Abstract
I characterized common milkweed (Asclepias
syriaca) leaf nitrogen content and condition in unfertilized nonagricultural
and fertilized agricultural habitats. Old
field milkweed ramets varied such that top and new leaves, leaves from
non-senescing plants, leaves from flowering plants, and leaves from
plants with high aphid and stem herbivory damage had higher leaf nitrogen
content than bottom leaves, leaves from senescing plants, leaves from
non-flowering plants, and leaves from plants with high leaf herbivory
damage, respectively. When pooled
by type of habitat, ramets in the three non-Bt cornfields had significantly
higher leaf nitrogen content than those in the four roadsides. These
results raise questions about how milkweed leaf nitrogen in the wild
affects monarch larvae
Introduction
While monarch butterflies in the Midwestern US originate
on milkweed that grows in a variety of habitats, most of these monarchs
come from agricultural habitats (Oberhauser et al. 2001). Monarch
per plant densities in agricultural fields are as high as or higher than
densities in nonagricultural habitats, and even though milkweed densities
are higher in nonagricultural than in agricultural habitats, more monarchs
originate in agricultural habitats because agricultural fields constitute
such a large portion of the landscape (Oberhauser et al. 2001).
In these different habitats, monarchs probably
experience varying levels of nitrogen. Fertilizing plants with nitrogen tends to increase
total leaf nitrogen content (Mattson 1980), and leaf nitrogen content
tends to decrease over the growing season (Mattson 1980, Slansky 1993). Young,
new shoots contain the most nitrogen, followed by leaves from plants
with flowers and seedpods, and then by leaves from old, senescing plants.
Plant protein yield and leaf nitrogen content
usually increase when plants are damaged by pathogens or herbivores because
damage stimulates compensatory plant growth and the saliva of some herbivores
contains chemicals that promote plant growth (Mattson 1980, Hamilton
et al. 1998). While terrestrial
forbs generally contain 1.6-5.0% leaf
nitrogen content by dry weight (dw) (Mattson 1980), the variation in
leaf nitrogen content for common milkweed between and within plants in
fertilized agricultural and unfertilized nonagricultural habitats has
not been determined.
Nitrogen is important for caterpillar growth (Scriber 1984,
Slansky and Scriber 1985), and insects are usually considered to be nitrogen
limited (McNeil and Southwood 1978, Mattson 1980, White 1993). While animal tissue generally consists of 7-14%
nitrogen (dw), plants consist of 0.03-7.0% nitrogen (dw) (Mattson 1980),
and herbivores must therefore consume large quantities of their host
plants in order to accumulate enough nitrogen for growth and development.
The monarch butterfly obtains its nitrogen requirements
for growth, development, and reproduction from plants in the family Asclepiadaceae
(milkweeds). Milkweeds defend
themselves from herbivores with a secretory canal system made of specialized
plant cells (laticifers) that run throughout each plant and contain latex
(Dussourd 1993). Latex provides
both mechanical and chemical protection to milkweeds. It
is a sticky plant secretion released upon injury that contains cardenolides,
or cardiac glycosides, heart poisons with potent effects on vertebrates
(Dussourd 1993). Zalucki and Brower (1992) found that milkweed
latex glued some first instar monarch larvae to the plant while the cardenolides
in the latex and the leaf tissue often immobilized them. Monarch larvae combat milkweed defenses through
feeding behaviors such as petiole cutting and leaf trenching to slow
the flow of latex (Zalucki and Brower 1992, Malcolm et al. 1999), and
metabolic processes such as sequestering the cardenolides in their exoskeletons
(Malcolm et al. 1999).
In this study I characterized milkweed leaf
nitrogen content within and between common milkweed (Ascelpias
syriaca) ramets in an old field and characterized milkweed leaf nitrogen
content and condition in unfertilized nonagricultural and fertilized
agricultural habitats. This study
addresses two questions. 1) How
does leaf nitrogen content vary within and between milkweed plants in
a Wisconsin old field? 2) How does leaf nitrogen
content vary between plants in fertilized agricultural and unfertilized
nonagricultural habitats in Hennepin County, Minnesota?

