Annotated List of Species

#Juniperus virginiana.#--Red cedar, the only native gymnosperm of

northeastern Kansas, occurs in nearly all woodlands of the region,

although individual trees are widely scattered. It has increased

remarkably in the past few years. No mature cedar trees grow anywhere

on the Reservation, but young trees, probably several dozen in all,

are widely scattered in a variety of situations on the area. Probably

in every instance the seeds have reached the area in droppings of

birds. Approximately 15 miles south and a little east of the

Reservation is a stand of cedars some of which are 100 to 300 years

old. Near the southwest corner of the section, at the site of a former

farm house there is a small grove of these trees, probably planted.

These may have been the source for some of the young trees on the

Reservation.

On several occasions cardinals (_Richmondena cardinalis_) were

observed to have nested in the young cedars, whose thick foliage

provided well sheltered nesting sites. This shelter was utilized

especially in early nestings when foliage had only begun to appear on

other trees and shrubs. However, two such nests in cedars, that were

checked repeatedly, were eventually destroyed by predators.

#Salix nigra.#--Black willow is localized in the vicinity of the one

small pond on the Reservation. The pond was made in 1936; at the

upper end of a small valley a dirt bank 100 yards long was built

across a ravine through which an intermittent creek drained. Hilltop

fields draining into this ravine were then under cultivation. In the

next few years heavy erosion occurred in the upland fields, and the

soil carried downstream was deposited in the pond. Most of the pond

was filled up with a silt flat about an acre in area. On the higher

part of this silt flat a dense thicket of saplings of elm, honey

locust and osage orange sprang up. On the lower, wetter part of the

silt bar a willow grove grew up, dominated by _S. nigra_, with _S.

eriocephala_, _S. interior_ and _S. amygdaloides_ in smaller numbers.

By 1955 some of these trees had attained a trunk diameter of eight

inches and a height of thirty feet. Elsewhere on the Reservation,

willow is represented only by a few scattered trees and bushes along

the two intermittent creeks. The silty soil preferred by the willow is

scarce as both streams are actively eroding their channels.

The moist, silty soil beneath the willow grove is covered with a dense

mat of low vegetation including giant ragweed, carpenter's square,

dayflower, and rice cutgrass. Short-tailed shrews, house mice (_Mus

musculus_), harvest mice and cotton rats thrive in this habitat.

Red-winged blackbirds (_Agelaius phoeniceus_), yellow-billed cuckoos

(_Coccyzus americanus_), red-eyed vireos (_Vireo olivaceus_), catbirds

(_Dumetella carolinensis_) and Kentucky warblers (_Oporornis

formosus_) use it for nesting. The high humidity and dense vegetation

in this grove render it favorable habitat for recently metamorphosed

frogs and toads, especially the tree frog, which is sometimes

extremely abundant there in summer.

#Populus deltoides.#--Cottonwood is one of the less common trees on

the area, but it attains a larger size than any of the other kinds.

The larger of the two creeks on the Reservation is lined with mature

cottonwoods along the lower part of its course. Along the smaller

creek large cottonwoods are also present but they are more widely

spaced. A few cottonwoods are present at well scattered points on

slopes and hilltops, usually in forest edge situations or in woodland

where other trees are sparse. By far the largest tree on the

Reservation is a cottonwood of 15-foot circumference (Plate 1),

growing on a hilltop near the south boundary of the Reservation, at

the edge of woodland adjacent to a cultivated field.

The heavy rainfall of 1951 resulted in the establishment of hundreds

of cottonwood seedlings, mostly in places remote from the mature

trees. So far as observed, all these were in recent silt deposits.

Many of them have survived the drought of 1952-1954.

Because of their great height, towering above the level of the

surrounding tree-tops, cottonwoods are preferred look-out perches

of certain of the larger birds, notably red-tailed hawks (_Buteo

jamaicensis_), barred owls (_Strix varia_), and crows (_Corvus

brachyrhynchos_). Flocks of robins (_Turdus migratorius_) and of rusty

blackbirds (_Euphagus carolinus_) preparing to roost have been noted

habitually to gather in the tops of tall cottonwoods. In spring,

large wandering flocks of goldfinches (_Spinus tristis_) have been

seen feeding on the leaf buds of cottonwoods. Baltimore orioles

(_Icterus galbula_) and yellow-billed cuckoos often forage in

cottonwoods. Red-bellied woodpeckers (_Centurus carolinus_) spend a

disproportionately large amount of their time in cottonwoods. These

woodpeckers have been observed nesting in the hollow branches on several

occasions. Downy woodpeckers (_Dendrocopos pubescens_) also have been

noticed foraging in cottonwoods on many occasions. Certain large

isolated cottonwoods along creeks were favorite stopping places of blue

jays (_Cyanocitta cristata_) which, on trips from one wooded hillside to

another, usually perched briefly in the tops of these tall trees.

Calling and looking about, the jays seemed to maintain contact with

distant mates or members of the flocks by using these high perches.

Often after a brief pause in the top of the cottonwood they flew off in

a new direction.

Both woodrats and opossums have been known to utilize hollow

cottonwoods as dens. Fox squirrels have been seen climbing in

cottonwoods occasionally.

#Juglans nigra.#--Black walnut is one of the more prominent hardwoods.

Under original conditions, evidently many of the larger trees were of

this species. Being the most valuable timber species of the area,

walnut has been subjected to heavy cutting over the past 85 years.

Most of the walnut trees still present are small or medium-sized, but

the species is still abundant over much of the area. Along certain

hilltop edges there are groves of walnuts, growing in nearly pure

stands, with an occasional elm, ash, coffee-tree or honey locust.

