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    In:  Supplement to: Li, Xiang; Hu, Xiumian; Cai, Yuanfeng; Han, Zhiyan (2011): Quantitative analysis of iron oxide concentrations within Aptian-Albian cyclic oceanic red beds in ODP Hole 1049C, North Atlantic. Sedimentary Geology, 235(1-2), 91-99, https://doi.org/10.1016/j.sedgeo.2010.06.024
    Publication Date: 2024-01-09
    Description: Aptian–Albian sediments in Core 12X of Hole 1049C (ODP Leg 171B) are characterized by high-frequency cycles that consist of alternating layers of red and green/white clayey chalk, and claystone. The first derivative curves of diffuse reflectance spectra (DRS) for samples of different colors reveal that red (brown and orange) samples show clear peaks corresponding to hematite and goethite. Following treatment using the CBD (citrate-bicarbonate-dithionite) procedure, the red samples lost their red color and corresponding peaks in the first derivative curve, and became greenish or whitish. Therefore, hematite and goethite are the minerals responsible for the reddish change in sample color. However, these minerals behave differently from each other in terms of determining the color of sediment: hematite imparts a red color, whereas goethite imparts a yellow color. Therefore, a change in the proportions of hematite and goethite can cause a change in sediment color from orange to brown. To obtain the absolute contents of iron oxides in these sediments, we performed a quantitative analysis using DRS with multiple linear regression. The results reveal that the Albian brown beds contain 0.13–0.82% hematite (average value, 0.51%) and 0.22–0.81% goethite (average value, 0.58%). The Aptian orange beds contain 0.19–0.46% hematite (average value, 0.35%) and 0.29–0.67% goethite (average value, 0.50%). X-ray diffraction analysis of the Aptian and Albian cycles reveals no clear variations in mineral content with sediment color. It is suggested that hematite and goethite were derived from oxic environments during the period of deposition and early diagenesis. The oxic conditions were probably determined by the low accumulation rate of organic matter and the high content of dissolved oxygen in bottom water.
    Keywords: 171-1049C; Blake Nose, North Atlantic Ocean; Color reflectance interval 400-450 nm wavelength; Color reflectance interval 450-490 nm wavelength; Color reflectance interval 490-560 nm wavelength; Color reflectance interval 560-590 nm wavelength; Color reflectance interval 590-630 nm wavelength; Color reflectance interval 630-700 nm wavelength; DEPTH, sediment/rock; DRILL; Drilling/drill rig; Goethite; Hematite, Fe2O3; Joides Resolution; Leg171B; Number; Ocean Drilling Program; ODP; Spectrophotometer Perkin-Elmer Lambda 6; X-ray diffraction (XRD)
    Type: Dataset
    Format: text/tab-separated-values, 189 data points
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  • 2
    Publication Date: 2012-02-18
    Description: Understanding the influence of complex interactions among hydrological factors, soil characteristics and biogeochemical functions on nutrient dynamics in overland flow is important for efficiently managing agricultural non-point pollution. Experiments were conducted to assess nutrient export from Ultisol soils in the Sunjia catchment, Jiangxi province, southern China, between 2003 and 2005. Four plots were divided into two groups: two peanut plots and two agro-forestry (peanut intercropped with citrus) plots. During the study period we collected water samples for chemical analyses after each rainfall event that generated overland flow in order to assess nutrient export dynamics. The concentrations of potassium (K) and nitrate-N (NO 3 – –N) in overland flow were higher during the wetting season (winter and early spring). This reflects the solubility of K and NO 3 – –N, the accumulation of NO 3 – –N during the dry season and an increase in desorption processes and mixing with pre-event water caused by prolonged contact with soil in areas with long-duration, low-intensity rainfall. In contrast, concentrations of total nitrogen (TN) and total phosphate (TP) were higher during the wet season (late March to early July) and during the dry season (mid-July to the end of September or early October). This was due to the interaction between specific hydrological regimes, the properties of the Ultisol and particulate transport processes. Variations in nutrient concentrations during storm events further identified that event water was the dominant source of TN and TP, and pre-event water was the dominant source of NO 3 – –N. In addition, the results obtained for the different land uses suggest that agro-forestry practices reduce nutrient loss via overland flow. Copyright © 2012 John Wiley & Sons, Ltd.
    Print ISSN: 0885-6087
    Electronic ISSN: 1099-1085
    Topics: Architecture, Civil Engineering, Surveying , Geography
    Published by Wiley-Blackwell
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