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Research article · 2025 · Full text

International Journal of Geography Geology and Environment

Soil erosion modeling using WEPP under climate change scenarios in the Korean Peninsula

Andrés ZuluagaPaula MonsalveSebastián Castaño

Volume 7(9) · Pages 210–213 · DOI: 10.22271/27067483.2025.v7.i9c.643 ↗

Research areasSoil erosion and sediment transportHydrology and Watershed Management StudiesEnvironmental and Agricultural Sciences

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Abstract

Author-written

Since the 1970s, South Korea has invested heavily in hillslope revegetation and terracing to curb soil losses that once stripped bare mountainsides at rates exceeding 40 t/ha/yr. Those gains are now at risk as shifting rainfall patterns push storm intensities beyond the design capacity of existing conservation measures. This research applied the Water Erosion Prediction Project (WEPP) model to simulate hillslope and watershed-scale soil erosion across four representative catchments in the central Korean Peninsula under two Representative Concentration Pathway scenarios (RCP 4.5 and RCP 8.5) for the period 2020-2100. Downscaled climate projections from three general circulation models (HadGEM2-ES, MPI-ESM-LR, CNRM-CM5) supplied daily precipitation, temperature, and solar radiation inputs. The model was calibrated against measured sediment yield data from 2010 to 2019 and validated for 2020-2022, achieving Nash-Sutcliffe efficiency coefficients of 0.72 to 0.81 across the four catchments. Baseline mean erosion stood at 12.4 t/ha/yr. Under RCP 4.5, erosion is projected to reach 22.3 t/ha/yr by 2100, while RCP 8.5 pushes the estimate to 38.1 t/ha/yr, a threefold increase over current conditions. Cropland contributed 55-62% of total sediment yield despite occupying only 31% of the catchment area. The simulations suggest that existing terraces and grass waterways will be overwhelmed by mid-century under the high-emission pathway unless supplemented by additional buffer strips and cover crop rotations.

Summary

Source-checked

Plain-language reading of the full paper, prepared with AI and checked against the text. Each point links to the authors' own words.

  1. Why it matters

    • South Korea has historically faced severe soil erosion, with rates once exceeding 40 t/ha/yr, leading to significant investments in revegetation and terracing since the 1970s. View evidence ↗

      Why it matters

      South Korea has historically faced severe soil erosion, with rates once exceeding 40 t/ha/yr, leading to significant investments in revegetation and terracing since the 1970s.

      In the paper's own words

      “Since the 1970s, South Korea has invested heavily in hillslope revegetation and terracing to curb soil losses that once stripped bare mountainsides at rates exceeding 40 t/ha/yr.”

      Page 1

      Found in: Introduction

      Read it in the full textOpen PDF at page 1 ↗
    • Current soil conservation gains are threatened because changing rainfall patterns are creating storm intensities that exceed the capacity of existing measures. View evidence ↗

      Why it matters

      Current soil conservation gains are threatened because changing rainfall patterns are creating storm intensities that exceed the capacity of existing measures.

      In the paper's own words

      “Those gains are now at risk as shifting rainfall patterns push storm intensities beyond the design capacity of existing conservation measures.”

      Page 1

      Found in: Introduction

      Read it in the full textOpen PDF at page 1 ↗
    • Soil erosion is highly sensitive to rainfall intensity; even small increases in storm magnitude can lead to significantly larger amounts of sediment loss. View evidence ↗

      Why it matters

      Soil erosion is highly sensitive to rainfall intensity; even small increases in storm magnitude can lead to significantly larger amounts of sediment loss.

      In the paper's own words

      “Because soil erosion responds nonlinearly to rainfall intensity, relatively modest increases in storm magnitude can translate into much larger increases in sediment flux”

      Page 1

      Found in: Introduction

      Read it in the full textOpen PDF at page 1 ↗
  2. The question

    • The study aimed to fill a research gap by calibrating and validating the Water Erosion Prediction Project (WEPP) model for four catchments in the Gangwon and Gyeonggi provinces. View evidence ↗

      The question

      The study aimed to fill a research gap by calibrating and validating the Water Erosion Prediction Project (WEPP) model for four catchments in the Gangwon and Gyeonggi provinces.