Elsewhere walnut trees are more scattered, but are distributed

throughout the woodland. Although the walnut trees growing in woods

are of various sizes from those of mature size down to saplings,

seedlings are to be found mainly in fields near the woodland edge. In

these situations it is one of the more prominent of the woody species

invading open lands. The seeds evidently are transported mainly by

rodents, especially fox squirrels.

In autumn every walnut tree that is bearing nuts becomes a focal

point of activity for squirrels. Over a period of weeks the squirrels

concentrate their attention on the walnut crop, continuing until

virtually every nut has been harvested. Walnut seems to be the one

most important food source, for both the fox squirrel and the gray

squirrel. Most of the nuts are stored for future use. Many buried

separately and never retrieved by the squirrels, grow into new trees.

White-footed mice often store the nuts in their nests, in burrows,

beneath rocks or in crevices. In summer, groves and isolated trees of

walnuts are favorite haunts of the yellow-billed cuckoo, which finds

concealment in the thick foliage, and probably feeds upon the tent

caterpillars that commonly infest these trees.

#Carya ovata.#--Shagbark hickory is one of the more important

hardwoods of the area. The trees are relatively small compared with

the larger oaks, elms, ashes and hackberry. However, on several parts

of the area this hickory is dominant. It grows mainly on north slopes

and hilltops. The trees most frequently associated with it are black

oak, American elm and chestnut oak. Scattered through the woodlands

are occasional mature hickories of DBH 18 inches or more. However,

many of the trees are six inches or less DBH and a large proportion of

these have originated as stump sprouts from trees cut in the early

thirties or before.

Shagbark is especially tolerant of shading. Numerous young trees and

seedlings noted all were growing in dense woods of larger hickories,

oaks, or mature elms. None has been found in open fields or even in

edge situations. This hickory is resistant to drought; relatively few

died during the drought of 1952-1954, and these were mostly small

trees in crowded stands.

In parts of the woodland dominated by shagbark hickory the trees are

mostly 5 to 6 inches or even smaller in trunk diameter and 20 to 30

feet high, sometimes growing in nearly pure stands, and with a leaf

canopy so dense that shrubs and herbaceous vegetation are sparse.

The mast crop produced by shagbark is an important food source for

both fox squirrels and gray squirrels. Both kinds of squirrels often

use these hickories as sites for their stick nests. White-footed mice

also store the nuts as a winter food source.

Birds which are most often seen in groves of shagbark include the

yellow-billed cuckoo, tufted titmouse (_Parus bicolor_), black-capped

chickadee (_P. atricapillus_), blue jay, summer tanager (_Piranga

rubra_), and red-eyed vireo. The Cooper hawk (_Accipiter cooperii_)

has been recorded nesting in this hickory. In dead trees of this

species that are still standing, the interiors may decay more rapidly

than the armorlike bark plates. On several occasions tufted titmice

and chickadees have been recorded as nesting in such cavities.

#Quercus stellata.#--Post oak is relatively scarce on the Reservation.

One area of approximately an acre on a south slope is dominated by it.

There are several other small groves and scattered trees. All are on

moderately steep south slopes in poor soil. Trees often found

associated with it include red elm, chestnut oak, chinquapin oak,

blackjack oak, hickory, and dogwood. It seems likely that under

original conditions this species occupied about the same area as it

does at present. It is not spreading, and there are few young trees

anywhere on the area. In every instance the groves are limited to a

rocky clay soil, and edaphic factors obviously are of major

importance. Under original conditions fire was probably a limiting

factor, and at the present time competition with other hardwoods may

be even more important.

#Quercus macrocarpa.#--Less than a dozen individuals of mossycup oak

have been noticed on the area, at well scattered points. Under

original conditions, it probably grew chiefly in the bottomlands that

have been completely cleared of timber for cultivation. The few now

present are all on hillsides, and are medium to large trees.

#Quercus Muehlenbergii.#--Chestnut oak was perhaps the one most

important tree species of the original climax forest on the area.

Because of its slow growth, scanty seed production, and large heavy

fruits with seeds lacking effective dispersal mechanisms, it has lost

ground to other kinds of trees as a result of the unnatural

disturbances which have occurred.

It still dominates on rocky upper slopes that have north, east or west

exposures and forms nearly pure stands in limited areas. Nearly all

the larger trees of this species now present have been cut one or more

times and have regenerated from stump sprouts. Seedlings and young

saplings of this oak are scarce even in parts of the woodland where

the species is most common. It is evident that reproduction is slow,

at least under present conditions. On the lower hill slopes these oaks

are scarce and scattered, but some of the largest are in such

situations. Chestnut oak seems to be relatively resistant to drought.

In the summer of 1954 when elms, and especially black oaks of all

sizes were dying in large numbers, the chestnut oaks growing among

them showed little evidence of injury in mature trees and only a small

percentage of mortality in saplings.

[Illustration: Fig. 5. Map of Reservation showing present

distribution of chestnut oak (shaded). The species is not

spreading and is thought to be largely confined to the area

that was wooded before 1860. Except in minor details,

shagbark hickory conforms to the same distribution pattern

on this area.]

Chestnut oak has a relatively slow growth rate. In 17 that were

recorded, there were, on the average, 4.59 annual rings per inch of

trunk diameter. Near Pigeon Lake, Miami County, Kansas, counts were

obtained from five cut in 1952 from a virgin stand in a habitat

similar to that on the Reservation. The five trees had trunk diameters

of 16-1/2 to 25 inches and ranged in age from 65 to 183 years. Several

still growing on the Reservation are larger and presumably are well

over 100 years old.

