The concentration of soil Olsen-P is rapidly increasing in many parts of China, where P budget(P input minus P output) is the main factor influencing soil Olsen-P. Understanding the relationship between soil Olsen-P a...The concentration of soil Olsen-P is rapidly increasing in many parts of China, where P budget(P input minus P output) is the main factor influencing soil Olsen-P. Understanding the relationship between soil Olsen-P and P budget is useful in estimating soil Olsen-P content and conducting P management strategies. To address this, a long-term experiment(1991–2011) was performed on a fluvo-aquic soil in Beijing, China, where seven fertilization treatments were used to study the response of soil Olsen-P to P budget. The results showed that the relationship between the decrease in soil Olsen-P and P deficit could be simulated by a simple linear model. In treatments without P fertilization(CK, N, and NK), soil Olsen-P decreased by 2.4, 1.9, and 1.4 mg kg^(–1) for every 100 kg ha^(–1) of P deficit, respectively. Under conditions of P addition, the relationship between the increase in soil Olsen-P and P surplus could be divided into two stages. When P surplus was lower than the range of 729–884 kg ha^(–1), soil Olsen-P fluctuated over the course of the experimental period with chemical fertilizers(NP and NPK), and increased by 5.0 and 2.0 mg kg^(–1), respectively, when treated with chemical fertilizers combined with manure(NPKM and 1.5 NPKM) for every 100 kg ha^(–1) of P surplus. When P surplus was higher than the range of 729–884 kg ha^(–1), soil Olsen-P increased by 49.0 and 37.0 mg kg^(–1) in NPKM and 1.5 NPKM treatments, respectively, for every 100 kg ha^(–1) P surplus. The relationship between the increase in soil Olsen-P and P surplus could be simulated by two-segment linear models. The cumulative P budget at the turning point was defined as the "storage threshold" of a fluvo-aquic soil in Beijing, and the storage thresholds under NPKM and 1.5 NPKM were 729 and 884 kg ha^(–1)P for more adsorption sites. According to the critical soil P values(CPVs) and the relationship between soil Olsen-P and P budget, the quantity of P fertilizers for winter wheat could be increased and that of summer maize could be decreased based on the results of treatments in chemical fertilization. Additionally, when chemical fertilizers are combined with manures(NPKM and 1.5 NPKM), it could take approximately 9–11 years for soil Olsen-P to decrease to the critical soil P values of crops grown in the absence of P fertilizer.展开更多
为了解生物炭施入不同类型土壤后对Olsen-P和CaCl2-P的影响,通过室内土壤培养试验,研究施用2%(20 t hm-2)、4%(40 t hm-2)、8%(80 t hm-2)比例的生物炭条件下土壤中Olsen-P、CaCl2-P含量变化,以探讨不同类型土壤中施入生物炭后Olsen-P和...为了解生物炭施入不同类型土壤后对Olsen-P和CaCl2-P的影响,通过室内土壤培养试验,研究施用2%(20 t hm-2)、4%(40 t hm-2)、8%(80 t hm-2)比例的生物炭条件下土壤中Olsen-P、CaCl2-P含量变化,以探讨不同类型土壤中施入生物炭后Olsen-P和CaCl2-P含量变化的差异。结果表明:(1)红壤、水稻土、潮褐土、潮土中施用生物炭后,土壤中Olsen-P含量显著增加(P<0.05),并随着生物炭施用比例增加而增大。(2)培养42天后,施用生物炭对红壤中CaCl2-P含量无显著的影响,水稻土、潮褐土、潮土中CaCl2-P含量则随着生物炭施用比例增加而显著增大。(3)在同一生物炭施用量条件下,潮褐土和潮土中Olsen-P和CaCl2-P的增加量均显著(P<0.05)高于红壤和水稻土。展开更多
基金supported by the National Natural Science Foundation of China (41471249)the Special Scientific Research Fund of Agricultural Public Welfare Profession of China (201503120)
文摘The concentration of soil Olsen-P is rapidly increasing in many parts of China, where P budget(P input minus P output) is the main factor influencing soil Olsen-P. Understanding the relationship between soil Olsen-P and P budget is useful in estimating soil Olsen-P content and conducting P management strategies. To address this, a long-term experiment(1991–2011) was performed on a fluvo-aquic soil in Beijing, China, where seven fertilization treatments were used to study the response of soil Olsen-P to P budget. The results showed that the relationship between the decrease in soil Olsen-P and P deficit could be simulated by a simple linear model. In treatments without P fertilization(CK, N, and NK), soil Olsen-P decreased by 2.4, 1.9, and 1.4 mg kg^(–1) for every 100 kg ha^(–1) of P deficit, respectively. Under conditions of P addition, the relationship between the increase in soil Olsen-P and P surplus could be divided into two stages. When P surplus was lower than the range of 729–884 kg ha^(–1), soil Olsen-P fluctuated over the course of the experimental period with chemical fertilizers(NP and NPK), and increased by 5.0 and 2.0 mg kg^(–1), respectively, when treated with chemical fertilizers combined with manure(NPKM and 1.5 NPKM) for every 100 kg ha^(–1) of P surplus. When P surplus was higher than the range of 729–884 kg ha^(–1), soil Olsen-P increased by 49.0 and 37.0 mg kg^(–1) in NPKM and 1.5 NPKM treatments, respectively, for every 100 kg ha^(–1) P surplus. The relationship between the increase in soil Olsen-P and P surplus could be simulated by two-segment linear models. The cumulative P budget at the turning point was defined as the "storage threshold" of a fluvo-aquic soil in Beijing, and the storage thresholds under NPKM and 1.5 NPKM were 729 and 884 kg ha^(–1)P for more adsorption sites. According to the critical soil P values(CPVs) and the relationship between soil Olsen-P and P budget, the quantity of P fertilizers for winter wheat could be increased and that of summer maize could be decreased based on the results of treatments in chemical fertilization. Additionally, when chemical fertilizers are combined with manures(NPKM and 1.5 NPKM), it could take approximately 9–11 years for soil Olsen-P to decrease to the critical soil P values of crops grown in the absence of P fertilizer.
文摘为了解生物炭施入不同类型土壤后对Olsen-P和CaCl2-P的影响,通过室内土壤培养试验,研究施用2%(20 t hm-2)、4%(40 t hm-2)、8%(80 t hm-2)比例的生物炭条件下土壤中Olsen-P、CaCl2-P含量变化,以探讨不同类型土壤中施入生物炭后Olsen-P和CaCl2-P含量变化的差异。结果表明:(1)红壤、水稻土、潮褐土、潮土中施用生物炭后,土壤中Olsen-P含量显著增加(P<0.05),并随着生物炭施用比例增加而增大。(2)培养42天后,施用生物炭对红壤中CaCl2-P含量无显著的影响,水稻土、潮褐土、潮土中CaCl2-P含量则随着生物炭施用比例增加而显著增大。(3)在同一生物炭施用量条件下,潮褐土和潮土中Olsen-P和CaCl2-P的增加量均显著(P<0.05)高于红壤和水稻土。
