id.).
Section 1781 of FLPMA states that the use of these desert resources
should be provided for in a multiple use and sustained yield management
plan (43 U.S.C. 1781(a)(4)). These resources specifically include
``certain rare and endangered species of wildlife, plants, and fishes .
. . [which] are seriously threatened by inadequate Federal management
authority, and pressures of increased use . . .'' (43 U.S.C.
1781(a)(3)). As a result, the Secretary of the Department of the
Interior is directed to prepare and implement a long-term plan for the
``management, use, development, and protection'' of the lands within
this Conservation Area (43 U.S.C. 1781(d)). This plan is to take into
account multiple use and sustained yield, and provide for resource use
and development, which is to include ``maintenance of environmental
quality, rights-of-way, and mineral development'' (Id.). So even though
FLPMA may contain language to protect the five plant species to a
certain degree through the maintenance of environmental quality, FLPMA
was written to provide for multiple use. Such use does not necessarily
elevate the needs of these species over other public land uses. Indeed,
regulations promulgated to implement certain provisions of FLPMA
provide for the approval of mining if the appropriate Federal official
has complied with the section 7 consultation provisions of the
Endangered Species Act (43 CFR 3809.1-6(a)(5)). However, the
protections afforded listed species pursuant to section 7 of the
Endangered Species Act are not required to be implemented unless
listing takes place. Therefore, listing affords another layer of
protection to these species.
Similar regulations have been promulgated for National Forest
System lands (36 CFR part 228) so that mining ``shall be conducted so
as to minimize adverse environmental impacts on National Forest System
surface resources'' (36 CFR 228.8). Although these regulations do not
specifically require compliance with section 7 of the Endangered
Species Act as a prerequisite to approval of a mining plan of
operations, the Act requires Service consultation for any action the
Federal action agency authorizes, funds, or carries out (16 U.S.C.
1536) that may affect a federally listed species. Therefore, Forest
Service approval of a mining plan of operations would require section 7
compliance, which would afford additional protection to listed plant
species.
The Forest Service has attempted to reduce impacts of mining within
carbonate plant habitat. As early as 1977, the Forest Service
recognized four of the plants (all but Oxytheca parishii var.
goodmaniana) as ``sensitive species;'' Oxytheca parishii var.
goodmaniana was added to its list of sensitive species in 1990. The
Forest Service has worked with the mining companies to minimize impacts
to the plants since at least 1987 (Forest Service, in litt., 1992). In
the Management Plan for the San Bernardino National Forest (Forest
Service 1988), the Forest Service recommended conserving at least two-
thirds of the existing populations for three of the taxa (Erigeron
parishii, Eriogonum ovalifolium var. vineum, and Astragalus albens) in
perpetuity by establishing refugia for conserving selected occurrences
of these five plants as part of a regional conservation plan. In
addition, all of the habitat for Lesquerella kingii ssp. bernardina was
recommended for protection. This would entail securing refugia sites
either by withdrawal from mineral entry or by transferring claim
rights. To date, the Forest Service has hosted several interagency
meetings to develop strategies to implement this forest management plan
direction by identifying criteria for refuge design and strategies for
establishing a minerals withdrawal. A draft habitat management guide
for the carbonate plants is expected to be released within several
years. However, approval and implementation of recommended actions may
not take place for several years subsequent to release of the guide.
In response to the proposal, Brown (in litt., 1992) has claimed
that the actual amount of limestone to be mined in the foreseeable
future (defined as 75 years) is only 2 percent of the existing surface
expression of limestone deposits in the San Bernardino Mountains. The
1872 mining law states that claimholders must have an actual intent to
mine. The Service, therefore, must assume that all claims are being
held with the intent to mine. One industry representative cited two
reasons why claimholders would not relinquish claims even if no future
mining were intended. First, it would prohibit a competing company from
mining the mineral resource. Secondly, the claims could be mined for
strategic minerals other than limestone. The 1872 mining law does not
include a mechanism for voluntary relinquishment of a claim or transfer
of a claim to a third party for the purposes of resource conservation
even if a claimholder wished to do so. Once it was proven that the
third party had no intent to mine, the claim could legally be seized by
other mining interests (Bill Tilden, Pfizer, Inc., pers. comm., 1992).