As this oak seems to be in process of being replaced by other trees,

is slow-growing, and slow in dispersal, it seems probable that the

areas now occupied by its stands supported stands of it under

original conditions. Whether it can regain dominance under present

conditions of protection from cutting, fire and grazing remains to be

seen.

The chestnut oak produces a mast crop which is utilized by many kinds

of animals. Fox squirrels, gray squirrels, and white-footed mice feed

upon the acorns and store them. Blue jays, red-headed woodpeckers

(_Melanerpes erythrocephalus_), and red-bellied woodpeckers also eat

them. The red-eyed vireo, summer tanager and tufted titmouse are among

the birds that most frequently forage for insect food in chestnut

oaks. Relatively few kinds of birds seem to use this tree as a nest

site.

#Quercus prinoides.#--The chinquapin oak on this area is a small

shrubby tree, usually not more than 15 feet high and more typically

only six to eight feet. It occurs chiefly in dry rocky situations

along hilltop edges and upper slopes, usually where the slope exposure

is at least partly to the south. In such situations it may grow in

nearly pure stands. Often it is associated with dogwood. The trunks

are usually two to four inches in diameter, gnarled and twisted. The

crowns are dense and spreading.

This oak is the dominant plant in certain small areas of its preferred

habitat. In other areas of hilltop edge and upper slope it is being

eliminated by stands of hickory, chestnut oak, black oak and elm,

which shade it out. The species is tolerant of moderate to heavy

browsing, but seemingly can be eliminated by more intensive

utilization; even the higher foliage is often within reach of

livestock. In "Horse Woods" one of the hillside areas that was open to

livestock until 1949, this oak was almost absent, but it was abundant

in adjoining parts of the woods that were fenced in the thirties to

exclude livestock.

The thickets formed by this shrubby oak are frequented by cottontails,

which feed upon the bark and foliage. The small acorns are used as

food by rodents, especially the white-footed mouse. On several

occasions, in winter, groups of long-eared owls (_Asio otus_) have

been found roosting in thickets of chinquapin oak. Crows also utilize

these thickets for roosting occasionally. The white-eyed vireo (_Vireo

griseus_), gnatcatcher (_Polioptila caerulea_), and tufted titmouse,

frequent the oak thickets.

#Quercus rubra.#--The red oak is one of the important climax species

of the area. At present it is largely confined to a ravine in the

northeastern part of the section. The woodland here is less disturbed

than on most other parts of the Reservation, and red oak is the

dominant species. There are large trees, rather evenly distributed,

growing on east-facing and west-facing slopes. Just east of the

Reservation, in the "Wall Creek" area, the small valley on either side

of the creek and the adjacent lower slopes are dominated by giant red

oaks larger than any now growing on the Reservation. Farther up the

slope in the area of limestone outcrops, dominance shifts to chestnut

oak. That red oaks of similar size, and even larger, formerly occurred

on the Reservation, at least in the area still dominated by the

species, is shown by the presence of a stump 49 inches in diameter,

now in an advanced state of decay.

[Illustration: Fig. 6. Map of Reservation showing present

distribution of black oak (smaller dots) and red oak (larger

dots). Neither species is spreading and both are thought to

be largely confined to the area that was wooded before 1860.]

The large acorns of the red oak are a favorite food of the gray

squirrel, which is most numerous on the parts of the Reservation where

these trees are present. The red-headed woodpecker on the area tends

to concentrate its activities where there are red oaks. The fox

squirrel, white-footed mouse, and blue jay are important consumers of

the acorns of red oak. A pair of barred owls resided in the deep woods

formed by these oaks and the associated trees.

#Quercus velutina.#--Black oak is one of the dominant species of the

original forest climax, and is still one of the more important trees

of the woodland. Like chestnut oak it shows little tendency to spread

beyond its present limits. Wherever there are small trees there are

old mature trees or remains of them nearby. For this reason the

present distribution of black oak on the area is thought to fall

entirely within the area occupied by the original forest. At present

it occurs throughout most of the woodland except in the warmer and

drier situations, such as on south slopes. In some hilltop situations

it is common, with occasional large mature trees. In some parts of the

bottomland and lower slopes it is abundant also, but there are

scarcely any on the upper dry rocky slopes that are the preferred

habitat of chestnut oak.

Growth in the black oak is somewhat more rapid than in the chestnut

oak, as the black oak usually grows on better soil. For 15 the average

growth amounted to 3.21 annual rings per inch of trunk diameter.

In 1954 a study of annual rings in a large, long dead, black oak at

the bottom of a north slope near the Reservation headquarters showed

that the tree was 96 years old, and hence was growing before the area

was settled. Within the period of this study black oak underwent

reduction in numbers more severe than that noted in any other species

of tree on the Reservation. The effect of drought may have been the

primary factor, although undoubtedly disease was involved also. In

1953, the second successive drought year, mortality was noticeable.

Precipitation continued below normal until August 1954. By then the

oaks had been decimated. On a sample strip of hilltop where 29 were

recorded, 21 had recently succumbed, and their leaves were dry and

withered; two were dying, though still having some green foliage, and

only six were surviving, all evidently in critical condition. The

mortality included trees of all sizes, even the largest and oldest. No

further mortality was noted in 1955 when precipitation was only

slightly below normal. On the Reservation there are many old logs, and

snags still standing, of mature black oaks long dead. Earlier drought

periods such as those of 1936-37 and 1925-26 possibly were also times

of unusually heavy mortality. In any case it seems clear that this oak

was originally more prominent in the woodlands than it is at present,

and has been steadily losing ground. Even where the mature trees

remain in greatest numbers the saplings are relatively scarce as

compared with those of elm, ash, hackberry, and hickory. The

westernmost limits of the range are nearly 100 miles west of the

Reservation.

