Abstract
Dredged slurry is used widely around the world for land reclamation as an important way to alleviate the lack of available land. This method involves hydraulically dredging slurry with extremely high water content to the site where soil is to be formed via sedimentation and consolidation. Therefore, a fundamental understanding of slurry sedimentation, especially in the marine environment, is very important if reclamation construction is to be done securely and economically. This paper investigates slurry sedimentation through laboratory sedimentation tests, considering the effects of the marine environment. It is found that (i) the sedimentation behavior of slurry prepared using seawater is significantly different from that of slurry prepared using distilled water and (ii) other hydrochemical conditions including salt (cation) types and concentrations also affect sedimentation behavior. A sedimentation model is proposed that is capable of quantitative characterization through defining several parameters associated with sedimentation type and sedimentation stabilization. The microscopic mechanism of sedimentation is revealed through scanning electron microscopy and zeta-potential measurements. Although specific to land reclamation construction in Tianjin, China, this study enhances the general understanding of slurry sedimentation affected by hydrochemical environments.
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Some or all data, models, or codes that support the findings of this study are available from the corresponding author upon reasonable request. Data is available upon reasonable request.
Abbreviations
- e 0 :
-
Initial void ratio
- e c :
-
Stable void ratio
- e f :
-
Void ratio at the end of sedimentation test
- e L :
-
Void ratio at liquid limit
- e s :
-
Critical void ratio
- G s :
-
Specific gravity of the slurry
- G w :
-
Specific gravity of water or seawater, = γf/γw
- H 0 :
-
Initial height of slurry
- H c :
-
Height of interface at the end of sedimentation stage
- H t :
-
Height of interface during the sedimentation test
- I p :
-
Plasticity index
- w 0 :
-
Initial water content (corrected considering the effect of salt)
- w 0 * :
-
Critical initial water content
- w f :
-
Water content of sediment at the end of the sedimentation test
- w L :
-
Liquid limit
- w m :
-
Water content in its conventional sense
- w p :
-
Plastic limit
- w t :
-
Water content of sediment during the sedimentation test
- P s :
-
Yield stress of flocs
- S c :
-
Settling of the interface when the consolidation stage starts
- S f :
-
Settling of the interface at the end of the sedimentation test
- S t :
-
Settling of the interface during the sedimentation test
- T :
-
Time
- T c :
-
Sedimentation stable time
- T f :
-
Duration of the flocculation stage
- V f :
-
Settling rate of interface in the flocculation stage
- β :
-
Salt content
- γ f :
-
Unit weight of the salt solution or seawater
- γ s :
-
Unit weight of soil particle
- γ w :
-
Unit weight of pure water
- γʹs :
-
Unit weight of sediment
- ζ :
-
Zeta potential
- ρ d :
-
Dry density
- σʹ:
-
Effective stress
References
ASTM D2487–17 (2017) Standard practice for classification of soils for engineering purposes (Unified Soil Classification System). ASTM International, West Conshohocken, PA
ASTM D4318–17 (2017) Standard test methods for liquid limit, plastic limit, and plasticity index of soils. ASTM International, West Conshohocken, PA
ASTM D4972–19 (2019) Standard test methods for pH of soils, ASTM International, West Conshohocken, PA
ASTM D7263–18 (2018) Standard test methods for laboratory determination of density (unit weight) of soil specimens. ASTM International, West Conshohocken, PA
ASTM D7503–10 (2010) Standard test method for measuring the exchange complex and cation exchange capacity of inorganic fine-grained soils. ASTM International, West Conshohocken, PA
ASTM D7928–21 (2021) Standard test method for particle-size distribution (gradation) of fine-grained soils using the sedimentation (hydrometer) analysis. ASTM International, West Conshohocken, PA
ASTM D854–14 (2014) Standard test methods for specific gravity of soil solids by water pycnometer. ASTM International, West Conshohocken, PA
Carrier WD III, Bromwell LG, Somogyi F (1983) Design capacity of slurried mineral waste ponds. J Geotech Eng 109(5):699–716. https://doi.org/10.1061/(ASCE)0733-9410(1983)109:5(699)
Choa V, Bo MW, Chu J (2001) Soil improvement works for Changi East reclamation project. Proceedings of the Institution of Civil Engineers-Ground Improvement 5(4):141–153. https://doi.org/10.1680/grim.2001.5.4.141
Everett DH (1989) Basic principles of colloid science, 2nd edn. The Royal Society of Chemistry, London