The surface management of public lands under U.S. mining laws (43
CFR part 3809) requires BLM to process applications to ``patent''
mining claims on all Federal lands. BLM has reported that since the
proposal to list the carbonate plants was published, it has received an
increase in patent applications submitted by industry claimholders with
claims occurring within the range of the five carbonate plants (Mike
Ford, geologist, formerly BLM, pers. comm., 1992). One industry
representative has indicated that changes in the 1872 mining law will
require that the cost of the required annual assessment work per 8-
hectare (20-acre) claim ($100) be paid as a fee directly to BLM, rather
than performed as on-the-ground assessment work. This may provide
additional incentive to claimholders to patent claims to avoid the
increase in out-of-pocket costs for the annual assessment work. An
increase in the number of claims being patented could remove these
lands from continued Federal jurisdiction. The elimination of Federal
jurisdiction becomes important regarding protection of plants because
of the reduced protection afforded by the Endangered Species Act for
plants on private lands.
E. Other natural or manmade factors affecting its continued
existence. Populations consisting of a small number of individuals
always face the possibility of stochastic extinction (i.e., extinction
due to random events, including fire, flood, drought, landslide,
disease, or predation). The total amount of annual precipitation, as
well as the timing of such precipitation, may be crucial for seedling
germination and subsequent establishment. A significant drop in the
size of Lesquerella kingii ssp. bernardina populations in the Bertha
Ridge area between 1980 and 1988 (from 25,000 to 15,000 individuals)
may be in part due to several years of drought conditions. Conversely,
the high amount of precipitation received during March 1992 may, in
part, account for the increased number of Astragalus albens individuals
observed during 1992 surveys compared to the number found in previous
surveys. Such fluctuations in population sizes should be expected, but
at the same time emphasize the need to maintain in situ seedbanks on
suitable habitat. Moreover, drought-stressed plants can become
vulnerable to additional damage from pathogens or insects. The risk of
stochastic extinction for A. albens and Oxytheca parishii var.
goodmaniana, which currently consist of fewer than 10,000 individuals
each, is considered high.
The Service has carefully assessed the best scientific and
commercial information available regarding the past, present, and
future threats faced by these five species in determining to issue this
final rule. Based on this evaluation, the preferred action is to list
Eriogonum ovalifolium var. vineum, Astragalus albens, Lesquerella
kingii ssp. bernardina, and Oxytheca parishii var. goodmaniana as
endangered. Destruction of their habitat by activities associated with
limestone mining, sand and gravel mining, off-road vehicle and other
recreational use, and energy development projects, as well as their
vulnerability to stochastic events, exposes these four plant species to
the danger of extinction throughout all or a significant portion of
their ranges. These species thus fit the Act's definition of
endangered. While Erigeron parishii faces the same threats as the other
four species, it has the widest range of distribution; at least a few
populations within the range of the species occur at locations with
non-carbonate substrates, which are not currently under mining claim.
Therefore, the preferred action is to list Erigeron parishii as
threatened.
