Cover Crop Selection for Arkansas Soils

Unprotected stream banks erode quickly under the pressure of livestock, foot traffic, and stormwater. Sediment washes into waterways, carrying nutrients and pesticides that degrade water quality for miles downstream. A well-established buffer intercepts that runoff before it reaches the water, filtering pollutants through root systems and soil biology. In the Arkansas River Valley, where agricultural runoff is a primary water quality concern, buffers are among the highest-impact practices a landowner can implement.

Native species are always preferred — they are adapted to local soils, require no irrigation once established, and provide the greatest wildlife value. For Sebastian County, recommended tree species include sycamore, cottonwood, and river birch for the wet zone closest to the water. Shrubs such as buttonbush, elderberry, and native willows work well in the mid-zone. The upland edge can be stabilized with native warm-season grasses like switchgrass and big bluestem.

A minimum buffer width of 35 feet is recommended for basic erosion control. For water quality benefits, 50–100 feet is more effective. On steeper slopes or highly erodible soils, wider buffers provide proportionally greater protection. The buffer should run continuously along the entire length of the waterway — gaps allow concentrated flow that can undermine the entire system.

Site preparation is critical. Remove existing invasive vegetation before planting, and consider a weed barrier or mulch layer around young trees for the first two growing seasons. Water transplants during dry spells in the first year. Once established — typically after two to three growing seasons — native buffers require minimal maintenance. Annual inspection for invasive species and any erosion breaches is sufficient for most sites.

Native plants have co-evolved with local soils, climate, insects, and wildlife over thousands of years. They require no fertilizer or irrigation once established, support far greater insect diversity than non-native ornamentals, and provide the specific food sources — seeds, berries, nectar, and larval host plants — that native wildlife depend on. A landscape dominated by native plants is a functioning ecosystem, not just a garden.

Eastern redbud is one of the most valuable native trees for pollinators — its early spring flowers are a critical nectar source before most other plants bloom. Bur oak and Shumard oak provide mast crops for deer, turkey, and dozens of songbird species. Possumhaw holly offers winter berries that sustain cedar waxwings and American robins through cold snaps. Roughleaf dogwood is a multi-stemmed shrub that thrives in disturbed areas and produces white berries consumed by over 40 bird species.

Purple coneflower is perhaps the most recognizable native wildflower of the region — its seed heads feed goldfinches through winter. Black-eyed Susan blooms prolifically on disturbed soils and roadsides. Wild bergamot and bee balm attract hummingbirds and native bees. Ironweed's deep purple late-summer flowers are a magnet for monarchs and swallowtails. For shaded sites, wild ginger and mayapple form dense groundcover that suppresses invasive species.

Native warm-season grasses are the backbone of prairie and savanna restoration. Big bluestem and indiangrass are the dominant species of the tallgrass prairie that once covered much of western Arkansas. Little bluestem is more drought-tolerant and works well on thin, rocky soils. For wet areas and stream margins, river oats and various native sedges provide erosion control and excellent cover for ground-nesting birds.

The most common water quality problems in Sebastian County ponds are excess nutrients (from livestock waste or fertilizer runoff), low dissolved oxygen, and turbidity from suspended clay particles. Nutrients fuel algae blooms that deplete oxygen when they die and decompose. Establishing a vegetated buffer around the pond perimeter — even a 10-foot strip of native grasses — dramatically reduces nutrient inputs from surrounding land.

Aeration is the single most effective management tool for pond health. Surface aerators or bottom diffusers increase dissolved oxygen, reduce stratification, and accelerate decomposition of organic matter on the pond floor. For ponds over half an acre, a bottom diffuser system running on a small air compressor is the most efficient option. Solar-powered aerators are increasingly cost-effective and eliminate the need for electrical service to the pond.

The classic Arkansas pond stocking combination is largemouth bass and bluegill, with channel catfish as a secondary species. The standard ratio is 100 bass to 500 bluegill per acre. Overharvesting bass — the primary predator — leads to stunted bluegill populations that crowd out other species. Harvest records and periodic electrofishing surveys help maintain a balanced population. Contact the Arkansas Game and Fish Commission for current stocking recommendations and assistance.

