Ratnayake, S., J.K. Rupprecht, W.M.
Potter, and J.L. McLaughlin. 1993. Evaluation of the pawpaw tree, Asimina
triloba (Annonaceae), as a commercial source of the pesticidal
annonaceous acetogenins. p. 644-648. In: J. Janick and J.E. Simon
(eds.), New crops. Wiley, New York.
Evaluation of the Pawpaw Tree, Asimina
triloba (Annonaceae), as a Commercial Source of the Pesticidal
Annonaceous Acetogenins
Sunil Ratnayake, J. Kent Rupprecht,
William M. Potter, and Jerry L. McLaughlin
The potent antitumor, pesticidal
and/or insect antifeedant properties of the Annonaceous
acetogenins have been previously reported (Rupprecht et al. 1986;
Hui et al. 1989; Alkofahi et al. 1989) and patented (Mikolajczak
et al. 1988, 1989). A recent compilation reviews the chemistry and
biological actions, known to date, of this new class of diversely
bioactive botanical compounds (Rupprecht et al. 1990). The
Annonaceae is almost exclusively a tropical plant family and
encompasses over 2000 species (Heywood 1978). However, the pawpaw
(Asimina triloba Dunal) is a temperate representative and
is an abundant native of eastern North America. Work on the seeds
and stem bark of the pawpaw initially revealed pesticidal actions
of the acetogenins and focused on asimicin (1), a major bioactive
component of a complex mixture of these compounds (Rupprecht et
al. 1986; Alkofahi et al. 1989).
Asimicin (1) (Fig. 1) was
originally isolated from a 90% aqueous methanol partition fraction
(Fig. 2) (F005) from the 95% ethanol extract of the stem bark of
pawpaw (Mikolajczak et al. 1988). F005 is identical to the F020 as
described in the initial patent of Mikolajczak et al. (1988). It
was isolated via bioactivity-directed fractionation using a simple
test involving lethality to brine shrimp larvae (Artemia salina
Leach) (BST). Promising pesticidal activities paralleled the BST
throughout the fractionation (Alkofahi et al. 1989) and included
significant activity against blowfly larvae (Colliphora vicina
Meig), two-spotted spider mite (Tetranychus urticae Koch),
melon aphid (Aphis gossyphii Glover), mosquito larvae (Aedes
aegypti Linnaeus), Mexican bean beetle (Epilachna
varivestis Mulsant), striped cucumber beetle (Acalymma
vittatum F.), and a free-living nematode [Caenorhabditis
elegans (Maupas) Dougherty]. Subsequent testing of F005 has
shown promising activities against a host of additional pests,
especially those of horticultural concern.
Asimicin (1) contains eight chiral
centers (256 possible stereoisomers) and, thus, is not a good
candidate for commercial chemical synthesis. However, plant
extracts, such as F005, containing a mixture of the bioactive
acetogenins can be quickly and inexpensively prepared. As is true
with the pyrethrins, such botanical mixtures often increase the
pesticidal spectrum and are less likely to induce pest resistance
after repeated application. Therefore, a plant extract, such as
F005, would be a logical means for incorporation of the
acetogenins into a pesticidal product. F005, obtained from the
stem bark of pawpaw and suspended with 2% aqueous Tween 80 in the
concentration range of 0.05 to 0.5% (500 to 5000 ppm), provides
effective pesticidal action and plant protection in laboratory and
field tests. Fig. 2 illustrates the protective effect of F005
against foliar damage on bush beans infested with bean leaf
beetles (Cerotoma trifurcata Forster).
Asimina triloba is quite
common as an understory shrub and small tree throughout the
eastern United States, and the edible fruits, called
"pawpaw" (Fig. 3), have generated considerable interest
for commercial production (Callaway 1990). Over 18 million trees
(3 to 13 cm diam) are growing in Indiana (Spencer et al. 1990),
and other eastern states have similarly high populations. Thus, an
evaluation of the relative biological potencies and percentage
yields of standardized extracts from the various plant parts is
needed. The development of such new, environmentally compatible,
biologically degradable, botanically-derived, pesticides has
become more desirable (Arnason et al. 1989).
The plant material was collected in
Indiana during July 1988 and October 1990 with the exception of
the seeds which were collected in November 1989 from plantings at
the University of Maryland, established in 1982 by R. Neal
Peterson. The Indiana collections came from a single clone at the
Horticultural Research Farm, Purdue University, and were
identified by George R. Parker, Professor of Forestry. The unripe
fruits were frozen and freeze-dried, while the seeds were air
dried at room temperature. The other plant materials were dried in
an oven at 40°C, and all of the materials were ground in a Wiley
mill (unless otherwise stated, 4 mm mesh size was used in all
cases). The woody collections were chipped and shredded (Mantis,
Chipmate) prior to drying.