Critical Habitat
Section 4(a)(3) of the Act requires that, to the maximum extent
prudent and determinable, the Secretary designate critical habitat at
the time a species is determined to be endangered or threatened. The
Service finds that designation of critical habitat for Eriogonum
ovalifolium var. vineum, Astragalus albens, Lesquerella kingii ssp.
bernardina, Oxytheca parishii var. goodmaniana, and Erigeron parishii
is not presently prudent. The publication of critical habitat
descriptions and maps required for critical habitat designation would
increase the degree of threat to these plants from possible take or
vandalism, and could contribute to their decline. The listing of
species as either endangered or threatened publicizes the rarity of the
plants and can make these plants attractive to researchers, curiosity
seekers, or collectors of rare plants. All appropriate Federal agencies
and local planning agencies have been notified of the location of these
species and importance of protecting their habitat. Protection of these
species' habitat will be addressed through the recovery process and
potentially through the section 7 consultation process. Therefore, the
Service finds that designation of critical habitat for these plants is
not prudent at this time; such designation likely would increase the
degree of threat from vandalism, collecting, or other human activities.
Available Conservation Measures
Conservation measures provided to species listed as endangered or
threatened under the Endangered Species Act include recognition,
recovery actions, requirements for Federal protection, and prohibitions
against certain practices. Recognition through listing encourages and
results in conservation actions by Federal, State, and private
agencies, groups, and individuals. The Endangered Species Act provides
for possible land acquisition and cooperation with the States and
requires that recovery actions be carried out for all listed species.
The protection required of Federal agencies and the prohibitions
against certain activities involving listed plants are discussed, in
part, below.
Section 7(a) of the Act, as amended, requires Federal agencies to
evaluate their actions with respect to any species that is proposed or
listed as endangered or threatened and with respect to its critical
habitat, if any is being designated. Regulations implementing this
interagency cooperation provision of the Act are codified at 50 CFR
part 402. Section 7(a)(2) requires Federal agencies to ensure that
activities they authorize, fund, or carry out are not likely to
jeopardize the continued existence of a listed species or to destroy or
adversely modify its critical habitat. If a Federal action may affect a
listed species or its critical habitat, the responsible Federal agency
must enter into formal consultation with the Service.
Populations of all five plant species occur in large part on
Federal land. Erigeron parishii, Eriogonum ovalifolium var. vineum, and
Astragalus albens occur on land managed by the San Bernardino National
Forest and the California Desert District of BLM. Lesquerella kingii
ssp. bernardina and Oxytheca parishii var. goodmaniana occur primarily
on land managed by the San Bernardino National Forest. Federal
activities potentially impacting one or more of the five plants and
likely to trigger formal consultation under section 7 of the Act
include the approval of mining plans of operations; approval of mining
reclamation plans; construction of recreational facilities, such as
off-highway vehicle trails and the ski run; rights-of-way for various
activities including access to mining claims and energy development
corridors; and grazing allotments. The patenting of mining claims are
processed by BLM; however, legal opinions differ as to whether this
process can be considered a Federal activity subject to section 7 of
the Endangered Species Act. The Army Corps of Engineers (Corps) will
have permitting authority as described under section 404 of the Clean
Water Act for construction of a hydroelectric power plant and a sand
and gravel mining operation being proposed for the Cushenbury Springs
area. By regulation, nationwide or individual permits cannot be issued
where a federally listed endangered or threatened species would be
affected by a proposed project without first completing formal
consultation pursuant to section 7 of the Endangered Species Act. In
addition, construction of the hydroelectric power plant most likely
will require the approval of the Federal Energy Regulatory Commission
and thus require formal consultation.
The Act and its implementing regulations found at 50 CFR 17.61,
17.62, and 17.63 for endangered plants and 17.71 and 17.72 for
threatened plants set forth a series of general prohibitions and
exceptions that apply to all listed plants. With respect to the five
carbonate endemics from southern California, all trade prohibitions of
section 9(a)(2) of the Act, implemented by 50 CFR 17.61 and 17.71,
apply. These prohibitions, in part, make it illegal for any person
subject to the jurisdiction of the United States to import or export;
transport in interstate or foreign commerce in the course of a
commercial activity; sell or offer for sale in interstate or foreign
commerce; or to remove and reduce to possession any such species from
areas under Federal jurisdiction; maliciously damage or destroy any
such species on any area under Federal jurisdiction, or remove, cut,
dig up, damage or destroy listed plants on any other area in knowing
violation of any State law or regulation, or in the course of any
violation of a State criminal trespass law. Seeds from cultivated
specimens of threatened plant species are exempt from these
prohibitions provided that a statement of ``cultivated origin'' appears
on their containers. Certain exceptions apply to agents of the Service
and State conservation agencies. The Act and 50 CFR 17.62, 17.63, and
17.72 also provide for the issuance of permits to carry out otherwise
prohibited activities involving endangered and threatened plant species
under certain circumstances.
