Variation in microbial biomass and enzymatic activities in metal contaminated soils during storage at low temperature (4°C)

化学 酸性磷酸酶 碱性磷酸酶 微生物种群生物学 土壤水分 生物量(生态学) 氨肽酶 动物科学 食品科学 亮氨酸 环境化学 农学 生物化学 生态学 生物 细菌 氨基酸 遗传学
作者
Alistar Moy,K. K. Nkongolo
出处
期刊:Chemistry and Ecology [Taylor & Francis]
卷期号:39 (7): 688-709
标识
DOI:10.1080/02757540.2023.2253222
摘要

ABSTRACTMicrobial response to soil storage at low temperature in limed and unlimed samples has not been investigated. For this study, soil samples were kept at 4°C for six weeks. Soil microbial biomass was determined using phospholipid fatty acid analysis (PLFA). Nine enzymes were targeted including β-glucosidase (BG), cellobiohydrolase (CBH), β-N-acetylglucosaminidase (NAGase), aryl sulfatase (AS), acid phosphatase (AP), alkaline phosphatase (AlP), glycine aminopeptidase (GAP), leucine aminopeptidase (LAP), and peroxidase (PER). PLFA results revealed a significant increase in total microbial biomass in limed area compared to unlimed soil samples. Microbial biomass decreased during the first two weeks of storage and remained unchanged thereafter for both limed and unlimed samples. Analysis of microbial activities revealed that most enzymes inconsistently decreased over time during storage at 4°C. Activities of BG, CBH, NAGase, AlP, AS, GAP, LAP were significantly higher in limed compared to the unlimed samples. Overall, the levels of activities of most enzymes in limed soils decreased significantly after the second week of storage and remained unchanged thereafter. The reduction of enzyme activity in the unlimed soil samples varied over time, with some enzymes such as LAP increasing on the sixth week. PER activity decreased after two weeks and increased thereafter.KEYWORDS: Enzymatic activitiesmicrobial biomasslow temperaturephospholipid fatty acid analysissoil limingstorage AcknowledgementAnalytical support of Dr. Paul Michael, Dr. Ramya Narendrula-Kotha, and Megan McKergow is greatly appreciated.Disclosure statementNo potential conflict of interest was reported by the author(s).Additional informationFundingThis work received financial support from the Natural Sciences and Engineering Research Council of Canada (NSERC), Vale Limited, and Sudbury Nickel Operations (Glencore Limited), Canada (Grant numbers NSERC-CRD-470535-14 and NSERC-RGPIN-5323-4).Notes on contributorsAlistar MoyAlistar Moy is a M.Sc. student in the Department of Biology at Laurentian University, Ontario, Canada.Kabwe NkongoloKabwe Nkongolo is a Professor of Genetics in the Department of Biology and the Biomolecular Science Program at Laurentian University in Sudbury (Ontario, Canada). He is the Coordinator of the Environmental Genetics and Biotechnology Research Laboratory. He runs a very productive research programme with a focus on genetic adaptation to soil metal contamination in plants.
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