A historical presentation by the USFS at the Southeast Equestrian Trail Conference in 2008.
Due to the urbanization of America, the general population has lost its contact with and innate understanding of most animals, including livestock. The horse, in particular, is a unique animal. Because it is large and seldom encountered, people assume that it is no different than other species of large animals. This paper is meant to help people understand horses and their interactions with the environment when they encounter equines on trails.
Every trail user potentially causes some impact to the environment by their use. For lightweight low-impact users, the effects are usually minimal. Scientific studies indicate that the horse may be more benign to wildlife than hikers, nature studiers and photographers. There are no studies that significantly implicate trail use by horses with spreading weeds. Natural erosive forces are likely to be the major alteration factors in trail erosion. Horses on trails are not detrimental to water quality according to the latest studies by NAHMS, University of Colorado and UC Davis-Tulare.
Equestrian Use of Trails is "Passive" Recreation
Every trail user potentially causes some impact to the environment by his/her use. Compared to motorized usage, hikers, bikers and horses have been variously described as passive, light-weight, and/or low-impact trail users. The effects of passive use on trails are usually minimal. In virtually every mixed use trail reference within the State of California and the nation, the horse has been defined as a passive, low impact or light weight user, even in the most sensitive environments: Natural Preserves.
Wildlife and Horses
Horses are prey animals. They have eyes on the side of the head. They are herbivores and leave the trace scent of an herbivore on the trail. Humans, dogs and cats are predators. Their eyes are on the front of the face. As they walk, they leave the trace scent of omnivore on the trail that can impact wildlife.
Horses are recognized by wildlife as prey animals, even when a person is sitting on their back. An approaching horse passing along a trail provides sound rhythms in the cadence of a four-footed hoofed prey animal to wildlife, which informs wildlife of a non-threatening presence. For reptiles, rodents and other terrestrial life forms, the percussion pulse of the approaching horse provides warning. Being warned diminishes flushing/flight response that consumes wildlife energy. It is not uncommon to find deer, bobcat and coyotes that allow horses to get within feet of them on trails before calmly moving off. Horses rarely step on lizards, mice and other fast moving wildlife. Riders can easily avoid slower moving wildlife.
Bennett and Zuelke (1999) undertook an extensive review of recreation effects on birds and concluded that disturbance from recreation has temporary effects on behavior and movement of birds. Direct approaches caused greater disturbance than tangential approaches, rapid movement by joggers was more disturbing than slower hikers; children and photographers were especially disturbing, and passing or stopping vehicles were less disturbing than human foot traffic. Horses and riders did not disturb birds.
Sporadic human use can disturb wildlife. However, "many animals are less afraid of horseback riders than hikers. Riders seldom dismount to touch flora or fauna. Riders can be a dedicated and energetic volunteer and advocacy group. The horse-rider relationship promotes a non-anthropocentric worldview that facilitates ecological understanding. Horses are useful for patrols, supplying trail maintenance, and doing surveys. Horse traffic can be used to maintain firebreaks and seldom-used trails." (Williams et al, 1998)
Weed Seeds and Horses
The primary vectors of weed seed spread are wind, water, avians, and rodents. There is no documented evidence of the horse spreading weeds. A Montana study by Tyser and Worley (1992) implicated timothy (Phleum pratense) and bluegrass (Poa pratensis) as species that had been included in past roadside seeding by the local highway authority. In California, the Department of Transportation (CalTrans) has recently been identified as the number one spreader of yellow star thistle by its past practices of scattering various weed-laden hays during roadside rehabilitation projects to control erosion. CalTrans has now switched to wetland chaff from rice crops for soil stabilization purposes which does not contain thistle seeds.
It is unknown to what extent high quality livestock forage available contains weed seeds. However, most horse owners would not buy junk hay for their horses. Garbage in, poor performance out! The days of large populations of lower-grade, inexpensive stock horses are long gone. Horses cost money, and the purchase price is only the down payment for ownership. Horsemen cannot afford to compromise their investments by feeding weedy hay. Responsible horse owners are concerned about getting quality feed that has been properly planted, harvested, and cured for their horse food dollar. (Berto 2001). Many horses are fed processed or pelletized feedstock. This is forage that is heated. The heat destroys weed seeds.
