Evaluation of Mehlich 3 as an Agri‐Environmental Soil Phosphorus Test for the Mid‐Atlantic United States of America
Laws and guidelines limiting P applications to cropland based on soil P exist in the Mid‐Atlantic USA because of water quality concerns. We evaluated Mehlich 3 (M3) as an environmental soil P test using 465 soils typical to the Mid‐Atlantic region and found M3‐P accurately predicted water soluble P...
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Published in | Soil Science Society of America journal Vol. 66; no. 6; pp. 2016 - 2032 |
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Main Authors | , , , , |
Format | Journal Article |
Language | English |
Published |
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Soil Science Society
01.11.2002
Soil Science Society of America American Society of Agronomy |
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Abstract | Laws and guidelines limiting P applications to cropland based on soil P exist in the Mid‐Atlantic USA because of water quality concerns. We evaluated Mehlich 3 (M3) as an environmental soil P test using 465 soils typical to the Mid‐Atlantic region and found M3‐P accurately predicted water soluble P (WSP), desorbable P (Fe oxide strip P [FeO‐P]), and total sorbed P (oxalate P). The M3‐P saturation ratio (M3 [P/(Al+Fe)]) was linearly related to the well‐established oxalate P saturation method (DPSox) and a M3 [P/(Al+Fe)] range of 0.10 to 0.15 corresponded to reported environmental limits for DPSox (25–40%). Rainfall simulation and column leaching studies showed M3 [P/(Al+Fe)] predicted runoff and leachate P concentrations better than M3‐P. We suggest consideration of the following approach now used in Delaware for agri‐environmental interpretation of M3‐P and M3 [P/(Al+Fe)]: (i) Below optimum (crop response likely; M3‐P ≤ 50 mg kg−1; M3 [P/(Al+Fe)] < 0.06); (ii) Optimum (economic response to P unlikely, recommendations for P rarely made; M3‐P = 51–100 mg kg−1; M3 [P/(Al+Fe)] = 0.06–0.11); (iii) Above Optimum (soil P will not limit crop yields, no P recommended; M3‐P > 100 mg kg−1; M3 [P/(Al+Fe)] > 0.11); (iv) Environmental (implement improved P management to reduce potential for nonpoint P pollution—in Delaware M3‐P > 150 mg kg−1; M3 [P/(Al+Fe)] > 0.15 is now used). (v) Natural Resource Conservation (no P applied even if the potential water quality impact is low to conserve P, a finite natural resource). |
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AbstractList | Laws and guidelines limiting P applications to cropland based on soil P exist in the Mid-Atlantic USA because of water quality concerns. Sims et al evaluated Mehlich 3 (M3) as an environmental soil P test using 465 soils typical to the Mid-Atlantic region and found M3-P accurately predicted water soluble P (WSP), desorbable P (Fe oxide strip P [FeO-P]), and total sorbed P (oxalate P). The M3-P saturation ratio (M3 [P/(Al+Fe)]) was linearly related to the well-established oxalate P saturation method (DPSox) and a M3 [P/(Al+Fe)] range of 0.10 to 0.15 corresponded to reported environmental limits for DPSox (25 and 40%). Rainfall simulation and column leaching studies showed M3 [P/(Al+Fe)] predicted runoff and leachate P concentrations better than M3-P. We suggest