Sadikshya Rana Dangi

Sadikshya Rana Dangi


Research Focus & Metrics

Academic Career Length

18Years (2009-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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1 June 2020 in Applied Soil Ecology
Verified
Journal Article
Closed access
SDSadikshya Rana Dangi
Sadikshya Rana Dangi
SGSuduan Gao
Suduan Gao
YDYinghua Duan
Yinghua Duan
DWDong Wang
Dong Wang

1 May 2012 in Soil Science Society of America Journal
Verified
Journal Article
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PDF file
SDSadikshya Rana Dangi
Sadikshya Rana Dangi
PSPeter D. Stahl
Peter D. Stahl
AWAbbey F. Wick
Abbey F. Wick
LILachlan J. Ingram
Lachlan J. Ingram
JBJeffrey S. Buyer
Jeffrey S. Buyer

7 March 2010 in Land Degradation & Development
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Journal Article
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SDSadikshya Rana Dangi
Sadikshya Rana Dangi
PSP. D. Stahl
P. D. Stahl
EPElise Pendall
Elise Pendall
MCM. B. Cleary
M. B. Cleary
JBJ. S. Buyer
J. S. Buyer

20 June 2016 in Plant and Soil
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Journal Article
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KRKurt O. Reinhart
Kurt O. Reinhart
SDSadikshya Rana Dangi
Sadikshya Rana Dangi
LVLance T. Vermeire
Lance T. Vermeire

24 May 2017 in Agronomy
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Journal Article
Open access
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SDSadikshya Rana Dangi
Sadikshya Rana Dangi
RTRebecca Tirado-Corbala
Rebecca Tirado-Corbala
JGJames Gerik
James Gerik
BHBradley D. Hanson
Bradley D. Hanson
High value crop producers in California rely heavily on soil fumigation to control a wide array of soil borne pests including nematodes, pathogens and weeds. Fumigants with broad biocidal activity can affect soil microbial communities that contribute to nutrient cycling and plant nutrient uptake which can impact soil health. It is often thought that soil microbial communities make a relatively rapid recovery following fumigation. However, recently it has been found that repeated application of fumigants over time can have greater and longer lasting impacts on soil microorganisms than single fumigation events. Therefore, the main objective of this study was to determine the effect of long-term repeated application of fumigants on soil microbial communities and compare them with non-fumigated and organic sites. Soil samples were collected from fields in Watsonville, CA. Chronosequence sites were defined by number of years of annual fumigation (yaf) with methyl bromide (15, 26, 33, 39 yaf) at the time of sampling, and representative non-fumigated sites were also included for comparison. Phospholipid fatty acid (PLFA) analysis was used to analyze the samples. The canonical variate analysis showed that microbial communities in sites with a longer history of fumigation (33 and 39 yaf) were similar to one another; however, they differed significantly from 15 yaf site and further analysis concluded that non-fumigated sites were significantly different than fumigated sites. This study showed that the proportion of arbuscular mycorrhizal fungi (AMF) was lower in all fumigated (15, 33 and 39 yaf) sites as compared to their non-fumigated counterparts, which could be a threat to sustainability since AMF plays a major role in soil health and quality.

23 August 2016 in Frontiers in Plant Science
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Journal Article
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GBGary Banuelos
Gary Banuelos
IAIrvin S. Arroyo
Irvin S. Arroyo
SDSadikshya Rana Dangi
Sadikshya Rana Dangi
MZMaria C. Zambrano
Maria C. Zambrano
Selenium (Se) biofortification has been practiced in Se-deficient regions throughout the world primarily by adding inorganic sources of Se to the soil. Considering the use of adding organic sources of Se could be useful as an alternative Se amendment for the production of Se-biofortified food crops. In this multi-year micro-plot study, we investigate growing carrots and broccoli in soils that had been previously amended with Se-enriched Stanleya pinnata Pursh (Britton) three and four years prior to planting one and two, respectively. Results showed that total and extractable Se concentrations in soils (0-30 cm) were 1.65 mg kg-1 and 88 µg L-1, and 0.92 mg kg-1 and 48.6 µg L-1 at the beginning of the growing season for planting one and two, respectively. After each respective growing season, total Se concentrations in the broccoli florets and carrots ranged from 6.99 to 7.83 mg kg-1 and 3.15 to 6.25 mg kg-1 in planting one and two, respectively. In broccoli and carrot plant tissues, SeMet (selenomethionine) was the predominant selenoamino acid identified in Se aqueous extracts. In postharvest soils from planting one, phospholipid analyses (PLFA) showed that amending the soil with S. pinnata exerted no effect on the microbial biomass, AMF (arbuscular mycorrhizal fungi), actinomycetes and Gram-positive and bacterial PLFA at both 0-5 and 0-30 cm, respectively, three years later. Successfully producing Se-enriched broccoli and carrots three and four years later after amending soil with Se-enriched S. pinnata clearly demonstrates its potential source as an organic Se enriched fertilizer for Se-deficient regions.