      In the paper's own words

      “This research addressed that gap by (a) calibrating and validating WEPP for four catchments in Gangwon and Gyeonggi provinces, (b) driving the calibrated model with downscaled”

      Page 1

      Found in: Introduction

      Read it in the full textOpen PDF at page 1 ↗
  3. What they did

    • The research focused on four catchments: Hwacheon (47.3 sq km), Pocheon (62.8 sq km), Hoengseong (53.1 sq km), and Yangpyeong (41.6 sq km). View evidence ↗

      What they did

      The research focused on four catchments: Hwacheon (47.3 sq km), Pocheon (62.8 sq km), Hoengseong (53.1 sq km), and Yangpyeong (41.6 sq km).

      In the paper's own words

      “The four catchments, Hwacheon (47.3 sq km), Pocheon (62.8 sq km), Hoengseong (53.1 sq km), and Yangpyeong (41.6 sq km), span the transition from mountainous Gangwon Province to the gentler terrain of Gyeonggi Province.”

      Page 2

      Found in: Introduction

      Read it in the full textOpen PDF at page 2 ↗
    • The model used daily precipitation, temperature, and solar radiation data from three general circulation models: HadGEM2-ES, MPI-ESM-LR, and CNRM-CM5. View evidence ↗

      What they did

      The model used daily precipitation, temperature, and solar radiation data from three general circulation models: HadGEM2-ES, MPI-ESM-LR, and CNRM-CM5.

      In the paper's own words

      “Downscaled climate projections from three general circulation models (HadGEM2-ES, MPI-ESM-LR, CNRM-CM5) supplied daily precipitation, temperature, and solar radiation inputs.”

      Page 1

      Found in: Scenario Development

      Read it in the full textOpen PDF at page 1 ↗
    • Model calibration was performed using sediment yield data from 2010-2019, with validation from 2020-2022, resulting in Nash-Sutcliffe efficiency coefficients between 0.72 and 0.81. View evidence ↗

      What they did

      Model calibration was performed using sediment yield data from 2010-2019, with validation from 2020-2022, resulting in Nash-Sutcliffe efficiency coefficients between 0.72 and 0.81.

      In the paper's own words

      “The model was calibrated against measured sediment yield data from 2010 to 2019 and validated for 2020-2022, achieving Nash-Sutcliffe efficiency coefficients of 0.72 to 0.81 across the four catchments.”

      Page 1

      Found in: Introduction

      Read it in the full textOpen PDF at page 1 ↗
    • The WEPP model simulated soil erosion from 2020 to 2100 under two climate scenarios: RCP 4.5 (moderate emissions) and RCP 8.5 (high emissions). View evidence ↗

      What they did

      The WEPP model simulated soil erosion from 2020 to 2100 under two climate scenarios: RCP 4.5 (moderate emissions) and RCP 8.5 (high emissions).

      In the paper's own words

      “This research applied the Water Erosion Prediction Project (WEPP) model to simulate hillslope and watershed-scale soil erosion across four representative catchments in the central Korean Peninsula under two Representative Concentration Pathway scenarios (RCP 4.5 and RCP 8.5) for the period 2020-2100.”

      Page 1

      Found in: Introduction

      Read it in the full textOpen PDF at page 1 ↗
  4. What they found

    • The baseline mean soil erosion rate was measured at 12.4 t/ha/yr. View evidence ↗

      What they found

      The baseline mean soil erosion rate was measured at 12.4 t/ha/yr.

      In the paper's own words

      “Baseline mean erosion stood at 12.4 t/ha/yr.”

      Page 1

      Found in: Methods

      Read it in the full textOpen PDF at page 1 ↗
    • Under the RCP 8.5 scenario, erosion is projected to reach 38.1 t/ha/yr by 2100, representing a threefold increase over baseline conditions. View evidence ↗

      What they found

      Under the RCP 8.5 scenario, erosion is projected to reach 38.1 t/ha/yr by 2100, representing a threefold increase over baseline conditions.

      In the paper's own words

      “Under RCP 8.5, the rise accelerates after mid-century, reaching 38.1 t/ha/yr by 2100, a threefold jump.”

      Page 2

      Found in: Discussion

      Read it in the full textOpen PDF at page 2 ↗
    • Cropland is the primary source of sediment, contributing 55-62% of the total yield while only occupying 31% of the land area. View evidence ↗

      What they found

      Cropland is the primary source of sediment, contributing 55-62% of the total yield while only occupying 31% of the land area.

      In the paper's own words

      “Cropland contributed 55-62% of total sediment yield despite occupying only 31% of the catchment area.”

      Page 1

      Found in: Discussion

      Read it in the full textOpen PDF at page 1 ↗
    • Under the high-emission RCP 8.5 scenario, cropland erosion rates are projected to climb from 6.8 to 23.8 t/ha/yr, the highest increase among all land uses. View evidence ↗

      What they found

      Under the high-emission RCP 8.5 scenario, cropland erosion rates are projected to climb from 6.8 to 23.8 t/ha/yr, the highest increase among all land uses.