The dried plant materials (100 g)
were then repeatedly extracted (Fig. 4) with 95% ethanol (5 x 750
ml). The combined extract was evaporated under reduced pressure
(below 40°C) to provide a syrupy residue (F001). F001 was
transferred to a 250 ml separatory funnel with a mixture of 100 ml
of water and 100 ml of chloroform. After removal of the chloroform
layer, the water layer was then extracted seven additional times
with 100 ml portions of chloroform, and the combined layers were
reduced under rotary vacuum (<40°C) to obtain the chloroform
residue (F003). F003 was further partitioned between hexane and
10% water in methanol (1:1, 4 x 100 ml), and the solvents were
evaporated under reduced pressure to afford the hexane solubles
(F006) and the 90% aqueous methanol solubles (F005). The yield of
F005 in grams from 100 g of plant material then directly
corresponded to the percentage yields from the various plant
parts.
The brine shrimp lethality bioassay
(BST) (Meyer et al. 1982) was performed with the aqueous methanol
soluble fractions (F005) as follows: 20 mg of each fraction was
dissolved in 2 ml of methanol and 5, 50, and 500 µl amounts were
transferred to 2 dram vials to correspond to 10, 100 and 1000 ppm
concentrations; three vials were prepared for each concentration.
These vials were dried overnight to permit evaporation of the
methanol, and control vials were prepared using 500 µl of
methanol alone. Ten brine shrimp larvae, taken 48 h after
initiation of hatching in 3.8% aqueous sea salt brine (Instant
Ocean, Metaframe) were added to each vial, and the final volume of
each vial was adjusted to 5 ml using the artificial sea water.
After 24 h, survivors were counted, and LC50 values
with 95% confidence intervals were computed using a Finney's
probit analysis program adapted to an IBM personal computer (discs
of the program are available from J.L. McLaughlin).
To access the pesticidal potential of
the available biomass of A. triloba, various plant parts
were collected and extracted in a standardized way (Fig. 4), and
the resulting 90% aqueous methanol fractions (F005) were
bioassayed in the BST. The percentage of F005 obtained from each
plant part was also calculated, and this yield was correlated with
the BST data to determine which plant part would yield the
greatest quantity of an extract that could be suitably active for
incorporation into a commercial product.
Table 1 shows the brine shrimp
lethality of F005 for the various plant parts extracted and
tested. The twigs, unripe fruit, seeds, root wood, and all the
stem bark samples were the most active plant parts with LC50
values ranging from 0.042 to 0.104 ppm. These differences in
activity, however, were not significant since the BST 95%
confidence intervals all overlap. The BST activity of the root
bark is very close to the above plant parts and is probably
equivalent in activity even though there is a slight difference in
the 95% confidence interval overlap between the root bark and the
unripe fruit and root wood (D 0.01 ppm). The whole above-ground
plant (leaves, stem, wood, and stem bark) and stems consisting of
wood and bark were approximately 1/8 to 1/2 as active as the above
plant parts. The BST of the wood and of the leaves were between 40
to 100 times and 500 to 1,200 times, respectively, less active
than the most active plant parts. Furthermore, there were no
significant differences in the bioactivities of the stem bark
collected in July 1988 and October 1990, indicating that
collections of bark made during the summer and fall are
biologically equivalent and that the pesticidal constituents are
stable over some period of time when the dried bark is stored.
The percentages of 90% aqueous
methanol extractables (F005) of each plant part tested were also
determined (Table 1). The unripe fruit, leaves, and seeds gave the
highest percentages of F005. They would appear to be suitable
sources of F005; however, the F005 from the leaves is the least
active of the plant parts tested, and therefore, the leaves are a
poor candidate for use. The extracts of the unripe fruit and seeds
are extremely bioactive and also give a very high yield of F005;
unfortunately, these plant parts represent the least available
forms of biomass and are therefore unsuitable for commercial
development. The root bark and stem bark afforded 1.96 to 2.72%
yields into the 90% aqueous methanol extractables, and both plant
parts possess potent brine shrimp activity. However, uprooting of
the trees would destroy the stands and would require replanting on
a commercial scale. When the stem bark was ground more finely (2
mm versus 4 mm sieves) the percentage of F005 increased by
approximately 20%. The amount of 90% aqueous methanol extractables
(F005) of the stem wood and bark, whole (above-ground) plant, root
wood, and stem wood were 1.61, 1.60, 1.27, and 0.90%,
respectively. The plant part which represents the best balance of
yield and biological activity to its availability as a source of
biomass is either the stem bark or the stem wood and stem bark in
combination. Stripping of the bark is quite labor intensive; thus,
mechanically chipping and shredding of the stem would be most
practical.