Imai G (1980) Settling behavior of clay suspension. Soils Found 20(2):61–77. https://doi.org/10.3208/sandf1972.20.2_61
Imai G (1981) Experimental studies on sedimentation mechanism and sediment formation of clay materials. Soils Found 21(1):7–20. https://doi.org/10.3208/sandf1972.21.7
Imai G, Tsuruya K, Yano K (1979) A treatment of salinity in water content determination of very soft clays. Soils Found 19(3):84–89. https://doi.org/10.3208/sandf1972.19.3_84
Jang JB, Cao SC, Stern LA, Jung JW, Waite WF (2018) Impact of pore fluid chemistry on fine-grained sediment fabric and compressibility. J Geophys Res-Sol Ea 123(7):5495–5514. https://doi.org/10.1029/2018JB015872
Klein C, Hurlbut CS (1999) Manual of mineralogy, 2nd edn. John Wiley and Sons, New York
Lambe TW (1953) The structure of inorganic soil. Proc Am Soc Civ Eng 79(10):1–49
Lambe TW (1958) The structure of compacted clay. J Soil Mech Found Eng Div 84(2):1–34. https://doi.org/10.1061/JSFEAQ.0000114
Lei HY, Bo Y, Zhang WD, Wang L, Toma A (2021) Effects of acidity and magnesium ions on the self-weight consolidation settlement of Tianjin dredged fill. Bull Eng Geol Environ 80(5):4035–4047. https://doi.org/10.1007/s10064-021-02177-7
Lei HY, Wang L, Jia R, Jiang MJ, Zhang WD, Li CY (2020) Effects of chemical conditions on the engineering properties and microscopic characteristics of Tianjin dredged fill. Eng Geol 269:105548. https://doi.org/10.1016/j.enggeo.2020.105548
Mitchell JK, Soga K (2005) Fundamentals of soil behavior, third ed. John Wiley and Sons, New Jersey. https://doi.org/10.2136/sssaj1976.03615995004000040003x
Monte JL, Krizek RJ (1976) One-dimensional mathematical model for large-strain consolidation. Géotechnique 26(3):495–510. https://doi.org/10.1680/geot.1976.26.3.495
O’Brien NR (1971) Fabric of kaolinite and illite floccules. Clay Goel Miner 19(6):353–359. https://doi.org/10.1346/CCMN.1971.0190603
Palomino AM, Burns SE, Santamarina JC (2008) Mixtures of fine-grained minerals–kaolinite and carbonate grains. Clay Goel Miner 56(6):599–611. https://doi.org/10.1346/CCMN.2008.0560601
Rhoades JD (1983) Soluble salts. Methods of soil analysis: Part 2 Chemical and Microbiological Properties, 9:167–179
Santamarina JC, Klein KA, Wang YH, Prencke E (2002) Specific surface: determination and relevance. Can Geotech J 39(1):233–241. https://doi.org/10.1139/T01-077
Shan WC, Chen HE, Yuan XQ, Ma WL, Li H (2021) Mechanism of pore water seepage in soil reinforced by step vacuum preloading. Bull Eng Geol Environ 80(3):2777–2787. https://doi.org/10.1007/s10064-020-02075-4
Tan TS, Yong KY, Leong EC, Lee SL (1990) Sedimentation of clayey slurry. J Geotech Eng 116(6):885–898. https://doi.org/10.1061/(ASCE)0733-9410(1990)116:6(885)
Toorman EA (1999) Sedimentation and self-weight consolidation: constitutive equations and numerical modelling. Géotechnique 49(6):709–726. https://doi.org/10.1680/geot.1999.49.6.709
Xu GZ, Gao YF, Hong ZS, Ding JW (2012a) Sedimentation behavior of four dredged slurries in China. Mar Georesour Geotec 30(2):143–156. https://doi.org/10.1080/1064119X.2011.602382
Xu GZ, Ji F, Weng JX (2012) Sedimentation behavior of dredged slurry at high water contents. J Civ Eng Manag 29(3):22–27 (in Chinese)
Yong RN, Sethi AJ (1977) Turbidity and zeta potential measurements of clay dispersibility. ASTM, STP 623:419–431
Zhang N, Zhu W, He HT, Lv YY, Wang SW (2017) Experimental study on settling velocity of soil particles in dredged slurry. Mar Georesour Geotec 35(6):747–757. https://doi.org/10.1080/1064119X.2016.1236862
Zurek-Pysz U (1992) Strength and deformability of an organic-calcareous lacustrine deposit (gyttja) in relation to its water content and colloid content. Bull Eng Geol Environ 45(1):117–126. https://doi.org/10.1007/BF02594911
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The authors are grateful for the constructive suggestions from editors and reviewers.
Funding
The financial supports from the National Natural Science Foundation of China (Nos. 41972285, 41972293, 52178372), the Youth Innovation Promotion Association CAS (Grant No. 2018363), and Science Fund for Distinguished Young Scholars of Hubei Province (2020CFA103) are thanked.
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Writing—original draft preparation: Xianwei Zhang, Xinyu Liu, Wei Zhang. Writing—review and editing: Xianwei Zhang, Xinyu Liu, Aiwu Yang. Data collection and analysis: Xianwei Zhang, Xinyu Liu, Yiqing Xu. Methodology: Xianwei Zhang, Xinyu Liu, Wei Zhang.
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Zhang, X., Liu, X., Zhang, W. et al. Sedimentation of the fine-grained dredged slurry in the marine environment. Bull Eng Geol Environ 81, 173 (2022). https://doi.org/10.1007/s10064-022-02680-5
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DOI: https://doi.org/10.1007/s10064-022-02680-5