7.9. SR 12-16-1996ITEM 7.9.
.ty of
TO:
iver
MEMORANDUM
DATE:
SUBJECT:
MAYOR AND CITY COUNCIL
STEPHEN ROHLF, BUILDING AND
ZONING ADMINISTRATOR
DECEMBER 16, 1996 ~
BEAVER CONTROL
Beaver numbers increased dramatically in Elk River over the last few years.
The price for their hides was very low and no one was trapping them. The
price for beaver hides is now about $15 to $20 depending on the hide. This
amount is enough to find people to trap them.
The problem of controlling beaver still remains, however, when they are out
of season. They can still be trapped with DNR permission, but the hides can
not be sold. Sherburne County pays for beaver control in county ditches in
the off season.
There are drainage systems in Elk River (i.e. abandoned Judicial Ditch #1)
that, although they are not under any official control, are as important to
drainage in the City as are county ditches. Staff recommends the Council
consider the following policy regarding beaver control:
· In a county ditch the City request that the County control beaver as
needed.
In other drainage areas during the legal season, the City contacts people
willing to trap beaver, when requested by a property owner.
When beaver are out of season, the City coordinate between the property
owner affected, the DNR and a trapper. Further, the City pays a bounty
of $20 per beaver with the front feet being proof of capture.
13065 Orono Parkway · P.O. Box 490 · Elk River, MN 55330 · (612) 441-7420 · Fax: (612) 441-7425
James E. Miller
Program Leader, Fish and Wildlife
USD^- Extension Service
Natural Resources and Rural
Development Unit
Washington, D.C. 20250
Figure 1. Beaver. Castor canadensis
BEAVERS
Damage Prevention and
Control Methods
Exclusion
Fence small critical areas such as
culverts, drains, small ponds or
lakes, and barriers around impor-
tant trees in urban settings
Cultural Methods and Habitat
Modification
Eliminate foods, trees and woody
vesetation where feasible; Continu-
used to build dams; use a three-log
drain or other structural device to
maintain a lower pond level and
avoid further pond expansion
Frightening
Can occasionally work by shooting
or dynamiting or other continued
destruction of lodges, bank dens
and dams
Repellents
None registered, however there is
some evidence that repellents may
be useful. More research is needed.
Toxicants
None registered
FUm[ganf~=' '
None registered
Traps
Conibear® type, size 330 are very
effective, mobile, practical and
humane, with no escapes. The
leghold types size No. 3 or'larger
(include coil-spring types with~
equivalent jaw spread and impact)
are also effective when properly
used. Basket/suitcase type traps are
primarily used for live trapping.
Where legal, snares can be useful
particularly in dive sets and slides.
Shooting
Rarely effective for complete con-
trol efforts and can be dangerous
to humans
Othee.~:M~tho~ .......
Other methods rarely solve a
beaver damage problem and may
cause more damage to nontarget
species than to beaver
Figure 2. Beaver tracks.
Tail mark
Marks of webs not always dis '
tlrl~.L
,,,~nches (76-152 mm)
Walking
Front foot
6 inches (152 mm)
Hind foot
Identification
The beaver Castor canadensis,
Figure 7] is our largest North
American rodent. ^ few rare in-
dividuals reach over 100 pounds
(45 kg). The weight of most adults
ranges from 35 to 50 pounds (15.75
to 22.5 kg], with some rarely
reaching 70 to 85 pounds (31.5 to
38.25 kg). The beaver is a stocky
appearing rodent adapted for
aquatic environments. It has
valvular ears and nose and lips
which close behind the four large
incisor teeth. Each of the four feet
have five digits with the hind feet
webbed between digits.and a split
second claw on each hind foot.
The front feet are small in com-
parison to the hind feet [Figure 2].
The underfur is dense and general-
ly gray in color, whereas the guard
hair is long and coarse with the
color ranging from yellowish-brown
to black, with reddish-brown most
common. Its prominent tail is flat-
tened dorsoventrally, scaled and
almost hairless. It is used as a prop
while the bea~er.~ is~sh.t, ing~,,~pr~ght
[Figure $). The tail is also used for
swimming and communication
while in the water. The beaver's
large front incisor teeth, bright
orange on the front, grow con-
tinuously ~hroughout its life. These
incisors on the back side are bev-
eled to be continuously sharpened
as the beaver gnaws and chews in
its feeding, girdling, and cutting of
trees. The only way to externally
Figure 3. A beaver uses/ts tail as a prop in
order to sit upright.
Figure 4. Range of the beaver in North
America.
~distinguish the sex of a beaver,
Unless the female is lactating, is to
~l~eel for the presence of a baculum
~="~ ~ ~ne in the penis) in males and
i~ absence in females.
