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Determination of Mehlich 3 Extractable Elements with Visible and Near Infrared Spectroscopy in a Mountainous Agricultural Land, the Caucasus Mountains
Soil spectroscopy is a promising alternative to evaluate and monitor soil and water quality, particularly in mountainous agricultural lands characterized by intense degradation and limited soil tests reports; a few studies have evaluated the feasibility of VIS-NIR spectroscopy to predict Mehlich 3 (...
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Published in: | Land (Basel) 2022-03, Vol.11 (3), p.363 |
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description | Soil spectroscopy is a promising alternative to evaluate and monitor soil and water quality, particularly in mountainous agricultural lands characterized by intense degradation and limited soil tests reports; a few studies have evaluated the feasibility of VIS-NIR spectroscopy to predict Mehlich 3 (M3) extractable nutrients. This study aimed to (i) examine the potential of VIS-NIR spectroscopy in combination with partial least squares regression to predict M3-extractable elements (Ca, K, Mg, P, Fe, Cd, Cu, Mn, Pb, and Zn) and basic soil properties (clay, silt, sand, CaCO3, pH, and soil organic carbon-SOC), (ii) find optimal pre-processing techniques, and (iii) determine primary prediction mechanisms for spectrally featureless soil properties. Topsoil samples were collected from a representative area (114 samples from 525 ha) located in the mountainous region of NW Azerbaijan. A series of pre-processing steps and transformations were applied to the spectral data, and the models were calibrated and evaluated based on the coefficient of determination (R2), root mean square error (RMSE), and the residual prediction deviation (RPD). The leave-one-out cross-validated predictions showed that the first derivative spectra produce higher prediction accuracies (R2 = 0.51–0.91; RPD = 1.20–2.29) for most soil properties. The evaluation of the model performance with optimal pre-processing techniques revealed that both calibration and validation models produce considerable differences in RPD values associated with sample size and the random partition of the calibration or validation subsets. The prediction models were excellent or very good (RPD > 2.0) for CaCO3, SOC, sand, silt, Ca, and Pb, good or fair (1.4 < RPD < 2.0) for clay, K, Cd, pH, Fe, Mn, and Cu, and poor (1.0 < RPD < 1.4) for Mg, P, and Zn. Principal component and correlation, stepwise regression analysis, and variable importance in projection procedures allowed to elucidate the underlying prediction mechanisms. Unlike the previous studies, the spectral estimations of pH, Ca, Mg, P, Fe, Pb, and Cd concentrations were linked to their correlation with CaCO3 rather than soil organic matter, whereas Mg and P concentrations were also connected to Fe-oxides. Soil particle sizes contributed to predicting K concentration but confounded the prediction of P and Zn concentration. The weaker correlations of Mn, Cu or Zn with CaCO3, particle sizes, SOC, Fe, and spectral data yielded to their lower prediction accuracy. Th |
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This study aimed to (i) examine the potential of VIS-NIR spectroscopy in combination with partial least squares regression to predict M3-extractable elements (Ca, K, Mg, P, Fe, Cd, Cu, Mn, Pb, and Zn) and basic soil properties (clay, silt, sand, CaCO3, pH, and soil organic carbon-SOC), (ii) find optimal pre-processing techniques, and (iii) determine primary prediction mechanisms for spectrally featureless soil properties. Topsoil samples were collected from a representative area (114 samples from 525 ha) located in the mountainous region of NW Azerbaijan. A series of pre-processing steps and transformations were applied to the spectral data, and the models were calibrated and evaluated based on the coefficient of determination (R2), root mean square error (RMSE), and the residual prediction deviation (RPD). The