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Rill

A rill is a small, shallow erosion channel typically less than 30 cm deep and often exceeding 10 m in length, formed by the concentrated flow of runoff water on bare or sparsely vegetated slopes.^[1] These features develop when water accelerates, detaching and transporting soil particles without necessarily following broader drainage patterns, and they are easily smoothed by tillage or natural processes.^[1] Rills represent an intermediate stage in water erosion, bridging sheet erosion—where thin layers of topsoil are uniformly removed—and more severe gully erosion.^[2] Rills form primarily through high-intensity rainfall or snowmelt on erodible soils, where overland flow concentrates into rivulets due to factors like slope steepness, soil texture, and lack of vegetation cover.^[2] The process begins with raindrop impact detaching soil particles in inter-rill areas, creating turbulent shallow flows that deliver sediment to incipient channels; these evolve into defined rills via headcut advancement and network expansion.^[3] Common in agricultural fields, rills often appear as finger-like incisions after sheet erosion, with water depths ranging from millimeters to several centimeters during active flow.^[1] Unlike larger gullies, which exceed 0.3 m in depth and involve complex subsurface processes, rills remain superficial and reversible, though unchecked they can deepen and connect into gully systems, exacerbating soil loss.^[2] Rill erosion significantly reduces soil productivity by stripping nutrient-rich topsoil, exposes subsoils to further degradation, and contributes to sediment delivery in waterways, impacting water quality and downstream ecosystems.^[3] Management strategies, such as contour farming and cover cropping, aim to disrupt rill initiation by minimizing runoff concentration and enhancing soil stability.^[1]

Definition and Characteristics

Definition

A rill is a shallow, incised channel in soil or unconsolidated sediment, typically less than 0.3 m deep and wide, formed by concentrated overland water flow during episodic events like rainfall.^[4] This geomorphological feature represents concentrated surface runoff that erodes the land surface in narrow paths, distinguishing it from broader, unchanneled flow.^[5] The term "rill" originates from Dutch ril or Low German rille, meaning a small stream or groove, and was adapted into English by the 16th century.^[6] In the fields of hydrology and soil science, rills are defined as an intermediate stage of erosion between diffuse sheet erosion, where water flows evenly over the surface, and deeper gully erosion.^[7] Key distinctions of rills include their limited scale, with depth and width generally under 0.3 m, unlike larger erosional forms such as gullies.^[8] They exhibit an ephemeral nature, often forming and partially eroding seasonally with rainfall events, and can typically be obliterated by routine tillage.^[5] In contrast to broad sheet flow, rills involve concentrated flow that incises the soil, marking the onset of channelized erosion.^[9]

Physical Properties

Rills exhibit a range of morphological features that define their physical structure. Typical cross-sectional shapes include V-shaped forms in early development stages, transitioning to U-shaped or trapezoidal profiles as erosion progresses and widens the channel base.^[10] These shapes arise from the balance between flow incision and sidewall slumping, with V-shapes predominant in cohesive soils and more rounded forms in less resistant substrates. Rill lengths generally span from a few meters to tens of meters or more in field settings, with experimental observations reaching up to 10-20 m in longer flumes under controlled conditions.^[11] In agricultural fields, rill lengths typically range from several meters to over 100 m, depending on slope length and runoff conditions.^[12] Sinuosity, or the degree of meandering, varies along rill paths, with curved patterns emerging where flow encounters obstacles or varying substrate resistance, often resulting in tortuous rather than straight alignments. Rills frequently form interconnected networks, where smaller tributaries merge into main channels, creating dendritic patterns that enhance drainage efficiency on slopes. The physical properties of rills are closely tied to interactions with soil and substrate conditions. Soil type significantly influences incision depth and overall form; for instance, loamy soils with higher clay content support deeper incisions due to greater cohesion, whereas sandy soils lead to shallower, wider channels prone to rapid widening. Vegetation cover plays a key role in rill stability, with sparse cover promoting persistence by minimizing flow interception and root reinforcement, allowing channels to remain active over multiple events. Slope angle further modulates morphology, as steeper gradients (e.g., >15%) yield narrower and deeper rills through increased shear stress and faster flow, contrasting with gentler slopes that favor broader, shallower forms. Rill properties show notable variability across environments. In urban settings, rills tend to be shorter and more discontinuous due to impervious paved surfaces that concentrate and redirect runoff, limiting channel extension compared to rural agricultural fields where longer rills develop across bare or tilled soils. Representative measurements include average flow velocities ranging from 0.1 to 3 m/s, influenced by channel geometry and discharge,^[13] and typical discharge rates on the order of 0.008 to 1.8 liters per second in small rills during moderate runoff events.

