Humberto Blanco‐Canqui, Paul Jasa, Richard B. Ferguson, Glen Slater
{"title":"覆盖作物与土壤深层碳积累:10 年后的研究显示了什么?","authors":"Humberto Blanco‐Canqui, Paul Jasa, Richard B. Ferguson, Glen Slater","doi":"10.1002/saj2.20747","DOIUrl":null,"url":null,"abstract":"The extent to which cover crops (CCs) accumulate soil organic carbon (SOC) in the entire soil profile is still unclear. We measured SOC, permanganate oxidizable C (POX‐C), and particulate organic matter (POM) concentrations down to 60‐cm soil depth in early [2–3 week before corn (<jats:italic>Zea mays</jats:italic> L.) planting]‐ and late‐terminated (at corn planting) winter rye (<jats:italic>Secale cereale</jats:italic> L.) CCs in rainfed and irrigated no‐till continuous corn systems in the U.S. Corn Belt after 10 years. CCs increased SOC stock and SOC, POX‐C, and POM concentrations but only in the irrigated system in the upper 5‐cm depth. Late‐terminated CC increased SOC concentration by 4.710 ± 3.501 g kg<jats:sup>−1</jats:sup> and accumulated SOC at 0.207 ± 0.145 Mg C ha<jats:sup>−1</jats:sup> year<jats:sup>−1</jats:sup>. It increased POX‐C and POM concentrations, on average, by 1.194 times. CCs likely increased SOC in the irrigated system by producing more biomass (2.247 ± 0.370 Mg ha<jats:sup>−1</jats:sup>) than in the rainfed system (0.949 ± 0.338 Mg ha<jats:sup>−1</jats:sup>). At least 2 Mg ha<jats:sup>−1</jats:sup> of CC biomass may be needed to increase SOC. Because winter CCs often produce <1 Mg ha<jats:sup>−1</jats:sup> of biomass when typically planted late and terminated early, extending the CC growing window by terminating CCs at or after crop planting (planting green) may boost CC biomass and SOC accumulation, although high‐C soils or Mollisols, such as our study soils (>22 g C kg<jats:sup>−1</jats:sup>), may limit SOC gains. We submit CCs would sequester more SOC in low‐C, eroded, and low‐fertility soils. Overall, winter rye CCs minimally alter soil C in the soil profile in no‐till continuous corn systems after 10 years.","PeriodicalId":22142,"journal":{"name":"Soil Science Society of America Journal","volume":null,"pages":null},"PeriodicalIF":2.4000,"publicationDate":"2024-08-27","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":"{\"title\":\"Cover crops and deep‐soil C accumulation: What does research show after 10 years?\",\"authors\":\"Humberto Blanco‐Canqui, Paul Jasa, Richard B. Ferguson, Glen Slater\",\"doi\":\"10.1002/saj2.20747\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"The extent to which cover crops (CCs) accumulate soil organic carbon (SOC) in the entire soil profile is still unclear. We measured SOC, permanganate oxidizable C (POX‐C), and particulate organic matter (POM) concentrations down to 60‐cm soil depth in early [2–3 week before corn (<jats:italic>Zea mays</jats:italic> L.) planting]‐ and late‐terminated (at corn planting) winter rye (<jats:italic>Secale cereale</jats:italic> L.) CCs in rainfed and irrigated no‐till continuous corn systems in the U.S. Corn Belt after 10 years. CCs increased SOC stock and SOC, POX‐C, and POM concentrations but only in the irrigated system in the upper 5‐cm depth. Late‐terminated CC increased SOC concentration by 4.710 ± 3.501 g kg<jats:sup>−1</jats:sup> and accumulated SOC at 0.207 ± 0.145 Mg C ha<jats:sup>−1</jats:sup> year<jats:sup>−1</jats:sup>. It increased POX‐C and POM concentrations, on average, by 1.194 times. CCs likely increased SOC in the irrigated system by producing more biomass (2.247 ± 0.370 Mg ha<jats:sup>−1</jats:sup>) than in the rainfed system (0.949 ± 0.338 Mg ha<jats:sup>−1</jats:sup>). 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引用次数: 0
