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储存、施肥和成本特性凸显了干燥微生物生物质作为有机肥料的潜力。

Storage, fertilization and cost properties highlight the potential of dried microbial biomass as organic fertilizer.

作者信息

Spanoghe Janne, Grunert Oliver, Wambacq Eva, Sakarika Myrsini, Papini Gustavo, Alloul Abbas, Spiller Marc, Derycke Veerle, Stragier Lutgart, Verstraete Harmien, Fauconnier Koen, Verstraete Willy, Haesaert Geert, Vlaeminck Siegfried E

机构信息

Research Group of Sustainable Energy, Air and Water Technology (DuEL), Department of Bioscience Engineering, University of Antwerp, Groenenborgerlaan 171, 2020, Antwerpen, Belgium.

Greenyard Horticulture Belgium NV, Skaldenstraat 7a, 9042, Gent, Belgium.

出版信息

Microb Biotechnol. 2020 Sep;13(5):1377-1389. doi: 10.1111/1751-7915.13554. Epub 2020 Mar 16.

DOI:10.1111/1751-7915.13554
PMID:32180337
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC7415357/
Abstract

The transition to sustainable agriculture and horticulture is a societal challenge of global importance. Fertilization with a minimum impact on the environment can facilitate this. Organic fertilizers can play an important role, given their typical release pattern and production through resource recovery. Microbial fertilizers (MFs) constitute an emerging class of organic fertilizers and consist of dried microbial biomass, for instance produced on effluents from the food and beverage industry. In this study, three groups of organisms were tested as MFs: a high-rate consortium aerobic bacteria (CAB), the microalga Arthrospira platensis ('Spirulina') and a purple non-sulfur bacterium (PNSB) Rhodobacter sp. During storage as dry products, the MFs showed light hygroscopic activity, but the mineral and organic fractions remained stable over a storage period of 91 days. For biological tests, a reference organic fertilizer (ROF) was used as positive control, and a commercial organic growing medium (GM) as substrate. The mineralization patterns without and with plants were similar for all MFs and ROF, with more than 70% of the organic nitrogen mineralized in 77 days. In a first fertilization trial with parsley, all MFs showed equal performance compared to ROF, and the plant fresh weight was even higher with CAB fertilization. CAB was subsequently used in a follow-up trial with petunia and resulted in elevated plant height, comparable chlorophyll content and a higher amount of flowers compared to ROF. Finally, a cost estimation for packed GM with supplemented fertilizer indicated that CAB and a blend of CAB/PNSB (85%/15%) were most cost competitive, with an increase of 6% and 7% in cost compared to ROF. In conclusion, as bio-based fertilizers, MFs have the potential to contribute to sustainable plant nutrition, performing as good as a commercially available organic fertilizer, and to a circular economy.

摘要

向可持续农业和园艺的转型是一项具有全球重要性的社会挑战。对环境影响最小的施肥方式有助于实现这一目标。鉴于有机肥料典型的养分释放模式以及通过资源回收进行生产,其在这方面可发挥重要作用。微生物肥料是一类新兴的有机肥料,由干燥的微生物生物质组成,例如利用食品和饮料行业的废水生产而成。在本研究中,测试了三组生物作为微生物肥料:高速率混合需氧菌(CAB)、微藻钝顶螺旋藻(“螺旋藻”)和紫色非硫细菌(PNSB)红假单胞菌。作为干燥产品储存期间,微生物肥料表现出轻微的吸湿活性,但在91天的储存期内,矿物质和有机成分保持稳定。进行生物学测试时,使用一种参考有机肥料(ROF)作为阳性对照,并使用一种商业有机种植基质(GM)作为底物。所有微生物肥料和ROF在有无植物的情况下矿化模式相似,77天内超过70%的有机氮被矿化。在首次用欧芹进行的施肥试验中,与ROF相比,所有微生物肥料表现相当,用CAB施肥时植物鲜重甚至更高。随后,CAB被用于矮牵牛的后续试验,与ROF相比,其使植株高度增加、叶绿素含量相当且花朵数量更多。最后,对添加肥料的包装GM进行成本估算表明,CAB以及CAB/PNSB混合物(85%/15%)在成本方面最具竞争力,与ROF相比成本分别增加了6%和7%。总之,作为生物基肥料,微生物肥料有潜力促进可持续植物营养,其性能与市售有机肥料相当,并有助于循环经济。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f50a/7415357/e819fe52d8f3/MBT2-13-1377-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f50a/7415357/dc896e127c5a/MBT2-13-1377-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f50a/7415357/8abb757cc6c5/MBT2-13-1377-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f50a/7415357/a4bc522b4ea1/MBT2-13-1377-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f50a/7415357/da63c127a96b/MBT2-13-1377-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f50a/7415357/7e65905f0938/MBT2-13-1377-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f50a/7415357/a2dbafe60993/MBT2-13-1377-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f50a/7415357/e819fe52d8f3/MBT2-13-1377-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f50a/7415357/dc896e127c5a/MBT2-13-1377-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f50a/7415357/8abb757cc6c5/MBT2-13-1377-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f50a/7415357/a4bc522b4ea1/MBT2-13-1377-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f50a/7415357/da63c127a96b/MBT2-13-1377-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f50a/7415357/7e65905f0938/MBT2-13-1377-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f50a/7415357/a2dbafe60993/MBT2-13-1377-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f50a/7415357/e819fe52d8f3/MBT2-13-1377-g007.jpg

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