Black oak provides a mast crop which is utilized by various small

mammals, notably squirrels and white-footed mice. Gray squirrels have

often been noticed in or about these trees. Hairy woodpeckers

(_Dendrocopos villosus_), black and white warblers (_Mniotilta

varia_), and brown creepers (_Certhia familiaris_) have often been

noticed foraging on the trunks. Blue jays, myrtle warblers (_Dendroica

coronata_), tufted titmice, and summer tanagers frequently forage

through the crowns. Often black oak trunks are hollow and the cavities

are utilized by various birds and mammals including the screech owl

(_Otus asio_), barred owl, raccoon, opossum, fox squirrel, gray

squirrel, woodrat, and white-footed mouse.

#Quercus marilandica.#--Black Jack oak is localized in four small

compact groves on the Reservation. These sites, though well separated,

are similar. All are on steep lower slopes, where there is dry rocky

clay soil and the exposure is mainly south. Probably all four groves

date back to the time when the area was still in an undisturbed state.

Originally they were perhaps largely separated from the remainder of

the woodland. Black Jack oak is more tolerant of heat and drought than

most of the other hardwoods are. The species is intolerant of fire,

but perhaps was partly protected under original conditions by the

sparseness of herbaceous vegetation on the poor soil where the groves

were situated.

These oaks are relatively slow-growing. One stump of 9-inch diameter,

typical of the larger Black Jack trees, had approximately 60 annual

rings. Under present conditions there is little or no reproduction and

these trees are dying out as a result of competition by other

hardwoods. Under protection from fire and browsing, elms, other oaks,

locust and dogwood have closed in about the groves and seem to be

shading them out.

There are several mature oaks of anomalous appearance, in different

places within a few hundred feet at most of the groves of Black Jack.

Most of these appear to be hybrids between the present species and _Q.

velutina_, as they are somewhat intermediate in size, bark texture,

and leaves.

This oak produces a mast crop used by various birds and mammals, and

groves are frequented by blue jays, fox squirrels, white-footed mice

and woodrats. In the mid-forties when the woodrat population was high,

there were many of the rats' stick houses in the groves, built either

at the bases of the trunks or among the dense branchlets in tops of

fallen trees. By 1952 the population of woodrats was much reduced and

had disappeared entirely from these groves. The houses were collapsed

and decaying.

Horned owls (_Bubo virginianus_) and barred owls often make their day

roosts among the dense interlacing twigs of these trees, and

red-tailed hawks have been known to roost for the night in the same

kinds of situations.

#Ulmus americana.#--On most parts of the area American elm is the

dominant tree. It occurs throughout the woodland, and most of the

larger trees are of this species. In each of the fields that were

formerly cultivated, and in the pasture areas, there are many

saplings. More than one hundred elms of DBH two feet or more have been

recorded. Presumably these mostly date back 90 years or more and were

already growing on the area when it was relatively undisturbed. On the

area the distribution of these large elms corresponds in a general way

with the present distribution of the oak-hickory type. The coinciding

distribution of the climax species and of the largest trees is

believed to reflect the distribution pattern of the original forest,

except that clearing was thorough in the bottomlands so that hardly

any trees of the climax species, or large trees of any kind remain.

Several elms of three feet or more DBH were recorded, and the largest

one measured was 46 inches. The largest elms are in alluvial soil near

small creeks in the two valleys. Also many large elms grow along the

upper slopes, especially along the outcrops of the two main strata of

the Oread Limestone. Such sites along the outcrops on open slopes are

the first to be invaded. The rock strata are relatively impervious to

water, which is held at a depth where it is readily available to the

trees. Along rocky upper slopes between the two outcrops, where

chestnut oak is abundant, elms are relatively scarce and seem unable

to compete successfully. It is noteworthy that elm is not mentioned in

several of the descriptions (Taft, 1950; Parks, 1854; Robinson, 1899)

of the original forest, even in listings of the species present. It

must have been much less prominent until favored by disturbed

conditions.

[Illustration: Fig. 7. Map of Reservation showing present

distribution of the largest American elms, those more than two

feet in trunk diameter. American elm is increasing and spreading

on the area, and smaller trees are abundant even in former

cultivated fields and pastures. Growth rate varies according to

site, but these larger trees are, in many instances, 90 years or

more in age and most of them are thought to be in the area

wooded in the eighteen sixties and before.]

In July and August, 1954, a large proportion of the elms on the area

died. The die-off included trees of all sizes, and evidently the

cumulative effect of drought in 1952 and 1953, continuing into the

spring and summer of 1954, was the primary cause, although

diseases such as phloem necrosis, and insect infestations, may have

intensified its effect. In August of 1954 the bare dead elms stood out

conspicuously in the mass of green foliage surrounding them. Most of

them had survived the two dry summers of 1952 and 1953 with little

evident loss in vitality. However, the continued lack of moisture as

the 1954 growing season progressed, and the extremely hot weather of

June and July caused heavy mortality. In the course of a few days the

foliage of the upper branches would wither, die and turn brown. In

some instances numerous sucker shoots grew from the trunk of the tree

as the top was dying. Mortality was especially heavy on south-facing

slopes. Certain ecologists believe that over the years, as trees

deplete subsoil moisture and periodic droughts make their effects

felt, other species also will die off and eventually prairie will

replace them where the present forests are growing in dry and exposed

situations.