It is anticipated that few trade permits would ever be sought or
issued because the five plant species are not common in cultivation or
in the wild. Requests for copies of the regulations on plants and
inquiries regarding them may be addressed to the U.S. Fish and Wildlife
Service, Endangered Species Permits, 911 N.E. 11th Avenue, Portland,
Oregon 97232-4181 (telephone 503/231-6241, facsimile 503/231-6243).
National Environmental Policy Act
The Fish and Wildlife Service has determined that an Environmental
Assessment, or Environmental Impact Statement, as defined under the
authority of the National Environmental Policy Act of 1969, need not be
prepared in connection with regulations adopted pursuant to section
4(a) of the Endangered Species Act of 1973, as amended. A notice
outlining the Service's reasons for this determination was published in
the Federal Register on October 25, 1983 (48 FR 49244).
References Cited
A complete list of all references cited herein, as well as others,
is available upon request from the Ventura Field Office (see ADDRESSES
section).
Author
The primary author of this rule is Constance Rutherford, U.S. Fish
and Wildlife Service, Ventura Field Office, 2140 Eastman Avenue, Suite
100, Ventura, California 93003 (805/644-1766).
List of Subjects in 50 CFR Part 17
Endangered and threatened species, Exports, Imports, Reporting and
recordkeeping requirements, and Transportation.
Regulation Promulgation
Accordingly, part 17, subchapter B of chapter I, title 50 of the
Code of Federal Regulations, is amended as set forth below:
PART 17--[AMENDED]
1. The authority citation for part 17 continues to read as follows:
Authority: 16 U.S.C. 1361-1407; 16 U.S.C. 1531-1544; 16 U.S.C.
4201-4245; Pub. L. 99-625, 100 Stat. 3500; unless otherwise noted.
2. Amend Sec. 17.12(h) by adding the following, in alphabetical
order under the plant families indicated, to the List of Endangered and
Threatened Plants:
Sec. 17.12 Endangered and threatened plants.
* * * * *
(h) * * *
----------------------------------------------------------------------------------------------------------------
Species
------------------------------------------- Historic range Status When listed Critical Special
Scientific name Common name habitat rules
----------------------------------------------------------------------------------------------------------------
****** *
Asteraceae--Aster
family:
****** *
Erigeron Parish's daisy...... U.S.A. (CA)........ T 548 NA NA
parishii .
****** *
Brassicaceae--Mustar
d family:
****** *
Lesquerella San Bernardino U.S.A. (CA)........ E 548 NA NA
kingii ssp. Mountains
bernardina. bladderpod.
****** *
Fabaceae--Pea
family:
****** *
Astragalus Cushenbury milk- U.S.A. (CA)........ E 548 NA NA
albens . vetch.
****** *
Polygonaceae--Buckwh
eat family:
****** *
Eriogonum Cushenbury buckwheat U.S.A. (CA)........ E 548 NA NA
ovalifolium
var. vineum .
****** *
Oxytheca Cushenbury oxytheca. U.S.A. (CA)........ E 548 NA NA
parishii var.
goodmaniana .
****** *
----------------------------------------------------------------------------------------------------------------
Dated: August 3, 1994.
Mollie H. Beattie,
Director, U.S. Fish and Wildlife Service.
[FR Doc. 94-20790 Filed 8-23-94; 8:45 am]
BILLING CODE 4310-55-P