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Understanding changes in soil fertility and soil environmental risks in protected agriculture with high irrigation and fertilizer inputs are of great significance for ecological protection. In this study, soil samples in the plow layer were collected from greenhouses >100 acres in the eastern Qinghai-Tibet Plateau after different durations of planting time (either ≤ 3, 3-5, 5-10, or 10-20 years) to assess the changing pattern of soil fertility indicators and the potential leaching risk of nitrogen and phosphorus. The results showed that soil organic matter (OM) and total nitrogen (TN) contents in protected agriculture were 17.1 and 1.3 g/kg, respectively, which suggests moderate content levels. Meanwhile, soil alkali-hydrolyzed nitrogen (AN), available phosphorus (Olsen-P), and available potassium (AK) contents were 160.9, 72.0, and 191.2 mg/kg, respectively, which suggests abundant content levels. As the number of planting years increased, the contents of soil OM, TN, AN, and Olsen-P increased significantly, especially after 10 years, with 41.6%, 44.2%, 26.5%, and 67.4% increases, respectively, compared to ≤ 3 years. As seen, Olsen-P had the most marked increase. In contrast, soil AK and pH decreased with planting years, and soil AK after 5 years decreased by 32% compared to ≤ 3 years. Moreover, the soil pH value in 3-5 years decreased by 2.3% compared to that of ≤ 3 years. The leaching risk of soil nitrogen and phosphorus was intensified after 10-20 years, and the probability of leaching was 0.74 and 0.84, respectively. This study indicated that, in protected agriculture, soil OM, AN, and Olsen-P contents improved, accompanied by a high risk of N and P loss, and AK and soil pH values decreased. It is recommended that the input of nitrogen and phosphorus fertilizers should be controlled, and the input of potassium fertilizer should be increased for more than 10 years of facility cultivation. This study provides a scientific basis for the rational fertilization of agricultural facilities. The findings indicate that after facility planting for 10-20 years, soil organic matter, nitrogen, and phosphorus significantly increased, yet the leaching risk of nitrogen and phosphorus increased as well, suggesting that the input of nitrogen and phosphorus fertilizer should be controlled. After 3-5 years of planting, soil AK and pH values decreased significantly, implicating that potassium and organic fertilizer should be supplemented in a timely manner. © 2022 Science Press. All rights reserved.  相似文献   
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煤矿开采是全世界应对不断增加的能源需求的主要手段.但随着煤矿开采,区域生态系统遭到不同程度的破坏,导致“碳汇”能力下降.植被恢复是矿区退化的生态系统和固碳功能恢复的基础.然而,目前尚未对全球范围内煤矿区植被恢复对土壤有机碳(SOC)的影响进行系统研究,因此无法准确预测全球SOC库对植被恢复的响应.通过搜集同行评议的112篇文章中植被恢复的土壤理化性质,以评估煤矿区植被恢复类型、土壤深度、恢复年份、年均温、年降水量和海拔等对SOC的影响,并明确相关的关键驱动因素.结果表明,受损煤矿区通过植被恢复能够显著改善土壤的理化性质,植被恢复后土壤相较于未恢复或自然恢复SOC储量提升了39.02%.当不考虑环境因素时,利于SOC储量积累的植被恢复类型为:农田>林地>草地>灌木林.4种类型的植被恢复对表层(0~20 cm)SOC储量均得到显著增加,草地和灌木能显著增加深层(>40 cm)的SOC储量,而林地和农田类型下深层的SOC储量与未恢复或自然恢复后的SOC储量无显著差异.植被恢复后SOC储量的增加趋势会随着土壤深度的增加而降低.具体的植被恢复策略应根据气候条件选择合适的植被类型.受损煤矿区在年均温<0℃和年均降水<500 mm的环境下,固碳效应较高的植被恢复类型为草地和灌木林,而在年均温>15℃和年降水量>800 mm的环境下,林地和农田恢复类型能够更好地增加SOC储量.TN、BD、AN和AK是影响土壤固碳能力的主要因素.研究可为量化受损煤矿区不同植被恢复措施的固碳效果和退化生态系统的恢复与重建提供理论参考.  相似文献   
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