Some aquatic vegetation is beneficial — it provides fish habitat, stabilizes banks, and absorbs nutrients. Problems arise when vegetation covers more than 20–30% of the pond surface. At that point, it begins to compete with fish for oxygen at night and impedes fishing access. Mechanical removal is preferred over herbicides for most situations. Grass carp (triploid, sterile) are an effective biological control for submersed vegetation and are legal in Arkansas with a permit.

The slake test is the simplest field indicator of aggregate stability — the soil's ability to hold its structure when wet. Drop a dry soil clod about the size of a golf ball into a jar of water and observe it for five minutes. Healthy soil with good aggregate stability will hold its shape or break slowly into smaller aggregates. Degraded soil will immediately disperse into a muddy cloud. This single test tells you more about your soil's biological health than most lab analyses.

Infiltration rate measures how quickly water moves into the soil — a direct indicator of compaction and biological activity. Cut both ends off a coffee can, push it two inches into the soil, fill it with water, and time how long it takes to drain. Healthy soil should infiltrate one inch of water in under 30 minutes. Rates slower than that indicate compaction or surface sealing that will cause runoff and erosion during rain events.

Earthworms are the most visible indicator of soil biological health. Dig a one-foot cube of soil and count the earthworms. Ten or more worms indicates good biological activity. Fewer than five suggests low organic matter, compaction, or chemical inputs that are suppressing the soil food web. Earthworm populations respond quickly to management changes — cover crops and reduced tillage typically produce measurable increases within two to three seasons.

Darker soil generally indicates higher organic matter — the decomposed plant and animal material that drives soil fertility, water retention, and structure. While color alone is not a precise measurement, a dramatic color difference between your topsoil and a neighboring field or an undisturbed reference area tells you something important about your management history. Organic matter below 2% is a warning sign for Sebastian County soils; above 4% indicates excellent biological health.

A pollinator strip is a narrow band of flowering plants — typically 10–30 feet wide — planted along field edges, waterways, or fence lines. The most effective strips include a mix of early, mid, and late-season bloomers to provide continuous forage from April through October. Recommended species for Sebastian County include partridge pea, purple coneflower, black-eyed Susan, wild bergamot, and native sunflowers. Strips can be established from seed mixes available through NRCS cost-share programs.

Hedgerows — linear plantings of shrubs and small trees along field boundaries — provide nesting habitat, overwintering sites, and food sources that pollinator strips alone cannot offer. Native shrubs like roughleaf dogwood, elderberry, and native plums provide berries for birds and nesting cover for ground-nesting bees. Hedgerows also serve as windbreaks, reducing soil moisture loss and crop stress during dry periods.

Seventy percent of native bee species nest in the ground, and another 30% nest in hollow stems or wood cavities. Maintaining areas of bare or sparsely vegetated ground — south-facing slopes, field corners, or disturbed areas — provides critical nesting habitat for ground-nesting bees. Brush piles from pruning or land clearing provide nesting sites for cavity-nesting species and overwintering habitat for beneficial insects.

Even the best habitat is undermined by poorly timed pesticide applications. Avoid applying insecticides during bloom periods, and never spray when pollinators are actively foraging (typically between 10 AM and 4 PM on warm days). If applications are necessary, choose products with lower bee toxicity and apply in the evening when bees have returned to their nests. Buffer zones around pollinator strips and hedgerows should be respected during all spray operations.

A swale is a shallow, vegetated channel designed to slow and spread water across a slope rather than letting it concentrate and accelerate. Paired with a berm on the downhill side, a swale captures runoff and holds it long enough to infiltrate. On gentle slopes, swales can be constructed with a tractor and box blade. They should follow the contour of the land precisely — even a slight grade will cause water to concentrate at the low end and defeat the purpose.

A rain garden is a shallow depression planted with deep-rooted native plants, designed to capture runoff from roofs, driveways, or compacted areas. The plants and their root systems create channels for water to move quickly into the soil. A properly sized rain garden should drain completely within 24–48 hours — standing water longer than that indicates either poor soil drainage or an undersized design. Rain gardens are particularly effective near buildings and in areas where traditional drainage infrastructure is impractical.