leave-one-out cross-validated predictions showed that the first derivative spectra produce higher prediction accuracies (R2 = 0.51–0.91; RPD = 1.20–2.29) for most soil properties. The evaluation of the model performance with optimal pre-processing techniques revealed that both calibration and validation models produce considerable differences in RPD values associated with sample size and the random partition of the calibration or validation subsets. The prediction models were excellent or very good (RPD > 2.0) for CaCO3, SOC, sand, silt, Ca, and Pb, good or fair (1.4 < RPD < 2.0) for clay, K, Cd, pH, Fe, Mn, and Cu, and poor (1.0 < RPD < 1.4) for Mg, P, and Zn. Principal component and correlation, stepwise regression analysis, and variable importance in projection procedures allowed to elucidate the underlying prediction mechanisms. Unlike the previous studies, the spectral estimations of pH, Ca, Mg, P, Fe, Pb, and Cd concentrations were linked to their correlation with CaCO3 rather than soil organic matter, whereas Mg and P concentrations were also connected to Fe-oxides. Soil particle sizes contributed to predicting K concentration but confounded the prediction of P and Zn concentration. The weaker correlations of Mn, Cu or Zn with CaCO3, particle sizes, SOC, Fe, and spectral data yielded to their lower prediction accuracy. The major prediction mechanisms for M3-extractable elements relied on their relations with CaCO3, pH, clay content and mineralogy, and exchangeable cations in the context of their association with land use. The results can be used in mountain lands to evaluate and control the effect of management on soil quality indices and land degradation neutrality. Further studies are needed to develop most advantageous sampling schemes and modeling.</description><identifier>ISSN: 2073-445X</identifier><identifier>EISSN: 2073-445X</identifier><identifier>DOI: 10.3390/land11030363</identifier><language>eng</language><publisher>Basel: MDPI AG</publisher><subject>Agricultural land ; Agriculture ; Cadmium ; Calcium carbonate ; Calibration ; Cations ; Caucasus Mountains ; Chemicals ; Clay ; Clay minerals ; Clay soils ; Copper ; Farming ; Feasibility studies ; Forecasting ; Infrared spectroscopy ; Iron ; Land degradation ; Land use ; Land use planning ; Lead ; Least squares method ; Manganese ; Mehlich 3 extractable elements ; Metals ; Mineralogy ; Mountain regions ; Mountain soils ; Mountains ; Near infrared radiation ; Nutrients ; Organic carbon ; Organic matter ; Organic soils ; partial least squares regression ; pH effects ; prediction mechanisms ; Prediction models ; Predictions ; Regression analysis ; Root-mean-square errors ; Sand ; Silt ; Soil erosion ; Soil fertility ; Soil organic matter ; Soil properties ; Soil quality ; Soil testing ; Spectra ; Spectroscopic analysis ; Spectrum analysis ; Topsoil ; VIS-NIR reflectance spectroscopy ; Water quality ; Zinc</subject><ispartof>Land (Basel), 2022-03, Vol.11 (3), p.363</ispartof><rights>2022 by the authors. Licensee MDPI, Basel, Switzerland. This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (https://creativecommons.org/licenses/by/4.0/). Notwithstanding the ProQuest Terms and Conditions, you may use this content in accordance with the terms of the License.</rights><lds50>peer_reviewed</lds50><oa>free_for_read</oa><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c367t-2b3d5c384c77a27624459a56e1b26f52361a6c0ed379a1d78604c08e1c7063983</citedby><cites>FETCH-LOGICAL-c367t-2b3d5c384c77a27624459a56e1b26f52361a6c0ed379a1d78604c08e1c7063983</cites><orcidid>0000-0002-9630-4855 ; 0000-0002-0569-983X ; 0000-0002-3446-9507 ; 0000-0002-8964-3920 ; 0000-0003-1806-1242</orcidid></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://www.proquest.com/docview/2642426851/fulltextPDF?pq-origsite=primo$$EPDF$$P50$$Gproquest$$Hfree_for_read</linktopdf><linktohtml>$$Uhttps://www.proquest.com/docview/2642426851?pq-origsite=primo$$EHTML$$P50$$Gproquest$$Hfree_for_read</linktohtml><link.rule.ids>314,780,784,25753,27924,27925,37012,44590,75126</link.rule.ids></links><search><creatorcontrib>Mammadov, Elton</creatorcontrib><creatorcontrib>Denk, Michael</creatorcontrib><creatorcontrib>Riedel, Frank</creatorcontrib><creatorcontrib>Kaźmierowski, Cezary</creatorcontrib><creatorcontrib>Lewinska, Karolina</creatorcontrib><creatorcontrib>Łukowiak, Remigiusz</creatorcontrib><creatorcontrib>Grzebisz, Witold</creatorcontrib><creatorcontrib>Mamedov, Amrakh I.