Formation Processes

Initiation Mechanisms

Rill initiation begins when the shear stress exerted by overland flow surpasses the critical shear stress of the soil, leading to the detachment of soil particles and the onset of concentrated flow channels. Critical shear stress values typically range from 1.33 to 2.63 Pa for many soils, with an average of about 1.94 Pa, and are inversely related to slope steepness but independent of rainfall intensity.^[14] When flow velocities exceed approximately 0.1 m/s, this threshold is often reached, causing initial particle dislodgement and the transition from sheet flow to localized erosion.^[13] High rainfall intensity and duration play key roles in this process by generating sufficient runoff volume to concentrate diffuse sheet flow into rivulets, particularly during intense storms that exceed soil infiltration capacity.^[15] The primary hydrodynamic triggers for rill formation involve infiltration-excess overland flow, known as the Hortonian mechanism, where rainfall intensity exceeds the soil's infiltration rate, producing shallow surface runoff that erodes and channels the soil surface.^[13] In contrast, saturation-excess overland flow occurs when the soil profile becomes fully saturated from below or prolonged wetting, leading to runoff, but this mechanism is less dominant for rill initiation compared to Hortonian flow in upland areas with moderate to high rainfall. An additional trigger is initial fingering instability, where heterogeneous soil properties—such as variations in texture, porosity, or microtopography—cause uniform overland flow to break into preferential small channels, amplifying local shear stress and promoting rill development.^[16] Laboratory and field observations have confirmed these thresholds through controlled experiments simulating overland flow on tilled soils. Early 20th-century studies, including those by Ellison (1947), demonstrated that rill onset occurs at flow rates exceeding approximately 2 L/min per unit width, marking the transition from interrill to concentrated erosion.^[17] More recent flume experiments across various U.S. soils report critical flow rates ranging from 0.002 to 0.217 L/s (equivalent to 0.12-13 L/min), with rill incision initiating when these rates combine with slopes greater than 2-5% to produce sufficient hydraulic force.^[18] Field studies under natural rainfall further validate that rill formation distances decrease with increasing slope and runoff, often starting within 5-10 m on bare slopes exceeding 5%.^[14]