Methods
Milkweed in the Field
Sampling and Site Descriptions
In 2001, I determined the natural variability in leaf nitrogen
content within and between common milkweed ramets (aboveground stems)
in a west central Wisconsin nonagricultural area. The site contained over 1000 milkweed ramets
and is an old field last used for agriculture approximately 20 years
ago and burned 2 years before the study to promote native plant growth. On
two different dates, I collected milkweed leaf samples from ramets along
randomly selected transects; ramets needed to be at least 2 m apart to
be included in the sample.
I collected samples on 26 July to characterize
the leaf nitrogen levels within ramets (top, bottom or new leaves) and
between ramets with varying reproductive status and varying types and
levels of damage from herbivory. For
each sample ramet, I identified whether or not it was flowering, its
level of stem and leaf damage from herbivory, and the number of aphids
on the ramet. Holes in the stem indicated stem damage from
herbivory (probably from the milkweed weevil, Rhyssomatus lineaticollis), and the length of the stem with holes divided by
the entire length of the stem provided an estimate of the
percentage of stem damage from herbivory (low: <6% or high: 6-25%). Holes or missing portions of leaves divided
by total leaf area on the plant provided a visual estimate of leaf damage from
herbivory (low: <6% or high: 6-25%). I
did not record higher percentages of damage from herbivory because they did
not occur. I estimated aphid herbivory
using the number of aphids on the ramet (low: <100 aphids or high: >100
aphids).
After
categorizing the ramet, I randomly selected a new, top, or bottom leaf
from the ramet. To be included
in the sample, ramets needed to have high levels of damage from one
type of herbivory and low levels from the other types. This process may have forced biological interactions
between the three types of herbivory. I repeated this process using many random transects
through the old field until I obtained samples from up to four ramets
for each combination of variables shown in Table 1a.
On 12 September I collected samples from the same old field
to characterize leaf nitrogen levels in senescing and not senescing ramets
with varying reproductive status. For
each sample ramet, I identified whether or not it had reproductive seedpods
and whether or not it was senescing. I
defined senescence using leaf yellowing. On
senescing ramets greater than 40% of the leaves were 100% yellow; ramets
that were not senescing had less than 10% yellowing on all leaves. I
collected the topmost mature leaf on each sample ramet. I
repeated this process using many random transects until I obtained samples
from six ramets for each combination of variables shown in Table 1b.
Table 1a. Milkweed leaves collected by
herbivory type and level, leaf location, and flowering status. X's
indicate combinations of variables for which samples were collected.
No samples were collected for the combinations of variables in the shaded
cells, because I did not find these in the field.
|
|
Low damage from herbivory (leaf
and stem damage from herbivory <6%, aphids <100)
|
High aphid herbivory (>100), low stem & leaf
damage from herbivory
|
High stem damage from herbivory
(6-25%), low aphid herbivory & leaf damage from herbivory
|
High leaf damage from herbivory
(6-25%), low aphid herbivory & stem damage from herbivory
|
|
Leaf location
|
New
|
Top
|
Bottom
|
New
|
Top
|
Bottom
|
New
|
Top
|
Bottom
|
New
|
Top
|
Bottom
|
|
Flowers
|
X
|
X
|
X
|
|
|
|
X
|
X
|
X
|
|
|
|
|
No flowers
|
X
|
X
|
X
|
X
|
X
|
X
|
X
|
X
|
X
|
X
|
X
|
X
|
Table 1b. Milkweed leaves collected from
senescing and not senescing ramets with and without seedpods. X's
indicate combinations of variables for which samples were collected.
|
|
Senescing
|
Not senescing
|
|
Plant with seedpods
|
X
|
X
|
|
Plant without seedpods
|
X
|
X
|
I determined how leaf nitrogen content varied
between common milkweed (Asclepias syriaca) plants
in fertilized agricultural and unfertilized nonagricultural habitats. The
sites included three cornfields and four nonagricultural roadside areas. I selected cornfields and roadsides in Hennepin
County, Minnesota within
15 km of each other to minimize differences in climate, parent material,
and relief at the sites. I minimized
the effect of fertilizer runoff for roadside sites by selecting sites
separated from nearby agricultural fields and residential lawns by roads
or parking lots. The roadside sites represented different types
of roadside habitats where common milkweed grows in the Minneapolis-St.
