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嘧菌酯污染土壤的生物强化

Bioaugmentation of Soil Contaminated with Azoxystrobin.

作者信息

Baćmaga Małgorzata, Wyszkowska Jadwiga, Kucharski Jan

机构信息

Department of Microbiology, University of Warmia and Mazury, Olsztyn|Plac Łódzki 3, 10-727 Olsztyn, Poland.

出版信息

Water Air Soil Pollut. 2017;228(1):19. doi: 10.1007/s11270-016-3200-9. Epub 2016 Dec 9.

Abstract

The presence of fungicides in the natural environment, either resulting from deliberate actions or not, has become a serious threat to many ecosystems, including soil. This can be prevented by taking appropriate measures to clear the environment of organic contamination, including fungicides. Therefore, a study was conducted aimed at determining the effect of bioaugmentation of soil exposed to azoxystrobin on its degradation and activity of selected enzymes (dehydrogenases, catalase, urease, acidic phosphatase, alkaline phosphatase). A model experiment was conducted for 90 days on two types of soil: loamy sand (pH-5.6) and sandy loam (pH-7.0), which were contaminated by azoxystrobin at 22.50 mg kg DM of soil and inoculated with a specific consortium of microorganisms. Four strains of bacteria were used in the experiment ( sp. LM655314.1, KC848897.1, KF831381.1, KJ843149.1) and two strains of mould fungi ( AB861677.1, JN943451.1). Inoculation of soil with the consortium of microorganisms accelerated the degradation of azoxystrobin. The isolated microorganisms were more active in loamy sand because within 90 days azoxystrobin was degraded by 24% ( sp., , , ) to 78% (, ). In sandy loam, azoxystrobin was degraded by 9% (, ) to 29% ( sp., , , and , ). The activity of soil enzymes was also changed as a result of inoculation of soil with microorganisms. The activity of all of the enzymes under study was found to have increased when soil augmentation was performed.

摘要

无论是否出于人为故意,自然环境中杀菌剂的存在已对包括土壤在内的许多生态系统构成严重威胁。可以通过采取适当措施清除包括杀菌剂在内的有机污染物来预防这种情况。因此,开展了一项研究,旨在确定对暴露于嘧菌酯的土壤进行生物强化对其降解及所选酶(脱氢酶、过氧化氢酶、脲酶、酸性磷酸酶、碱性磷酸酶)活性的影响。在两种土壤上进行了为期90天的模型实验:壤质砂土(pH值为5.6)和砂壤土(pH值为7.0),这两种土壤均被22.50毫克/千克干土的嘧菌酯污染,并接种了特定的微生物群落。实验使用了四株细菌(菌株编号分别为LM655314.1、KC848897.1、KF831381.1、KJ843149.1)和两株霉菌(菌株编号分别为AB861677.1、JN943451.1)。用微生物群落接种土壤加速了嘧菌酯的降解。分离出的微生物在壤质砂土中活性更高,因为在90天内嘧菌酯的降解率为24%(菌株编号为……)至78%(菌株编号为……)。在砂壤土中,嘧菌酯的降解率为9%(菌株编号为……)至29%(菌株编号为……和……)。用微生物接种土壤也导致了土壤酶活性的变化。研究发现,进行土壤强化时,所有研究的酶的活性均有所增加。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/f5bc/5145903/e3fb2411b527/11270_2016_3200_Fig1_HTML.jpg

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