Rang
Beavers are found throughout
North America, except for the arc-
tic tundra, most of peninsular
Florida and the southwestern
desert areas (Figure 4). The species
is locally abundant throughout the
Great Plains wherever aquatic
habitats are found, e.g., streams,
lakes, farm ponds, wetlands and
Iow Iyin$ lands or swamps and
along flood-prone creek and river
bottoms.
Habitat
Beaver habitat is almost anywhere
there is a year-round source of
water, e.g., streams, lakes, farm
ponds, swamps and wetland areas.
Personal observations have located
beaver in highway roadside ditch-
es drainage ditches, canals, mine
, oxbows, railroad dumps,
drains from sewage disposal ponds,
and below natural springs or arte-
sian wells. In areas beavers move
into they seem to be stimulated by
running water. They will quickly
begin building dams to modify the
environment more to their liking.
Some of the surrounding timber is
cut down or girdled by beavers to
form dams. Subsequent flooding of
growing timber causes it to die,
and aquatic vegetation soon begins
growing. Other pioneer species,
e.g., willow, sweetgum and button-
bush, soon are' 8rowing around the.
edge of the flooded area adding to
the available food supply. The
beaver thus helps create its own
habitat.
Food .Habi,ts?
Beavers prefer certain trees and
woody species depending on avail-
ability, such as populus species,
e.g.', aspen and cottonwood, and
willow, sweetsum, blackgum, and
pine. However, they can and will
eat the leaves, twigs and bark of
most species of woOdy plants
which grow near the water, as well
as a wide variety of herbaceous
and aquatic plants. Beavers often
will travel 100 yards (90 m) or more
from the pond or stream to get to
corn fields, soybean fields and
other growing crops, where they
generally cut the plant off at the
8round and drag the entire plant
back tothe water. Adding insult to
injury, they not only eat part of
these plants, they often use the re-
mainder as construction material in
the dam.
General Biology,
Reproduction and
Behavior
Beavers are active for approximate-
ly 12 hours each night except for
the coldest of winter nights. The
phrase "busy as a beaver" is ap-
propriate. However, it is not Un-
common to see beavers during'
daylight hours, particularly in
larger reservoirs. Because of the
valvular ears and nose and other
physical adaptations, they can re-
main underwater for over 15
minutes when necessary.
After a gestation period of about
128 days, the female beaver
generally gives birth to three or '
four kittens between March and
June, and nurses them for from iix
weeks to three months, The kittens
are born fully furred with their
eyes partially opened and the in-
cisors erupted through the gums.
They generally become sexually
mature by the age of 1 1/2 years.
BeaverS'have a relatively long life
span, with individuals known to.
have lived to 21 years. Most,
however, do not live beyond 10
years. The beaver is unparalleled at
dam building and can build dams
on fast-moving streams as well as
slow-moving ones. They also build
Figure 5. Cross section of a beaver lodge.
B-3
B-4
lodges and bank dens, depending
on the situation. All lodges and
bank dens have at least two en-
trances and may have four or more.
The ledge or bank den is used
primarily for raising young, sleep-
ing and some food storage during
severe weather (Figure 5).
The length or height of a dam
generally depends upon what is
necessary to essentially stop the
flow of water and create a pond.
In areas of flat topography, the
dam, re, ay, not be~,.ov~,~. 3~, i. nches,.(.9~,.
m) high, but as much as 1/4 mile (.4
km) long. In hilly or mountain
country, the dam may be q0 feet (3
m) high and only 50 feet (15 m)
long. The size of the tree the
beaver cuts is highly variable, from
a 1-inch (2.54 cm) DBH (diameter
at breast height) softwood to a six-
foot (1.8 m) DBH hardwood. In
some areas beavers seem to cut
down trees up to about 10 inches
(25 cm) DBH and merely girdle or
partially cut larger ones, although
they often cut down much larger
trees. For some reason the bea~ers
seem to like to girdle large pines
and sweetgums. They like the gum
or storax that seeps out of the
girdled area of sweetgum and
other species.
An important factor about beaver
biology is thei~ territoriality. A col-
ony generally consists of four to
eight related beavers, who resist
additions or outsiders to the col-
ony or the pond. Young beavers
commonly are displaced from the
colony shortly after they become
sexually mature, at about 2 years
old. They often move to another
area to begin a new pond and col-
ony. However, some become
solitary hermits inhabiting old
abandoned ponds or a farm pond
if one is available.
Beavers have a few natural
predators aside from man, in-
cluding coyote, bobcat, river otter
and mink on young kittens. In
other areas, bear, wolves, and
wolverines may prey on beavers.
They are hosts for several ectopar-
Figure 6. Pine plantation in Arkansas killed
by floodin8 caused by beavers.
asites and internal parasites in-
cluding nematodes, trematodes
and coccidians. Giardia lamblia is a
pathogenic intestinal parasite
transmitted by beavers, which has
caused human health problems in
water supply systems. In fact, the
Centers for Disease Control have
reports of at least 41 waterborne
Giardiasis outbreaks affecting more
than 15,000 people. For more infor-
mation about Giardiasis, see von
Oettingen (1982). 'This thesis con-
tains a number of additional
references.