According to Dr. Deanne Meyer, UC Davis Manure Management Specialist, the majority of all horse excrement occurs at home in pastures or paddocks. It is, therefore, highly unlikely for the horse ever to be a major vector of weed seed spread simply from its use on a trail. By 2003, all forage brought into trailheads on federally- and state-managed properties will be required to have a weed-free feed certificate. Equestrian trail users have been active participants in designing this program in collaboration with land managers.
The horse has a very inefficient gut: it's a one-way through-put system. Horses are physiologically incapable of vomiting or regurgitating. If something gets stuck on the way through, the only way to get it out is by surgery or physical intervention (at arm's length!). As a consequence, horses must be fed carefully to avoid the common and potentially fatal condition of colic. The bulk of unprocessed forage consumed by California horses is alfalfa (Medicago sativa), rye grass (Lolium multiflorum or perenne), Timothy hay (Phleum pratense) and oat hay (Avena sativa (white cultivated oats)). If horses were a vector of seed spread, these grasses could be prevalent in our open spaces and parks, but they are not, except possibly in places where they were introduced in earlier times as grazing forage for cattle.
The California Exotic Pest Plant Council (www.caleppc.org) lists the following plants as the major invasive culprits: Tamarisk, knapweed, and thistles. Horses do not eat these species, many of which are actually toxic to the equine. Star thistle consumed by horses can cause a potentially fatal Parkinson-like disease. Stinging nettles recently killed two trail horses at Pt. Reyes National Seashore. Knapweeds are very toxic to horses. For the health of our animals, equestrians are keenly interested in the abatement of exotic and invasive plants. Because the horse is not perceived as a major contributor to the spread of weed seed from trail use, trail manure has been little studied. However, there is much literature on composted horse manure. Harmon (1934) notes that composted horse manure virtually kills all weed seeds.
Janzen is the researcher who has done the most studies on seeds in horse manure. Among his conclusions are:
Finally, Benninger-Truax studied edge effects of trails in Colorado. She notes that seeds can pass through horses unharmed and be deposited in feces. She states that she found no documentation that horses are major source of exotic species in her literature search. In her Master's thesis, Benninger did a greenhouse study on seeds extracted from horse manure. Seeds from 15 plants grew, but only 8 were identified. While all 8 were exotic, NONE of them appeared in her test plots on the trail, although she observed them elsewhere along trails. She determined that horses from the stable in the park that were not allowed to graze in the park (which had exotics along some trails) and had controlled diets were not a problem for weed seed dispersal along the trails. A simple Best Management Practice (BMP) is obvious here.
The erroneous assumption that manure is a major source of exotic species suggested by some should be put to rest by Benninger-Truax's statement: "…however, I have found no documentation of this in the literature." Neither has EnviroHorse a decade later. While some seeds can survive the journey through the horse mouth and gut, Janzen's statement suggests its fate: " While an Enterolobium seedling germinating in a dung pile is picturesque, its chances of surviving the dung beetles, mice, dryness, and root exposure characteristic of dung piles are very slim."
Seeds are primarily dispersed by gravity, wind, surface water movement, soil erosion, birds, ants, dung beetles and rodents. Since the majority of horses are carefully fed domestic grasses, have physiology mitigating against seed survival, and primarily defecate in their home paddocks/pastures, it is unlikely that horses are a significant vector for seed spread when they are on trails.
Trails and Horses
Soil erosion is a two-part process: soil particles are loosened largely by wind or raindrop impact (lesser by freeze/thaw, wet/dry cycles) and transported by the flow of wind and water. The four primary factors involved in erosion are climate, soil characteristics, topography and ground cover. In the United States soil erosion removes an estimated 2,100,000,000 tons of soil per year. (Gergus, 2002)
According to public testimony to the MROSD on December 16, 1998 given by Professor and Chair Gordon E. Brown Jr., Stanford University Dept. of Earth Sciences Synchrotron Radiation Laboratory Faculty, the primary causes of erosion are natural and far surpass any impact of use of horses on trails.