To assess further the pesticidal
potential of the combined stem wood and stem bark biomass, stems
of various diameters were collected, chipped and shredded, dried,
and pulverized, and standardized extracts were prepared; the BST
was made on the F005 extract from stems of the different
diameters. The percentage of F005 obtained and the brine shrimp
activity were both inversely proportional to the stem diameter
(Table 2). The activity of the smallest stems, 64 mm or less in
diameter, was significantly greater than the other diameters
tested.
Asimicin (1) and several other
acetogenin compounds play the major role in the pesticidal
activity. Asimicin alone gives BST LC50 values at 0.03 ppm (Rupprecht
et al. 1986), whereas its stereoisomer, bullatacin gives LC50
values at 0.00159 ppm (Hui et al. 1989). In addition to asimicin,
bullatacin, bullatacinone, and trilobacin are all potent
acetogenins recently isolated from F005 of pawpaw (Zhao et al.
1992). The variations of observed toxicity are probably due to
quantitative variations of these and additional toxic acetogenins
as distributed in different parts of the plant. The amounts of
these compounds may also vary seasonally, but this variable has
not been studied.
It is probable that the toxicities
are higher in the twigs, unripe fruit, seeds, and bark because
these are the plant parts which can be most easily damaged by
herbivores, environmental pests and pathogens, and, therefore, for
the purpose of defense, higher concentrations of the protective
acetogenins may accumulate in these parts. The root (both bark and
wood) may accumulate these compounds to avoid attack by nematodes
and other soil pathogens.
In conclusion, the bioactivity of
the A. triloba tree is concentrated mainly in the twigs,
unripe fruits, seeds, root, and bark, but stems, especially those
with the smallest diameters, are also significantly toxic.
Therefore, the smaller aerial parts, minus the leaves, could be
used as a biomass for the pesticidal extract. Finer milling would
give more solubles while maintaining the level of the bioactivity.
The stem bark collected in July showed more activity which,
however, was not significantly different from the values of F005
obtained from the batch collected in October from the same clone.
It is possible that further screenings of wild populations of
pawpaw could identify some clones with acceptably high levels of
bioactivity in the leaves. The brine shrimp toxicity bioassay can
be conveniently used as a rapid quality control measure of the
total bioactivity of mixtures of the acetogenin compounds. Thus,
the commercially used extract could be easily standardized as to
bioactivity in furnishing a consistently bioactive product. A
recent study with asimicin and F005 in the guinea pig maximization
test showed only weak skin sensitization and suggested that few or
no dermatologic problems are expected as a result of the pesticide
use and human dermal contact (Avalos et al. 1992). Furthermore, in
the Ames test, F005 was negative in nine of ten determinations
with five histidine mutants of Salmonella typhimurium (Loeffler),
with and without hepatic enzyme activation; such results are
superior to many common substances, such as caffeine, and suggest
that F005 is not a serious mutagen (P.E. Kirby pers. commun.).
Mode of action studies in three separate laboratories have
recently determined that F005, asimicin, and bullatacin are superb
inhibitors (at subnanomolar concentrations) of Complex I in
mitochondrial electron transport systems from several organisms;
this is very similar to the site of action of rotenone, an
established and approved botanical pesticide (J.T. Arnason; R.
Hollingworth, C.E. Snipes pers. commun.).
- Alkofahi, A., J.K. Rupprecht,
J.E. Anderson, J.L. McLaughlin, K. L. Mikolajczak, and B.A.
Scott. 1989. Search for new pesticides from higher plants, p.
25-43. In: J.T. Arnason, B. J.R. Philogene, P. Morand (eds.).
Insecticides of plant origin. Amer. Chem. Soc., Washington,
DC.
- Alvalos, J., J.K. Rupprecht, J.L.
McLaughlin, and E. Rodriguez. 1992. Guinea pig maximization
test of pawpaw, Asimina triloba (Annonaceae). Contact
Dermatitis.
- Arnason, J.T., B.J.R. Philogene,
and P. Morand (eds.). 1989. Insecticides of plant origin.
Amer. Chem. Soc., Washington, DC.
- Callaway, M.B. 1990. The Pawpaw Asimina
triloba). Kentucky State Univ., Frankfort, KY, Pub. CRS-Hort
1-901 T.
- Heywood, V.H. 1978. Flowering
plants of the world. University Press, Oxford.
- Hui, Y.-H., J.K. Rupprecht,
Y.-M. Liu, J.E. Anderson, D.L. Smith, C.-J. Chang, and J.L.
McLaughlin. 1989. Bullatacin and bullatacinone: Two highly
potent bioactive acetogenins from Annona bullata. J.
Nat. Prod. 52: 463-477.
- Meyer, B.N., N.R. Ferrigni, J.E.
