Modelling of rainwater reduction and hydrological performance of selected green infrastructure (GI) facilities in urban catchments
11 mar 2025
O artykule
Data publikacji: 11 mar 2025
Zakres stron: 1 - 20
DOI: https://doi.org/10.2478/oszn-2025-0005
Słowa kluczowe
© 2025 Krzysztof Muszyński et al., published by Sciendo
This work is licensed under the Creative Commons Attribution-NonCommercial-NoDerivatives 3.0 License.
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![Maximum, minimum and average values of the rainwater inflow limit [L/m2] per 1 m2 of surface area of LID facilities for scenarios S0–S7 for which there was a 100% quantitative reduction of inflow](https://sciendo-parsed.s3.eu-central-1.amazonaws.com/64726ab0215d2f6c89dc731c/j_oszn-2025-0005_fig_010.jpg?X-Amz-Algorithm=AWS4-HMAC-SHA256&X-Amz-Content-Sha256=UNSIGNED-PAYLOAD&X-Amz-Credential=AKIA6AP2G7AKOUXAVR44%2F20250912%2Feu-central-1%2Fs3%2Faws4_request&X-Amz-Date=20250912T113223Z&X-Amz-Expires=3600&X-Amz-Signature=5fcf3e6b78a20c95fc4d3ecd1f207e266d2c3f710e3b9e060f48dd7f92cdb99a&X-Amz-SignedHeaders=host&x-amz-checksum-mode=ENABLED&x-id=GetObject)
The basic measures of fitness coefficients for built SWMM model
NSEC | Nash-Sutcliffe Efficiency Coefficient | Compare the results of model’s response and measurement data |
|
0.885 | -∞ - 1; very good | [ |
ISE | Integral Square Error | The accuracy of the matching between simulated and observed data |
|
0.02 | 0 – 3; excellent | [ |
RMSE | Root Mean Square Error | Differences between observed and simulated values |
|
0.442; < 0.5*1.307 | less than half of the standard deviation; good | [ |
Spatial analyses based on the Database of Topographical Objects of the study area
Roofs | 1.12 | 26.9 |
Roadways, pavement, alleys | 0.40 | 9.6 |
Single- and multi-family residential land | 2.17 | 52.0 |
Biologically active areas | 0.48 | 11.5 |
Summary of the LID parameters used in the calibrated SWMM model according to [Bond et al_ 2021]
Surface layer | Berm height | mm | 250 |
Vegetation volume | share | 0.1 | |
Surface roughness | – | 0.3 | |
Surface slope | % | 1 | |
Swale Side Slope | run/rise | – | |
Soil layer | Thickness | mm | 600 |
Porosity | share vol. | 0.45 | |
Field capacity | share vol. | 0.121 | |
Wilting point | share vol. | 0.057 | |
Conductivity | mm/hr | 91 | |
Conductivity slope | – | 44 | |
Suction head | mm | 50 | |
Storage layer | Thickness | mm | 400 |
Void ratio | voids/solids | 0.54 | |
Seepage rate | mm/hr | 2.6 | |
Clogging factor | – | 0 | |
Drain | Flow coefficient | mm/hr | 5.4 |
Drain exponent | – | 0.5 | |
Offset height | mm | 200 |
The simulation results of the calibrated model for the entire study area at the sewer outfall for scenarios S0–S7
Max flow [LPS] | 4.6 | 449.2 | 464.0 | 454.8 | 393.1 | 359.3 | 349.9 | 266.2 |
Total volume [m3] | 17 | 539 | 752 | 916 | 953 | 1008 | 1072 | 1139 |
Max flow [LPS] | 0.0 | 17.5 | 31.6 | 31.7 | 25.2 | 22.6 | 22.1 | 17.6 |
Total volume [m3] | 0 | 29 | 56 | 111 | 134 | 167 | 204 | 246 |
Max flow [LPS] | 100% | 96% | 93% | 93% | 94% | 94% | 94% | 93% |
Total volume [m3] | 100% | 95% | 93% | 88% | 86% | 83% | 81% | 78% |
Summary of the simulation results of the calibrated SWMM for individual LID facilities implemented in the study area for scenarios S0–S7
Total Inflow (m3) | 37.9 | 658.2 | 987.1 | 1234.8 | 1304.7 | 1404.0 | 1512.8 | 1629.2 |
Surface and Drain Outflow (m3) | 0.0 | 32.7 | 133.6 | 273.6 | 318.7 | 385.4 | 458.9 | 538.8 |
Average inflow (L/m2) | 0.008 | 0.139 | 0.208 | 0.260 | 0.275 | 0.296 | 0.319 | 0.344 |
Average outflow (L/m2) | 0.000 | 0.007 | 0.028 | 0.058 | 0.067 | 0.081 | 0.097 | 0.114 |
Analyzed scenarios
90 min (4.2 mm) | 15 min | 30 min | 45 min | 60 min | 90 min | 120 min | 180 min | |
7.8 | 273.32 | 175.33 | 134.52 | 105.37 | 74.81 | 59.55 | 42.46 | |
4.2 | 24.60 | 31.56 | 36.32 | 37.93 | 40.40 | 42.88 | 45.86 | |
2.80 | 98.40 | 63.12 | 48.43 | 37.93 | 26.93 | 21.44 | 15.29 |
Values of the basic parameters for the land use groups in the study area obtained during the SWMM calibration process
Building roofs-BUBD | 87.47 | 0.010 | 0.045 | 3.69 | 3.69 | 36.00 | 0.7 | |
Other roadway-SKJZ08 | 13.1 | 36.0 | 0.015 | 0.300 | 1.20 | 5.08 | 40.00 | 0.3 |
Local roadway-SKJZ06 | 34.6 | 49.5 | 0.010 | 0.300 | 1.20 | 5.08 | 40.00 | |
Alley-SKRP01 | 2.0 | 3.2 | 0.011 | 0.280 | 1.20 | 5.08 | 40.00 | |
Grass vegetation-PTTR01 | 1.0 | 2.5 | 0.140 | 0.280 | 5.08 | 7.62 | 20.00 | 0.3 |
Orchard-PTUT03 | 1.1 | 2.88 | 0.210 | 0.280 | 5.08 | 7.62 | 20.00 | |
Single-family dwelling-PTZB02 | 2.0 | 4.02 | 0.105 | 0.280 | 5.08 | 7.62 | 20.00 |
Summary of the results obtained for the considered precipitation scenarios S0–S7
1A | Rainwater volume [m3] | 365 | 2137 | 2742 | 3156 | 3296 | 3510 | 3725 | 3984 |
1B | Final LID storage [m3] | 41 | 788 | 970 | 1024 | 1036 | 1057 | 1081 | 1108 |
2A | Average inflow [L/m2] | 0.008 | 0.139 | 0.208 | 0.260 | 0.275 | 0.296 | 0.319 | 0.344 |
2B | Average outflow [L/m2] | 0.000 | 0.007 | 0.028 | 0.058 | 0.067 | 0.081 | 0.097 | 0.114 |
4A | Total volume [m3] | 17 | 539 | 752 | 916 | 953 | 1,008 | 1,072 | 1139 |
4B | Reduced volume [m3] | 0 | 29 | 56 | 111 | 134 | 167 | 204 | 246 |
5A | Peak flow [LPS] | 4.60 | 449.16 | 464.03 | 454.78 | 393.10 | 359.34 | 349.85 | 266.20 |
5B | Reduced peak flow [LPS] | 0.00 | 17.51 | 31.63 | 31.66 | 25.19 | 22.57 | 22.05 | 17.58 |