Paul area, including mowed and unmowed sites with 100 to over 1000 milkweed
ramets (aboveground stems) along wetlands and woods, near interstate
ramps, and in highway medians. At the cornfield sites, I used milkweed ramets
along the field edge (within 0.5 m of the outer row of corn). The farmers
fertilized the three cornfields before planting the corn and sprayed
herbicide targeting dicot plants once during the last week of June. At
each site, I collected the topmost mature milkweed leaf from 10 ramets
along randomly selected transects; ramets needed to be at least 2 m apart
to be included in the sample. I collected all leaf samples on 28-29 July.
Data Collection
I determined leaf nitrogen content (% dw) of milkweed leaf
samples harvested from the old field, cornfield, and roadside sites. As I collected leaf samples, I stored them
in paper envelopes in a cooler with an ice pack for up to 8 hours. Upon returning to the lab, I immediately dried
the leaves at 65°C for 48 hours in a drying oven. Then I milled the leaves using a Wiley mill
with a 20 mesh screen and determined the nitrogen content using a Perkin
Elmer Series II CHNS/O Analyzer 2400.
Statistical Analyses
I analyzed the leaf nitrogen content of milkweed plants
in the old field, cornfield and roadside sites using ANOVA. To
compare the leaf nitrogen content of senescing and not senescing milkweed
ramets with and without pods, I used two-way ANOVA. I used one-way ANOVA to compare leaf nitrogen
content of top, mature leaves among plants with different types of damage
due to herbivory and used Tukey's HSD to make all possible pairwise comparisons. To compare the leaf nitrogen content of leaves
from different locations on the ramets, with different types of herbivory,
and with and without flowers, I used three-way ANOVA and Tukey's HSD
for all possible pairwise comparisons. I
pooled data from the top leaves of the three cornfields and four roadsides,
respectively, and used an independent samples t-test to compare the leaf
nitrogen content of cornfields and roadsides because these data were
independent observations, were normally distributed (Kolmogorov-Smirnov
with a Lilliefors significance correction and Shapiro-Wilk tests) and
had homogeneous variances (Levene test).
Results
A. syriaca ramets
and leaves varied in leaf nitrogen content. Senescing
ramets in the old field had significantly lower leaf nitrogen content
than non-senescing ramets, and there was a significant interaction between
senescence and presence of pods such that senescing plants with no pods
had the lowest nitrogen levels (Table 3 and Figure 1a).
For top, mature leaves of old field ramets without flowers,
ramets with aphid herbivory and stem damage from herbivory had significantly
higher leaf nitrogen content than ramets with leaf damage from herbivory
(Fig 1b). Old field ramets with flowers had marginally
higher leaf nitrogen content than ramets without flowers, and top and
new leaves had significantly higher leaf nitrogen content than bottom
leaves (Tables 3a & b and Figure 2). 
Table 3a. Old field
A. syriaca leaf nitrogen content (% dry weight) group means
for top, new, and bottom leaves on ramets with differing reproductive
status (flowering or not) and levels of damage from herbivory on
July 26, 2001. Herbivory categories were low damage from herbivory
(< 6% stem and leaf damage from herbivory and < 100
aphids) and high stem damage from herbivory (6-25%) with < 100
aphids and < 6% leaf damage from herbivory.
Analysis with ANOVA (Table 3b). Means followed by the same letter are not significantly
different at the 0.05 level of confidence (Tukey HSD comparisons).
