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Moles live underground and inhabit the lawns of residential homes, golf courses, cemeteries, and parks, as well as fallow fields, forest edges, or pastures where moist, sandy loam soils are common and digging is easy. Three species of moles are native to Virginia: the eastern mole (Scalopus aquaticus), the star-nosed mole (Condylura cristata), and the hairy-tailed mole (Parascalopusbreweri).

The most widely distributed species in Virginia is the eastern mole, which is found statewide. The distribution of the star-nosed mole is restricted to the Coastal Plain, the northern Piedmont, and throughout the Shenandoah and New River Valleys. The hairy-tailed mole is found only in the Appalachian Mountain region (i.e., west of the Blue Ridge).

The type of soil, its moisture content, and the availability of food all can limit mole activity. In general, moles tend to avoid heavy clay or stony, coarse gravel soils where tunneling is difficult. Similarly, areas with soils that are either too dry or too wet to maintain the structure of their tunnel system usually are avoided. The star-nosed mole prefers habitats with damp (not saturated) soils, particularly near streams, lakes, and wetlands, whereas both the eastern and hairy-tailed moles prefer the drier soils of upland habitats.Individuals of any of the three species can swim, but the star-nosed is most adept and seen frequently in water.

Moles are approximately 4-8 inches in length from nose to tail. They have short, powerful forefeet with broad outward-turned palms and prominent digging claws, small eyes and ears, short, black or brownish-gray velvety fur, and a somewhat elongated head and snout. The snout of the star-nosed mole, as its name suggests, is characterized by a prominent fleshy protuberance with 22 short tentacles radiating from it. These tentacles are believed to aid the animal in sensing its environment and are found in no other mammal. Eastern and hairy-tailed moles may be distinguished by differences in their tails. The tail of an eastern mole is short(0.6-1.2 in.) and naked whereas that of the hairy-tailed is slightly longer (0.9-1.4 in.) and covered with short, stiff hairs. Male eastern and hairy-tailed moles typically are larger in size than respective females whereas both male and female star-nosed moles are approximately equal in size. Tactile hairs on the snout, forepaws, top of the head, and tail enhance a moles sense of touch; moles have a poor sense of smell and are virtually blind (but they do detect light and dark).

Although many people believe that moles are rodents, like mice or rats, they actually are members of the scientific order Insectivora,which includes animals like shrews and bats. The diet of a mole consists of earthworms, snails, slugs, and insects (both adult and larval stages), but also may include small amounts of vegetation and seeds taken inadvertently. Moles destroy very few plants or bulbs by direct feeding, but may dislodge plants while tunneling in search of food. Because they expend a tremendous amount of energy when constructing tunnels, moles often remain active day and night year-round in their search for food. They often consume an amount of food equal to 60-100% of their body weight daily. To satisfy this almost insatiable demand for food, one mole can dig up to150 feet of new tunnels each day. They are most active in early morning and late evening on damp, cloudy days during the spring and fall and may be seen above ground at night or when they disperse to new areas.

Moles typically are solitary creatures, although the star-nosed mole is somewhat more social than either the eastern or hairy tail mole.The only time individuals are seen together is during the spring (February-March) breeding season or when a female is rearing young. After a 4-6 week gestation period, females produce one litter of 2-5 young (up to 7 with star-nosed moles) each year. Nest chambers are constructed 12-18 inches underground, often beneath a large stone, tree, sidewalk, or roadway. Young moles leave the nest at about 5-6 weeks of age and become sexually mature by the end of their first year. Moles may live up to 4 years in the wild.Predators of moles include snakes, skunks, foxes, weasels, hawks, owls, and domestic cats and dogs.

Moles construct two types of tunnels-those at or near the ground surface and those deep (6-20 in.) underground. The networks of inter connecting trails visible above ground and just under the surface are feeding tunnels that often are used only once.

Deep tunnels are the highways that lead between feeding areas and the living chambers and also provide cover against predators.Hairy-tailed moles have been observed using the same burrow system continuously for up to 8 years, but this is not common.Although all species of moles make feeding tunnels, eastern moles usually create the prominent ridges of heaved soil visible at the surface whereas star-nosed moles typically are responsible for the large (1-2 ft. diameter, 4-9 in. high) mole hills” that give the appearance of a basketball being pushed up through the soil.