They generally are monogamous;
copulation may take place either
in 'the. water or in the lodge or
bank den. They communicate by
vocalizations, posture, tail slapping
and scent posts or mud dobs or
mounds placed around the bank
and dam. The beaver's castor
glands secrete a substance that is
deposited on mud dobs to mark
territorial boundaries. These scent
posts are found more frequently at
certain seasOns, but.are found
year-round in active ponds.
The habitat modification by
beavers, caused primarily by dam
building, is Often beneficial to fish,
furbearers, reptiles and amphibians
and to waterfowl and shorebirds.
However, when this modification
comes in conflict with man's objec-
tives, the impacts of damage may
far outweigh the benefits.
Damage and Damage
Identification
Most of the damage caused by
beavers is a result of dam building,
bank burrowing, tree cutting or
flooding. Some individual south-
eastern states where beaver~dam-
age is extensive have determined
from surveys that beaver damage
estimates range from $3 million to
$5 million dollars annually to
timber loss, crop losses, roads,
dwel in&~,, a.nd property flooded,
'and other damage. In some of
these states, bottomland hardwood
timber in areas of several thousand
acres in one watershed maybe lost
because of beaVer pond flooding.
Some unusual cases observed over
the years include state highways
flooded because of beaver ponds,
reservoir dams destroyed by bank
den burrows collapsing, and train
derailments caused by burrowing.
Housing developments have been
threatened by beaver dam flood-
ing, and thousands of acres of
croplands and young pine planta-
tions have been flooded by beaver
dams (Figure 6). Road ditches, drain
pipes and culverts have been stop-
ped up so badly that they 'had to
be dynamited out.and replaced, as
well as bridges destroyed.
The most unusual and difficultto
explain was the beaver-cut tree by
a highway bridge that, when felled,
by the beaver, dropped across the
hood of a family's automobile
traveling down the highway. The
damage caused by beavers is not
also very frustrating to landowners
and others.
Identifying beaver damage general-
ly is not difficult. Dams, dammed-
up culverts, bridges, or drain pipes
resulting in flooded lands, timber,
roads, crops, and cut-down or gird-
led trees and crops, or burrows in
pond and reservoir levees or dams.
Sometimes when drain pipes in a
levee or reservoir are stopped up,
it may be very difficult to get the
sticks, logs, mud and debris re-
moved so that the water will move
out and beaver can be trapped. In
large watersheds, it may be dif-
ficult to locate bank dens.
However, the limbs, cuttings and
debris around such areas as well as
dams along tributaries usually help
pinpoint the area.
Legal Status
· The legal status of beavers varies
from state to state. In some states
the beaver is protected except dur-
ing furbearer seasons; in others it is
classified as a pest and may be
taken ye ar-round when'~¢aus~ng~'
damage. Because of its fur value,
dam building, and resulting water
conservation, it is generally not
considered a pest until economic
losses become extensive. However,
fur prices for beaver in some
states, particularly in southern
states, make it hardly worth the
skinning and stretching. In some
northern states, trapping is pro-
hibited near lodges or bank dens to
protect and perpetuate beaver col-
onies; however, fur prices for
beaver pelts are substantially
higher in these areas.
Before attempting to trap or other-
wise take beavers in any state,
always check the existing regula-
tions.
Damage .Prevention and
Control Methods
Exclusion
i3~avers carT' be: ex.~r~ded,~from· ....
ponds, lakes or impoundments.
However, if the primary reason for
fencing is to exclude beaver, fenc-
ing is not practical. Fencing of
culverts, drain pipes or other struc-
tures can sometimes prevent
damage, but often results in a dam
with the beavers using the fence as
construction material. Metal bar-
riers around valuable trees may
prevent damage where feasible.
Cultural Methods
Because beavers usually alter or
modify their aquatic habitat so ex-
tensively over a period of time,
most practices generally thought of
as cultural have little impact on
beavers. With the exception of the
elimination of food sources and in
cases where the aquatic habitat
can be eliminated, most other cul-
tural practices have no significant
impact on beavers. Daily tearing
out dams and removing dam con-
struction materials will (depending
on availability of construction ma-
terials) sometimes cause a colony
or individual beaver to move to
another site. HOwever, theymigh~' ~
be even more troublesome at the
new location.
The use of a three-log drain or
other type of structural device
which prevents beavers from con-
trolling the water level will occa-
sionally cause movement to other
habitat. However, once beavers
have become commonly abundant
in a watershed or in a large con-
tiguous area, such as a stream
system, swamp, or 'other wetlands
area, periodic replacements or rein-
vasions of suitable habitat can be
expected to occur.