Infestations of the introduced bark beetle, _Scolytus multistriatus_,

were common and probably contributed to death of many elms. In the

winter of 1953-54 before much mortality had occurred, the bark beetle

infestations had become conspicuous. Especially on south slopes elms

of about six inches DBH were heavily infested. Woodpeckers, including

the downy, hairy, and red-bellied, habitually resorted to the elm

trunks to forage. As a result of their activities chips of bark

accumulated sometimes to a depth of several inches around the bases of

the trunks, and the exposed inner layers of brown bark caused the

infested trees to contrast with the predominantly gray color of those

that were still healthy and retained the outer layer of bark.

In April and early May seeds of the American elm constitute a major

food source for birds, including the black-capped chickadee, tufted

titmouse, junco (_Junco hyemalis_), red-eyed towhee (_Pipilo

erythrophthalmus_), Harris sparrow (_Zonotrichia querula_), cardinal,

goldfinch, tree sparrow (_Spizella arborea_) and field sparrow (_S.

pusilla_). Birds recorded as nesting in the American elm include the

mourning dove (_Zenaidura macroura_), Cooper hawk, red-tailed hawk,

broad-winged hawk (_Buteo platypterus_), turkey vulture (_Cathartes

aura_), screech owl, horned owl, barred owl, red-bellied woodpecker,

downy woodpecker, tufted titmouse, black-capped chickadee,

gnatcatcher, red-eyed vireo, summer tanager, indigo bunting

(_Passerina cyanea_), field sparrow and cardinal.

Opossums, raccoons, fox squirrels and white-footed mice often live in

cavities in elms.

Insectivorous birds that find their food on foliage and prefer elm or

use it to a large extent are: yellow-billed cuckoo, tufted titmouse,

black-capped chickadee, blue-gray gnatcatcher, red-eyed vireo,

white-eyed vireo and warblers, including the myrtle, Audubon

(_Dendroica auduboni_), yellow (_D. petechia_), black-throated green

(_D. virens_), black-poll (_D. striata_), Tennessee (_Vermivora

peregrina_), orange-crowned (_V. celata_), Nashville (_V.

ruficapilla_) and American redstart (_Setophaga ruticilla_).

#Ulmus rubra.#--The red elm (or slippery elm) is widely distributed

over the area, but only a few trees with a trunk diameter of twelve

inches or more are present. Throughout the woodlands of the

Reservation the saplings of this species constitute a prominent part

of the understory. However, few survive beyond the sapling stage. The

red elm is never abundant in Kansas woodlands. It is intolerant of

drought conditions, and is one of the first trees to die. This fact

probably explains the scarcity of mature trees of this species on the

Reservation.

#Celtis occidentalis.#--Hackberry is widely distributed on the area,

but is not dominant anywhere. Its favorite site is along hilltop

limestone outcrops, especially where there is south exposure. There

are few on hilltops away from the outcrops. Hackberries are scattered

in small numbers over the wooded slopes. There are a few of unusually

large size, along edges of the bottomlands. Hackberries are

slow-growing. Counts of annual rings for four indicated an average of

7.1 rings per inch of trunk diameter. Young hackberries of all sizes

are numerous throughout the woodland. Therefore it seems likely that

this species is in process of spreading and probably has already

extended beyond the situations which it originally occupied.

The fruits of hackberry provide a fall and winter food supply for

various animals. Opossums are especially fond of them. Red-bellied

woodpeckers have been seen storing them. Migrating flocks of robins

may utilize them as a major food source temporarily. White-footed mice

and woodrats store them and eat them.

#Morus rubra.#--Red mulberry is moderately common in certain heavily

wooded areas, especially the lower parts of north slopes. A few are

present on wooded hilltops. Most of the trees are between ten and

twenty feet tall, and generally die before growing larger. Red

mulberry is present in most woodlands of eastern Kansas and is

seemingly distributed by birds. It is never an important component of

woodlands in the area. Catbirds (_Dumetella carolinensis_) and wood

thrushes (_Hylocichla mustelina_) especially have been noted

frequenting the vicinity of mulberry trees in fruit. Probably many

other kinds of birds utilize the fruits to some extent.

#Maclura pomifera.#--Osage orange was not a member of the original

flora, but early settlers in Kansas valued it for windbreaks and fence

posts, and they made extensive plantings. Presumably it was introduced

onto the area of the present study in the eighteen sixties. At the

present time it occurs throughout the woodland, with scattered mature

trees and many young trees on the former pastures. This aggressive

invader spread despite frequent cutting, and now plays an important

part in the ecology of the area. Most of the larger trees have been

cut one or more times, but have regenerated from stump sprouts with

multiple stems and spreading habit. The tough and durable wood is

useful for fence posts. The growth rate is slow, similar to that of

oaks and elms.

Osage orange is intolerant of fire and is easily killed by scorching.

It is damaged by browsing, and cannot grow in deep shade. It is

drought resistant. Mortality was light during the drought period of

1952-1954, although many of the trees were growing on poor soil in the

hotter and drier sites.

Where there are stands of mixed hardwoods, osage orange is relatively

scarce and tends to be on or near the edges of the stands. The osage

orange trees growing in competition with oaks, elms and hickories may

have tall, slender trunks and narrow crowns, in contrast with the

spreading habit of those growing in more open sites. In the woodlands

small and medium-sized trees are scarce and there is hardly any

reproduction. Obviously the osage orange, like honey locust became

established in the forests when the stands were more open, probably

after cutting of the large trees. In contrast to the meager

reproduction in shaded sites is the abundant crop of young saplings

along edges of fields adjacent to woods or about isolated osage orange

trees. Evidently the tree does not become established readily on

bluestem prairie. On a hillside adjoining the northwest corner of the

Reservation, long subjected to heavy grazing, osage orange dominates,

but just across the fence on the Reservation side, it is almost

absent. This area had been maintained as bluestem prairie until about

1934 by occasional burning and since then had partly grown up into

thickets in which dogwood, and saplings of elm and hackberry were

abundant.