</creatorcontrib><creatorcontrib>Glaesser, Cornelia</creatorcontrib><title>Determination of Mehlich 3 Extractable Elements with Visible and Near Infrared Spectroscopy in a Mountainous Agricultural Land, the Caucasus Mountains</title><title>Land (Basel)</title><description>Soil spectroscopy is a promising alternative to evaluate and monitor soil and water quality, particularly in mountainous agricultural lands characterized by intense degradation and limited soil tests reports; a few studies have evaluated the feasibility of VIS-NIR spectroscopy to predict Mehlich 3 (M3) extractable nutrients. This study aimed to (i) examine the potential of VIS-NIR spectroscopy in combination with partial least squares regression to predict M3-extractable elements (Ca, K, Mg, P, Fe, Cd, Cu, Mn, Pb, and Zn) and basic soil properties (clay, silt, sand, CaCO3, pH, and soil organic carbon-SOC), (ii) find optimal pre-processing techniques, and (iii) determine primary prediction mechanisms for spectrally featureless soil properties. Topsoil samples were collected from a representative area (114 samples from 525 ha) located in the mountainous region of NW Azerbaijan. A series of pre-processing steps and transformations were applied to the spectral data, and the models were calibrated and evaluated based on the coefficient of determination (R2), root mean square error (RMSE), and the residual prediction deviation (RPD). The leave-one-out cross-validated predictions showed that the first derivative spectra produce higher prediction accuracies (R2 = 0.51–0.91; RPD = 1.20–2.29) for most soil properties. The evaluation of the model performance with optimal pre-processing techniques revealed that both calibration and validation models produce considerable differences in RPD values associated with sample size and the random partition of the calibration or validation subsets. The prediction models were excellent or very good (RPD > 2.0) for CaCO3, SOC, sand, silt, Ca, and Pb, good or fair (1.4 < RPD < 2.0) for clay, K, Cd, pH, Fe, Mn, and Cu, and poor (1.0 < RPD < 1.4) for Mg, P, and Zn. Principal component and correlation, stepwise regression analysis, and variable importance in projection procedures allowed to elucidate the underlying prediction mechanisms. Unlike the previous studies, the spectral estimations of pH, Ca, Mg, P, Fe, Pb, and Cd concentrations were linked to their correlation with CaCO3 rather than soil organic matter, whereas Mg and P concentrations were also connected to Fe-oxides. Soil particle sizes contributed to predicting K concentration but confounded the prediction of P and Zn concentration. The weaker correlations of Mn, Cu or Zn with CaCO3, particle sizes, SOC, Fe, and spectral data yielded to their lower prediction accuracy. The major prediction mechanisms for M3-extractable elements relied on their relations with CaCO3, pH, clay content and mineralogy, and exchangeable cations in the context of their association with land use. The results can be used in mountain lands to evaluate and control the effect of management on soil quality indices and land degradation neutrality. Further studies are needed to develop most advantageous sampling schemes and modeling.