Influencing Factors

The development and prevalence of rills are significantly influenced by climatic factors, particularly rainfall patterns and seasonal variations. High-intensity storms accelerate rill formation by generating concentrated overland flow that incises the soil surface, with extreme precipitation events contributing significantly to annual erosion in vulnerable regions like semi-arid areas.^[19] In semi-arid environments, such storms in the Loess Plateau of China have been shown to stimulate rill development on slopes by increasing runoff erosivity.^[20] Seasonal wet-dry cycles further exacerbate this, as consecutive wet days can increase rill erosion rates by 0.16 t·ha⁻¹·yr⁻¹ per additional day.^[19] These patterns highlight the role of intense wet seasons in rill formation. Topographic and edaphic factors play a critical role in controlling rill incision, with slope gradient and soil erodibility being primary determinants. Rill formation is optimal on slopes of 5-25%, where increased flow velocity and shear stress promote channel incision without excessive dispersion, as observed in loessial hillslopes where erosion rates peak around 10-15° gradients.^[21] Steeper gradients beyond this range may lead to gully development, while gentler slopes favor sheet erosion. Soil erodibility, influenced by texture and cohesion, is highest in silty soils with low organic matter and weak aggregate stability, which detach easily under runoff shear, contributing to rill initiation in up to 80% of cases on cultivated lands.^[22] Land use practices that expose such soils, like bare fallow periods, amplify vulnerability by reducing surface protection.^[23] Anthropogenic activities intensify rill prevalence through alterations to surface hydrology and soil structure. Agricultural practices, such as tillage along upslope furrows, concentrate runoff and promote rill networks by directing flow into linear paths, increasing erosion by 2-3 times compared to contour tillage on slopes.^[24] Deforestation removes root reinforcement, elevating rill erosion risk in formerly vegetated areas by up to 50% due to diminished soil cohesion and increased bare soil exposure.^[23] Urbanization exacerbates this via impervious surfaces like roads and buildings, which boost runoff volumes by 2-6 times during storms, channeling excess water into erodible peri-urban soils and accelerating rill incision.^[25] These human-induced changes often compound natural factors, leading to widespread rill expansion in modified landscapes.^[26]

Erosion Dynamics

Hydraulic and Sediment Transport Processes

In established rills, the hydraulic regime is characterized by concentrated overland flow that exerts significant shear on the channel bed, driving soil detachment and transport. Flow velocity V is commonly estimated using Manning's equation:

V = \frac{1}{n} R^{2/3} S^{1/2}

where n is the Manning's roughness coefficient (typically 0.03–0.1 for rill beds, depending on soil and vegetation), R is the hydraulic radius (cross-sectional area divided by wetted perimeter), and S is the bed slope. This empirical relation, derived from open-channel flow principles, has been validated in laboratory and field studies of rill hydraulics, though it may overestimate velocities in actively eroding channels due to variable roughness from sediment interactions.^[27]^[28] The primary force for soil detachment is the bed shear stress \tau, calculated as:

\tau = \gamma R S

where \gamma is the specific weight of water (approximately 9800 N/m³). This stress increases with flow depth and slope, often exceeding critical thresholds (0.5–5 Pa for most soils) in rills steeper than 5%, promoting incision. When \tau surpasses the soil's critical shear stress, detachment rates can reach 0.001–6 kg/m²/s under varying storm flows in flume and field experiments.^[28]^[29]^[30] Sediment transport in rills occurs predominantly as bedload, involving rolling, sliding, and saltation of particles larger than 0.1 mm, which constitutes 60–90% of total load in shallow flows (depths <0.1 m). Suspended load, comprising finer silt and clay (<0.06 mm), is limited by low flow turbulence but can increase with higher velocities (>0.8 m/s). Transport capacity is often modeled using adaptations of the Hjulström curve tailored to rill scales, where erosion initiates at velocities exceeding ~0.5 m/s for medium sands and silts, reflecting higher competence than in sheet flow due to concentrated energy. Deposition prevails at velocities below this threshold, as settling velocities (0.01–0.1 m/s for fine particles) outpace turbulent diffusion, leading to net aggradation in low-gradient sections. These thresholds align with field observations where rill sediment yields peak at 1–10 t/ha during events with peak flows >0.2 m³/s.^[31]^[28]^[32] Feedback mechanisms amplify or stabilize rill evolution through interactions between hydraulics and sediment dynamics. Headcut formation creates abrupt vertical steps (0.05–0.5 m high) at points of flow acceleration, often at soil layer interfaces, where supercritical flow (Froude number >1) plunges over the lip, generating high shear and upstream knickpoint migration at rates of 0.001–0.005 m/s. This process erodes cohesive soils rapidly, contributing up to 50% of rill sediment in heterogeneous profiles, though upstream sediment supply can reduce migration by 20–70% via energy dissipation. Conversely, rill armoring develops as selective transport removes fines, leaving a pavement of coarser gravel or aggregates (d50 >2 mm) that elevates critical shear stress by 2–5 times and increases roughness (n >0.05), thereby limiting further incision and stabilizing channels during waning flows. These loops highlight the self-regulating nature of rill systems, where initial incision promotes transport until thresholds for stabilization are met.^[33]^[34]

