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dc.contributor.advisor許正一zh_TW
dc.contributor.advisorZeng-Yei Hseu Ph.D.en
dc.contributor.authorMarvin D. Cascantezh_TW
dc.contributor.authorMarvin D. Cascanteen
dc.date.accessioned2025-04-24T16:07:36Z-
dc.date.available2025-04-25-
dc.date.copyright2025-04-24-
dc.date.issued2025-
dc.date.submitted2025-04-21-
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dc.identifier.urihttp://tdr.lib.ntu.edu.tw/jspui/handle/123456789/97319-
dc.description.abstractNonezh_TW
dc.description.abstractOphiolitic soils are derived from mafic and ultramafic parent materials and exhibit distinctive geochemical properties commonly characterized by elevated concentrations of trace metals such as Cr, Ni, and Co, as well as REEs. These soils, however, are often nutrient-deficient and present environmental challenges due to the mobility and bioavailability of potentially toxic metals. This study investigates the pedogenesis, geochemistry, and elemental mobility of ophiolitic soils in Taiwan and the Philippines, focusing on major, trace, and REE distributions across different landscape positions. Soil samples were collected from two ophiolite complexes: one in eastern Taiwan (mudstone-derived soils) and another in Zambales, Philippines (serpentine-derived soils). Comprehensive analyses, including XRD, soil micromorphology, total elemental quantification via ICP-OES/MS, and spectroscopic techniques, were employed to assess mineralogical composition, trace metal distribution, and REE fractionation. Statistical approaches, including Pearson’s correlation and PCA, were applied to elucidate geochemical relationships.
The results revealed distinct textural and chemical differences between the two sites. In Taiwan (CP1 to CP4), soils were clay-rich (45.0%–62.5%), with OC levels ranging from 5.0% to 5.4% in surface horizons, decreasing to 1.3%–3.4% in subsurface layers. In contrast, soil in Zambales (ZB1 and ZB2) exhibited low amounts of clay (31%-50%) but comparable OC levels in surface and subsurface horizons. The concentrations of the trace metals in pedons CP1 to CP4 (Cr: 71.2–105 mg kg⁻¹; Ni: 26.6–43.2 mg kg⁻¹; Co: 20.2–27.9 mg kg⁻¹) were ten times lower than in pedons ZB1 and ZB2 (Cr: 2,437– 3,410 mg kg⁻¹; Ni: 2,919– 4,309 mg kg⁻¹; Co: 209– 300 mg kg⁻¹), consistent with their mafic and ultramafic parent material. Results also indicate significant differences in soil properties, with Taiwan soils displaying higher SiO₂, Al₂O₃, and CaO, indicative of sedimentary influence, whereas Zambales soils exhibit enrichment in Fe₂O₃ and MgO, characteristic of ultramafic origins. Weathering indices suggest that soils in Taiwan have undergone moderate weathering (CIA: 70.6-79.5; RR: 3.28-4.32; VRI: 2.92-5.38), resulting in elemental redistribution, whereas soils in Zambales exhibit lower degrees of weathering (RR: 7.22-16.9), reflecting the less clay contents. The Ca and Mg differed significantly, with the Taiwan soils showing higher Ca/Mg (0.31–1.13), while the Zambales soils had lower Ca/Mg levels (0.00–0.03). Results revealed that Cr, Ni, and Co concentrations in pedons CP1 to CP4 were highly correlated with clay content (p < 0.001) and Fe oxides (p < 0.01, p < 0.05), indicating that trace metals were immobilized through co-precipitation and adsorption. REE fractionation patterns showed significant enrichment of LREEs relative to HREEs, with ΣREEs ranging from 95.7 to 229.5 mg kg⁻¹ in Taiwan and 17.7 to 51.7 mg kg⁻¹ in Zambales, indicating the preferential adsorption of LREEs and greater solubility and weaker affinity of HREEs onto secondary minerals. Environmental risk assessments indicated that while Cr and Ni levels in Taiwan soils were below contamination thresholds (Cr: 175 mg kg⁻¹; Ni: 130 mg kg⁻¹), Zambales soils exceeded global averages (Cr: 100 mg kg⁻¹; Ni: 35 mg kg⁻¹), posing potential toxicity risks for vegetation and groundwater. These findings highlight the impact of parent material, topography, and pedogenic processes on elemental mobility and soil development in the ophiolite complex.
