中国农业科学 ›› 2019, Vol. 52 ›› Issue (14): 2468-2483.doi: 10.3864/j.issn.0578-1752.2019.14.007
申凤敏1,姜桂英1(),张玉军1,2,刘芳1,刘世亮1(),柳开楼3
收稿日期:
2019-01-22
接受日期:
2019-04-11
出版日期:
2019-07-16
发布日期:
2019-07-26
通讯作者:
姜桂英,刘世亮
作者简介:
申凤敏,E-mail: shenfengmin@henau.edu.cn。
基金资助:
SHEN FengMin1,JIANG GuiYing1(),ZHANG YuJun1,2,LIU Fang1,LIU ShiLiang1(),LIU KaiLou3
Received:
2019-01-22
Accepted:
2019-04-11
Online:
2019-07-16
Published:
2019-07-26
Contact:
GuiYing JIANG,ShiLiang LIU
摘要:
【目的】基于长期定位试验,探讨典型红壤水稻土不同施肥制度下不同形态土壤氮素迁移特征,为红壤水稻土氮肥合理施用提供理论依据。【方法】选取始于1981年的进贤红壤长期定位试验站4个典型施肥处理,分别为不施肥对照(CK)、施氮磷钾肥(NPK)、氮磷钾配施秸秆(NPKS)、氮磷钾配施有机肥(NPKSM),测定并分析0—10 cm、10—20 cm、20—40 cm和40—60 cm土层土壤全氮(TN)、碱解氮(AN)、硝态氮(NO3 --N)、铵态氮(NH4 +-N)、可溶性有机氮(DON)和微生物生物量氮(SMBN)变化特征。 【结果】不同处理不同形态氮素基本均随土层加深呈下降趋势,但不同形态氮素在不同层次下降特征不同。其中有效态氮,如AN、NO3 --N、NH4 +-N、DON和SMBN主要集中分布在0—20 cm土层,且20—60 cm土层含量较0—20 cm明显降低;而TN在表层0—40 cm土层变化不明显。与CK相比,施肥处理可不同程度地提高0—60 cm各土层各形态氮素含量。其中NPKSM处理显著提高各形态氮素含量,其次为NPKS和NPK处理。相同处理下,TN在0—40 cm土层变化不明显;但在0—60 cm土层TN含量均表现为NPKSM>NPKS>NPK>CK。各处理AN含量随土层深度增加降低幅度显著,其中,20—40 cm土层AN含量相比10—20 cm土层分别降低了42%(CK)、50%(NPK)、44%(NPKS)、44%(NPKSM)。各处理不同土层NO3 --N和NH4 +-N含量均以NPKSM处理显著高于其他处理;其中40—60 cm土层中NO3 --N和NH4 +-N与0—10 cm土层相比,NH4 +-N含量下降幅度更大,分别为51%(CK)、48%(NPK)、54%(NPKS)、36%(NPKSM),且NO3 --N和NH4 +-N均以NPKS处理下降幅度最大,NPKSM处理最小。各处理DON含量在0—20 cm土层差异显著,且均以化肥与有机肥配施处理显著高于其他处理;CK和NPK处理40—60 cm土层的DON含量较20—40 cm略有增加,但NPKS和NPKSM处理则显著降低。各处理SMBN在10—20 cm土层差异最大,表现为NPKSM>NPKS>NPK>CK。相同处理下各形态氮素占TN的比例随土层深度的增加而下降,其中在0—20 cm土层各比例变化较明显;整体上NPKS与NPKSM处理的SMBN占TN比例较高,为2%—4%。耕层土壤(0—20 cm)的TN、AN、NO3 --N、DON和SMBN两两之间均存在显著的正相关关系(P≤0.05),其中TN、DON、AN与SMBN之间存在极显著正相关关系(P≤0.01)。施肥处理(NPK、NPKS、NPKSM)较不施肥处理(CK)可显著提高早、晚稻稻谷、稻草产量和总生物量及其相应的氮吸收量,其中以NPKSM处理最高;但NPKSM处理的无机氮残留量及氮表观损失也显著高于其他处理。 【结论】不同施肥处理对各形态氮素的影响主要集中在土壤耕层(0—20 cm),且各形态氮素含量整体上随土层深度的增加而降低,化肥与有机肥配施可以更好改善红壤区各土层氮素的供应情况;同时化肥与有机肥配施能显著提高作物产量及其氮吸收量,但也增加了其无机氮残留量及氮表观损失量。
申凤敏,姜桂英,张玉军,刘芳,刘世亮,柳开楼. 典型红壤不同形态氮素迁移对长期施肥制度的响应[J]. 中国农业科学, 2019, 52(14): 2468-2483.
