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在盆栽试验中,生物炭与氮肥的联合施用提高了水稻产量、微生物活性和氮代谢。

Combined application of biochar and nitrogen fertilizer improves rice yield, microbial activity and N-metabolism in a pot experiment.

作者信息

Ali Izhar, Ullah Saif, He Liang, Zhao Quan, Iqbal Anas, Wei Shangqing, Shah Tariq, Ali Niyaz, Bo Yan, Adnan Muhammad, Jiang Ligeng

机构信息

Key Laboratory of Crop Cultivation and Farming System, College of Agriculture, Guangxi University, Nanning, Guangxi, China.

Department of Agronomy, Faculty of Crop Production Sciences, University of Agriculture, Peshawar, Pakistan.

出版信息

PeerJ. 2020 Nov 13;8:e10311. doi: 10.7717/peerj.10311. eCollection 2020.

DOI:10.7717/peerj.10311
PMID:33240639
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC7668215/
Abstract

The excessive use of synthetic nitrogen (N) fertilizers in rice ( L.) has resulted in high N loss, soil degradation, and environmental pollution in a changing climate. Soil biochar amendment is proposed as a climate change mitigation tool that supports carbon sequestration and reduces N losses and greenhouse gas (GHG) emissions from the soil. The current study evaluated the impact of four different rates of biochar (B) (C/B-0 t ha, B-20 t ha, B-40 t ha, and B-60 t ha) and two N levels (N; low (270 kg N ha) and N; high (360 kg N ha)), on rice (cultivar Zhenguiai) grown in pots. Significant increases in the average soil microbial biomass N (SMBN) (88%) and carbon (87%) were recorded at the highest rate of 60-ton haB and 360 kg N ha compared to the control (NC) during both seasons (S1 and S2). The photochemical efficiency (Fv/Fm), quantum yield of the photosystem (PS) II (ΦPS II), electron transport rate (ETR), and photochemical quenching () were enhanced at low rates of biochar applications (20 to 40 t B ha) for high and low N rates across the seasons. Nitrate reductase (NR), glutamine synthetase (GS), and glutamine 2-oxoglutarate aminotransferase (GOGAT) activity were, on average, 39%, 55%, and 63% higher in the NB, NB, and NB treatments, respectively than the NC. The grain quality was higher in the N1B treatment than the NC, i.e., the protein content (PC), amylose content (AC), percent brown rice (BRP), and percent milled rice (MRP) were, on average, 16%, 28%, 4.6%, and 5% higher, respectively in both seasons. The results of this study indicated that biochar addition to the soil in combination with N fertilizers increased the dry matter (DM) content, N uptake, and grain yield of rice by 24%, 27%, and 64%, respectively, compared to the NC.

摘要

在气候变化背景下,水稻种植中过量使用合成氮肥导致了大量氮素流失、土壤退化和环境污染。土壤生物炭改良被提议作为一种缓解气候变化的工具,它有助于碳固存,并减少土壤中的氮素流失和温室气体排放。本研究评估了四种不同施用量的生物炭(B)(C/B - 0 t·ha⁻¹、B - 20 t·ha⁻¹、B - 40 t·ha⁻¹和B - 60 t·ha⁻¹)以及两种氮水平(N;低氮(270 kg N·ha⁻¹)和N;高氮(360 kg N·ha⁻¹))对盆栽种植的水稻(品种镇谷矮)的影响。与对照(NC)相比,在两个季节(S1和S2)中,60 t·ha⁻¹的最高生物炭施用量和360 kg N·ha⁻¹的氮水平下,土壤微生物生物量氮(SMBN)(88%)和碳(87%)显著增加。在两个季节中,对于高氮和低氮水平,低生物炭施用量(20至40 t B·ha⁻¹)提高了光化学效率(Fv/Fm)、光系统(PS)II的量子产率(ΦPS II)、电子传递速率(ETR)和光化学猝灭(qP)。平均而言,在NB₄₀、NB₆₀和NB₆₀处理中,硝酸还原酶(NR)、谷氨酰胺合成酶(GS)和谷氨酰胺 - 2 - 酮戊二酸氨基转移酶(GOGAT)的活性分别比NC高39%、55%和63%。在N₁B₄₀处理中,稻米品质高于NC,即在两个季节中,蛋白质含量(PC)、直链淀粉含量(AC)、糙米率(BRP)和精米率(MRP)平均分别高出16%、28%、4.6%和5%。本研究结果表明,与NC相比,向土壤中添加生物炭并结合氮肥,水稻的干物质(DM)含量、氮素吸收量和籽粒产量分别提高了24%、27%和64%。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2989/7668215/7cae0b26bf56/peerj-08-10311-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2989/7668215/0c0a871ca905/peerj-08-10311-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2989/7668215/3212ade95e45/peerj-08-10311-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2989/7668215/c3a911fb7d23/peerj-08-10311-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2989/7668215/c43d3148c45c/peerj-08-10311-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2989/7668215/e6907f3e82c4/peerj-08-10311-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2989/7668215/8a68605a7a27/peerj-08-10311-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2989/7668215/7cae0b26bf56/peerj-08-10311-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2989/7668215/0c0a871ca905/peerj-08-10311-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2989/7668215/3212ade95e45/peerj-08-10311-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2989/7668215/c3a911fb7d23/peerj-08-10311-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2989/7668215/c43d3148c45c/peerj-08-10311-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2989/7668215/e6907f3e82c4/peerj-08-10311-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2989/7668215/8a68605a7a27/peerj-08-10311-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2989/7668215/7cae0b26bf56/peerj-08-10311-g007.jpg

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