
Michael B. Sady, Western Nevada Community College, Carson City, NV 89703
USA
Send comments to: mbsady@wncc.nevada.edu
James N. Seiber, Center for Environmental Sciences and Engineering,
University of Nevada, Reno, NV 89557 USA
Current Address: USDA-ARS 800 Buchanan St., Albany, CA. 94710
USA
*A portion of this report was presented at the Nevada Environmental
Conference,
University of Nevada, Reno, 30 September - 01 October 1996.
Abstract
The blue milkweed beetle Chrysochus colbaltinus LeConte (Coleoptera:
Chrysomelidae) has been studied since 1992 living on selected host milkweed
(Asclepiadaceae) populations of Asclepias eriocarpa Benth. in California,
and Asclepias speciosa Torr. in western Nevada. The adult whole
beetles appear to contain little to no toxic cardenolides typically produced
by milkweeds when collected in the wild on hosts of A. eriocarpa
in coastal foothills of California, and no detectable cardenolide when
collected in the wild on hosts of A. speciosa in western Nevada.
The egg cases of C. colbaltinus collected from the same milkweed
patches contained moderate to high amounts of cardenolide when found on
A. eriocarpa, but no detectable cardenolide when found on A.
speciosa. Since the leaf cardenolide content for the former milkweed
is 20 fold higher than the latter, the use of cardenolides for chemical
defense in this chrysomelid may be host-dependent. The population structure
of C. colbaltinus reveals a propensity to aggregate in very dense
numbers, emerging in an exponential growth rate in the late spring on several
A. speciosa patches studied in western Nevada. The adult beetle
also appears to utilize minimal amounts of plant resource for ovipositioning
and herbivory. A study of headspace components of the adult beetle reveals
that common fatty acids may serve as important semiochemicals for aggregation.
Key Words
Chrysomelidae. Host. Asclepias. Fatty Acids. Cardenolide. Chrysochus
colbaltinus.
Introduction
Defensive chemicals that are biosynthesized by leaf beetles and used
at some life stage have been studied (Hilker 1992). Cardenolides serve
a protective role in species of Chrysomelidae both in adult beetles and
eggs (Hilker 1994). While some chrysomelids biosynthesize cardenolides
of varying types and quantity (Dobler and Rowell-Rahier 1994; Hilker et
al. 1992), other chrysomelid species appear to exploit host plant cardenolides
for a putative chemical defense (Isman et al. 1977a; Sady 1994).
In North America Chrysochus spp. is reported by Arnett (1985) to feed on dogbane (Apocynaceae) preferentially to milkweed (Asclepiadaceae). Both of these lactiferous plant families have variable cardenolide content (Seiber et al. 1983). The eastern North American beetle species C. auratus Fabricius, is ordinarily found on a host of Apocynum spp. (Williams 1988; 1991), while the western North American species, C. colbaltinus (spelling of the species binomial conforms to Arnett 1985), is found on a host of Asclepias spp. (Isman et al. 1977a; Root 1986; Sady 1994). In this study we concentrate on the western blue milkweed beetle and comparing cardenolide content for populations of the beetle feeding on two species of milkweed that differ greatly in their cardenolide content and biogeographic range.
Eastern and mid-western North American milkweed leaf beetle species found on Asclepias spp. tend to have a high degree of fidelity to small isolated patches of their primary host plants (Dickinson 1992). In this study we present data on four populations of C. colbaltinus living on hosts of A. speciosa in western Nevada that we have monitored since 1992 for their rate of emergence, aggregation, ovipositioning and herbivory patterns.
Also we report on the analysis of headspace chemical components of female adult C. colbaltinus that may influence the aggregation of beetles into the small dense patches they occupy on some host milkweeds populations.
Currently we have an interest in studying the microbial influence, if any, with respect to the plant - herbivore interaction. This work is of interest because of our unpublished observations, and the presence of bacteria (Flynn and Vidaver 1995) and mycoplasmalike organisms (Griffiths et al. 1994) in North American milkweeds. We would like know whether the herbivores of milkweeds infect, or are infected by, the host milkweed. In Tetraopes spp. feeding on showy milkweed in western Nevada gram positive rod bacteria were found in the gut contents. The latex of the host milkweed had bacteria of similar morphology (Evett and Austin 1998). In 1999 C. colbaltinus will be examined for bacteria.
Materials and methods
Plant and beetle collection and census.