Evolution from Sheet to Gully Erosion

The evolution of erosion from sheet flow to rill formation and subsequently to gully incision represents a progressive concentration of surface runoff that amplifies soil detachment and transport. Sheet erosion begins as uniform, thin overland flow across slopes, typically resulting in minimal soil loss of less than 1 mm per event due to diffuse hydraulic shear and raindrop impact, without forming distinct channels.^[35] As flow paths converge in subtle depressions or micro-topographic lows, concentrated streamlets emerge, incising the soil surface to create rills—narrow channels generally less than 30 cm deep and 10-30 cm wide, with annual soil loss rates of 1-10 tons per hectare in agricultural settings, accounting for 50-70% of total hillslope erosion.^[9]^[36] This transition marks a shift from laminar, low-velocity sheet flow to turbulent, higher-velocity concentrated flow, enhancing erosive power through increased shear stress.^[37] Rill networks develop through interconnectivity, where individual incisions merge via bifurcation, cross-grading, and micropiracy, forming dendritic patterns that funnel water and sediment downslope.^[9] These networks increase discharge volume and velocity, promoting further incision and the coalescence of rills into larger tributaries that evolve into gullies—channels exceeding 30 cm in depth with permanent headwalls and banks, often reaching 0.5-30 m deep over time.^[36] Knickpoints, steep local gradients at rill confluences or headcuts, play a critical role by facilitating upstream migration through plunge-pool scour and waterfall undercutting, propagating erosion retrogressively and linking rill systems to broader drainage networks.^[38] This merging amplifies erosive capacity, as combined flows exceed soil shear strength, leading to sidewall collapse and channel widening.^[39] Temporal dynamics of this progression span short- and long-term scales, influenced by rainfall intensity, slope, and soil properties. In single storm events, rills can deepen by several centimeters—such as up to 4 cm in post-fire landscapes—through rapid headcut advance and sediment evacuation.^[40]^[41] Over longer periods, repeated events culminate in proto-gully formation; in vulnerable regions like China's Loess Plateau, ephemeral gullies evolve from rill networks over decades, with average annual length increases of 1.66 m and erosion volumes of 743 m³ per year observed across 12-year monitoring, reflecting cumulative incision in erodible silty soils.^[42] This long-term development transforms transient rills into entrenched gullies, altering landscape hydrology and sediment budgets.^[9]

Significance and Impacts

Environmental Consequences

Rill erosion significantly contributes to soil degradation by removing nutrient-rich topsoil, resulting in the loss of organic matter and essential nutrients such as nitrogen and phosphorus. Studies indicate that rill erosion can lead to annual losses of up to 106.44 kg ha⁻¹ of soil organic matter in semiarid farmlands, with eroded sediments often retaining only 20-25% of their original carbon content due to selective transport of finer particles.^[43]^[44] This depletion impairs soil structure and fertility, promoting desertification in arid and semiarid zones where repeated events exacerbate land degradation and reduce vegetation cover.^[45] Additionally, the fragmentation of soil habitats from rill incision disrupts biodiversity, particularly affecting soil organisms like earthworms and microbes that rely on stable topsoil layers for survival and nutrient cycling.^[46] Hydrological alterations induced by rill erosion include increased surface runoff due to reduced soil infiltration capacity, which can diminish groundwater recharge and heighten the risk of flash floods. In rill-prone landscapes, concentrated flow paths accelerate water velocity, leading to higher runoff volumes compared to uneroded areas during intense rainfall events.^[47] This process not only lowers aquifer replenishment—potentially reducing recharge rates by over 30% in degraded catchments—but also intensifies downstream flooding by delivering sediment-laden water more rapidly.^[48]^[49] Case studies highlight the landscape-scale impacts of rill erosion. In the badlands of Spain's middle Ebro Basin, rill processes contribute approximately 8-13% to total sediment yield on steep clay slopes, accounting for 8-17 mm yr⁻¹ of erosion and amplifying overall hillslope degradation in Mediterranean climates.^[50] Globally, rills are a major contributor to hillslope soil loss, driving a substantial portion of the estimated 20-30 gigatons of annual soil erosion by water from terrestrial systems to aquatic environments (as of 2021).^[51]^[52] These effects underscore rill erosion's role in broader ecosystem disruptions, with indirect ties to agricultural productivity declines through sustained soil impoverishment.^[47]

