An advanced geometric mean model for predicting the effective thermal conductivity (λ\documentclass[12pt]{minimal}
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\begin{document}$$\lambda $$\end{document}) of unsaturated soils has been developed and successfully verified against an experimental λ\documentclass[12pt]{minimal}
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\begin{document}$$\lambda $$\end{document} database consisting of 40 Canadian soils, 15 American soils, 10 Chinese soils, four Japanese soils, three standard sands, and one pyroclasticsoil (Pozzolana) from Italy (a total of 667 experimental λ\documentclass[12pt]{minimal}
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\begin{document}$$\lambda $$\end{document} entries). Three soil structure-based parameters were used in the model, namely an inter-particle thermal contact resistance factor (α\documentclass[12pt]{minimal}
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\begin{document}$$\alpha $$\end{document}), the degree of saturation of a miniscule pore space (sr)\documentclass[12pt]{minimal}
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\begin{document}$$(s_{\mathrm{r}})$$\end{document}, and the bulk thermal conductivity of soil solids (λs)\documentclass[12pt]{minimal}
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\begin{document}$$(\lambda _{\mathrm{s}})$$\end{document}. The α\documentclass[12pt]{minimal}
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\begin{document}$$\alpha $$\end{document} factor strongly depended on the ratio of λs\documentclass[12pt]{minimal}
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\begin{document}$$\lambda _{\mathrm{s}}$$\end{document} to λf\documentclass[12pt]{minimal}
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\begin{document}$$\lambda _{\mathrm{f}}$$\end{document} (where λf\documentclass[12pt]{minimal}
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\begin{document}$$\lambda _{\mathrm{f}}$$\end{document} is the thermal conductivity of interfacial fluid) and an inter-particle contact coefficient (ε\documentclass[12pt]{minimal}
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\begin{document}$$\varepsilon $$\end{document}) whose value was obtained by reverse modeling of experimental λ\documentclass[12pt]{minimal}
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\begin{document}$$\lambda $$\end{document} data of 40 Canadian soils; the average values of ε\documentclass[12pt]{minimal}
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\begin{document}$$\varepsilon $$\end{document} varied between 0.988 and 0.994 for coarse and fine soils, respectively. In general, ε\documentclass[12pt]{minimal}
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\begin{document}$$\varepsilon $$\end{document} depends on soil compaction, soil specific surface area, and grain size distribution. The use of α\documentclass[12pt]{minimal}
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\begin{document}$$\alpha $$\end{document} was essential for close λ\documentclass[12pt]{minimal}
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\begin{document}$$\lambda $$\end{document} estimates of experimental data at a low range of degree of saturation (Sr)\documentclass[12pt]{minimal}
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\begin{document}$$(S_{\mathrm{r}})$$\end{document}. For λs\documentclass[12pt]{minimal}
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\begin{document}$$\lambda _{\mathrm{s}}$$\end{document} estimates obtained from measured λ\documentclass[12pt]{minimal}
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\begin{document}$$\lambda $$\end{document} at soil saturation or a complete soil mineral composition data or experimental quartz content, 69 % of λ\documentclass[12pt]{minimal}
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\begin{document}$$\lambda $$\end{document} predictions were less than 0.08W·m-1·K-1\documentclass[12pt]{minimal}
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\begin{document}$$0.08\, \hbox {W} {\cdot } \hbox {m}^{-1} {\cdot } \hbox {K}^{-1}$$\end{document}, 15 % were between 0.08W·m-1·K-1\documentclass[12pt]{minimal}
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\begin{document}$$0.08\,\hbox {W} {\cdot } \hbox {m}^{-1} {\cdot } \hbox {K}^{-1}$$\end{document} and 0.13W·m-1·K-1\documentclass[12pt]{minimal}
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\begin{document}$$0.13\,\hbox {W} {\cdot } \hbox {m}^{-1} {\cdot } \hbox {K}^{-1}$$\end{document}, and 13 % were between 0.13W·m-1·K-1\documentclass[12pt]{minimal}
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\begin{document}$$0.13\,\hbox {W} {\cdot } \hbox {m}^{-1} {\cdot } \hbox {K}^{-1}$$\end{document} and 0.24W·m-1·K-1\documentclass[12pt]{minimal}
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\begin{document}$$0.24\,\hbox {W} {\cdot } \hbox {m}^{-1} {\cdot } \hbox {K}^{-1}$$\end{document} with respect to experimental data (λexp)\documentclass[12pt]{minimal}
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\begin{document}$$(\lambda _{\mathrm{exp}})$$\end{document}. The model gives close λ\documentclass[12pt]{minimal}
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\begin{document}$$\lambda $$\end{document} estimates with an average root-mean-square error (RMSE) of 0.051W·m-1·K-1\documentclass[12pt]{minimal}
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\begin{document}$$0.051\,\hbox {W} {\cdot } \hbox {m}^{-1} {\cdot } \hbox {K}^{-1}$$\end{document} for 22 Canadian fine soils and an average RMSE of 0.092W·m-1·K-1\documentclass[12pt]{minimal}
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\begin{document}$$0.092\,\hbox {W} {\cdot } \hbox {m}^{-1} {\cdot } \hbox {K}^{-1}$$\end{document} for 18 Canadian coarse soils. In general, better λ\documentclass[12pt]{minimal}
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\begin{document}$$\lambda $$\end{document} estimates were obtained for soils containing less content of quartz. Overall, the model estimates were good for all soils at dry state (RMSE=0.050W·m-1·K-1\documentclass[12pt]{minimal}
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\begin{document}$$\hbox {RMSE} = 0.050\, \hbox {W} {\cdot } \hbox {m}^{-1} {\cdot } \hbox {K}^{-1}$$\end{document}; 22 % of the average λexp\documentclass[12pt]{minimal}
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\begin{document}$$\lambda _{\mathrm{exp}}$$\end{document}), saturated state (RMSE=0.090W·m-1·K-1\documentclass[12pt]{minimal}
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\begin{document}$$\hbox {RMSE} = 0.090\,\hbox {W} {\cdot } \hbox {m}^{-1} {\cdot } \hbox {K}^{-1}$$\end{document}; 5 % of the average λexp\documentclass[12pt]{minimal}
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\begin{document}$$\lambda _{\mathrm{exp}}$$\end{document}), soil field capacity (RMSE=0.105W·m-1·K-1\documentclass[12pt]{minimal}
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\begin{document}$$\hbox {RMSE} = 0.105\,\hbox {W} {\cdot } \hbox {m}^{-1} {\cdot } \hbox {K}^{-1}$$\end{document}; 9 % of the average λexp\documentclass[12pt]{minimal}
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\begin{document}$$\lambda _{\mathrm{exp}}$$\end{document}), and satisfactory near a critical degree of saturation, Sr-cr\documentclass[12pt]{minimal}
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\begin{document}$$S_{\mathrm{r-cr}}$$\end{document} (RMSE=0.162W·m-1·K-1\documentclass[12pt]{minimal}
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\begin{document}$$\hbox {RMSE} = 0.162\,\hbox {W} {\cdot } \hbox {m}^{-1} {\cdot } \hbox {K}^{-1}$$\end{document}; 26 % of the average λexp\documentclass[12pt]{minimal}
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\begin{document}$$\lambda _{\mathrm{exp}}$$\end{document}).