Repellents
There are no chemical repellents
registered for beavers. Some
research efforts in past years have
tried to determine the effec-
tiveness of potential repellent ~
materials, however, none were
found which were effective, reg- .
vironmentally safe, or practical.
One study in Georgia using a deer
repellent (Hicks 1978)indicated
some potential benefit. Many
mechanical devices have been
tried in attempts to repel
beavers. The only effective and en-
vironmentally safe methods known
do not in effect repel beavers, but
do in some cases prevent damage.
These would include fencing of
structures in some areas, e.g., drain
pipes or structures, fencing or
Other barriers around valuable
trees, shrubs, or other crops, and
construction of concrete 0r other
permanent materials in spillways or
other drainage systems.
As alluded to in an earlier section,
in some drainage systems, total
elimination of foods (aquatic vege-
tation and trees adjacent to the
drainage system) will, where feas-
ible, usually prevent colonization.
Continual destruction of dams,
especially where construction
materials are scarce, will some-
times cause abandonment of the
.~,~aL ar~:~owev, e~,person al
observations have included dams
constructed entirely of mud and
crop materials, such as soybean
plants, corn stalks, watermelon
vines, cane, grasses, rice, wheat
and others. The author has also .
observed dams constructed of mud
and other native plant materials,
aside from trees, such as vines,
water lilies, cattails, ragweed,
pigweed, coffeebean, and others.
Beavers are adaptable and will use
whatever materials are available to
construct dams -- fencing mater-
ials, bridge planking, Crossties,
rocks, w.i~e,, ancf"otftet'rhetal, wood
and fiber materials. Therefore,
about the only available aquatic
habitat beavers avoid are those
systems lacking acceptable foods,
lodge or denning sites and where
no suitable site exists to construct
dams. Additional research is need-
ed on repellents for beaver damage
prevention.
Toxicants
None are registered. However,
there have been research efforts
conducted to find effective, en-
vironmentally safe and. practk:a~,..
toxicants. Currently there are none
which meet these criteria.
Fumigants
None are registered. The situation
is similar as alluded to under the
toxicants section.
Traps
A variety of trapping methods and
different types of traps are effec-
tive for beavers depending upon
the situation. Fish and wildlife
agency regulations vary from state
to state. Some tYPes of traps and
trapping methods, although effec-
tive and legal in some states, may
be totally prohibited by law in
other states. Individual state
regulations must be reviewed an-
nually before beginning a trapping
program.
The use of traps in most situations
where beavers are causing damage
is the most effective, practical and
environmentally safe method of
control. The effectiveness of any
type of trap for beaver control is
dependent on the trapper's knowl-
, e.d&e..of~be-a~vef~h~ab~tS~ i'ncluding
food preferences, ability to read
beaver signs, use of the proper trap
to fit the situation, and trap place-
ment. Ntost anyone with trapping
experience and some outdoor "sav-
vy'' can become an effective
beaver trapper in a short time.~ Ob-
viously, in an area where beavers
~re common and have not been ex-
~osed to trapping, 'one can expect
its capability to kill the beaver
quickly, traps can'be set quickly.
Only one trap per site generally is
necessary, thus reducing the need
for extra traps. It exerts tremen-
dous pressure and impact when
tripped. Therefore, as with most
traps, appropriate care must be ex-
ercised when setting and p acing
the trap.
Figure 7. Basic method of setting and stak-
ing a Conibear® 330 trap·
Additional stakes are normally used (see
Figure 8 ).
g°°d's~cceS~;i AdditiOnal expertise
and improved techniques will be
gained through experience.
In some states where beavers have
become serious economic pests,
special regulations and exemptions
have been passed to allow for in-
creased control efforts. For exam-
ple, some allow trapping and snar-
ing of beavers and other control
measures throughout the year.'
However, other states prohibit trap-
ping except during the established
fur trapping seasons. Others have
allowed exemptions for removal of
beavers only on lands owned or
controlled by persons who are suf-
fering losses. Still, others require a
special permit from the state fish
and wildlife agency.
Of the variety of traps commonly
allowed for use in beaver control,
the Conibear® type, size 330, is
one of the most effective for most
situations (Figure 7). Not all trap-
pers will agree that this type trap is
most effective; however, it is the
Some additional equipment will ·
help when trapping beavers. This'
includes an axe, hatchet, or large .
cutting tool, hip boots or w~,de[~,
wire and wire'~c~tters. When using
the Conibear type trap, some peo-
ple employ a device or tool called
"setting tongs." Others use a piece
of 3/8 or 1/2-inch (9.53 or 12.7 mm)
nylon or other rope. Most people
who use these traps extensively. use
only their hands. Regardless of the
techniques used to set the trap,
care should be exercised.
Earlier models of this type of trap
came with some round, heavy steel
coils which were dangerous to han-
dle unless properly utilized in set-
ting the trap. They are not
necessary to safely set the trap..