consideration of the following approach now used in Delaware for agri-environmental interpretation of M3-P and M3 [P/(Al+Fe)]: (i) Below optimum (crop response likely; M3-P 50 mg kg-1; M3 [P/(Al+Fe)] < 0.06); (ii) Optimum (economic response to P unlikely, recommendations for P rarely made; M3-P = 51 and 100 mg kg-1; M3 [P/(Al+Fe)] = 0.06 and 0.11); (iii) Above Optimum (soil P will not limit crop yields, no P recommended; M3-P > 100 mg kg-1; M3 [P/(Al+Fe)] > 0.11); (iv) Environmental (implement improved P management to reduce potential for nonpoint P pollution and in Delaware M3-P > 150 mg kg-1; M3 [P/(Al+Fe)] > 0.15 is now used). (v) Natural Resource Conservation (no P applied even if the potential water quality impact is low to conserve P, a finite natural resource). Laws and guidelines limiting P applications to cropland based on soil P exist in the Mid‐Atlantic USA because of water quality concerns. We evaluated Mehlich 3 (M3) as an environmental soil P test using 465 soils typical to the Mid‐Atlantic region and found M3‐P accurately predicted water soluble P (WSP), desorbable P (Fe oxide strip P [FeO‐P]), and total sorbed P (oxalate P). The M3‐P saturation ratio (M3 [P/(Al+Fe)]) was linearly related to the well‐established oxalate P saturation method (DPSox) and a M3 [P/(Al+Fe)] range of 0.10 to 0.15 corresponded to reported environmental limits for DPSox (25–40%). Rainfall simulation and column leaching studies showed M3 [P/(Al+Fe)] predicted runoff and leachate P concentrations better than M3‐P. We suggest consideration of the following approach now used in Delaware for agri‐environmental interpretation of M3‐P and M3 [P/(Al+Fe)]: (i) Below optimum (crop response likely; M3‐P ≤ 50 mg kg−1; M3 [P/(Al+Fe)] < 0.06); (ii) Optimum (economic response to P unlikely, recommendations for P rarely made; M3‐P = 51–100 mg kg−1; M3 [P/(Al+Fe)] = 0.06–0.11); (iii) Above Optimum (soil P will not limit crop yields, no P recommended; M3‐P > 100 mg kg−1; M3 [P/(Al+Fe)] > 0.11); (iv) Environmental (implement improved P management to reduce potential for nonpoint P pollution—in Delaware M3‐P > 150 mg kg−1; M3 [P/(Al+Fe)] > 0.15 is now used). (v) Natural Resource Conservation (no P applied even if the potential water quality impact is low to conserve P, a finite natural resource). Laws and guidelines limiting P applications to cropland based on soil P exist in the Mid‐Atlantic USA because of water quality concerns. We evaluated Mehlich 3 (M3) as an environmental soil P test using 465 soils typical to the Mid‐Atlantic region and found M3‐P accurately predicted water soluble P (WSP), desorbable P (Fe oxide strip P [FeO‐P]), and total sorbed P (oxalate P). The M3‐P saturation ratio (M3 [P/(Al+Fe)]) was linearly related to the well‐established oxalate P saturation method (DPS ox ) and a M3 [P/(Al+Fe)] range of 0.10 to 0.15 corresponded to reported environmental limits for DPS ox (25–40%). Rainfall simulation and column leaching studies showed M3 [P/(Al+Fe)] predicted runoff and leachate P concentrations better than M3‐P. We suggest consideration of the following approach now used in Delaware for agri‐environmental interpretation of M3‐P and M3 [P/(Al+Fe)]: (i) Below optimum (crop response likely; M3‐P ≤ 50 mg kg −1 ; M3 [P/(Al+Fe)] < 