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Changes in water characteristics and pore distributions in loam soil under the coexistence of microplastics and salts

Geoderma 2025 4 citations ? Citation count from OpenAlex, updated daily. May differ slightly from the publisher's own count. Score: 58 ? 0–100 AI score estimating relevance to the microplastics field. Papers below 30 are filtered from public browse.
Xuguang Xing, Xuguang Xing, Xuguang Xing, Xuguang Xing, Liuchang Su, Liuchang Su, Xuguang Xing, Xuguang Xing, Liuchang Su, Liuchang Su, Xuguang Xing, Fengyue Zhao, Fengyue Zhao, Xuguang Xing, Fengyue Zhao, Fengyue Zhao, Dongwei Li, Fengyue Zhao, Fengyue Zhao, Dongwei Li, Xuguang Xing, Xuguang Xing, Liuchang Su, Xuguang Xing, Weihua Wang Liuchang Su, Weihua Wang Fengyue Zhao, Fengyue Zhao, Xuguang Xing, Weihua Wang

Summary

This study investigated how microplastics interact with soil salinity to affect water movement and retention in loam soil. Researchers found that microplastics generally reduced the soil's ability to conduct water and hold moisture, but these effects were weaker in saltier soils. The findings matter for agriculture because they suggest microplastic pollution could worsen water availability for crops, particularly in non-saline farmland.

• Microplastics (MPs) and salts have different effect mechanisms on soil properties. • Increased soil salinity weakens the effects of MPs on soil saturated conductivity. • MPs have greater impacts on water retention of non-saline soil than of saline soil. • MPs have different effects on water constants for saline and non-saline soils. • MPs have different effects on pore distribution for saline and non-saline soils. Farmland salinization and microplastics (MPs) pollution are increasing worldwide, posing threats to environmental health and accelerating land degradation. In the context of the global ecological challenges of land degradation and pollution, clarifying the interactions between MPs and salts is beneficial for land development and sustainable management. We measured the hydraulic parameters and calculated the water characteristics and pore distributions of the soils with different salinities (i.e., 0, 1, 3, and 5 g/kg) and MPs mixing contents (i.e., 0, 5, 10, and 30 g/kg). Results indicated that MPs generally reduced the soil saturated hydraulic conductivity, but the increased soil salinity weakened the effects of MPs on it. According to the soil water retention curves, MPs weakened the water-holding capacity, with a greater impact in non-saline soil than in saline soil. In non-saline soil, MPs caused the saturated water content to decrease by 4.6 %–8.1 %. In addition, MPs reduced the field capacity and wilting coefficient of both soils. The effect of MPs on available water was greater in non-saline soil than in saline soil. Furthermore, MPs reduced the total porosity of both soils. However, MPs had no significant effect on pore distribution in non-saline soil, whereas, in saline soil, MPs increased the proportion of micro pores and small pores but decreased the proportion of macro pores and voids. We determined that, in addition to changing the pore distribution, MPs and salts changed the water characteristics through hydrophobicity and ionic interactions, respectively. Our findings provide evidence of the influence of MPs on the physical properties of saline soil, highlighting the need for improved regulation and land management in plastic-polluted soil–crop systems.

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