SHEN FengMin,JIANG GuiYing,ZHANG YuJun,LIU Fang,LIU ShiLiang,LIU KaiLou. Response of Different Forms of Nitrogen Migration in Typical Red Soil to Long-Term Different Fertilization Systems[J]. Scientia Agricultura Sinica, 2019, 52(14): 2468-2483.
表3
不同处理早、晚稻产量"
处理 Treatment | 早稻Early rice | 晚稻Late rice | |||||
---|---|---|---|---|---|---|---|
稻谷产量 Grain yield | 稻草产量 Straw yield | 总生物量 Total biomass | 稻谷产量 Grain yield | 稻草产量 Straw yield | 总生物量 Total biomass | ||
CK | 2463c | 2985c | 5448c | 4271bc | 5177bc | 9448c | |
NPK | 4023b | 4877b | 8900b | 4744b | 5751b | 10495b | |
NPKS | 3915b | 4633b | 8548b | 4807b | 5689b | 10497b | |
NPKSM | 5272a | 6239a | 11512a | 5858a | 6933a | 12791a |
表4
不同处理早、晚稻稻谷和稻草氮含量及氮吸收量"
处理 Treatment | 氮含量 N content (g·kg-1) | 氮吸收量 N accumulation (kg·hm-2) | ||||
---|---|---|---|---|---|---|
稻谷Grain | 稻草Straw | 稻谷Grain | 稻草Straw | 植株 Total | ||
早稻 Early rice | ||||||
CK | 10.44b | 4.22a | 22.11d | 10.83d | 32.94d | |
NPK | 11.22b | 4.69a | 38.82c | 19.66b | 58.48c | |
NPKS | 13.87a | 4.29a | 46.70b | 17.09c | 63.79b | |
NPKSM | 13.61a | 4.42a | 61.71a | 23.71a | 85.42a | |
晚稻 Late rice | ||||||
CK | 11.33a | 3.83b | 41.61c | 17.05c | 58.67c | |
NPK | 10.09a | 4.44a | 41.17c | 21.96b | 63.13bc | |
NPKS | 11.43a | 4.37a | 47.28b | 21.38b | 68.66b | |
NPKSM | 11.79a | 4.48a | 59.38a | 26.71a | 86.09a |
表5
双季稻体系氮素平衡"
处理 Treatment | 氮投入 Nitrogen input | 氮输出Nitrogen output | 氮表观损失 Apparent N loss | ||||||
---|---|---|---|---|---|---|---|---|---|
化肥 Mineral fertilizer | 稻草 Straw | 紫云英 Green manure | 猪粪 Pig manure | 起始无机氮 Initial Nmin | 作物吸收 Crop uptake | 残留无机氮 Residual Nmin | |||
CK | 233.04c | 91.60c | 180.00c | -38.56d | |||||
NPK | 90.0 | 247.68c | 121.61b | 203.04c | 13.03c | ||||
NPKS | 90.0 | 35.2 | 135.5 | 329.28b | 132.44b | 383.18b | 74.35b | ||
NPKSM | 90.0 | 35.2 | 135.5 | 140.9 | 371.83a | 171.51a | 425.78a | 176.14a |
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