      In the paper's own words

      “Its erosion rate climbed from 6.8 to 23.8 t/ha/yr under RCP 8.5, the largest absolute increase.”

      Page 3

      Found in: Introduction

      Read it in the full textOpen PDF at page 3 ↗
    • Converting 10% of cropland to grass buffer strips reduced erosion by 14-19% under RCP 4.5 and 11-16% under RCP 8.5. View evidence ↗

      What they found

      Converting 10% of cropland to grass buffer strips reduced erosion by 14-19% under RCP 4.5 and 11-16% under RCP 8.5.

      In the paper's own words

      “The sensitivity test converting 10% of cropland to permanent grass buffer strips reduced catchment-scale erosion by 14-19% under RCP 4.5 and 11-16% under RCP 8.5”

      Page 3

      Found in: Discussion

      Read it in the full textOpen PDF at page 3 ↗
  5. What it means

    • The authors conclude that existing conservation measures will be overwhelmed by mid-century under high emissions unless supplemented by cover crop rotations and additional buffer strips. View evidence ↗

      What it means

      The authors conclude that existing conservation measures will be overwhelmed by mid-century under high emissions unless supplemented by cover crop rotations and additional buffer strips.

      In the paper's own words

      “The simulations suggest that existing terraces and grass waterways will be overwhelmed by mid-century under the high-emission pathway unless supplemented by additional buffer strips and cover crop rotations.”

      Page 1

      Found in: Discussion

      Read it in the full textOpen PDF at page 1 ↗
    • To keep erosion within tolerable limits, the authors recommend a portfolio approach including modified tillage, cover crops, vegetative buffers, and targeted land retirement. View evidence ↗

      What it means

      To keep erosion within tolerable limits, the authors recommend a portfolio approach including modified tillage, cover crops, vegetative buffers, and targeted land retirement.

      In the paper's own words

      “A portfolio approach combining vegetative buffers, modified tillage, cover crops, and targeted land retirement appears necessary to maintain erosion within tolerable limits.”

      Page 3

      Found in: Discussion

      Read it in the full textOpen PDF at page 3 ↗
    • A stated limitation of the study is the assumption that land use remains static over the projection period. View evidence ↗

      What it means

      A stated limitation of the study is the assumption that land use remains static over the projection period.

      In the paper's own words

      “A limitation of the projections is the static land use assumption.”

      Page 3

      Found in: Discussion

      Read it in the full textOpen PDF at page 3 ↗
    • The authors note that using only three general circulation models does not cover the full CMIP5 distribution, and adding more models would better define uncertainty. View evidence ↗

      What it means

      The authors note that using only three general circulation models does not cover the full CMIP5 distribution, and adding more models would better define uncertainty.

      In the paper's own words

      “The three-GCM ensemble, while capturing a reasonable range of precipitation futures, does not span the full CMIP5 distribution; inclusion of additional models would widen the uncertainty bounds”

      Page 3

      Found in: Discussion

      Read it in the full textOpen PDF at page 3 ↗

Visual summary

2 visuals

Illustrations explain the paper; they do not show study data.

AI-generated illustration
AI-generated conceptual illustration (Korean Peninsula landscape with sloping agricultural soil). It explains the idea and does not show study data.↗ Enlarge
Climate Scenario Erosion Trajectories
AI-generated conceptual illustration (Korean Peninsula landscape with sloping agricultural soil). It explains the idea and does not show study data.

AI-generated conceptual illustration (Korean Peninsula landscape with sloping agricultural soil). It explains the idea and does not show study data.

Open full-size image ↗

Climate Scenario Erosion Trajectories

AI-generated conceptual illustration (Korean Peninsula landscape with sloping agricultural soil). It explains the idea and does not show study data.

View source evidence ↗
AI-generated illustration
AI-generated conceptual illustration (Korean Peninsula landscape with cropland and forest). It explains the idea and does not show study data.↗ Enlarge
Land Use vs. Erosion Contribution
AI-generated conceptual illustration (Korean Peninsula landscape with cropland and forest). It explains the idea and does not show study data.

AI-generated conceptual illustration (Korean Peninsula landscape with cropland and forest). It explains the idea and does not show study data.

Open full-size image ↗

Land Use vs. Erosion Contribution

AI-generated conceptual illustration (Korean Peninsula landscape with cropland and forest). It explains the idea and does not show study data.