However, the two safety hooks,
one on each spring, must be
carefully utilized as each spring is
depressed, as well as during the
procedure of trap placement. On
newer packaging of this type trap,
an additional safety catch (not at-
tached to the springs) is included
for extra precaution against in-
advertent spring release. The'last
step before leaving a set once the
trap is in place is to lift the safety
hook attached to each spring,
type most commonly used by pro- sliding,the..safet, y,,hook back from
fessional trappers and..fur~ t~appeF~.:...· .,the trap part toward the spring eye
who ~re t~apping principally for
making sure to keep hands and
beavers. This trap kills a trapped
beaver almost instantly. When pro-
perly set, this type trap prevents
any escape by a beaver, regardless
of its size. Designed primarily for
water use, it is equa'lly effective in
deep and shallow water. Because
of its size, effectiveness, mobility
-- no need for additional ap-
paratus to'drown the beaver, and
feet safely away from the center, of
the trap. If the extra (unattached)
safety catch is employed, it should
be removed prior to removal of
those attached to the springs to
avoid it being in the way of move-
ment of the safety hooks.
~ This type of trap is easier to
prepare for setting while on solid
~g~'ound with dry hands. Once the
ings are depressed and the safe-
~, nooks in place, the trap or traps
can be carried into the water for
proper placement. Additional
preparation before getting to trap
placement is selection of some
stakes for use in staking the trap
down. In most beaver ponds and
around beaver dams, plenty of
suitable stakes can be found. At
least two strong stakes, preferably
st ra'ig ht-.:and~ wff'hot~f,o ~e~ o~: sr~ag~;.~
should be chosen to place through
each spring eye (Figure 7). Addi-
tional stakes may be useful to put
between the spring arms and help
hold the trap in place. Do not
place stakes on the outside of
spring arms. Aside from serving to
hold the trap in place, these stakes
also help to guide the beaver into
the trap. Where needed, they are
useful to hold a dive stick at or
just beneath the water surface
(Figure 8). If felt necessary, the
chain and circle attached to one
' "~g eye can be attached to
~. ~ther stake. In deep water sets
where the set trap is slid into place
deeper than the trapper can reach,
the chain with attached wire
should be tied to something at or
above the surface. Otherwise the
trap may be lost.
Trap Sets. There are many sets that
can be made with this type of trap,
depending on the situation, such as
dam sets, slide sets, lodge sets,
bank den sets, "run"/trail sets,
under log/dive sets, pole sets, sets
u. nde~. the.~ic.e,.~deel~.water .sets
drain pipe sets, and others depend-
ing on the trapper's capability and
ingenuity. However, in many
beaver ponds, most beavers can be
trapped using dam sets, lodge or
bank den sets, sets in "runs"/trails,
dive sets or sets in slides entering
the water from places beavers are
feeding. Beavers swim mostly at
the surface or along the bottom of
r ~ds, depending upon the habitat.
, ~allow ponds, they obviously
Dive s~ick.
Figure 8. Conibear trap in dive set.
Levee
Run
Figure 9. Runs or underwater entrances to
lodges are good places to set beaver traps,
Entranc
swim extensively along the bottom.
They are scouring out runs or trails
which they habitually use in travel-
ing from lodge or den to the dam
or to feeding areas, much like cow
trails in a pasture. Where these
"runs" can be found, they are sure
sets for this type of trap if the trap
is placed directly across the path
of the run and on the bottom
(Figure 9).
A helpful hint when wading in a
beaver pond to locate runs or trails
is to choose a good stake or "walk-
ing staff" to help locate deep holes
or runs. This will prevent your step-
ping off over waders or hip boots
in winter, and will help ward off
curious cottonmouth snakes in the
summer. Used to feel along in
front as one wades, your stake also
can help locate good dive holes ,
under logs as you walk out runs or
trails. In old beaver ponds, par-
ticularly in bottomland swamps, it
is not uncommon to find runs,
lodge or bank den entrances where
the run or hole is scoured out two
to three feet (.6 to .9 m) below the
rest of the bottom.
B-7
One of the things you can depend
on is that if you tear a hole in a
beaver dam and get the water
moving out of a pond, you will
stimulate beaver movement that
night, except on the coldest of
winter nights. Timing is also impor-
tant if you plan to make dam sets.
Tearing a hole in the dam or dams
about 18 inches to 2 feet (45.72 to
60.96 cra) wide and 2 to 3 feet (.6
to .9 m) below the water level on
the upper side of the dam in the
morning generally will move a
good bit of Water out or'the pond .....
before evening (Figure ~0). Evening
is the prime time to set traps. If
you set in front of the dam open-
lng in the morning as soon as a
hole is dug out, two problems can
arise: (1) by late evening when the
beavers become active the trap
may be out of the water, and inef-
fective; or (2) a stick, branch or
other debris in the moving water
may trip the trap, again rendering
it ineffective. Ideally, you should
tear out the holes in a dam in the
morning, let the water flow out un-
til mid-afternoon, then set traps un-
til early evening.