The dense thorny branches provide shelter and nesting sites for many

kinds of animals. On this area the cardinal utilizes it for nesting

sites more frequently than any other kind of tree. Some nests were so

well protected by the thorns that they could scarcely be reached.

Indigo buntings, field sparrows, and yellow-billed cuckoos also use

these trees or young saplings for nesting sites.

In the forties, when the woodrat was common on the area, its local

distribution seemed to be determined mainly by the osage orange. Many

houses of the woodrat were built around old stumps at the bases of

large, spreading osage orange trees. Frequently the houses were in the

main crotch of a tree two to eight feet from the ground.

Characteristically the rats used horizontal or gently inclined, low

branches of the tree as runways to and from the house. In summer and

early autumn these rats stored foliage of the osage orange in large

quantities in chambers adjacent to the nest. The seeds also provided

an important food source. During the period 1948 to 1951 the woodrat

population steadily decreased, and one by one the houses in osage

orange trees were deserted, until the small surviving population of

woodrats was limited to hilltop rock outcrops not associated with

osage orange trees.

The seeds are well liked by other rodents also. In late fall and

winter after the "hedge balls" have fallen, fox squirrels visit the

trees and shred the fruits to gain access to the seeds. Over periods

of weeks heaps of the shredded refuse accumulate at the base of the

tree trunk. The seeds probably constitute the one most important

winter food of the fox squirrel. The tufted titmouse also relies to a

large extent on the seeds for its winter food. Being unable to shred

the bulky hedge balls itself, it depends almost entirely on the seeds

in fruits torn open by the squirrel but not fully utilized by it. At

times when the ground and trees are snow-covered, making unavailable

most other food sources, the osage orange seeds gleaned from refuse

heaps in the sheltered feeding places of the squirrels are probably of

critical importance to the titmouse.

The cottontail and white-footed mouse also eat the seeds.

#Platanus occidentalis.#--Sycamores are few and scattered on the area,

but those present seem to be holding their own if not gaining in

numbers. They include some of the largest trees on the Reservation.

The most typical habitat is along rocky ravines on wooded slopes.

Occasional trees are scattered through the woods away from ravines on

slopes of north, east, or west exposures, or on hilltop edges,

providing strong evidence that these areas were more open at the time

the sycamore seedlings became established. Cutting of the mature trees

in the original forest and subsequent grazing might have created the

conditions favorable for their establishment. Many saplings have

sprung up in the fallow hilltop fields that were formerly cultivated.

Many of the larger sycamores have cavities and these are inhabited by

various animals. A large sycamore in a ravine below a pond had a

cavity in its base within which a raccoon reared its litter of young

one summer. At other times this same cavity was inhabited by woodrats

and by fox squirrels. Seemingly this cavity was the habitat of a

certain chigger which was found on both the squirrels and the woodrat.

Red-bellied woodpeckers excavated a cavity high on this same tree

trunk, in which they reared their brood.

Several large sycamores died as a result of the cumulative effect of

drought in the summers of 1952, 1953 and 1954, but many others

survived.

#Prunus americana.#--Wild plum is a small tree, usually not more than

three inches in trunk diameter, nor more than twelve feet high. It

tends to grow in dense thickets which are spotty in distribution.

Several of these thickets are in edges of former pastures at the

woodland edge. Other extensive thickets are in the following

situations: along hilltop rock ledges and encroaching into adjacent

prairie on upper south-facing slope maintained as bluestem prairie by

mowing and burning, until 1934; along a ravine in formerly cultivated

hilltop fields; along tops of steep creek banks at edge of old corn

field. In a few situations within the woodland there are dead and

dying thickets of wild plum, shaded out by the closing in of the tree

canopy, as fast-growing trees such as elm, honey locust, and cherry

sprang up in former clearings.

The woodrat lived in several plum thickets that provided the type of

shelter from predators that it requires. The bark, fruit and foliage

are used as food. In autumn the plums sometimes are the chief food of

the opossum. Plum thickets provide the preferred habitat for the Bell

vireo (_Vireo bellii_). The white-eyed vireo, field sparrow, tree

sparrow, Harris sparrow, and white-throated sparrow (_Zonotrichia

albicollis_) also frequently use these thickets.

#Prunus serotina.#--Isolated trees of black cherry six to fifteen

inches in trunk diameter, have been noted on various parts of the

Reservation at widely scattered points. On a flat hilltop at the

southeastern corner of the Reservation there are many large trees of

black cherry, which make up a major portion of the stand, and trunks

of some are as much as 21 inches in diameter. Other trees in the

vicinity are mostly elms and honey locusts, and seemingly the area was

more open or perhaps entirely treeless in the recent past. The

presence of black cherry in forest often can be interpreted as

indicating more open conditions at the time the seedling became

established. Black cherry prefers a rich soil and an open habitat;

hence it is generally not common in woodlands of northeastern Kansas.

The fruits of black cherry are a favorite food of the opossum, and the

seeds have often been noticed in the scats of this animal.

White-footed mice store and eat the seeds. Two trees of black cherry

well isolated from other trees except for saplings in low thickets,

constituted the headquarters of a Bell vireo's territory each summer

from 1951 through 1955.