Agricultural and Human Effects

Rill erosion significantly impacts agricultural productivity by removing nutrient-rich topsoil and exposing less fertile subsoil, leading to reduced crop yields. In row-crop fields, yield losses from rill erosion can reach up to 46% in affected areas compared to uneroded sections, primarily due to soil relocation and nutrient depletion.^[53] This exposure of subsoil, which often has unfavorable conditions for plant growth, further diminishes soil fertility unless actively restored through management practices.^[54] Beyond crop losses, rill erosion damages infrastructure such as roads and trails by incising surfaces and widening channels, which can undermine stability and trigger slope failures. On unpaved roads, rill formation is a primary cause of structural degradation, with erosion rates accelerating under heavy rainfall and contributing to overall road failure.^[55] Additionally, the sediment mobilized by rills increases loading in nearby waterways, degrading water quality and adversely affecting fisheries through gill irritation, reduced visibility for feeding, and smothering of aquatic habitats.^[56]^[57] The economic repercussions of rill erosion are substantial, with global costs tied to lost agricultural value and increased input needs. Erosion-induced increases in fertilizer use alone account for annual expenses of US$33–60 billion for nitrogen and US$77–140 billion for phosphorus worldwide (as of 2015), according to FAO assessments.^[58] More recent estimates indicate overall annual economic losses from soil erosion around USD 400 billion globally (as of 2024).^[59] Historical events, such as the Dust Bowl in the 1930s, illustrate how water erosion processes including rills exacerbated soil loss on overcultivated lands, amplifying drought effects and contributing to widespread farm failures and economic hardship across the Great Plains.^[60]

Assessment and Management

Measurement Techniques

Field methods for quantifying rill erosion primarily involve direct in-situ measurements to capture morphological changes and sediment yields over time. Stake profiling entails installing reference stakes along transects perpendicular to rill channels to establish baseline cross-sectional profiles, with subsequent surveys using rulers or calipers to measure depth and width increments after erosion events, enabling precise tracking of incision and headcut advancement.^[61] Erosion pins, thin metal rods inserted into the soil perpendicular to the surface, provide a simple yet effective way to monitor vertical incision rates, typically recording changes on the order of millimeters per storm event by measuring exposed pin lengths before and after rainfall.^[62] Runoff plot experiments complement these by delineating bounded field areas, often 10-100 m², with borders that channel overland flow and eroded sediment into collection traps; sediment yield is then quantified by drying and weighing samples, offering insights into rill-initiated transport rates under natural or simulated rainfall.^[63] Remote sensing techniques have advanced the spatial and temporal assessment of rill erosion, particularly for larger scales where field methods are labor-intensive. Drone-based photogrammetry generates high-resolution digital elevation models (DEMs) by stitching overlapping aerial images, allowing volumetric calculations of rill cross-sections with accuracies reaching ±1 cm through structure-from-motion algorithms.^[64] LiDAR-equipped drones enhance this by providing direct 3D point clouds that penetrate vegetation for bare-earth modeling, facilitating detailed mapping of rill networks and erosion depths in complex terrains.^[65] At broader basin levels, satellite imagery such as Landsat multispectral data detects rill networks via spectral indices like the normalized difference vegetation index (NDVI) combined with texture analysis, identifying erosion-prone areas through changes in soil exposure over multi-year periods.^[66] Modeling tools integrate these measurements into predictive frameworks for rill erosion assessment. Adaptations of the Revised Universal Soil Loss Equation (RUSLE) estimate average annual soil loss A as A = R \cdot K \cdot LS \cdot C \cdot P, where the topographic LS factor specifically accounts for rill formation on slopes by incorporating flow accumulation and steepness, often calibrated with field data to refine predictions for rill-dominated landscapes.^[67] Geographic Information Systems (GIS) enable spatial prediction by overlaying RUSLE factors with DEMs derived from remote sensing, simulating rill erosion hotspots across watersheds while validating outputs against plot-scale observations.^[68]