In a 5-year study, Summer (1990, 1996) concluded that horse traffic was not the single dominant process active on trails. Trail degradation was a function of landform, climatic and catastrophic events, and geomorphic processes. Seasonal use was important in keeping the soil exposed and vegetative cover absent on trails. Such processes as sheetwash, rilling, gullying, and soil creep actively modified and eroded the trails and resulted in a measurable fluctuating rate of change over time. Limited data suggested that foot traffic produced effects similar to horse traffic in exposing the trail to the effects of geomorphic process or climatic events. Intensive runoff resulting form natural events can cause significant geomorphic change in a trail from such processes as gullying and earth slumps. Erosion from these events may overshadow effects of horse use on trails.
Williams et al (1998) concur that factors other than user type are more closely linked to trail degradation. Lightly used trails may grow over and require more maintenance, whereas moderate horse activity may help to maintain a multiple-use trail. The bottom line is that horse trails can be maintained on most natural preserves without unacceptably impacting ecological values.
The physical impact of horses on trails is highly variable-dependent. In high rain regimes and certain soil types, more physical impact would be expected. Seasonal closure of some trails may be appropriate. Water should be diverted off of all trails to prevent erosion. In order to further mitigate an impact in more susceptible areas, rocking equestrian trails may be appropriate. Spreading 3/4" hard native rock, decomposed granite (DG), or basalt provides a firmer trail tread. Over time, this rock sinks into the soil and "hardens" the trail tread, improving year-round conditions for all users. Repeated rock application over time provides excellent tread surfaces for mixed users and does not significantly alter soil chemistry in sensitive habitats (Murarka, 1996). The Clarkia Trail in San Mateo County's Edgewood Park and Natural Preserve is an excellent example of how a trail can be maintained year-round in potentially mucky black clay soil using local serpentine rock.
Water Quality and Horses on Trails
The endpoints of scientific inquiry for water quality studies are human exposure to pathogens for health implications and nutrient/sedimentation pollution for environmental implications. Excrement or wastes of any type should never be deposited or disposed of in water bodies.
Coliforms are ubiquitous in the environment. While they are not necessarily harmful to people if ingested, coliforms are an indicator that unwanted matter is present in the water system. Their virulence is little understood; hence the precautionary care to prevent human exposure to excess amounts of them. Coliforms, however, have not been known to injure aquatic organisms or wildlife according to Dr. Michael Rugg, Toxicologist, California State Fish and Game, Yountville CA. Recent scientific studies and their replicates confirm that adult horse guts do not significantly contain E. coli 0157:H7, Salmonella, Cryptosporidium, or Giardia, which are the organisms of most concern in water-borne spread of disease. (Atwill, et al; see several references.)
We have found no studies that we found implicating equids in groundwater contamination. Horses eliminate primarily in their pastures and paddocks (Meyer 1997). Manure left in a loose heap in deposits on trails loses its nitrogen rapidly (New Hampshire 1990). It is inconceivable that trail horses making dispersed deposits could possibly impact ground water. Most contamination of this sort occurs from areas associated with feedlots where thousands of commercially harvested animals are confined at one time, or from excessive fertilization added to soils.
Compared to other large livestock, horse manure is relatively "dry" and "hot" due to unique digestive enzymes and flora. Once deposited, it can achieve total mineralization in as short a time as 21 days (Ajwa, et al 1994). Because it is so dry at excretion, nutrients tend to volatilize rapidly into the atmosphere. One of the challenges in preserving nutrients in horse manure is to get them turned into the soil as rapidly as possible before the nutrients are lost to the air.
Again, there are very little data about impacts from horses. Bacteriological and nutrient effects (on water bodies) are seldom detectable except next to stables. (Williams et al, 1998). As part of the 319(h) grants from the Clean Water Act, new data are becoming available. Five studies have taken place in the San Mateo County watersheds to date (2002). It is important to keep in perspective that these studies involve settings where horses live 24 hours/day next to a creek. Thus far, data have not confirmed significant adverse affects on the surface waters immediately adjacent to them. Leaking aging septic systems, residential over-fertilizing, and certain agricultural practices are suspected where data exceed recommended standards. Given this, it is difficult to conceive of a situation where the manure from a few horses on a trail could adversely impact surface water nearby. Again, most trails are not sited immediately adjacent to water bodies and Mother Nature has a marvelous buffering capacity when even as little as 10 feet of vegetation is available at the side of a trail.