</description><subject>Agricultural land</subject><subject>Agriculture</subject><subject>Cadmium</subject><subject>Calcium carbonate</subject><subject>Calibration</subject><subject>Cations</subject><subject>Caucasus Mountains</subject><subject>Chemicals</subject><subject>Clay</subject><subject>Clay minerals</subject><subject>Clay soils</subject><subject>Copper</subject><subject>Farming</subject><subject>Feasibility studies</subject><subject>Forecasting</subject><subject>Infrared spectroscopy</subject><subject>Iron</subject><subject>Land degradation</subject><subject>Land use</subject><subject>Land use planning</subject><subject>Lead</subject><subject>Least squares method</subject><subject>Manganese</subject><subject>Mehlich 3 extractable elements</subject><subject>Metals</subject><subject>Mineralogy</subject><subject>Mountain regions</subject><subject>Mountain soils</subject><subject>Mountains</subject><subject>Near infrared radiation</subject><subject>Nutrients</subject><subject>Organic carbon</subject><subject>Organic matter</subject><subject>Organic soils</subject><subject>partial least squares regression</subject><subject>pH effects</subject><subject>prediction mechanisms</subject><subject>Prediction models</subject><subject>Predictions</subject><subject>Regression analysis</subject><subject>Root-mean-square errors</subject><subject>Sand</subject><subject>Silt</subject><subject>Soil erosion</subject><subject>Soil fertility</subject><subject>Soil organic matter</subject><subject>Soil properties</subject><subject>Soil quality</subject><subject>Soil testing</subject><subject>Spectra</subject><subject>Spectroscopic analysis</subject><subject>Spectrum analysis</subject><subject>Topsoil</subject><subject>VIS-NIR reflectance spectroscopy</subject><subject>Water quality</subject><subject>Zinc</subject><issn>2073-445X</issn><issn>2073-445X</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2022</creationdate><recordtype>article</recordtype><sourceid>PIMPY</sourceid><sourceid>DOA</sourceid><recordid>eNpNUU1vEzEQXSGQqEpv_ABLXBuwPWvv7rEKASKlcOBD3KyJPds42tjB9qr0j_T31iWAOpcZzbx5bz6a5rXgbwEG_m7C4ITgwEHDs-ZM8g4Wbat-Pn8Sv2wuct7zaoOAvlVnzf17KpQOPmDxMbA4smvaTd7uGLDV75LQFtxOxFYTHSiUzG592bEfPvvHbJVknwkTW4cxYSLHvh7JlhSzjcc75gNDdh3nUNCHOGd2dZO8nacyJ5zYpnZfsrIjtsTZYq71f9j8qnkx4pTp4q8_b75_WH1bflpsvnxcL682Cwu6Kwu5Bads3cR2HcpOy7rkgEqT2Eo9KglaoLacHHQDCtf1mreW9yRsxzUMPZw36xOvi7g3x-QPmO5MRG_-JGK6MZiKtxMZ6rctOQmKy7G1UgxK8UGD7QW5XnJXud6cuI4p_popF7OPcwp1fCN1K1upeyUq6vKEsvVKOdH4X1Vw8_hI8_SR8ABaW5D7</recordid><startdate>20220301</startdate><enddate>20220301</enddate><creator>Mammadov, Elton</creator><creator>Denk, Michael</creator><creator>Riedel, Frank</creator><creator>Kaźmierowski, Cezary</creator><creator>Lewinska, Karolina</creator><creator>Łukowiak, Remigiusz</creator><creator>Grzebisz, Witold</creator><creator>Mamedov, Amrakh I.</creator><creator>Glaesser, Cornelia</creator><general>MDPI AG</general><scope>AAYXX</scope><scope>CITATION</scope><scope>7SN</scope><scope>7ST</scope><scope>ABUWG</scope><scope>AFKRA</scope><scope>ATCPS</scope><scope>AZQEC</scope><scope>BENPR</scope><scope>BHPHI</scope><scope>C1K</scope><scope>CCPQU</scope><scope>DWQXO</scope><scope>GNUQQ</scope><scope>HCIFZ</scope><scope>PATMY</scope><scope>PIMPY</scope><scope>PQEST</scope><scope>PQQKQ</scope><scope>PQUKI</scope><scope>PYCSY</scope><scope>SOI</scope><scope>DOA</scope><orcidid>https://orcid.org/0000-0002-9630-4855</orcidid><orcidid>https://orcid.org/0000-0002-0569-983X</orcidid><orcidid>https://orcid.org/0000-0002-3446-9507</orcidid><orcidid>https://orcid.org/0000-0002-8964-3920</orcidid><orcidid>https://orcid.org/0000-0003-1806-1242</orcidid></search><sort><creationdate>20220301</creationdate><title>Determination of Mehlich 3 Extractable Elements with Visible and Near Infrared Spectroscopy in a Mountainous Agricultural Land, the Caucasus Mountains</title><author>Mammadov, Elton ; Denk, Michael ; Riedel, Frank ; Kaźmierowski, Cezary ; Lewinska, Karolina ; Łukowiak, Remigiusz ; Grzebisz, Witold ; Mamedov, Amrakh I. ; Glaesser, Cornelia</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c367t-2b3d5c384c77a27624459a56e1b26f52361a6c0ed379a1d78604c08e1c7063983</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2022</creationdate><topic>Agricultural land</topic><topic>Agriculture</topic><topic>Cadmium</topic><topic>Calcium carbonate</topic><topic>Calibration</topic><topic>Cations</topic><topic>Caucasus Mountains</topic><topic>Chemicals</topic><topic>Clay</topic><topic>Clay