View source evidence ↗

Figures & tables

From the original paper
WEPP calibration and validation performance for fourTable 1Page 2Ensemble-mean projected annual soil erosion under RCPFigure 1Page 2Projected erosion rates by land use class under RCP 8.5Table 2Page 3Stacked area chart of erosion contributions by land use classFigure 2Page 3
FULL TEXT Original article · reflowed for reading

Introduction

Half a century ago, aerial photographs of central Korea showed a landscape stripped nearly bare by decades of deforestation, overgrazing, and wartime devastation. The massive reforestation campaign launched in 1973, one of the most successful in modern history, planted over 11 billion trees and reduced national erosion rates by an estimated 70% within two decades [1] . Yet the replanted hillslopes now face a different adversary: rainfall that is becoming more intense and concentrated in fewer, heavier events as the East Asian monsoon responds to a warming climate [2] . The Korean Peninsula receives roughly 60-70% of its annual precipitation (1,200-1,500 mm) between June and September. Climate projections under CMIP5 indicate that maximum daily precipitation could increase by 15-30% by mid-century even under moderate emission pathways, with a disproportionate rise in events exceeding 80 mm/day [3] . Because soil erosion responds nonlinearly to rainfall intensity, relatively modest increases in storm magnitude can translate into much larger increases in sediment flux [4] . Process-based models like the Water Erosion Prediction Project (WEPP) offer a physically grounded framework for projecting erosion under altered climate regimes. WEPP simulates rill and interrill erosion, sediment transport, and deposition along hillslope profiles and through small watershed channel networks, accounting for canopy cover, residue, tillage, and soil properties on a daily time step [5] . It has been validated across temperate, tropical, and semi-arid settings but has seen limited application in East Asian monsoon environments, where short-duration high-intensity storms and distinctive paddy-field hydrology create conditions not well represented in the default parameterisations [6] . This research addressed that gap by (a) calibrating and validating WEPP for four catchments in Gangwon and Gyeonggi provinces, (b) driving the calibrated model with downscaled projections from three GCMs under RCP 4.5 and RCP 8.5, and (c) partitioning projected erosion by land use to identify where conservation interventions are most needed. The work was carried out at the Department of Geography and Planning, School of Geography and Environment, Cartagena, Colombia, between May 2021 and September 2023 [7] .

Model Description and Parameterisation

WEPP version 2012.8 was configured in watershed mode for each of the four catchments, with hillslope elements derived from a 5 m national DEM resampled to 10 m resolution. Soil erodibility parameters (interrill erodibility Ki, rill erodibility Kr, critical shear stress tauc) were estimated from measured soil texture, organic matter content, and saturated hydraulic conductivity following the WEPP Technical Documentation [5] . Land management files were constructed for four cover types: deciduous forest, coniferous plantation, rainfed cropland (rice-soybean rotation), and urban fringe. Cropland management sequences specified spring tillage on 20 April, rice transplanting on 25 May, harvest on 15 October, and soybean planting on 1 November where double-cropping occurred. Leaf area index growth curves were fitted to MODIS LAI 8-day composites (2015-2019) for each cover type [8] . Climate input files were generated from biascorrected daily data using the CLIGEN stochastic weather generator seeded with station-specific statistics from the Korea Meteorological Administration network [9] .

Scenario Development

Two emission pathways were considered: RCP 4.5 (moderate mitigation) and RCP 8.5 (high emissions). Downscaled daily precipitation, maximum and minimum temperature, and solar radiation from HadGEM2-ES, MPI-ESM-LR, and CNRM-CM5 were obtained from the Korea Meteorological Administration's regional climate projections at 12.5 km resolution [10] . For each GCM-RCP combination, WEPP was run for the period 2020-2100 in 20-year moving windows. The ensemble mean and range across the three GCMs were reported. Land use was held constant at 2020 distribution to isolate the climate signal; a supplementary sensitivity test examined the effect of converting 10% of cropland to permanent grass cover [11] .

Material and Methods Material

The four catchments, Hwacheon (47. Rainfall was recorded at 10-minute resolution at seven automatic weather stations within or adjacent to the catchments [12] .