Reproductive Status
|
Herbivory
|
Leaf Location
|
N
|
Leaf Nitrogen Content
Mean ± SE (% dw)
|
|
Not flowering
|
Low
|
Top
|
4
|
2.52 ± 0.40a
|
|
New
|
4
|
2.61 ± 0.69 a
|
|
Bottom
|
4
|
2.26 ± 0.29 b
|
|
High Stem
|
Top
|
4
|
2.90 ± 0.43 a
|
|
New
|
4
|
2.71 ± 0.87 a
|
|
Bottom
|
4
|
2.15 ± 0.81 b
|
|
Flowering
|
Low
|
Top
|
4
|
2.80 ± 0.44 a
|
|
New
|
4
|
3.10 ± 0.46 a
|
|
Bottom
|
4
|
2.36 ± 0.34 b
|
|
High Stem
|
Top
|
4
|
3.16 ± 0.84 a
|
|
New
|
4
|
3.36 ± 0.33 a
|
|
Bottom
|
4
|
2.35 ± 0.60 b
|
Table 3b. Three-way ANOVA for A. syriaca leaf nitrogen content in top, new, and bottom leaves of
ramets with and without flowers and with low and high stem herbivory.
|
Factor
|
Sum of squares
|
df
|
F
|
P
|
|
Flowering
|
1.306
|
1
|
3.915
|
0.056
|
|
Herbivory
|
0.322
|
1
|
0.965
|
0.333
|
|
Leaf location
|
4.137
|
2
|
6.198
|
0.005
|
|
Flowering*herbivory
|
0.01857
|
1
|
0.056
|
0.815
|
|
Flowering*leaf location
|
0.377
|
2
|
0.564
|
0.574
|
|
Herbivory*leaf location
|
0.370
|
2
|
0.554
|
0.580
|
|
Flowering*herbivory*leaf location
|
0.01647
|
2
|
0.025
|
0.976
|
|
Error
|
12.014
|
36
|
|
|
When pooled by type
of habitat, ramets in the cornfields had significantly higher leaf nitrogen
content than those in the roadsides (Figure 3).
Discussion
The variation in leaf nitrogen for milkweed plants in the
field approximates leaf nitrogen variation in other herbaceous plants. Forb
leaves tend to range from 1.6% to 5.0% nitrogen (dw) with top leaves
containing more nitrogen than bottom leaves (Mattson 1980). Old field milkweed leaves ranged from 1.14 ± 0.36%
to 3.36 ± 0.33%
nitrogen (dw), and top and new leaves had significantly higher leaf nitrogen
content than bottom leaves. Leaf
nitrogen content of leaves also increases with fertilization (Mattson
1980), and fertilized cornfields, pooled, had milkweed with higher leaf
nitrogen content than unfertilized roadsides.
Leaf nitrogen content tends to decrease over
the growing season (Slansky 1993, Mattson 1980). As
plants invest in reproduction, they allocate more nitrogen to the reproductive
structures and less to their leaves (Mattson 1980). Young,
actively growing tissues require higher nitrogen concentrations to support
the rapid protein synthesis needed for growth, while senescing plants
do not need to synthesize proteins (Mattson 1980). Old field milkweed leaves partially followed
this pattern; senescing ramets had significantly lower leaf nitrogen
content than ramets not senescing. Reproductive
ramets (pods or flowers) did not have lower leaf nitrogen content than
non-reproductive ramets, possibly because comparisons were made between
ramets at one time point instead of within the same ramets over the growing
season. Perhaps only those ramets with high enough
nitrogen levels develop reproductive structures.
Actual and simulated herbivory tend to increase
the protein yield (Mattson 1980) and leaf nitrogen content of plants
(Hamilton et al. 1998), but sometimes plants concentrate this additional
nitrogen in the damaged tissue (de Nooij et al. 1992). Old
field milkweed leaves on plants with higher levels of herbivory contained
similar leaf nitrogen content to those with low levels of herbivory,
possibly because they concentrated any additional nitrogen in the damaged
tissues and not in the leaves I sampled.