Phosphorus and potassium are the trace constituents of most concern in horse urine. They bind to soil particles and may be eroded away into surface water bodies. They would be present only in the minutest of quantities in manure on trails, thus of little concern. For horses paddocked near streams, a recent study by Dr. Michael Rugg on accumulation of urine salts in soil in arid climates demonstrated that these salts could be dissipated in just three days by watering dry paddocks to invite biological degraders to the soil. Thus a simple BMP of turning on a sprinkler once a day will not only keep dust down, but will mitigate urine salt accumulation in paddock soils.
There is a trend to protect stream banks from erosion by trail use and discourage trail users from disturbing streams that support fisheries. Bridges are being built across historic fords. It is known that as little as 0.025ppm of ammonia in water can kill salmonoid species (Rugg).
While horses can readily defecate on trails, they do not as readily urinate on trails. (Gosslin and Wolford, 2001). Because of their physiology, horses under saddle generally signal riders of their need/intent to urinate. They are allowed to stop walking. Horses then stretch their bodies out in a rather awkward position to urinate, often standing on the front edges of their hooves simultaneously in a splayed posture. This places them in a vulnerable position if attacked by a predator. 60 million years of evolution and survival means that this is an activity not undertaken lightly by the horse. Many horses prefer the safety and security of their stall or paddock to undertake this function (UC Davis Book of Horses 1996). Because of this unique behavior, it is easy for the rider to spur the horse out of a stream to avoid urination in a water body. Because the urination posture is impossible to achieve during locomotion, it will be more apt to occur with a relaxed horse at rest (Horst 2000). Urination can be readily managed to avoid elimination in water bodies.
Equestrians are being educated not to allow their animals to eliminate during stream crossings. BMPs have evolved such as stopping prior to a crossing to allow the animal to rest, relax, and (hopefully) eliminate PRIOR to the crossing. Simply not allowing the horse to stop and dawdle in the water will also help to prevent contamination. Many horses do not like getting their feet wet and have a natural aversion to taking any more time than necessary in water. A small study is underway to collect data on horses eliminating while crossing streams. It is expected to take several years before a robust database is available. But preliminary data collected in 2000-2001 indicated that very few horses eliminated during stream crossings. In a letter to equestrians dated July 2, 2001 Dr. Michael Rugg described the risk of stream crossing to fish and aquatic species, but concluded by saying, "However, as long as the riders are aware of the risks, and make an effort to avoid having their animals urinate or defecate in or near the creek, the risks to fish and aquatic life (of horses making a stream crossing) are acceptable."
Trail Etiquette and Horse Physiology
For safety sake, other trail users should always yield the right-of-way to equestrians. Would you argue with a Mack Truck if you were a VW bug on the highway? Stop and stand quietly off the trail until the horse passes. Failure to do so can endanger the hiker / runner as well as the horse and rider. Fast-moving trail users may startle horses and slower-moving people. Please verbally announce your presence immediately, especially when approaching horses from behind, and ask the rider for instructions on how to pass the animal. The rider may ask you to step off the trail so he/she can ride by, or may ask you to walk by while he/she stands the horse. The circumstance may vary depending on the personality of the horse involved and physical conditions of the site.
Why do horses "spook"? Horses have large eyes that provide a wide range of peripheral vision. Each eye boasts a field of 215 degrees of monocular fixation (focusing one eye on a subject) with the fields overlapping in front of the horse's head to create 60-70 degrees of binocular fixation (where both eyes can focus on a single object). This allows the horse to view the ground ahead more sharply and with depth perception (stereopsis). However, horses have small blind spots in front of and behind them that can only be clarified by turning the head to observe with its monocular vision. Any stationary object in the horse's blind spots may seem to "jump" when its image moves in and out of the peripheral field of vision, as the horse turns its head in a an attempt to focus. This can result in a typical fleeing or "spooking" behavioral response. Unlike humans, a horse must move its head up and down to focus its eyes on an object. When a horse holds its head upright and high, it is usually focusing on an object in the distance and cannot clearly see the ground directly beneath its nose. The vision of a trotting or galloping horse is not as acute as that of a stationary horse. A horse's range of vision along with its degree of visual acuity should always be taken into consideration when you approach a horse on the trail, particularly from behind. (UC Davis Book of Horses 1996)
EnviroHorse has prepared these materials for information purposes only and are not legal advice. Subscribers and online readers should not act upon this information without seeking professional counsel. Every attempt has been made to assure that the information contained in this publication is accurate. EnviroHorse assumes no responsibility and disclaims any liability for any injury or damage resulting from the use or effect of any product or information specified in this publication.