Moles are extremely beneficial because they consume the larvae and adults of numerous pest insects, such as Japanese beetles,that affect garden, landscape, and flowering plants. Additionally, their tunneling activity loosens the soil, improves aeration, and mixes deeper soils with surface organic material, all of which enhance soil quality. However, moles can be a nuisance where their tunneling disturbs lawns and recreational facilities. Although moles frequently are blamed for feeding damage on the roots of vegetation or seeds planted in gardens, they rarely cause such damage. Garden plants may be uprooted or heaved out of the soil inadvertently as these animals burrow. In fact, commercial bulb growers and producers of row crops can sustain economic loss from moles where plants are dislodged and subsequently become desiccated and die, or when harvesting equipment comes in contact with the raised mounds or ridges created by moles and is damaged.


For commercial agricultural producers, elimination of moles over large areas is difficult, if not impossible. For the homeowner,problems with moles usually can be managed with minimal effort and persistence. Because of the moles solitary habit and a rather low productivity, most residential yards can be maintained “mole-free” for a number of years. The sonic or vibration producing devices advertised commercially as mole deterrents generally have no proven effect on moles. Similarly, many “home remedies,”such as gassing with auto exhaust, placing broken glass, pins or other sharp objects in the tunnels, and use of harsh household chemicals, usually are totally ineffective, can be hazardous to residents and non-target animals, and may be illegal.


Although several fumigant products are registered for use in Virginia, all formulations are classified as restricted use only products. Similarly, many formulations of registered toxicants developed to kill moles also are classified as “Restricted Use Only” products. In such situations, unless you have current Pesticide Applicator Certification in Category 10 (Vertebrates), these materials are unavailable to you. Therefore, use of fumigants and toxicants should be left to licensed or certified pesticide applicators. In instances where use of a particular toxicant formulation is not restricted (e.g., certain formulations of chlorophacinone and zincphosphide), it is imperative that these materials are placed into the burrow system below ground as a means to reduce non-target exposure. One thought to keep in mind-given that moles are insectivores, they usually don’t recognize treated grains or pellets as food. Therefore, toxicant treatments often are ineffective in reducing mole activity and damage.

In the past, insecticides frequently were applied to lawns in an attempt to reduce populations of various beetle grubs, which are a major food of moles. The assumption used to justify this approach was that with a reduced food supply, moles would leave the area.However, in practice, applications of insecticide rarely were effective in removing all potential food sources. Because moles feed on such a variety of invertebrates, not just grubs, they simply switch to another readily available food (usually earthworms or night crawlers) rather than leave the area. Furthermore, some insecticides that have been applied in the past were toxic to wildlife,particularly granular formulations that were especially attractive to songbirds. This approach is no longer recommended-insecticides should be used to resolve insect problems, not mole problems.

White milky spore, a naturally-occurring fungus now available in commercial form, has been promoted as a means to help reduce the number of grubs and somewhat limit the mole’s food supply. However, the fungus does not seem to survive well in cold climates, so it may not persist through the winter months, particularly in the western parts of the commonwealth. Additionally, even where milky spore is present, it is effective only on certain insects. Thus, with other natural food items still available, this option alone may not provide desired control.

Until recently, repellents have not been proven effective in reducing or eliminating mole activity. A new repellent formulation, which contains castor or ricinus oils, recently received registration for use in Virginia. This repellent is designed to be applied as a soil drench. However, because this product is relatively new, comprehensive testing has yet to be performed to assess its overall effectiveness under field conditions in Virginia.


Sometimes limited areas, such as seedbeds or small gardens, sustain persistent mole damage. For such areas, installation of a perimeter barrier constructed of sheet metal or hardware cloth may be appropriate. To install such a barrier, first dig a trench about12-15 inches deep and 10 inches wide around the entire outer edge of the bed to be protected. Place about 8-10 inches of the barrier material into the bottom of the trench, then fold or bend the material upright to create with the foot of the extending out away from the bed. The barrier material should then extend upward and about 5 inches above the ground surface for complete protection. Back fill the trench with soil to hold the barrier in place and to give it support. All connections in the barrier, especially the corners, must be secure if this barrier is to be effective.