Prevention Strategies

Vegetative measures play a crucial role in preventing rill formation by enhancing soil cover, improving infiltration, and reducing surface runoff velocity. Cover crops, such as rye or legumes planted between main crop seasons, provide living ground cover that intercepts rainfall, absorbs excess water through root systems, and stabilizes soil aggregates, thereby decreasing sheet and rill erosion by up to 90% and sediment transport by 75% in agricultural fields.^[69] Contour planting, where crops are aligned along the contour lines of slopes rather than up and down, slows water flow and promotes even distribution of runoff, reducing soil erosion by approximately 50% on gentle slopes compared to straight-row farming.^[70] Mulching with organic materials like straw or wood chips further aids prevention by protecting bare soil from raindrop impact, increasing water infiltration rates by 29-77% depending on application thickness, and minimizing evaporation to maintain soil moisture.^[71] Structural controls offer engineered solutions to interrupt concentrated flow and reinforce soil stability, effectively mitigating rill initiation and progression. Terracing involves constructing level benches or steps on slopes to shorten flow paths and trap sediment, which can reduce rill erosion risks in hilly agricultural areas by diverting and slowing runoff.^[70] Check dams, typically made of rock or logs placed across drainage channels, decrease flow velocity in potential rill paths, allowing sediment to settle and preventing channel incision, with applications particularly effective in swales and ephemeral streams.^[72] No-till farming, which avoids plowing and leaves crop residues on the surface, preserves soil structure by minimizing disturbance to organic matter and pore spaces, reducing sheet and rill erosion by 70% or more relative to conventional tillage systems.^[73] Policy and monitoring frameworks support widespread adoption of these strategies through integrated watershed management, emphasizing coordinated efforts across scales to address erosion holistically. The EU Water Framework Directive provides guidelines for member states to integrate soil protection measures, including erosion control practices, into river basin management plans to achieve good ecological status and reduce sediment delivery to water bodies.^[74] Cost-benefit analyses of such preventive investments, including vegetative and structural interventions, demonstrate strong returns, with average economic benefits exceeding costs by 176% through reduced restoration needs and improved productivity, underscoring the value of proactive implementation.^[75]