For larger properties with significant runoff volumes, retention ponds (permanent water) or detention basins (dry between storms) provide storage capacity that protects downstream areas from flood peaks. Retention ponds double as wildlife habitat and livestock water sources. Detention basins can be planted with native wetland vegetation that filters nutrients from the captured water before it infiltrates or is released slowly.

Every square foot of impervious surface — rooftops, concrete, compacted gravel — generates runoff that would otherwise infiltrate. Gravel driveways can be improved with permeable gravel or open-cell pavers. Roof runoff can be directed to rain gardens or cisterns rather than draining directly to streams. Even small changes in how water is directed off buildings and paved areas can meaningfully reduce the runoff load on downstream land.

Successful composting depends on balancing carbon-rich materials (browns) with nitrogen-rich materials (greens) in roughly a 25:1 to 30:1 ratio by weight. Browns include dry leaves, straw, wood chips, and cardboard. Greens include fresh grass clippings, kitchen scraps, manure, and green plant material. Too much carbon and the pile decomposes slowly; too much nitrogen and it becomes anaerobic and smelly. A simple rule of thumb: three parts browns to one part greens by volume works well for most farm situations.

Hot composting — maintaining pile temperatures between 130°F and 160°F — produces finished compost in 30–60 days and kills weed seeds and pathogens. The pile needs to be at least three feet in each dimension to hold heat, and it needs to be turned every three to five days to maintain oxygen levels and even decomposition. A compost thermometer is a worthwhile investment. When the pile no longer reheats after turning, it is ready to cure for two to four weeks before use.

For larger volumes — livestock manure, crop residues, or municipal organic waste — windrow composting is the standard approach. Windrows are elongated piles typically four to six feet tall and eight to twelve feet wide, turned with a tractor or dedicated windrow turner. On a working farm, a simple three-bin system using concrete blocks or wooden pallets allows continuous production: one bin filling, one actively composting, one curing.

For general soil improvement, apply one to three inches of finished compost and incorporate it into the top six inches of soil. For severely degraded soils, higher rates of three to five inches may be warranted in the first year. Compost can also be applied as a surface mulch without incorporation — particularly effective in no-till systems where it feeds soil biology from the top down. Avoid applying more than five inches in a single season, as excess nitrogen can leach into groundwater.

Several native species are rarely browsed by deer under normal population pressures. Aromatic plants are generally avoided — wild bergamot, bee balm, and mountain mint are seldom touched. Spiny or rough-textured plants like native thistles, ironweed, and roughleaf dogwood are also low on the deer menu. Ferns — particularly Christmas fern and cinnamon fern — are almost never browsed and make excellent groundcover under established trees.

Trees and shrubs are most vulnerable in their first two years, before they develop bark thick enough to resist browsing. Individual tree tubes — plastic cylinders staked around each transplant — are the most effective protection for young trees and pay for themselves quickly by eliminating replacement costs. For larger areas, a temporary electric fence during the establishment period is cost-effective. Once trees reach six to eight feet in height, deer browse pressure drops significantly.

Planting resistant species as a perimeter around more vulnerable ones can reduce browse pressure on the interior. Dense plantings also help — deer are less likely to push into a thick planting than to browse along an open edge. Avoid planting in long, thin strips along field edges where deer can easily access every plant from both sides. Compact, irregular plantings with multiple species are more resilient than monoculture rows.

Commercial deer repellents can be effective for small, high-value plantings. Products containing putrescent egg solids are among the most effective and longest-lasting. Repellents must be reapplied after rain and as new growth emerges — they protect only the tissue that was treated at the time of application. For large-scale restoration plantings, repellents are generally not cost-effective compared to physical protection or species selection.

The most common bat species in Sebastian County are the big brown bat, little brown bat, and evening bat. All three are colonial roosters that readily use artificial bat houses. The Brazilian free-tailed bat — famous for the massive colonies at Carlsbad Caverns — also migrates through the region in summer and will use bat houses near water. All Arkansas bat species are insectivorous and protected under state and federal law.

Bat houses must meet specific design criteria to be used consistently. The interior chamber should be 3/4 inch wide — narrow enough to retain heat but wide enough for bats to move. Interior surfaces must be roughened (scored or covered with plastic mesh) so bats can grip them. The house should be at least 24 inches tall with multiple chambers. Avoid houses with perch boards on the outside — these are a design feature that bats do not use and that predators can exploit.