#Pyrus ioensis.#--Crab-apple is a small tree, usually less than five

inches in trunk diameter and less than 12 feet high. It grows both in

woodlands and in former pastures, but chiefly along the line of

contact. After removal of livestock in early 1949, crab-apple spread

into the edges of hilltop pastures, from the adjacent protected

woodland. Each year thickets of encroaching crab-apple have extended

farther into the fields, until, in 1955, there were graded series from

the trees along the fence, six feet high or more, to the seedlings 30

to 50 feet out in the fields. Dogwood, red haw, and smooth sumac are

among the most common associates of crab-apple as they share its

tendency to invade open land adjacent to the forest.

Evidently the tree is intolerant of browsing by livestock, as few were

growing in the pastured areas in 1948, but as soon as livestock were

removed these areas were rapidly invaded.

The thickets formed by crab-apple provide shelter for many kinds of

animals. Cottontails, especially, tend to stay in or near these

thickets. In autumn the fruits are eaten by them, and in winter, when

the ground is covered with snow, the bark is a major food source. Most

mature or partly grown trees show old scars near their bases, where

the rabbits have attacked them. Often the trees are completely

girdled. In years when snow lies on the ground for long periods

girdling is extensive and a substantial portion of the trees in the

thickets may be killed, but this mortality has been insufficient to

check the rapid spread of crab-apple.

The crab-apple is one of the trees preferred as a nesting site by the

cardinal. Other birds that frequently use the crab-apple tree as a

nest site include the field sparrow, towhee and indigo bunting.

White-footed mice, prairie voles and pine voles eat the fruit and

seed.

#Crataegus mollis.#--Red haw occurs over much of the Reservation, both

in woodland and former pastures. The trees are scattered, and are not

dominant, even on small areas. In the woodland, haw usually grows in

the more open situations. Where there are haws in denser woods, they

are usually large and old; seemingly they are survivors from a time

when the woods were more open. Haw is intolerant of shading, and being

of lesser height than any of the climax species, it cannot compete

with them. The present wide distribution of haw on the area is

secondary, resulting from the extensive cutting of the larger trees

and opening up of the woodland. Haw trees are most numerous on south

facing slopes that have grown up into thickets in the last 30 years.

Here its associates are chiefly honey locust, osage orange, dogwood

and elm.

Red haws have been recorded as nest trees of horned owls,

yellow-billed cuckoos, cardinals, and fox squirrels. Cavities in the

trunks are used by downy woodpeckers, titmice, chickadees and

white-footed mice.

#Cercis canadensis.#--Redbud is abundant in some parts of the

woodland. Trees are up to nine inches in diameter and 25 feet high.

They grow chiefly in rich soil on hillsides in moist situations.

Redbud and dogwood are in part complementary in distribution, each

forming an understory in parts of the woodland where the leaf canopy

of larger trees is not too dense. However, redbud is more tolerant of

shade. In general dogwood grows in the drier, more rocky situations

and redbud in better soil and damper sites. In the southeastern part

of the Reservation, on a west facing slope, redbud dominates, with

smaller numbers of elm, blackjack oak, and dogwood.

Several times nests of yellow-billed cuckoos were found in redbuds.

Titmice, chickadees, and red-eyed vireos forage in redbuds on many

occasions. Brown creepers forage on the trunks. Titmice, chickadees,

and downy woodpeckers used cavities in dead or dying redbuds. However,

there is no evidence that this tree is especially attractive to any

kind of vertebrate, or plays an important part in the ecology of the

area.

#Gymnocladus dioica.#--Kentucky coffee-tree is one of the less

important trees on the area but it is widely distributed. In general

it is absent from the denser woods. On limited areas of certain slopes

it is the dominant species. The groves sometimes are in nearly pure

stands. Slope exposure evidently is not the determining factor in the

local distribution as groves have been found on hillsides of varying

exposure. The tree seems to flourish where the forest has been opened

by cutting of the larger trees. Groves are mainly on the more gently

sloping parts of the hillsides, or on the nearly level terrace. There

are few coffee-trees more than 12 inches in trunk diameter. The

largest tree examined was 27 inches.

In May, groups of orchard orioles (_Icterus spurius_) have been

observed in coffee-trees, seemingly attracted by the blossoms. These

concentrations never lasted more than a few days and seemed to involve

individuals that were still migrating or newly arrived and not yet

established on their territories.

In winter the large pods of this tree are used as food to a limited

extent by cottontails. The large hard shelled seeds resist attack by

most animals. Seemingly they are used by white-footed mice, as they

have often been found stored in the nest cavities of these mice,

beneath rocks or in logs.

#Gleditsia triacanthos.#--Honey locust is at present one of the more

important species of trees on the area. There are scattered locusts

throughout most parts of the woodland. In the bottomland fields there

are groves and scattered trees of medium to large size. On south

slopes honey locust, osage orange and red elm form thickets. On

hilltops, along woodland edges where fences were installed in the

mid-thirties, young honey locusts have become established and are now

abundant. Some have grown to a diameter of 8 inches or more. Honey

locust is the fastest growing of the trees on the area and therefore

has an early advantage in competing with other kinds. A locust of

25-inch diameter cut in 1950 was found to have 32 annual rings, an

average of only 1.3 rings per inch as contrasted with an average of

3.8 for all the trees studied, and more than 9 for some of the slowest

growing. In open fields, both those used for pasture and those

formerly cultivated, young honey locusts have sprung up in abundance

since the discontinuance of grazing in 1948. The species is resistant

to drought. It seems to have been limited on the area mainly by

grazing and shading. The locusts growing in the woods tend to be

concentrated near its edges. Those that are deeper in woodland

evidently became established after heavy tree-cutting had opened

clearings. Locusts in such situations, competing with other hardwoods

are of much different form than those growing in the open; the trunks

are long and slender and the crowns are narrow.