minerals</topic><topic>Clay soils</topic><topic>Copper</topic><topic>Farming</topic><topic>Feasibility studies</topic><topic>Forecasting</topic><topic>Infrared spectroscopy</topic><topic>Iron</topic><topic>Land degradation</topic><topic>Land use</topic><topic>Land use planning</topic><topic>Lead</topic><topic>Least squares method</topic><topic>Manganese</topic><topic>Mehlich 3 extractable elements</topic><topic>Metals</topic><topic>Mineralogy</topic><topic>Mountain regions</topic><topic>Mountain soils</topic><topic>Mountains</topic><topic>Near infrared radiation</topic><topic>Nutrients</topic><topic>Organic carbon</topic><topic>Organic matter</topic><topic>Organic soils</topic><topic>partial least squares regression</topic><topic>pH effects</topic><topic>prediction mechanisms</topic><topic>Prediction models</topic><topic>Predictions</topic><topic>Regression analysis</topic><topic>Root-mean-square errors</topic><topic>Sand</topic><topic>Silt</topic><topic>Soil erosion</topic><topic>Soil fertility</topic><topic>Soil organic matter</topic><topic>Soil properties</topic><topic>Soil quality</topic><topic>Soil testing</topic><topic>Spectra</topic><topic>Spectroscopic analysis</topic><topic>Spectrum analysis</topic><topic>Topsoil</topic><topic>VIS-NIR reflectance spectroscopy</topic><topic>Water quality</topic><topic>Zinc</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Mammadov, Elton</creatorcontrib><creatorcontrib>Denk, Michael</creatorcontrib><creatorcontrib>Riedel, Frank</creatorcontrib><creatorcontrib>Kaźmierowski, Cezary</creatorcontrib><creatorcontrib>Lewinska, Karolina</creatorcontrib><creatorcontrib>Łukowiak, Remigiusz</creatorcontrib><creatorcontrib>Grzebisz, Witold</creatorcontrib><creatorcontrib>Mamedov, Amrakh I.</creatorcontrib><creatorcontrib>Glaesser, Cornelia</creatorcontrib><collection>CrossRef</collection><collection>Ecology Abstracts</collection><collection>Environment Abstracts</collection><collection>ProQuest Central (Alumni)</collection><collection>ProQuest Central</collection><collection>Agricultural & Environmental Science Collection</collection><collection>ProQuest Central Essentials</collection><collection>ProQuest Central</collection><collection>ProQuest Natural Science Collection</collection><collection>Environmental Sciences and Pollution Management</collection><collection>ProQuest One Community College</collection><collection>ProQuest Central</collection><collection>ProQuest Central Student</collection><collection>SciTech Premium Collection</collection><collection>Environmental Science Database</collection><collection>Publicly Available Content Database (Proquest) (PQ_SDU_P3)</collection><collection>ProQuest One Academic Eastern Edition (DO NOT USE)</collection><collection>ProQuest One Academic</collection><collection>ProQuest One Academic UKI Edition</collection><collection>Environmental Science Collection</collection><collection>Environment Abstracts</collection><collection>DOAJ Directory of Open Access Journals</collection><jtitle>Land (Basel)</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Mammadov, Elton</au><au>Denk, Michael</au><au>Riedel, Frank</au><au>Kaźmierowski, Cezary</au><au>Lewinska, Karolina</au><au>Łukowiak, Remigiusz</au><au>Grzebisz, Witold</au><au>Mamedov, Amrakh I.</au><au>Glaesser, Cornelia</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Determination of Mehlich 3 Extractable Elements with Visible and Near Infrared Spectroscopy in a Mountainous Agricultural Land, the Caucasus Mountains</atitle><jtitle>Land (Basel)</jtitle><date>2022-03-01</date><risdate>2022</risdate><volume>11</volume><issue>3</issue><spage>363</spage><pages>363-</pages><issn>2073-445X</issn><eissn>2073-445X</eissn><abstract>Soil spectroscopy is a promising alternative to evaluate and monitor soil and water quality, particularly in mountainous agricultural lands characterized by intense degradation and limited soil tests reports; a few studies have evaluated the feasibility of VIS-NIR spectroscopy to predict Mehlich 3 (M3) extractable nutrients. This study aimed to (i) examine