Trapping should be viewed only as a temporary fix to mole problems because it treats a symptom rather than the root cause of the problem. If you are successful in removing an offending individual from the environment, that effort alone does nothing to alleviate or alter the conditions that attracted that animal initially. If the habitat, food supply or other attractant is not modified, other individuals are likely to replace the individual(s) you removed.

To live trap moles, one uses a container into which the moles will fall and be unable to escape, commonly referred to as a pit trap. However, you must first determine which runways are active before installing these devices. The best time to trap moles is in the spring, as soon as the first ridges are noted, or after the fall rains. The identification of main or frequently-used runways is of prime importance. To determine which runways are active, stamp down a short section of each runway with your foot and place a marker at each of these locations so that you will be able to relocate them. Observe daily for several days, stomping down any freshly raised sections. If a tunnel is raised each day, you have found an active runway. This is where a trap should be placed.

Dig a hole through the center of the most active runway sufficiently large enough to place a #10 tin can (approximately 7 inches in diameter and 10-12 inches deep) upright in the hole. Be sure the top of the can is level with the bottom of the runway. Fill and pack dirt tightly around the sides of the can, and then plug both sides of the runway with soil right up to the lip of the can. You may also want to stamp the runway about 1 foot on both sides of the can. Lay a board, plywood scrap or other suitable material on the ground over the pit to block out light and prevent pets or children from falling into the hole, but allow you to maintain easy access for monitoring. In reopening the runway, the mole will fall into the can and usually is unable to escape. If the tunnels are not reopened or you fail to catch a mole within 1-2 days, move the device to another active runway.

Captured animals can be released in other areas of your property where their activity will not be objectionable or you may perform humane euthanasia (recommended methods include lethal injection by veterinarian, cervical dislocation, gassing with CO2). Before handling any animals, wear heavy gloves and long-sleeved garments to protect yourself from scratches and bites. Regardless of whether you believe any harm will result from your action, it is illegal in Virginia to transport and liberate any wild animal captured on your property to property of another (including federal, state, or municipal lands) unless you have first obtained a permit to do so from the Virginia Department of Game and Inland Fisheries.

Although a variety of kill traps (e.g., harpoon, scissor, or body gripping types) can be purchased at many farm supply and hardware outlets, their use as a means of eliminating or reducing mole damage can be dangerous. These traps often are difficult to set and properly place without risking personal injury. Additionally, there is potential for injury to small children and pets that play near or with unattended mole traps. For these reasons, lethal trapping should be left only to those trained in the operation of such devices and the handling of wild animals.


Godfrey, G., and P. Crowcroft. 1960. The life of the mole. London Museum Press, London. 152pp.

Henderson, F. R. 1994. Moles. Pages D-51 to D58 in S. E. Hygnstrom, R. M. Timm, and G. E. Larson, eds. Prevention and control of wildlife damage. University of Nebraska Cooperative Extension, USDA APHIS-ADC, and the Great Plains Agricultural Council.

Webster, W. D., J. F. Parnell, and W. C. Biggs, Jr. 1985. Mammals of the Carolinas, Virginia, and Maryland. University of North Carolina Press, Chapel Hill, NC. 255pp.



Voles are active day and night, year-round. They do not hibernate. Home range is usually 1/4 acre or less but varies with season,population density, habitat, food supply, and other factors. Voles are semifossorial and construct many tunnels and surface runways with numerous burrow entrances. A single burrow system may contain several adults and young.

Voles may breed throughout the year, but most commonly in spring and summer. In the field, they have 1 to 5 litters per year. They have produced up to 17 litters per year in a laboratory. Litter sizes range from 1 to 11, but usually average 3 to 6. The gestation period is about 21 days. Young are weaned by the time they are 21 days old, and females mature in 35 to 40 days. Lifespans are short, probably ranging from 2 to 16 months. In one population, there was 88% mortality during the first month of life.

Large population fluctuations are characteristic of voles. Population levels generally peak every 2 to 5 years; however, these cycles are not predictable. Occasionally during population irruptions, extremely high vole densities are reached. Dispersal, food quality,climate, predation, physiological stress, and genetics have been shown to influence population levels. Other factors probably also play a part.