Adult beetles and egg cases of C. colbaltinus (voucher specimen
FMNH-Z18,400) were collected in the field on host milkweed of A. eriocarpa
(voucher specimen RENO-69190) in Monterey county California USA, and
on A. speciosa (voucher specimen RENO-67804) in Douglas county Nevada
USA during the spring and summer months. Gender sorting of the adult beetles
was accomplished by finding copulating pairs in embrace for at least 1
minute and assuming the male to be mounted on the dorsal side of the female.
Verification of this technique was confirmed by aedeagus dissection. Whole
adult beetles and egg cases were stored at -20 C for the cardenolide studies,
and at 20 C in a headspace chamber for 1 week until senescence for the
GC-MS analysis. Daily census of beetles on host milkweed populations in
western Nevada took place around noon on 14 randomly chosen patches of
A. speciosa in Douglas county, Nevada since 1992. Beetles, herbivory
patterns, and egg cases ovideposited, along with total host milkweed plants,
stems, and leaves, were counted and assessed during each visitation at
each patch site.
Chemical analyses of whole beetles and egg cases.
The whole beetles and egg cases stored at -20 C were thawed and dried
in an oven at 40 C for 48 hours and then placed in 2 ml spectral grade
methanol for 24 hrs to extract cardenolide. The total cardenolide content
was determined on three or more beetles or samples of eggs using the methods
of TNDP spectroassay reported in Isman et al. (1977a) and Seiber et al.
(1983). (As of 1996 the Seiber lab has been exploring the use of supercritical
fluid extraction of milkweed plant parts and herbivorous insects to improve
yields of cardenolide with results that appear promising but have yet to
be reproduced). Egg cases analyzed included the fecal covering and the
eggs within, usually between 8 to 10 eggs per clutch. Approximately 12
live female adult C. colbaltinus beetles collected in summer of
1995 on a host of A. speciosa in Douglas county, Nevada were placed
in an empty 250 ml amber headspace chamber at 20 C without food for 1 week.
Volatile components were analyzed by injecting a 2 ml sample of the headspace
atmosphere from the chamber into a gas chromatograph - Varian 3400 equipped
with a DB-5 column (J & W Scientific) set at a programmed temperature
range of 50 to 310 C, and coupled to a mass spectrometer - Finnigan MAT
SSQ710 scanning masses m/z 35 to 300. The GC-MS software library identified
two major peaks on the gas chromatogram at a retention time of approximately
16:00 and 17:50 minutes to be hexadecanoic (palmitic) and octadecanoic
(stearic) acids, which was confirmed by reference to authentic standards
of both acids. GC-MS analysis of the headspace atmosphere of a live male
beetle confined to a 20 ml headspace vial showed the same two GC peaks
for the two fatty acids given above for female beetles.
Results
The cardenolide content of whole beetles and egg cases of C. colbaltinus
are compared and contrasted on two different host milkweeds in Table
1. The beetle and eggs cases have no detectable host cardenolide when
collected on A. speciosa either in California (Isman et al. 1977a),
or in western Nevada (this report). However the cardenolide content is
low but detectable in some C. colbaltinus beetles and quite significant
for the egg cases collected on A. eriocarpa in California. This
might suggest that the 20 fold difference in the leaf cardenolide content
in A. eriocarpa and A. speciosa provides a host-dependency
to any putative chemical protection afforded the chrysomelid on these hosts,
or other asclepiad hosts.
The gas chromatogram of headspace components of female adult C.
colbaltinus is consistent with that of an internal standard for palmitic
and stearic acids. The mass spectrum showed characteristic fragments of
m/z M+ 43, 57, 73, and 129, and m/z M 256 and 284 for palmitic
and stearic acids respectively (McLafferty and Turecek 1993).
Three patches of A. speciosa in western Nevada have been subjected
to a census since 1992. The data suggests that the beetle appears to utilize
only a small portion of available milkweed patches and the smaller and
less phenologically developed plants for herbivory and ovipositioning (Table
2). There were three particularly dense populations of beetles on three
different host patches of A. speciosa which conformed to an exponential
growth pattern with respect to the emergence/appearance of beetles in the
late spring approximating a doubling time of about 2.5 to 3 days (Table
3). The populations of these dense patches of beetles nearly doubled
the second year , but reverted to very low population numbers in the third
year. The adult beetles emerge in the late spring in western Nevada cued
to a thermally dependent signal as warming in western Nevada varies greatly
from year to year (Table
4).