Methods

Calibration targeted three parameters: effective hydraulic conductivity (Ke), interrill erodibility (Ki), and rill erodibility (Kr). Optimisation used the Shuffled Complex Evolution (SCE-UA) algorithm, minimising the root mean square error between observed and simulated monthly sediment yields. Performance was evaluated with Nash-Sutcliffe efficiency (NSE), percent bias (PBIAS), and the ratio of RMSE to the standard deviation of observations (RSR) [13] . Validation applied the calibrated parameter sets to the 2020-2022 period without further adjustment. Climate-driven projections were run with the same parameter sets, replacing observed climate inputs with biascorrected GCM outputs. Erosion rates were aggregated to annual means per land use class using zonal statistics in QGIS 3.28. 1 shows that calibration NSE ranged from 0.76 to 0.81 and validation NSE from 0.72 to 0.78, indicating satisfactory model performance according to the benchmarks proposed by Moriasi et al. [13] . PBIAS remained within plus or minus 15% for all catchments, and RSR stayed below 0.54, confirming that simulated sediment yields tracked observed values without systematic over-or underprediction. Figure 2 shows how the erosion budget shifts over time.

Figure 2. Stacked area chart of erosion contributions by land use class
Stacked area chart of erosion contributions by land use class↗ Enlarge
Figure 2
Stacked area chart of erosion contributions by land use class

Stacked area chart of erosion contributions by land use class

Open full-size image ↗
Original paper figureSource PDF · page 3 ↗

Results

Cropland's share grows slightly in both absolute and relative terms, while forest and grassland contribute modestly. The urban-fringe category, although small in area, displays a steep proportional rise driven by exposed construction surfaces and reduced infiltration.

Discussion

The projected erosion increases align broadly with findings from WEPP applications in other monsoon-dominated regions. Nearing et al. [14] estimated that a 1% rise in total precipitation could raise erosion by roughly 1.7% in the US, a sensitivity ratio that, when extrapolated to the Korean precipitation projections (+18 to +34% by end-century), predicts a 30-58% erosion increase, somewhat lower than the 80-207% simulated here. The discrepancy reflects Korea's steeper slopes and the dominance of high-intensity convective events during the monsoon, which amplify interrill detachment disproportionately. Cropland's outsized contribution to sediment yield underscores the importance of targeted management. The sensitivity test converting 10% of cropland to permanent grass buffer strips reduced catchment-scale erosion by 14-19% under RCP 4.5 and 11-16% under RCP 8.5, a meaningful but not sufficient offset. Additional strategies, such as no-till rice cultivation, winter cover cropping, and straw mulching after soybean harvest, would need to be combined with grass buffers to keep erosion below the 12 t/ha/yr tolerable threshold proposed by the Korean Rural Development Administration [15,16] . A limitation of the projections is the static land use assumption. In reality, ongoing urbanisation around Seoul's satellite cities is converting agricultural land to impervious surfaces, which may simultaneously reduce cropland erosion area and increase surface runoff volumes downstream [17] . Coupling WEPP with a land-use change model such as CLUE-S would improve the realism of longterm projections. The three-GCM ensemble, while capturing a reasonable range of precipitation futures, does not span the full CMIP5 distribution; inclusion of additional models would widen the uncertainty bounds [18] .

Conclusion

This research projected soil erosion across four catchments in the central Korean Peninsula through the end of the 21st century using the WEPP model driven by bias-corrected outputs from three general circulation models under RCP 4.5 and RCP 8.

Acknowledgement

Acknowledgements Funding SourcesThis research was supported by departmental funds from the School of Geography and Environment, Cartagena, Colombia.

Figures and tables from the paper

Table 1. WEPP calibration and validation performance for four
WEPP calibration and validation performance for four↗ Enlarge
Table 1
WEPP calibration and validation performance for four

WEPP calibration and validation performance for four

Open full-size image ↗
Original paper figureSource PDF · page 2 ↗
Figure 1. Ensemble-mean projected annual soil erosion under RCP
Ensemble-mean projected annual soil erosion under RCP↗ Enlarge
Figure 1
Ensemble-mean projected annual soil erosion under RCP

Ensemble-mean projected annual soil erosion under RCP

Open full-size image ↗
Original paper figureSource PDF · page 2 ↗
Table 2. Projected erosion rates by land use class under RCP 8.5
Land UseArea (%)2020s2040s2060s2080sChange (%)
Cropland316.810.116.323.8+250
Forest422.12.83.95.7+171
Grassland161.92.94.15.4+184
Urban fringe111.62.63.85.2+225

Table text extracted from the original PDF; superscript letters are shown inline. The original table image is below.

View original table image
Projected erosion rates by land use class under RCP 8.5↗ Enlarge
Table 2
Projected erosion rates by land use class under RCP 8.5

Projected erosion rates by land use class under RCP 8.5

Open full-size image ↗
Original paper tableSource PDF · page 3 ↗

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