Population densities are variable. Smolen and Keller (1987) list densities of long-tailed vole populations. A California population ranged from about 2 to 7 voles per acre and a New Mexico population ranged from around 8 to 49 voles per acre. Cole and Batzli(1979) found that prairie vole populations averaged 15 per acre in prairie, 52 per acre in bluegrass, and 99 per acre in alfalfa.Another vole population ranged from 1 to 14 per acre over 3 years in western mixed prairie. Variability in meadow vole population density was reported by Taitt and Krebs (1985). An Ontario, Canada population ranged from 32 to 162 per acre over 1 year while an Illinois population ranged from 2 to 6 per acre also over 1 year. Other populations show similar year-to-year variability. Much higher densities may be reached during population irruptions. In Klamath Basin, Oregon, montane vole densities ranged from 200 to 500per acre and may have reached 4,000 per acre in some instances during a 1957 to 1958 irruption.

Many voles are excellent swimmers. The water vole, in fact, escapes predators by swimming and diving. The climbing ability of voles varies. The long-tailed vole, for example, is a good climber (Johnson and Johnson 1982) while the pine vole is a bit clumsy in this regard.

Voles are prey for many predators (for example, coyotes, snakes, hawks, owls, and weasels); however, predators do not normally control vole populations.


Voles may cause extensive damage to orchards, ornamentals, and tree plantings due to their girdling of seedlings and mature trees.Girdling damage usually occurs in fall and winter. Field crops (for example, alfalfa, clover, grain, potatoes, and sugar beets) may be damaged or completely destroyed by voles. Voles eat crops and also damage them when they build extensive runway and tunnel systems. These systems interfere with crop irrigation by displacing water and causing levees and checks to wash out. Voles also can ruin lawns, golf courses, and ground covers.

Girdling and gnaw marks alone are not necessarily indicative of the presence of voles, since other animals, such as rabbits, may cause similar damage. Vole girdling can be differentiated from girdling by other animals by the non-uniform gnaw marks. They occur at various angles and in irregular patches. Marks are about 1/8 inch (0.3 cm) wide, 3/8 inch (1.0 cm) long, and 1/16 inch (0.2 cm) or more deep. Rabbit gnaw marks are larger and not distinct. Rabbits neatly clip branches with oblique clean cuts. Examine girdling damage and accompanying signs (feces, tracks, and burrow systems) to identify the animal causing the damage.

The most easily identifiable sign of voles is an extensive surface runway system with numerous burrow opening. Runways are 1 to 2inches (2.5 to 5 cm) in width. Vegetation near well-traveled runways may be clipped close to the ground. Feces and small pieces of vegetation are found in the runways.

The pine vole does not use surface runways. It builds an extensive system of underground tunnels. The surface runways of long-tailed voles are not as extensive as those of most other voles.

Voles pose no major public health hazard because of their infrequent contact with humans; however, they are capable of carryingdisease organisms, such as plague (Yersinia pestis) and tularemia (Francisilla tularensis). Be careful and use protective clothing when handling voles.


Voles are classified as non game mammals and can be controlled when causing damage. Contact your local state wildlife agency for details regarding applicable codes and regulations.



Hardware cloth cylinders exclude voles from seedlings and young trees. The mesh should be 1/4 inch (0.6 cm) or less in size. Bury the wire 6 inches (15 cm) to keep voles from burrowing under the cylinder. Large scale fencing of areas is probably not cost-effective.Drift fences with pit traps may be used to monitor populations and can indicate when voles are immigrating to crops, orchards, or other cultivated areas.

Cultural Methods and Habitat Modification

Cultural and habitat modification practices can reduce the likelihood and severity of vole damage. Eliminate weeds, ground cover,and litter in and around crops, lawns, and cultivated areas to reduce the capacity of these areas to support voles. Lawn and turf should be mowed regularly. Mulch should be cleared 3 feet (1 m) or more from the bases of trees.

Voles can live in dense populations in ditch banks, rights-of-way, and water ways that are un-managed. Adjacent crop fields can be cost-effectively protected by controlling vegetation through mowing, spraying, or grazing.

Soil tillage is effective in reducing vole damage as it removes cover, destroys existing runway-burrow systems and kills some voles out right. Because of tillage, annual crops tend to have lower vole population levels than perennial crops. Voles are nevertheless capable of invading and damaging annual crops, especially those that provide them with cover for extended periods of time.


