Potential Implications of Implementing River Diversion Systems on Soil Productivity
Abstract
1. Literature Review of the Impact Flooding Has on Agricultural Land
- Nitrogen losses can happen due to denitrification and nitrate leaching, causing increases in greenhouse gas emission and the amount of nitrate in flowing water. Increased nitrate in leaching water can potentially degrade groundwater quality, and excessive nitrate leaching will also have a significant impact on aquatic ecosystems.
- Soluble phosphorus can be lost via runoff and by being dissolved in the flooding water and leaching away as the flooding water recedes or infiltrates the soil. Increased P in receding waters and runoff can potentially increase algal bloom in freshwater systems.
- Other nutrients that are water soluble such as potassium and sulfur can also be lost from the system as the flooding water recedes, or in the case of sulfur lost due to sulfur reduction in redox reactions in saturated soils.
- Flooding can also cause changes in microbial mediated reactions that can have a significant impact on a soil’s productivity status.
2. Flooding Frequency and Duration
3. Flooding Impacts on Soil Properties
3.1. How Flooding Can Impact Soil Aggregation and Structure
3.2. Impact of Flooding on Soil Water-Holding Capacity and Soil Porosity
3.3. Flooding Effects on Soil Texture
3.4. Flooding Effects on Soil Organic Matter Turnover
4. Changes in Soil Chemical Properties Due to Flooding
4.1. Soil pH and Acidity/Alkalinity
4.2. Flooding Impact on Nutrient Cycling: Availability, Relocation, and Losses
5. Impact of Flooding on Soil Biological Properties
5.1. Flooding Impacts on Microbial Communities
5.2. Soil Enzymatic Activity in Waterlogged Soils
6. Interactions Among Soil Physical, Chemical, and Biological Properties Under Flooding Conditions
6.1. Feedback Loops
6.2. Soil Texture and Its Role on Flood Impacts on Soil Properties
7. Potential Implication of Implementing the River Diversion System
7.1. Impact on Soil Productivity
- Impact on Nitrogen: Depending on severity and flooding duration significant amounts of N can be lost from the system. Increased breakdown of organic matter releases increased levels of ammonium to the soil solution, causing a reduction in potentially mineralizable nitrogen (nitrogen that would become available throughout the growing season); nitrate that is present in the soil can be denitrified and lost to the atmosphere; nitrate and ammonium that might be in the solution will leach with the receding and draining water. The amount of nitrogen a corn crop can remove on an acre basis can be around 350 lb N ac−1 for a yield of 220 bu ac−1, and for this yield farmers will usually add 200 lb N ac−1 applied at some point in the spring. The difference in nitrogen taken up by corn (350 − 200 = 150 lb N ac−1) is supplied by the soil by means of residual nitrate from the previous season combined with ammonium mineralized from organic matter. The anaerobic conditions caused by flooding early on can reduce the amount of total nitrogen supplied by the soil, which could cause a deficit in total nitrogen in the system and increase the amount of nitrogen the farmer would have to supplement, increasing the final cost of production and reducing profits for the farmer.
- Impact on Phosphorus: Phosphorus can be impacted by flooding in two ways; inorganic phosphorus that can be solubilized as metals are reduced during oxi/redox reactions, and organic matter decomposition can also increase the amount of inorganic phosphorus in solution. The increase in inorganic phosphorus in solution can increase the amount of phosphorus that leaves the system primarily as the flooding water recedes which can cause pollution. In terms of phosphorus availability, it is unclear how flooding can really impact soil phosphorus availability in this region. Depending on soil test levels, increased amounts of fertilizer phosphorus would have to be added to compensate for phosphorus lost during flooding.
- Impact on soluble nutrients: Nutrients such as potassium that are soluble have high risk of being lost by leaching because of flooding. Nutrients such as sulfur, iron and manganese can also be lost by leaching as well when in a reduced form. As with all nutrients, increased amount of fertilizer will likely be needed to be applied to replenish the nutrients being lost.
- Impact on organic matter decomposition: Organic matter decomposition changes under flooding conditions and the rate of breakdown and processes involved in the breakdown changes significantly. Carbon is converted into methane and lignin breakdown slows down and potentially stops. The change in microbial community can lead to the development of conditions that can hinder crop development, such as the accumulation of phenolic acids which is linked to decreased seeding growth. As a result, there is potential for further reduction in productivity.
7.2. Impact on Crop Yield
8. Final Considerations
Funding
Data Availability Statement
Conflicts of Interest
References
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Pagliari, P.H. Potential Implications of Implementing River Diversion Systems on Soil Productivity. Agronomy 2025, 15, 2208. https://doi.org/10.3390/agronomy15092208
Pagliari PH. Potential Implications of Implementing River Diversion Systems on Soil Productivity. Agronomy. 2025; 15(9):2208. https://doi.org/10.3390/agronomy15092208
Chicago/Turabian StylePagliari, Paulo H. 2025. "Potential Implications of Implementing River Diversion Systems on Soil Productivity" Agronomy 15, no. 9: 2208. https://doi.org/10.3390/agronomy15092208
APA StylePagliari, P. H. (2025). Potential Implications of Implementing River Diversion Systems on Soil Productivity. Agronomy, 15(9), 2208. https://doi.org/10.3390/agronomy15092208