The best dam sets are made some
12 to 18 inches (30.48 to 45.72 cra)
in front of the dam itself. Using
stakes or debris on either side of
the trap springs will help make the
beaver go where you want it to --
into the jaws of the trap. Generally
speaking, it is always best to set
the trigger on the Conibear type
Hole torn through dam to release water
he trap underwater
in front of the hole created in the dam. -
When the beaver returns to patch the hole,
it will go into the trap and be caught.
Figure 11. Leghold trap (No. 3 or No. 4 size,
double spring) attached to wire for drown
set.
trap in the first notch, which helps
prevent debris from tripping it
before the beaver swims into it.
T he~twe., hea,~y-gau ge; wire., t r i p per. s~ ......
can be bent outward and the trig-
ger can be set away from the mid-
dle if necessary, to avoid debris
tripping it or to suit the trapper's
approximation of beaver size. If
signs indicate small beaver or
possible fish or turtles moving
through the trap, this technique
sometimes prevents premature trap
spring.
Dig out slide underwater to
spnngs Slide wire fastened to stake
and weight
Figure 12. Leghold trap in slide set..
B-8
Double spring leghold traps have
been used for hundreds of years
and are still very effective when
properly used by skilled trappers.
Trap size of double (long) spring or
coil spring type leg leghold traps
for beavers should be at least No.
3 or equivalent size jaw spread and
strength. Any leghold trap should
be used with a drown set attach-
ment (Figure 17). As the traps are
tripped, the beaver will head for
the water. A weight is used to hold
the trapped beaver underwater
where-, i~. t~hi ~atefy.'i~d~ned~.'.
Some trappers stake the wire in
deep water to accomplish the
drowning. If leghold traps are not
used in a manner to accomplish
drowning, there is a good
likelihood that legs or toes will be
twisted off or pulled loose, leaving
an escaped, trap-wise beaver.
The placement of leghold traps is
equally as important as with the
Conibear type, if not more so.
Generally, such traps are placed
just at the water's edge, slightly
underwater, with the pan, jaws and
springs covered lightly with leaves
or debris or pressed gently into the
bottom in soft mud. For this set,
there must be a cavity under the
pan so that when the beaver's foot
hits the pan, it will trip the springs
and allow the jaws to snap closed.
Traps should be placed off-center
of the trail or run to prevent belly
pinching or a miss by the foot or
leg. With some experience, beaver
trappers learn to make sets that
will catch the beaver by a hind leg
rather than a front one, which is
n~u~h~,sma,[[er..,ar~cL easier to. twist
off or pull out. Where trapping
with leghold traps without drown
sets is done, it is not uncommon to
catch a beaver with toes and even
entire front legs missing.
It is sometimes wise when using
leghold traps to make two sets in a
slide, run, dam or feeding place to
increase trapping success and more
quickly obtain beaver control. In
some situations, a combined use of
Conibear type traps, snares if legal,
and traps will be necessary to
shorten trapping time and increase'
success.
Trappers have come up with
unique methods of making drown
sets. One of the simplest and most,
practical to use is a slide wire with
a heavy weight attached to one
end or that end can be staked to
the bottom in 3 or more feet (.9 +
m) of water depth. The other end
of the wire is threaded through a
hole in one end of a small piece of
angle iron; the trap cFiain i's' attach:
ed to a hole in the other end of the
angle. The end of the wire is then
attached to a tree or stake driven
into the bank (Figure 12).
When the beaver gets a foot or leg
in-the trap, it immediately dives
back into the water. As the angle
slides down the wire, it prohibits
the beaver from reaching the sur-
face. The angle iron piece will not
slide back up the wire and most
often bends the wire as the beaver
struggles, thus preventing it from
coming up for air. Most trappers
are prepared if a beaver is not
drowned and dispatch it appropri-
ately with a .22 caliber slug in the
head as quickly as possible.
The leghold trap set in lodges or
bank dens is also effective,
especially for trapping young
beavers. This set can be placed on
the edge of the hole 'where the
beaver first turns upward to enter
the lodge or den. Another good set
is on the bottom of the dive hole.
The jaws and pan should be thrust
upward, by the springs being pulled
backward, thus placing the pan
and jaws off the bottom where a
swimming foot will trip the pan.
These sets can usually be staked
closely to the bottom or wired to a
stake, log or root on the bottom,
thus avoiding the need for drown-
ing weights, wires and angle iron
pieces. Generally speaking, more
time and expertise is necessary to
make effective sets with leghold
traps and snares than is required
with the Conibear type.