Frightening agents are not effective in reducing vole damage.


Repellents utilizing thiram (also a fungicide) or capsaicin (the hot in chilis) as an active ingredient are registered for meadow voles(see Supplies and Materials). These products (or repellents registered for other species) may afford short-term protection, but this has not been demonstrated. Check with your state pesticide regulatory agency for availability.


Zinc phosphide is the most commonly used toxicant for vole control. It is a single-dose toxicant available in pelleted and grain bait formulations and as a concentrate. Zinc phosphide baits generally are broadcast at rates of 6 to 10 pounds per acre, or are placed by hand in runways and burrow openings. Although pre-baiting (application of similar non-treated bait prior to applying toxic bait) is not usually needed to obtain good control, it may be required in some situations, such as when a population has been baited several times and bait shyness has developed. Zinc phosphide baits are potentially hazardous to ground-feeding birds, especially waterfowl.Placing bait into burrow openings may reduce this hazard.

Anticoagulant baits are also effective in controlling voles. Anticoagulants are slow-acting toxicants requiring from 5 to 15 days to take effect. Multiple feedings are needed for most anticoagulants to be effective. In many states, one or more anticoagulant baits arer egistered for controlling voles.

In addition to broadcast and hand placement, anticoagulant baits also can be placed in various types of bait containers (Byers and Merson 1982, Radvanyi 1980). Water repellent paper tubes with an anticoagulant bait glued to the inside surface make effective,disposable bait containers. Tube size is about 5 inches (12 cm) long by 1 1/2 inches (4 cm) in diameter (Libby and Abrams 1966,Marsh et al. 1967). Bait containers protect bait from moisture and reduce the likelihood of non target animals and small children consuming bait.


Fumigants usually are not effective because the complexity and shallowness of vole burrow systems allow the fumigant to escape.They may work in new, small burrow systems with only one or two entrances.


Trapping is not effective in controlling large vole populations because time and labor costs are prohibitive. Mouse snap traps can be used to control a small population by placing the trap perpendicular to the runway with the trigger end in the runway. A peanut butter-oatmeal mixture or apple slices make good baits. Fall and late winter are periods when many vole species are easiest to trap.

Although voles rarely invade houses, in the event that they do, they can be controlled by setting snap traps or live traps (Sherman or box-type) as you would for house mice (see Trapping in the House Mice chapter).


Shooting is not practical or effective in controlling voles.

Other Methods

A wide variety of predators feed on voles. Voles are relatively easy for most predators to catch and are active, and there fore available, day and night year-round. Despite their vulnerability and availability, voles are not usually controlled by predators. This is because voles have a high reproductive potential. Postpartum breeding is common and females may breed as early as 2 weeks of age. Synchronous breeding also occurs. These factors enable voles to increase at a faster rate than predators (Pearson 1985).

Economics of Damage and Control

Jameson (1958) calculated that 100 meadow voles per acre destroyed about 4% of an alfalfa crop, which amounted to about 1,000pounds per acre over 7 months.

Populations of 1,700 voles per acre in Washington State apple orchards decreased production by 35%. This amounted to a loss of$3,036 per acre due to reduced fruit quality and quantity. One year after eliminating voles, the production in the orchard increased but was still below the production of orchards that had not incurred vole damage. Total losses for the 2-year period were estimated at$6,100 per acre (Askham 1988). Similar apple orchard loss figures were calculated for pine voles in New York. Known densities of voles were stocked in fenced blocks of McIntosh trees for 2 years. There was little impact the first year. The second year, the highest vole population reduced fruit yield 65.5% and increased undersized fruit from 3.1% to 57.5%. These factors caused a $2,745 per acre reduction in income. In addition, survival of the trees through a third year was considered unlikely. The worst vole outbreak in the United States probably occurred in Nevada in 1908 and 1909. Ten thousand acres of alfalfa were completely destroyed. Vole populations were estimated at 25,000 per acre.

Often a control program may not appear to be justified in comparison to the damage being incurred. It should be remembered,however, that the ounce of prevention rule frequently applies in vertebrate pest control. Preventive control measures that at first appear too costly may eventually prove to be a bargain.