About the Author and this Paper
Adda Quinn worked for a nationally known research institute for 21 years prior to her retirement. Her research projects focused on contaminated soil and groundwater issues. As a trail advocate, she has provided research results in a variety of regulatory debates, both nationally and locally. She is a founding member of and on the Board of Directors for EnviroHorse. This paper is a work in progress. It is our intention to update it periodically as new information becomes available.
EnviroHorse identifies, gathers, and disseminates information to ensure/enhance equine access to public / private lands. Where data gaps exist, EnviroHorse sponsors research to fill them with these goals:
1). To establish and provide a clearinghouse for information on horses, horse trails and other related equine uses. This effort will include · synthesis papers on important environmental and health issues · hard copy of source data by subscription · electronic network site with linkage to other resources · electronic database for pertinent papers · linkage to environmental and community benefits from horses · linkage to legal resources for equine issues
2). To identify and raise funding for research on priority issues.
3). To work with other equestrian organizations to assure continued equine access to public and private lands. If you have any scientific studies that you think would be helpful, these papers are a work-in-progress and EnviroHorse would love to have copies of them.
Ajwa, H. A. and Tabatabai, M. A. 1994. "Decomposition of different organic materials in soils". Biol. Fertil. Soils Vol. 18. Pp. 175-182.
Atwill A number of excellent references are now available on horse gut pahogens E. Johnson, Atwill, E. R., Filkins, M. E., and Kalush, J. "The prevalence of shedding of Cryptosporidium and Giardia spp. based on a single fecal sample collection from each of 91 horses used for backcountry recreation." Journal of Veterinary Diagnostic Investigation. Vol. 9. Pp. 56-60. 1997. In the winter 2000-2001, Dr. Atwill of UC Davis-Tulare, conducted a further research study on 250 horses in the San Francisco Bay Area. Due to concerns expressed by organic gardeners about the safety of using composted horse manure as a soil amendment, Atwill determined again that insignificant levels of E. coli 0157:H7 and Salmonella were in adult horse guts. Composted manure showed no E. coli 0157:H7 after 24 hours in pile residence. Research results should be available in the near future. A 1998 NAHMS study on "Salmonella and the US Horse Population" confirms Salmonella is not an issue in horses (www.aphis.usda.gov/vs/ceah/cahm/Equine/eq98salm.htm). K. N. Ford, Swinker, A.M., Traub-Dargatz, J. L., and Cheney, J. M. "The Prevalence of Cryptosporidium/Giardia in the Trail Horse Population Utilizing Public Lands." Proceedings of 15th Equine Nutritional Physiology Symposium. Pp. 223-237. 1997, and JEVS 18 (1) 1998. And paper available by Laurie Fio with Rob Atwill: "Cryptosporidium in the Water - Are Horses to Blame?" M. M. Peng,1 Xiao, L., 2 Freeman, A. R., 2 Arrowood, M. J., 2 Escalente, A. A., 2 Weltman, A. C., 3 Ong, C. S. L., 4 MacKenzie, W. R., 2 Lal, A. A. 2, and Beard, C. B. 2 "Genetic Polymorphism Among Cryptosporidium parvum Isolates: Evidence of 2 Distinct Human Transmission Cycles." Emerging Infectious Diseases. Vol. 3. No. 4. Oct.-Dec. 1997. Pp. 567-573. University of Michigan1, CDC Atlanta2, PA Dept. of Health3, University of British Columbia4.
Bennett, KA and E. Zuelke. 1999. The effects of recreation on birds: a literature review. Delaware Natural Heritage Program, Smyrna, DE 1977.
Berto, Connie. Marin County Horse Council. Personal Conversation, 2000.
Brown, Gordon E., Jr. D.W. Kirby Professor of Earth Sciences, Professor and Chair, Stanford Synchrotron Radiation Laboratory Faculty Stanford Universit. on December 16, 1998 public testimony before the Midpeninsula Regional Open Space District (MROSD).