The us~ of scent or freslT Cut cot-
tonwood, aspen, willow or sweat-
gum limbs may be an asset in en-
ticing beavers to leghold trap
placements. Bait or scent is. espe~
cially enticing around scent
mounds and up slides along the
bank or dams. ^lthough occasion-
ally helpful, most trappers who use
Conibear tNpe traps rarely employ
baits or scents. In some states it is
illegal to use bait or scent.
Several other types of traps can be
used, including basket/suitcase
t'~)'e'.~ive~t~D~:.. ~oweve~ th~: ~.~..
are rarely used in beaver damage
situations, exceDt by Drofessionals
in urban .areas where anti-trap sen-
timent or other reasons prevent
killing the beaver. These traps are
difficult and cumbersome to use, ·
and will not be further discussed
here for use in beaver damage con-
trol. Any type of traps used for
beavers or other animals should be
checked daily. Note: Snare sets are
not discussed in detail because
many states prohibit their use.
Shooting
In some states, because 0f the ex-
tent of damage caused by beavers,
regulations have been relaxed to
allow shooting. Some states even
allow the use of a light at night to
spot and shoot beavers. Before at-
tempting to shoot beavers, check
regulations, and if applicable,
secure permits and let the local en-
forcement officer or game warden
know what is being attempted.
Beavers are most active from .late
afternoon to shortly after day-
bre~, depending,on the time of
the year. They begin about 6 to 8
pm and are active until ab'out 7
am, when they generally retire to
the lodge or bank den for the day.
Therefore, if night shooting is not
permitted, the early evening and
early morning hours are most pro-
ductive. Choice of weapons
depends on the range and situa-
tion. Generally speaking, the time
spent trying to shoot damaging
beavers would be much more pro-
ductive if devoted to trapping.
Rarely can one eliminate damaging
beavers by shooting alone.
Other Methods
Because of the frustration and
damage beavers have caused land-
owners, almost every kind of
method imaginable -- legal and il-
legal -- has been tried. These
range from dynamiting lodges dur-
ing mid-day to using snag-type fish
hooks in front of dams, road cul-
verts and drain pipes. Such
methods rarely solve a damage
problem, although they may kill a
few beavers and non-target species
and cause severe head'aches for
those that are not killed. One
method used occasionally along
streams prone to flooding is shoot-
lng beavers that have been flooded
out of lodges and bank dens. This
method is often dangerous and
rarely solves a damage problem.
^ final section on control methods:
Beaver damage can be severe and
cause extensive economic losses
and frustration in many situations.
However, the efforts necessary to
effect control of beavers causing
the damage is most often over-
estimated. Beaver colonies have a
tendency, like other wildlife spe-
cies, to build up the population to
a certain level, then part of the
population moves into other suit-
able habitat of nearby water
sources. The beavers then develop
or modify the habitat to their lik-
ing.
Beavers are territorial and even in
old ponds that have held beavers
for years, it is rare to find more
han 8 to 13 beavers in any par-
ticular pond. Most often the num-
ber is from 4 to 8. The older and
larger the pond, as long as food is
plentiful, the more likely it is to
have the higher number of beavers.
^ good trapper with a dozen traps
can generally trap all the beavers
in a given pond (behind one dam)
in a week of trap nights. Obviously
in a large watershed with several
colonies, more trapping effort will
be required.
Figure 13, ConiC)ear® in culvert set, When
beavers are stopping up a drainage culvert,
(1) clean out the pipe to get water flowing
through freely; (2) set the trap at the level of
the drain pipe entrance, but far enough
away to clear the culvert when the beaver
enters; (3) put stakes on either side to make
the beaver enter the trap correctly,
Landowners with beaver problems
frequently overestimate the
number of beavers in a pond and ·
the difficulty of control. Many are
reluctant to personally attempt
trapping them out. Most would
prefer having someone else do the
job for them. Beaver trapping is
hard, dirty work, but anyone with
reasonable strength, and some out-
door experience can learn to be an
effective beaver trapper.
Where legal to trap in lodges and
bank dens, a good trapper can
remove every beaver from a pond
if dams are kept broken and the
water is kept moving out on a
nightly basis. In most cases, a week
of trap nights is sufficient to
remove all the beavers from a
single pond. Periodic checks will
make sure there are no survivors or
that beavers from adjacent areas
have not moved in.
Economic~ o.t~., Damage ...... .~,
and Control
The economics of beaver damage
is somewhat dependent on the ex-
tent of damage that has occurred
before the landowner or manager
realizes that a problem exists and
begins to attempt control. Some '
· beaver damage problems are inten-
sive, such as one or two beavers in
a new pond caused by their dam-
ming or stopping up a culvert or
drain pipe, flooding roads or crops:
Others are extensive, such as = .
several beaver colonies in a flat-
land area,.responsible for ~he
flooding of several hundred acres
of merchantable timber that will
die unless the water is removed
quickly. Cenerally speaking, if the
culvert or drain pipe can be
unstopped, a knowledgeable trap-
per can trap one or two beavers in
a night or two and'eliminate fur-
ther damage in the intenslve
damage situation (Figure 13).'