the potential of VIS-NIR spectroscopy in combination with partial least squares regression to predict M3-extractable elements (Ca, K, Mg, P, Fe, Cd, Cu, Mn, Pb, and Zn) and basic soil properties (clay, silt, sand, CaCO3, pH, and soil organic carbon-SOC), (ii) find optimal pre-processing techniques, and (iii) determine primary prediction mechanisms for spectrally featureless soil properties. Topsoil samples were collected from a representative area (114 samples from 525 ha) located in the mountainous region of NW Azerbaijan. A series of pre-processing steps and transformations were applied to the spectral data, and the models were calibrated and evaluated based on the coefficient of determination (R2), root mean square error (RMSE), and the residual prediction deviation (RPD). The leave-one-out cross-validated predictions showed that the first derivative spectra produce higher prediction accuracies (R2 = 0.51–0.91; RPD = 1.20–2.29) for most soil properties. The evaluation of the model performance with optimal pre-processing techniques revealed that both calibration and validation models produce considerable differences in RPD values associated with sample size and the random partition of the calibration or validation subsets. The prediction models were excellent or very good (RPD > 2.0) for CaCO3, SOC, sand, silt, Ca, and Pb, good or fair (1.4 < RPD < 2.0) for clay, K, Cd, pH, Fe, Mn, and Cu, and poor (1.0 < RPD < 1.4) for Mg, P, and Zn. Principal component and correlation, stepwise regression analysis, and variable importance in projection procedures allowed to elucidate the underlying prediction mechanisms. Unlike the previous studies, the spectral estimations of pH, Ca, Mg, P, Fe, Pb, and Cd concentrations were linked to their correlation with CaCO3 rather than soil organic matter, whereas Mg and P concentrations were also connected to Fe-oxides. Soil particle sizes contributed to predicting K concentration but confounded the prediction of P and Zn concentration. The weaker correlations of Mn, Cu or Zn with CaCO3, particle sizes, SOC, Fe, and spectral data yielded to their lower prediction accuracy. The major prediction mechanisms for M3-extractable elements relied on their relations with CaCO3, pH, clay content and mineralogy, and exchangeable cations in the context of their association with land use. The results can be used in mountain lands to evaluate and control the effect of management on soil quality indices and land degradation neutrality. Further studies are needed to develop most advantageous sampling schemes and modeling.</abstract><cop>Basel</cop><pub>MDPI AG</pub><doi>10.3390/land11030363</doi><orcidid>https://orcid.org/0000-0002-9630-4855</orcidid><orcidid>https://orcid.org/0000-0002-0569-983X</orcidid><orcidid>https://orcid.org/0000-0002-3446-9507</orcidid><orcidid>https://orcid.org/0000-0002-8964-3920</orcidid><orcidid>https://orcid.org/0000-0003-1806-1242</orcidid><oa>free_for_read</oa></addata></record> |
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subjects | Agricultural land Agriculture Cadmium Calcium carbonate Calibration Cations Caucasus Mountains Chemicals Clay Clay minerals Clay soils Copper Farming Feasibility studies Forecasting Infrared spectroscopy Iron Land degradation Land use Land use planning Lead Least squares method Manganese Mehlich 3 extractable elements Metals Mineralogy Mountain regions Mountain soils Mountains Near infrared radiation Nutrients Organic carbon Organic matter Organic soils partial least squares regression pH effects prediction mechanisms Prediction models Predictions Regression analysis Root-mean-square errors Sand Silt Soil erosion Soil fertility Soil organic matter Soil properties Soil quality Soil testing Spectra Spectroscopic analysis Spectrum analysis Topsoil VIS-NIR reflectance spectroscopy Water quality Zinc |
title | Determination of Mehlich 3 Extractable Elements with Visible and Near Infrared Spectroscopy in a Mountainous Agricultural Land, the Caucasus Mountains |
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