References
De Nooij,
M. P., Biere, A., and Linders, E. G. A. 1992. Interaction of pests
and pathogens
through
host predisposition. Pages 143-160 in P. G. Ayres, editor. Pests and pathogens: Plant responses to foliar
attack. BIOS
Scientific Publishers Ltd., Oxford, UK.
Dussourd,
D. E. 1993. Foraging with finesse:
Caterpillar adaptations for circumventing
plant
defenses. Pages
92-131 in N. E. Stamp and
T. M. Casey, editors. Caterpillars:
Ecological and evolutionary constraints on foraging. Chapman & Hall, New York, New York, USA.
Hamilton,
W., III., Giovannini,
M. S., Moses, S. A., Coleman, J. S., and McNaughton,
S.
J. 1998. Biomass
and mineral element responses of a Serengeti short-grass species to nitrogen
supply and defoliation: compensation requires a critical [N]. Oecologia 116:407-418.
Malcolm, S.
B., Zalucki, M. P., Cockrell, B. J., and Mwakamela,
B. J. A. A. 1999. The
lethal
plant defense paradox and the influence of milkweed latex on larval
feeding
behavior
of the monarch butterfly. Pages 139-149 in J. Hoth,
L. Merino, K.
Oberhauser,
I. Pisanty, S. Price, and T. Wilkinson, editors. 1997
North American
conference
on the monarch butterfly conference proceedings. Commission for
Environmental
Cooperation, Montreal, Quebec, Canada.
Mattson, W. J., Jr. 1980. Herbivory
in relation to plant nitrogen content. Annual
Review
of Ecology and Systematics, 11:119-161.
McNeil, S.,
and Southwood, T. R. E. 1978. The role of nitrogen in
the development of
insect/plant
relationships. Pages
77-98 in J. B. Harborne,
editor. Biochemical aspects of plant and animal coevolution. Academic, London, UK.
Oberhauser,
K. S., Prysby, M. D., Mattila, H. R.,
Stanley-Horn, D. E., Sears, M. K.,
Dively,
G., Olson, E., Pleasants, J. M., Lam, W. F., and Hellmich, R. L. 2001. Temporal
and spatial overlap between monarch larvae and corn pollen. Proceedings
of the National Academy of
the Sciences of the United States of America 98:11913-11918.
Ozkan, A.,
and Yanikolu, A. 1999. Effects
of 2, 4-D and maleic hydrazide on the
glycogen
level in the embryonic development of Pimpla turionellae (L.)
(Hym., Ichneumonidae). Journal of Applied Entomology 123:211-216.
Scriber, J.
M. 1984. Host-plant suitability. Pages 159-202 in W. J. Bell and R. T. Carde,
editors. Chemical ecology of insects. Sinauer, Sunderland, Massachusetts, USA.
Slansky, F.,
Jr. 1993. Nutritional ecology: The fundamental quest
for nutrients. Pages
29-91 in N.
E. Stamp and T. M. Casey, editors. Caterpillars:
Ecological and evolutionary constraints on foraging. Chapman & Hall, New York, New York, USA.
Slansky, F.,
Jr., and Scriber, J. M. 1985. Food
consumption and utilization. Pages
87-
163 in G.
A. Kerkut and L. I. Gilbert, editors. Comprehensive
insect physiology, biochemistry, and pharmacology, Vol. 4. Pergamon, Oxford, UK.
White, T. C. R. 1993. The
inadequate environment: Nitrogen and the abundance of
animals.
Springer-Verlag, New York, New York, USA.
Zalucki, M.
P., and Brower, L. P. 1992.
Survival of first instar larvae of Danaus
plexippus (Lepidoptera: Danainae) in relation
to cardiac glycoside and latex content of Asclepias
humistrata (Asclepiadaceae). Chemoecology 3:81-93.
Back
to top | Interactions with Milkweed | Student/Teacher
Research | Research Topics | Site
Overview
|