Discussion
This study and previously cited work suggest that the blue milkweed
beetle does not appear to biosynthesize cardenolides as other chrysomelids
do, but may utilize host milkweed cardenolides when they are present in
significant concentration. A. eriocarpa may be an evolutionarily
advanced milkweed showing an apparent phylogenetic progression toward biosynthesis
of more toxic and complex cardenolides, which, moreover, become increasingly
concentrated in the latex, vis-a-vis A. speciosa (Farrell et al.
1992). Furthermore, in Tetraopes spp. (Coleoptera: Cerambycidae)
the gap may have been bridged in plant chemical defense by circumventing
it with unique feeding behaviors (Farrell et al. 1991). More information
on C. auratus feeding on dogbane in a variety of biogeographically
different settings would be helpful in order to further elucidate the diffuse
character of host specificity in Chrysochus spp. As with most asclepiadaceous
herbivores interspecific cardenolide content of host plants cannot alone
account for the variability found in insects, even between populations
feeding on the same plant part (Isman et al. 1977b). Interest is robust
concerning the evolutionary significance of host shifts influenced by a
change in plant chemistry (Secord and Kareiva 1996; Becerra 1997). Recent
reports in Chrysochus, employing different methods and experimental
appoach than those described here, demonstrate that it may well be the
secretions vis-a-vis the whole beetle that contain the most significant
quantities of toxic cardenolides and other defensive chemicals (Dobler
et al. 1998).
The propensity of C. colbaltinus adults to aggregate in very
dense patches in a given region where over 100 of them at a time will utilize
only a very small portion of the plants in a patch could be a selective
characteristic to increase mating success (Dickinson 1992). But it is enigmatic
why some populations of beetles emerge, after overwintering in the larval
stage on the host roots, as adults in late spring, doubling in numbers
the next generation, and drop off to very few adults in the ensuing years.
The host does not seem to change in size or nature, yet the population
approaches extinction. Other milkweed beetle studies with Tetraopes
spp. suggest a similarly short colonization and extinction population structure
limited to a few years (McCauley 1989).
Finally despite their almost ubiquitous presence in nature, long-chain
fatty acids appear to be of importance as behavioral cues for arthropods
(Hibbard et al. 1994). Whether this is true for C. colbaltinus requires
yet more controlled laboratory studies of beetle behavior to verify if
palmitic and stearic acids, or yet to be discovered chemicals as a part
of our current research interests, provide semiochemical behavioral aggregation
cues that keep the dense patches of these beetles maintained throughout
their short month or so of life. And what of unconscious olfactory signals
that are presently being studied and their influence on plant - herbivore
or animal - animal interactions (Hines 1997)?
We are also evaluating whether induced responses to herbivory may play
a role in the milkweed - herbivore relationship as has been reported in
other plant - insect relationships (Agrawal 1998).
Research in a variety of lab groups focusing on genetic make-up of
the leaf beetles (Farrell 1998) and their hosts should also provide valuable
insights on the host specificity in chrysomelidae.
Acknowledgments
This work was supported in part by the Nevada-NSF-EPSCoR Trec program
which is funded by the UCCSN and matching grants from the National Science
Foundation OSR-9353227 and OSR-9553369. We appreciate the assistance of
Jim Lenoir and Loretta Raley of the Seiber lab, Dan Summers of the Field
Museum of Natural History of Chicago, Brian Harris of the Natural History
Museum of Los Angeles County, Christy Malone of the University of Nevada,
Reno Herbarium, Adrian Wenner of U.C. Santa Barabara and Alice and Astrid
Sady in the field collection and population census. We are particularly
grateful for the watercolor painting of milkweeds and herbivores and the
line drawing of the population and seasonal variations with milkweed phenology
done by graphic artist Chris Olesen. We would also like to extend our thanks
to the Summer 1997 Biology 280 Field Ecology class (taught by M. Sady at
WNCC) for their data and comments. Prof. Gary Evett of WNCC and Fred Austin,
a student of WNCC are acknowledged for their interest and work in identifying
bacteria associated with beetles feeding on milkweeds in western Nevada.
Finally we are very appreciative of the technical assistance of Leonard
MacKey of WNCC, and Sherry Berg and Corky Goldade of Bently Nevada Corporation
(and students of M. Sady at WNCC) in setting up the internet web site.
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