en
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dc.description.tableofcontentsTABLE OF CONTENTS

APPROVAL SHEET i
ACKNOWLEDGMENT v
ABSTRACT vii
TABLE OF CONTENTS ix
LIST OF TABLES xi
LIST OF FIGURES xii
LIST OF EQUATIONS xiv
LIST OF APPENDIX TABLES xv
CHAPTER I. Introduction 1
1.1. Background of ophiolite 1
1.2. Trace elements in soils 2
1.3. Rare earth elements in soils 4
1.4. Conceptual framework of this study 6
1.5. Objectives of the study 7
CHAPTER II. Review of Literature 9
2.1. Genesis of soils derived in ophiolite complex 9
2.2. Primary minerals in soils from ophiolite complex 12
2.3. General characteristics of soils in ophiolite complex 14
2.4. Major elements in the ophiolite complex 16
2.5. Characteristics of trace metals in soils from ophiolite complex 19
2.6. Characteristics of REEs in ophiolite complex 21
2.7. The use of Vis-NIR Spectroscopy in Soil Characterization and Monitoring 25
2.8. The uses of statistical tools, mass balance model, and soil indexes for the determination of the distribution and relationships of soil components 27
CHAPTER III. Materials and Methods 35
3.1. Site description and sampling 35
3.2. Profile description and soil collection 39
3.3. X-ray diffraction mineral identification 40
3.4. Soil micromorphology sample collection, thin section preparation, and observation 40
3.5. Soil physical and chemical analysis 41
3.5.1. Bulk density 41
3.5.2. Particle size analysis 42
6.5.3. Soil pH 43
3.5.3. Soil organic matter 43
3.5.4. Exchangeable bases and base saturation 44
3.5.5. Cation exchange capacity 45
3.5.6. Extractable Fe and Al 46
3.6. Total elemental analysis 46
3.6.1. Major elements 46
3.6.2. Trace metals 47
3.6.3. Rare earth elements 49
3.7. Normalization, fractionation, and anomalies of REEs 51
3.8. Weathering indices of soils 51
3.9. Elemental mass balance calculation 53
3.10. Vis-NIR spectra 54
3.11. Statistical analysis and graphical illustrations 55
CHAPTER IV. Results and Discussion 57
4.1. Soil morphological characteristics 57
4.2. Parent material and micromorphology 61
4.3. Soil physical and chemical characteristics 66
4.4. Soil total content of major oxides and Ca/Mg 73
4.5. Weathering intensity 77
4.6. Total concentrations of trace metals 80
4.7. Concentration of rare earth elements and their normalized pattern 84
4.8. Mobility of soil components 94
4.9. Relationships between soil properties, major elements, trace metals, REEs, and fractionation proxies 101
4.10. Vis-NIR spectra 116
CHAPTER V. Summary and Conclusions 121
CHAPTER X. Literature Cited 125
APPENDICES 141
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dc.language.isoen-
dc.subject蛇紋石土壤zh_TW
dc.subject土壤分類zh_TW
dc.subject土壤化育zh_TW
dc.subject母質層zh_TW
dc.subject生物地球化學zh_TW
dc.subjectsoil classificationen
dc.subjectbiogeochemistryen
dc.subjectparent materialen
dc.subjectpedogenesisen
dc.subjectserpentine soilen
dc.title臺灣與菲律賓蛇綠岩母質土壤中主要、微量與稀土元素的化育特徵zh_TW
dc.titlePedogenetic Characteristics of Major, Trace, and Rare Earth Elements in Ophiolitic Soils of Taiwan and the Philippinesen
dc.typeThesis-
dc.date.schoolyear113-2-
dc.description.degree博士-
dc.contributor.oralexamcommittee陳尊賢;簡士濠;李家興;王尚禮;蔡呈奇zh_TW
dc.contributor.oralexamcommitteeZueng-Sang Chen;Shih-Hao Jien;Chia-Hsing Lee;Shan-Li Wang;Chen-Chi Tsaien
dc.subject.keyword生物地球化學,母質層,土壤化育,蛇紋石土壤,土壤分類,zh_TW
dc.subject.keywordbiogeochemistry,parent material,pedogenesis,serpentine soil,soil classification,en
dc.relation.page152-
dc.identifier.doi10.6342/NTU202500844-
dc.rights.note同意授權(限校園內公開)-
dc.date.accepted2025-04-21-
dc.contributor.author-college生物資源暨農學院-
dc.contributor.author-dept農業化學系-
dc.date.embargo-lift2030-04-18-
顯示於系所單位:農業化學系

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