Gosselin, Dr. Larry DVM, pers. comm. 4-10-01; Dr. Larry Wolford specializing in equids, pers. comm. 4-5-01.
Gergus, Scott. North Coast Regional Water Quality Control Board. "Soil Erosion Causes and its Problems". April 10, 2002. Equestrian Planning Course Santa Rosa Junior College. Many citations offered.
Horst, Toby. Chairman BackCountry Horsemen, pers. comm. 2000.
Meyer, Dr. Deanne. 1997. "Horses spend most of their time in pastures or paddocks where the majority of their excrement is deposited, collected and managed. Horse manure is about 70-80% liquid and 20-30% solids." Personal communication, UCDavis Manure Management Specialist.
Murarka, Dr. Ishwar. Edgewood Park and Natural Preserve Master Plan Adopted May 1997, Environmental Services Agency Parks and Recreation Division, San Mateo County California. Appendix C-1 "Potential Impacts of Using Identified Non-Native Rocking Materials in Serpentine Grassland".
New Hampshire Dept. of Ag and USDA. Good Neighbor Guide for Horse-Keeping: Manure Management. 1990.
Rugg, Dr. Michael Toxicologist, Calif. Dept. Fish and Game in personal communication to Adda Quinn and Alistair Bleifuss (RCD TAC), 1998. That year, EnviroHorse provided Dr. Rugg with a bucket of soil heavily contaminated by horse urine from an equine who refused to urinate anywhere but in one spot for 10 years. His analysis indicated that urine salts could be mitigated by light watering of dry paddocks during summer. Introduction of water improves the ability of biological soil degraders to decompose urine salts in three days. A letter dated July 2, 2001 by Dr. Michael Rugg to Michael Murphy, an RCD liaison, described the risk of stream crossing to fish and aquatic species, but concluded by saying "However, as long as the riders are aware of the risks, and make an effort to avoid having their animals urinate or defecate in or near the creek, the risks to fish and aquatic life (of horses making a stream crossing) are acceptable."
Santa Clara County Countywide Trails Master Plan. November 1995. Figures G-2 and 3. Permission to use only if distributed at no cost.
Summer, RM. 1996. Geomorphic Impacts of horse traffic on montane landforms 41(2): 126-128.
Summer, RM. 1980. Impacts of horse traffic on trails in RMNP. J. Soil and Water Cons. 35(2): 85-87.
Tyser, RW and CA Worley. 1992. Alien flora in grasslands adjacent to road and trail corridors in Glacier National Park, Montana USA. Conservation Biology 6:253-262.
Williams, B. and L. Conway-Durver. "HORSE TRAILS IN ECOLOGICAL RESERVES" presented at Clemson University Horse Trails Symposium, 1998. Mr. Williams holds a BS Degree in Forestry from Clemson University. He worked for the U.S. Forest Service as a River Ranger on the Sumter National, organized the Association of Forest Service Employees for Environmental Ethics and is the Executive Director of the Chattooga River Watershed Coalition.
UCDavis School of Veterinary Medicine, Ed. Mordecai Siegal. Book of Horses: A complete Medical Reference Guide for Horses and Foals 1996. Chapter 4 Equine Behavior by Carolyn Stull Pg 59.
Published July 01, 2008
Q&A on hiking trail building, design and maintenance.
The best answer that you will get for how wide a trail should be is “It depends.”
Animas and Berg Parks are home to a network of trails along the Animas River in Farmington. These trails run along the river’s edges, wind through groves of native cottonwoods, and cross the Animas River by bridge at two points.
The 62-mile rail trail in the northern Lower Peninsula is managed by the Michigan Department of Natural Resources. It is open to bicycling, walking, and horseback riding, as well as snowmobiles in the winter months.
Spanning nearly 400 miles across eight counties, this backcountry trail system provides for a variety of trail uses, including all-terrain vehicle use, mountain biking, hiking, and horseback riding.
This 5.6 mile section of the Niobrara River offers visitors a unique scenic recreational floating experience. The river cuts a deep canyon in the limestone rocks that underlie Nebraska’s famed Sand Hills.