The south slopes that were originally prairie, were evidently only

sparsely clothed with trees up until the thirties when livestock were

fenced out. Then the abundant growth of shrubs and young trees formed

thickets. Honey locust, growing rapidly tended to dominate. The

younger locust saplings that were shaded beneath the leaf canopy died

in large numbers.

Honey locust plays an important part in the over-all ecology of the

area, providing both food and shelter for many kinds of animals. The

foliage is well liked by livestock; consequently young trees have

little chance of surviving in heavily grazed pastures. Rabbits like

both the foliage, and the bark. Often they girdle or injure young

trees, and eat the beans. Both the prairie vole and the pine vole

often feed upon the inner bark and root crowns of small saplings,

sometimes completely undermining them. These voles also store and eat

the seeds. Beneath large mature locusts, runway systems and burrows

of the pine vole are sometimes much in evidence. As ground vegetation

is scanty in these places it seems that the voles are attracted by the

abundant supply of locust seeds.

The spiny branches of locusts provide well protected nesting sites

that are utilized by various kinds of birds; mourning dove, horned

owl, yellow-billed cuckoo, gnatcatcher, cardinal and goldfinch have

been recorded nesting in locusts. The wood is relatively soft. The

hairy woodpecker has been recorded nesting in a cavity which it had

dug in a living honey locust, while the black-capped chickadee and

red-bellied woodpecker have been recorded nesting in cavities in dead

limbs. The summer tanager prefers large locusts near the edge of

woodland as singing stations.

Fox squirrels also often exploit the spiny protection provided by

locust trunks, and build their stick nests in these trees, usually in

a fork of the main trunk eight to twelve feet above the ground. Such

nest trees often are either isolated or are in groves of other

locusts. Presumably the squirrels are attracted to them by the supply

of locust seeds.

#Acer Negundo.#--Boxelder probably was not a part of the original

flora of the Reservation. The trees present now are few and scattered,

and most are not more than eight inches in trunk diameter. The species

seems intolerant of shade and does not grow in the denser woodlands. A

few are present along the banks of the intermittent streams, and there

are others in open woodlands of south slopes. The small patch of

bluestem prairie remaining at the northwest corner of the Reservation

is being invaded by a variety of shrubs and saplings, and boxelder is

by far the most prominent of these invaders, with two hundred

seedlings and saplings per acre.

#Ailanthus altissima.#--Tree-of-heaven is an Asiatic species that was

introduced early into northeastern Kansas, and has become established

locally in the woodland. Most of those on the Reservation are near the

central part of the southwestern one-fourth. Concentrated about the

site of an old homestead, occupied in the eighteen-seventies, within a

few acres, there are dozens of mature trees, up to 22 inches in trunk

diameter, and hundreds of saplings. Elsewhere on the Reservation the

species is scarce and is represented by isolated trees and scattered

clumps at a few places.

#Cornus Drummondi.#--This dogwood is the most abundant tree on the

area. However, it scarcely reaches the size of a tree. Most mature

examples are 1-1/2 to 3-1/2 inches in trunk diameter, and rarely more

than twelve feet high. Dogwood grows in greatest abundance on dry

rocky slopes where other trees are scarce. In small areas it may be

the dominant tree, often closely associated with chinquapin oak and

red elm. In parts of the woodland where there are larger trees,

dogwood may form an understory, its development depending largely on

the amount of light passing through the upper leaf canopy. Where the

canopy is dense and nearly continuous, dogwood tends to be eliminated

by shading. In some situations where forest has recently closed in,

most of the dogwoods are dead or dying. Especially on formerly

cut-over north slopes, where oak and hickory have sprung up in a dense

stand 20 feet high, with a thick canopy, most of the dogwoods have

been eliminated.

On the remaining hillside prairie near the northwest corner of the

Reservation, dogwood is the most prominent of the trees and shrubs

encroaching onto the area since it has been protected from fire--a

period of approximately 20 years. There are dense thickets of dogwood

along the borders of the prairie and the woodland edge.

The white-eyed vireo and Bell vireo both forage and nest in thickets

of dogwood and other shrubs.

#Fraxinus americana.#--White ash is localized on the Reservation and

most of the mature trees are within an area of perhaps three acres on

a steep slope of northwest exposure. Several of the largest trees,

well over a foot in trunk diameter, grow at the lower limestone

outcrop. Ash is most abundant at this level and at the terrace just

below it. On the one slope where it is concentrated, ash is one of the

most common trees, growing in association with American elm, chestnut

oak, black oak, and shagbark hickory. This area is one of the most

mesic on the Reservation. The soil is usually damp, with thick leaf

litter and rich humus. In hilltop fields, formerly cultivated or

pastured, saplings of white ash are among the most prominent invaders.

The leaves of this tree and especially its saplings, are favorite

foraging places for the tree frog. The groves of this tree provide

favorable habitat for the opossum, short-tailed shrew, gray squirrel,

and white-footed mouse. Birds that frequent the same habitat include

the black-capped chickadee, tufted titmouse, blue jay, rose-breasted

grosbeak (_Pheucticus ludovicianus_), yellow-billed cuckoo, red-eyed

vireo, gnatcatcher, hairy woodpecker, Kentucky warbler, and crested

flycatcher (_Myiarchus crinitus_).

[Illustration: PLATE 7

The Forest Habitat of the University of Kansas Natural History Reservation · 第 13 / 22 题