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[49]
Rill Erosion Reduces Current Crop Yields
Yield losses up to 46 percent were measured in the rilled areas compared to nonrilled areas. Even shallow rills appeared to cause a yield loss, apparently ...Missing: 20-50% | Show results with:20-50%
[50]
Soil erosion: An agricultural production challenge
Rill erosion occurs during heavy rains, when small rills form over an entire hillside, making farming difficult. Gully erosion makes gullies, some of them huge, ...
[51]
[PDF] Factors Affecting Erosion in Unpaved Roads - Avestia
Apr 9, 2019 · Bulk of the 71 studies found that inter-rill and rill erosion were the most prominent types of erosion that cause most of earth road failures.
[52]
Water pollution: erosion and sedimentation - Canada.ca
Sep 10, 2017 · Suspended sediment in high concentrations irritates the gills of fish, and can cause death. Sediment can destroy the protective mucous covering ...
[53]
Soil Erosion and Sediment Pollution - Lake Superior Streams
Suspended sediment decreases the penetration of light into the water. This affects fish feeding and schooling practices, and can lead to reduced survival.Missing: rill | Show results with:rill
[54]
[PDF] Global Symposium on Soil Erosion (GSER19) |Concept note
The annual economic cost of erosion-induced fertilizer use increase was found to be US$ 33-60 billion for nitrogen and US$ 77-140 billion for phosphorus (FAO ...
[55]
The Dangers of Neglecting Soil Erosion - Penn State Extension
May 2, 2023 · The ravages of soil erosion led to decreased land productivity, reduced land values, and hundreds of thousands of environmental refugees. Even ...
[56]
A Measurement Method for Rill and Ephemeral Gully Erosion ...
Feb 5, 2016 · Rill and gully erosion have been quantified using pin measurements, runoff-monitoring samples, sediment surrogates, total station survey, ...
[57]
[PDF] Erosion Pins: Installation, Readings, and Calculations of Soil Losses ...
May 22, 2023 · Pins are widely used to measure the retreat of gully edges and riverbanks. On slopes, pins have enabled measurements of sheet erosion and ...
[58]
[PDF] A field method for soil erosion measurements in agricultural and ...
R unoff-plot methods use artificial boundaries to define a plot area and direct runoff and eroded soil into a collector for soil erosion assessment. R.unoff ...
[59]
Measurement of rill erosion through a new UAV-GIS methodology
For each rill point the circular neighbouring form is intended to calculate the difference between the elevation of the rill rim and the elevation of the point.Missing: stake | Show results with:stake
[60]
Rill Erosion and Drainage Development in Post-Landslide Settings ...
This study demonstrates that a commercial UAV–LiDAR system can effectively describe microtopography in a post-landslide landscape and facilitate analysis.
[61]
Dynamic Assessment of Soil Erosion Risk Using Landsat TM and HJ ...
The objective of this study is to assess the water erosion (rill and sheet erosion) risk and dynamic change trend of spatial distribution in erosion status and ...
[62]
Extension of a GIS procedure for calculating the RUSLE equation LS ...
Oct 12, 2025 · A slope length factor that varies with soil susceptibility to rill erosion. A nearly linear slope steepness relationship that reduces ...
[63]
[PDF] Integration of GIS and Remote Sensing with RUSLE Model for ...
Dec 30, 2022 · In this study, GIS and remote sensing techniques have been integrated with the Revised Universal Soil. Loss Equation (RUSLE) model to estimate ...
[64]
[PDF] Effects of Erosion Control Practices on Nutrient Loss - US EPA
Coarse- textured sediment and sediment from sheet and rill erosion are less likely to reach a stream than fine-grained sediment or sediment from channel erosion ...
[65]
[PDF] Conservation Practice Standard Mulching (Code 484)
Mulch material may affect microbial activity in the soil surface, increase infiltration, and decrease runoff, erosion, and evaporation. The temperature of ...
[66]
[PDF] Conservation Practice Standard Contour Farming (Code 330)
• Reduce sheet and rill erosion. • Reduce sediment transport to surface ... Several factors influence the effectiveness of contour farming to reduce soil erosion.
[67]
[PDF] Check Dams
Check dams reduce erosion by reducing flow velocities. Sediment trapping can occur at lower flow velocities, but construction staff should not use check dams ...Missing: rill | Show results with:rill
[68]
[PDF] Preparing your Fields for Extreme Weather - Dane Demo Farms
Jul 3, 2024 · Research shows soil erosion rates may be reduced by 70 percent or more on no-till fields versus convention- ally tilled fields and ...
[69]
[PDF] Integrated sediment management Guidelines and good practices in ...
Sediments mostly enter river systems through erosion and delivery in the river catchment, and are transported from the headwater to the sea. Sediments enter ...
[70]
Banking on Soil Health | Farmers.gov
Aug 20, 2019 · The average return on investment was 176%, with a range from 35% to 343%. The practices led to increased infiltration, thereby reducing water ...