Location is the most important factor in bat house success. Mount houses on poles or buildings rather than trees — trees provide too much shade and too many predator access points. The house should receive at least six to eight hours of direct sun per day; in Sebastian County's climate, south or southeast exposure is ideal. Mount at least 12–15 feet off the ground. Proximity to water dramatically increases occupancy rates — houses within a quarter mile of a pond, stream, or wetland are colonized far more quickly than those in dry upland areas.

Most bat houses are not occupied in their first year. Bats are cautious about new roost sites and typically scout a house for one to two seasons before committing. Monitoring for guano accumulation below the house is the easiest way to confirm occupancy. Once a colony establishes, it will return year after year and grow over time. Do not disturb an occupied house — bats are protected, and disturbance during the maternity season (May through August) can cause colony abandonment.

When a slope has been disturbed — by grading, construction, or logging — temporary stabilization is the first priority. Erosion control blankets (ECBs) are woven or bonded mats of straw, coconut fiber, or wood excelsior that protect bare soil from raindrop impact and surface flow while vegetation establishes. They are stapled to the slope and seeded through or under them. For very steep slopes or areas with concentrated flow, heavier-duty turf reinforcement mats (TRMs) provide more durable protection.

Hydromulch — a slurry of wood fiber, seed, fertilizer, and tackifier sprayed onto bare slopes — is effective for large areas where blanket installation is impractical. The tackifier bonds the mulch to the soil surface, providing immediate protection while seed germinates. Hydromulch is particularly useful on road cuts and embankments. It is less effective than blankets on slopes steeper than 3:1 or in areas with concentrated flow.

Permanent stabilization requires deep-rooted vegetation that can anchor soil against both surface erosion and shallow mass movement. Native warm-season grasses — big bluestem, indiangrass, and switchgrass — are ideal for most slope situations in Sebastian County. Their root systems extend four to eight feet deep, far exceeding the depth of most erosion processes. For very steep or rocky slopes, native legumes like partridge pea and wild senna establish quickly and fix nitrogen to support subsequent grass establishment.

On slopes longer than 100 feet, terraces or grade breaks interrupt the flow path and prevent runoff from accelerating to erosive velocities. Broad-based terraces — gentle, nearly level benches cut into the slope — are the most durable option and can be maintained with farm equipment. Simpler rock check dams or log wattles installed across drainage channels provide grade breaks at lower cost and with less disturbance, though they require more frequent maintenance.

The most common water quality concerns in Sebastian County fall into three categories: agricultural (nitrates, phosphorus, pesticides, and coliform bacteria from livestock waste), geological (naturally occurring arsenic and iron in some groundwater formations), and infrastructure-related (lead from older plumbing, chlorination byproducts in municipal water). Pond and surface water quality is most commonly affected by nutrient loading from surrounding land use, while well water quality depends heavily on the depth and geology of the aquifer.

For drinking water wells, the minimum recommended test panel includes total coliform bacteria, nitrates, pH, hardness, and iron. If you are in an area with known agricultural activity, add a pesticide screen and arsenic. For livestock water, coliform bacteria and nitrates are the primary concerns — both can cause health problems in cattle and poultry at levels that would not affect humans. For ponds, a basic water quality panel including pH, dissolved oxygen, total phosphorus, and total nitrogen gives you the information needed to manage the system effectively.

Sample collection technique matters as much as the analysis itself. For well water, run the tap for two to three minutes before collecting to flush standing water from the pressure tank and lines. Use only the sterile containers provided by the lab — never substitute household containers. For pond samples, collect from mid-depth at multiple locations and combine into a single composite sample. Label all samples clearly with date, time, location, and your contact information, and get them to the lab within 24 hours of collection.

The University of Arkansas Cooperative Extension Service operates a water testing laboratory that serves Sebastian County residents at subsidized rates. The Arkansas Department of Health also provides well water testing services. Private certified labs are available for more comprehensive testing panels. A basic drinking water panel typically costs $30–$80; a comprehensive agricultural water panel runs $100–$200. Contact our office for current lab contacts and any available cost-share programs for water quality testing.