Putnam, L.B. Jacobsen, D.E. Nichols, and J.L. McLaughlin.
1982. Brine shrimp: A convenient general bioassay for active
plant constituents. Planta Medica 45:31-34.
- Mikolajczak, K.L., J.K.
Rupprecht, and J.L. McLaughlin. 1988. Control of pests with
acetogenins. U.S. Patent No. 4,721,727, issued January 1988.
- Mikolajczak, K.L., J.K.
Rupprecht, and J.L. McLaughlin. 1988. Control of pests with
Annonaceous acetogenins. U.S. Patent No. 4,855,319, issued
August 1989.
- Ratnayake, S., J.K. Rupprecht,
W.M. Potter, and J.L. McLaughlin. 1992. Evaluation of various
parts of the pawpaw tree, Asimina triloba (Annonaceae),
as commercial sources of the pesticidal Annonaceous
acetogenins. J. Econ. Entomol.
- Rupprecht, J.K., Y.-H. Hui, and
J.L. McLaughlin. 1990. Annonaceous acetogenins: A review. J.
Nat. Prod. 53: 237-278.
- Rupprecht, J.K., C.-J. Chang,
J.M. Cassady, J.L. McLaughlin, K.L. Mikolajczak, and D.
Weisleder. 1986. Asimicin, a new cytotoxic and pesticidal
acetogenin from the pawpaw, Asimina triloba (Annonaceae).
Heterocycles 24:1197-1201.
- Spencer, J.S. Jr., N.P.
Kingsley, and R.W. Mayer. 1990. Indiana timber resources,
1986: An analysis. Resour. Bul. NC-113. St. Paul, MN. U.S.
Department of Agriculture, Forest Service, North Central
Forest Experimental Station, St. Paul, Minnesota.
- Zhao, G.-X., Y.-H. Hui, J.K.
Rupprecht, J.L. McLaughlin, and K.V. Wood. 1992. Additional
bioactive compounds and trilobacin, a novel highly cytotoxic
acetogenin, from the bark of Asimina triloba (Annonaceae).
J. Nat. Prod. 55:347-356.
*This work was
supported by NIH/NCI RO1 grant no. CA 30909.
Table 1. Brine
shrimp lethality and percentage yields of F005 (90% aqueous
methanol fraction) from various plant parts of Asimina triloba.
| Plant part extracted |
LC50
(ppm)z |
Yield of
F005 (%) |
| Twigsy |
0.042
(0.02-0.09) |
1.78 |
| Unripe fruitx |
0.060
(0.03-0.08) |
5.11 |
| Root woodw |
0.060
(0.03-0.08) |
1.27 |
| Seedv |
0.065
(0.03-0.10) |
4.03 |
| Stem barkx,u |
0.077
(0.04-0.12) |
2.71 |
| Stem barky,u |
0.102
(0.06-0.15) |
1.96 |
| Stem barky |
0.104
(0.03-0.20) |
2.52 |
| Root barkw |
0.135
(0.09-0.21) |
2.72 |
| Whole stem: wood, bark and
leavesy |
0.202
(0.14-0.31) |
1.60 |
| Stem woody |
4.86
(0.37-11.93) |
0.90 |
| Leavesy |
53.6
(33-82) |
4.36 |
zWith 95%
confidence intervals in parenthesis.
yCollected in October 1990.
xCollected in July 1988.
wCollected in November 1990.
vCollected in November 1989.
uGround to a mesh size of 2 mm, all other samples were
ground to a 4 mm mesh size.
Table
2. Variation of the percentage F005 (90% aqueous methanol
solubles and brine shrimp lethality with differing stem diameters.
|
Stem diameter of
extracted material (mm)
|
Percentage of
F005
|
LC50
(ppm)z
|
|
251-500
|
1.36
|
0.36 (0.23-0.55)
|
|
189-250
|
1.45
|
0.22 (0.13-0.34)
|
|
65-188
|
1.76
|
0.22 (0.13-0.34)
|
|
0-64 (twigs)
|
1.78
|
0.04 (0.01-0.09)
|
zWith 95%
confidence intervals in parentheses.

Fig. 1. Structure
of asimicin

Fig. 2. Scheme for
extraction and partitioning of Asimina triloba.

Fig. 3. Bush beans
(cv. Blue Lake). The row on the left has a natural infestation with bean
leaf beetles (Cerotoma trifurcata Forster). The row on the right
was sprayed three times during a ten day period with 0.5% of F005
(F020), suspended with 2% Tween 80, in water. F005 (F020) is prepared
from the bark of the pawpaw tree (Asimina triloba). Note the
protective effect of the Annonaceous acetogenins in a field test against
garden insects.
Fig. 4. Fruits and
seeds of pawpaw (Asimina triloba)
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