However, in the extensive situation,
it may require a concentrated ef-
fort with several trappers,
dynamiting or pulling dams, and a
month or more of extensive trap-
ping to get the water off the
timber and reduce further timber
losses.
The economics of 'each situation
are obvious. Economically, one
must weigh the tradeoffs, hundred
of thousands of board feet of
timber, and years of regeneration
losses versus the cost of trahs, time
and effort or contractural ar-
rangements with a damage con-
tractor, for the worse case. For the
least case, consider a couple of
nights trapping effort and a half-
day of labor to clear the culvert
versus the cost of rebuilding a
Washed-out,road or loss of some
flooded crops or timber.
B-lO ~
The most important point is that
damage control should begin as
soon as it is evident that a beaver
problem exists or appears likely to
develop. Once beaver colonies
become well established over a
large contiguous area, achieving
control will be difficult and costly.
One of the most difficult situations
is where a landowner adjacent to
one who needs to control beavers
will not allow beavers on his place
to be controlled. In this situation,
one, c am e~pect, pe~ie~i¢..,,r~ei~va~
sions of beavers and beaver
damage.
To the author's knowledge, no one
has compiled beaver damage data
nationwide, however, if it were
done, a conservative estimate
would be $75 million per year. In
the southeastern states alone, the
figure is probably close to $50
million annually. This would in-
clude all damage to crops, forests,
roads, pastures, and other rural and
urban proPerties, to commercial
timber cOmpany lands, and to .
public lands.
Although not covered in depth
here, there are a number of bene-
fits that can be credited to beavers
and beaver ponds aside from the
significance of creating fish, water-
fowl, furbearer, shorebird, reptile,
and amphibian habitat. The beaver
in many areas is an important fur ·
resource, and for those who have
not yet tried it, beaver meat is ex-
cellent table fare if properly
prepared. Recipes for preparation
and cooking beaver are found in a
number o~ pubHc~at'ix~. ~f~"cYne'"~s'"-
trapping beavers, the meat is a
valuable resource and can be
utilized whether the pelts are
worth skinning or not. After the fat
is removed and the meat is sliced
into thin steaks, it should be cook-
ed in the same manner as venison.
In fact, the taste is remarkably
similar. Carcasses of beavers also
make good dog food, and it is a
rare hunting dog that will not fight
over a piece of beaver meat. When
trapping for predators, beaver
meat also makes good bait.
Acknowledgments
I wish to thank past and present employees
of the Fish and Wildlife Service, U.S.
Department of the Interior, those county ex-
tension agents employed by the Arkansas
Cooperative Extension Service, and the
many landowners with beaver problems
across the mid-South whom I worked with
for many years for their cooperation. The
experience gained in efforts to assist land-
owners to learn to control beavers and other
wildlife damage problems provided most of
the information contained herein.
Figures 1, 2, 4, and 5 from Schwartz and
Schwartz (1981).
Figure 3 by Jill Sack Johnson.
Figure 6 by the author.
Figures 7 through 11 and 13 from Miller
(1978).
Figure 12 by Jill Sack Johnson after Miller
(1978).
For Addition, l
Information
Byford, J.L 1976. Beavers in Tennessee:
control, utilization and management.
Tennessee Cooperative Extension Service,
Knoxville, Publication 687.15 pp.
Hicks, J.T. 1978. Methods of Beaver
Control. Final Report. Research
Project No, W-37-R, Georgia 'Game
and Fish Division, Dept. of Natural
Resources, 3 pp.
Hill, E,H, 1974 Trapping beaver and
processinli their fur, Alabama Cooperative
Wildlife Research Unit, Agricultural
Experiment Station, A'uburn'Lrnrversfty;.
Auburn, Alabama. Publication No. 1.
10 pp.
Manitoba Wildlife Branch. Trapper
Education Program. Beaver Trap Sets.
Winnipeg. 5 pp.
Miller, J.E. 1972. Muskrat and beaver
control. Proceedings First Natiohal
Extension Wildlife Workshop, Estes Park,
Colorado, pp. 35-37.
Miller, i.E. 1978. Beaver -- friend or foe.
Arkansas Cooperative Extension Service,
Little Rock. Circular 539.15 pp.
Schwartz, C.W. and E.R. Schwartz. 1981. The
· Wild Mammals of Missouri, Revised
'Edition. University:of Missouri Press,
Columbia. 356 pp.
yon Oettingen, S.L. 1982. A survey of
beaver in central Massachusetts for
Giardia lamblia. M.S. Thesis,
University of Massachusetts, Amherst.
58 pp.
8-1'