摘要
目前还不清楚覆盖作物(CC)在整个土壤剖面中积累土壤有机碳(SOC)的程度。我们测量了美国玉米带雨养和灌溉免耕连作玉米系统中早期(玉米(Zea mays L.)播种前 2-3 周)和晚期(玉米播种时)冬黑麦(Secale cereale L.)CCs 的 SOC、高锰酸盐可氧化碳(POX-C)和颗粒有机质(POM)在 60 厘米深土壤中的浓度。CC 增加了 SOC 储量以及 SOC、POX-C 和 POM 的浓度,但只在灌溉系统的上部 5 厘米深度。末期 CC 使 SOC 浓度增加了 4.710 ± 3.501 g kg-1,SOC 累积量为 0.207 ± 0.145 Mg C ha-1 year-1。POX-C 和 POM 浓度平均增加了 1.194 倍。与雨水灌溉系统(0.949 ± 0.338 兆克/公顷-1)相比,灌溉系统中的 CC 可能通过产生更多生物量(2.247 ± 0.370 兆克/公顷-1)来增加 SOC。要增加 SOC,可能至少需要 2 Mg ha-1 的 CC 生物量。由于冬季 CC 通常在晚种植和早结束时产生 1 兆克/公顷-1 的生物量,因此通过在作物播种时或播种后(绿色种植)结束 CC 来延长 CC 的生长期可能会增加 CC 的生物量和 SOC 积累,尽管高碳土壤或 Mollisols(如我们的研究土壤(22 克碳氢化合物/千克-1))可能会限制 SOC 的增加。我们认为,CC 会在低碳土壤、侵蚀土壤和低肥力土壤中封存更多的 SOC。总的来说,在免耕连作玉米系统中,冬黑麦 CC 在 10 年后对土壤剖面中的土壤碳含量的改变微乎其微。
Cover crops and deep‐soil C accumulation: What does research show after 10 years?
The extent to which cover crops (CCs) accumulate soil organic carbon (SOC) in the entire soil profile is still unclear. We measured SOC, permanganate oxidizable C (POX‐C), and particulate organic matter (POM) concentrations down to 60‐cm soil depth in early [2–3 week before corn (Zea mays L.) planting]‐ and late‐terminated (at corn planting) winter rye (Secale cereale L.) CCs in rainfed and irrigated no‐till continuous corn systems in the U.S. Corn Belt after 10 years. CCs increased SOC stock and SOC, POX‐C, and POM concentrations but only in the irrigated system in the upper 5‐cm depth. Late‐terminated CC increased SOC concentration by 4.710 ± 3.501 g kg−1 and accumulated SOC at 0.207 ± 0.145 Mg C ha−1 year−1. It increased POX‐C and POM concentrations, on average, by 1.194 times. CCs likely increased SOC in the irrigated system by producing more biomass (2.247 ± 0.370 Mg ha−1) than in the rainfed system (0.949 ± 0.338 Mg ha−1). At least 2 Mg ha−1 of CC biomass may be needed to increase SOC. Because winter CCs often produce <1 Mg ha−1 of biomass when typically planted late and terminated early, extending the CC growing window by terminating CCs at or after crop planting (planting green) may boost CC biomass and SOC accumulation, although high‐C soils or Mollisols, such as our study soils (>22 g C kg−1), may limit SOC gains. We submit CCs would sequester more SOC in low‐C, eroded, and low‐fertility soils. Overall, winter rye CCs minimally alter soil C in the soil profile in no‐till continuous corn systems after 10 years.
期刊介绍:
SSSA Journal publishes content on soil physics; hydrology; soil chemistry; soil biology; soil biochemistry; soil fertility; plant nutrition; pedology; soil and water conservation and management; forest, range, and wildland soils; soil and plant analysis; soil mineralogy, wetland soils. The audience is researchers, students, soil scientists, hydrologists, pedologist, geologists, agronomists, arborists, ecologists, engineers, certified practitioners, soil microbiologists, and environmentalists.
The journal publishes original research, issue papers, reviews, notes, comments and letters to the editor, and book reviews. Invitational papers may be published in the journal if accepted by the editorial board.