A newer version of this dataset is available. View the latest version.
Version DOI Comment Publication Date
3 10.13012/B2IDB-2865725_V3 The updates added a few more records and rearranged the sequence of the tables in order to support the upcoming publication. 2021-04-19
2 10.13012/B2IDB-2865725_V2 Updated data by adding more records and columns 2019-10-22
1 10.13012/B2IDB-2865725_V1 2018-06-01
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update: {"nested_updated_at"=>[Thu, 01 Feb 2024 17:55:57.713226000 UTC +00:00, Thu, 01 Feb 2024 17:55:57.992902000 UTC +00:00]} 2024-02-01T17:55:57Z
update: {"nested_updated_at"=>[Thu, 01 Feb 2024 17:55:57.675304000 UTC +00:00, Thu, 01 Feb 2024 17:55:57.713226000 UTC +00:00]} 2024-02-01T17:55:57Z
update: {"nested_updated_at"=>[Thu, 01 Feb 2024 17:55:57.626724000 UTC +00:00, Thu, 01 Feb 2024 17:55:57.675304000 UTC +00:00]} 2024-02-01T17:55:57Z
update: {"nested_updated_at"=>[Tue, 22 Oct 2019 16:19:53.346804000 UTC +00:00, Thu, 01 Feb 2024 17:55:57.626724000 UTC +00:00]} 2024-02-01T17:55:57Z
update: {"nested_updated_at"=>[nil, Tue, 22 Oct 2019 16:19:53.346804000 UTC +00:00]} 2024-01-03T18:23:23Z
update: {"subject"=>["", "Life Sciences"]} 2018-07-23T14:08:23Z
update: {"description"=>["Dataset compiled by Yushu Xia and Michelle Wander for the Soil Health Institute (need agreement #)\r\nData were recovered from peer reviewed literature reporting results for three ‘Tier 2’ indicators (β-glucosidase (BG), fluorescein diacetate (FDA) hydrolysis, and permanganate oxidizable carbon (POXC)) in terms of their relative response to management where soils under cover crops, grassland cover, organic amendments and residue return compared to conventionally managed controls. \r\nPeer-reviewed articles published between January of 1990 and December 2017 were searched using the Thomas Reuters Web of Science database (Thomas Reuters, Philadelphia, Pennsylvania) and Google Scholar to identify studies reporting results for: “β-glucosidase”, “permanganate oxidizable carbon”, “active carbon”, “readily oxidizable carbon”, and “fluorescein diacetate hydrolysis”, together with one or more of the following: “management practice”, “tillage”, “cover crop”, “residue”, “organic fertilizer”, or “manure”. Records were tabulated to compare SQI abundance in soil maintained under a control (conventional cropping with that found under soil health promoting practice) and soil aggrading practice with the intent to contribute to SQI databases that will support development of interpretive frameworks and/or algorithms including pedo-transfer functions relating indicator abundance to management practices and site specific factors. \r\nMeta-data include key descriptor variables and covariates useful for development of scoring functions which include: 1) identifying factors for the study site (location, year of initiation of study and year in which data was reported), 2) soil textural class and pH, 3) depth of sampling, 4) analytical methods for quantification (i.e.: loss on ignition, combustion), 5) units used in published works (i.e.: equivalent mass, concentration), 6) SOM class (L,M.H), and 7) statistical significance of difference comparisons. \r\n\r\n", "Dataset compiled by Yushu Xia and Michelle Wander for the Soil Health Institute.\r\nData were recovered from peer reviewed literature reporting results for three ‘Tier 2’ indicators (β-glucosidase (BG), fluorescein diacetate (FDA) hydrolysis, and permanganate oxidizable carbon (POXC)) in terms of their relative response to management where soils under cover crops, grassland cover, organic amendments and residue return compared to conventionally managed controls. \r\nPeer-reviewed articles published between January of 1990 and December 2017 were searched using the Thomas Reuters Web of Science database (Thomas Reuters, Philadelphia, Pennsylvania) and Google Scholar to identify studies reporting results for: “β-glucosidase”, “permanganate oxidizable carbon”, “active carbon”, “readily oxidizable carbon”, and “fluorescein diacetate hydrolysis”, together with one or more of the following: “management practice”, “tillage”, “cover crop”, “residue”, “organic fertilizer”, or “manure”. Records were tabulated to compare SQI abundance in soil maintained under a control (conventional cropping with that found under soil health promoting practice) and soil aggrading practice with the intent to contribute to SQI databases that will support development of interpretive frameworks and/or algorithms including pedo-transfer functions relating indicator abundance to management practices and site specific factors. \r\nMeta-data include key descriptor variables and covariates useful for development of scoring functions which include: 1) identifying factors for the study site (location, year of initiation of study and year in which data was reported), 2) soil textural class and pH, 3) depth of sampling, 4) analytical methods for quantification (i.e.: loss on ignition, combustion), 5) units used in published works (i.e.: equivalent mass, concentration), 6) SOC class (L,M,H), and 7) statistical significance of difference comparisons. \r\n\r\n"], "version_comment"=>[nil, ""], "subject"=>[nil, ""]} 2018-06-01T20:19:09Z