0.06); (ii) Optimum (economic response to P unlikely, recommendations for P rarely made; M3‐P = 51–100 mg kg −1 ; M3 [P/(Al+Fe)] = 0.06–0.11); (iii) Above Optimum (soil P will not limit crop yields, no P recommended; M3‐P > 100 mg kg −1 ; M3 [P/(Al+Fe)] > 0.11); (iv) Environmental (implement improved P management to reduce potential for nonpoint P pollution—in Delaware M3‐P > 150 mg kg −1 ; M3 [P/(Al+Fe)] > 0.15 is now used). (v) Natural Resource Conservation (no P applied even if the potential water quality impact is low to conserve P, a finite natural resource). |
Author | Pautler, M. C. Sims, J. T. Maguire, R. O. Gartley, K. L. Leytem, A. B. |
Author_xml | – sequence: 1 givenname: J. T. surname: Sims fullname: Sims, J. T. email: jtsims@udel.edu organization: Univ. Delaware – sequence: 2 givenname: R. O. surname: Maguire fullname: Maguire, R. O. organization: Univ. Delaware – sequence: 3 givenname: A. B. surname: Leytem fullname: Leytem, A. B. organization: Univ. Delaware – sequence: 4 givenname: K. L. surname: Gartley fullname: Gartley, K. L. organization: Univ. Delaware – sequence: 5 givenname: M. C. surname: Pautler fullname: Pautler, M. C. organization: Univ. Delaware |
BackLink | http://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=14000664$$DView record in Pascal Francis |
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ContentType | Journal Article |
Copyright | Published in Soil Sci. Soc. Am. J.66:2016–2032. 2003 INIST-CNRS Copyright American Society of Agronomy Nov/Dec 2002 |
Copyright_xml | – notice: Published in Soil Sci. Soc. Am. J.66:2016–2032. – notice: 2003 INIST-CNRS – notice: Copyright American Society of Agronomy Nov/Dec 2002 |
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References | 1998; 27 1994; 157 2000; 29 1987; 51 2002; 31 2001b; 278 1997; 26 1999; 28 2002; 33 2000; 64 1998 1994; 23 1997 1996 1974 1995 1994 1992 2002 1991 1993; 4 2001; 42 1999 1993; 6 1990; 21 2001 1990 2000 1997; 10 1984; 15 1995; 24 1995; 66 1999; 79 1962; 27 1996; 60 2000b 2001a; 30 2000a 1996; 46 1966; 46 1996; 43 2001; 30 Sims J.T. (e_1_2_7_66_1) 2001 e_1_2_7_3_1 e_1_2_7_9_1 USEPA (e_1_2_7_70_1) 2000 Simpson T.W. (e_1_2_7_57_1) 1998 e_1_2_7_17_1 e_1_2_7_62_1 SPAC (Soil and Plant Analysis Council) (e_1_2_7_67_1) 1999 e_1_2_7_41_1 e_1_2_7_43_1 e_1_2_7_45_1 Brookes P.C. (e_1_2_7_13_1) 1997 e_1_2_7_26_1 Shedlock R.J. (e_1_2_7_56_1) 1999 e_1_2_7_28_1 Zee S.E.A.T.M. (e_1_2_7_74_1) 1990 Beegle D.B. (e_1_2_7_7_1) 1998 Sims J.T. (e_1_2_7_64_1) 1996 Heckman J.R. (e_1_2_7_24_1) 1998 Mallarino A.P. (e_1_2_7_36_1) 1997; 10 Lanyon L.E. (e_1_2_7_31_1) 2000 SAS Institute (e_1_2_7_48_1) 1998 e_1_2_7_73_1 e_1_2_7_25_1 Sims J.T. (e_1_2_7_59_1) 1999 e_1_2_7_23_1 e_1_2_7_33_1 e_1_2_7_54_1 e_1_2_7_75_1 e_1_2_7_35_1 Mallarino A.P. (e_1_2_7_37_1) 1999 Beegle D. (e_1_2_7_5_1) 1997 Sawyer S.E. (e_1_2_7_49_1) 1999 e_1_2_7_58_1 e_1_2_7_39_1 Cabrera M.L. (e_1_2_7_15_1) 2000 USDA‐SCS (e_1_2_7_69_1) 1974 Sims J.T. (e_1_2_7_60_1) 2000 Sen‐Tran T (e_1_2_7_52_1) 1990; 21 Tunney H. (e_1_2_7_68_1) 1997 e_1_2_7_6_1 USEPA (e_1_2_7_71_1) 2001 e_1_2_7_4_1 Klausner S.D. (e_1_2_7_29_1) 1994 e_1_2_7_8_1 Sims J.T. (e_1_2_7_65_1) 1991 e_1_2_7_18_1 e_1_2_7_40_1 e_1_2_7_2_1 Coale F.J. (e_1_2_7_19_1) 2000 e_1_2_7_14_1 e_1_2_7_42_1 e_1_2_7_63_1 e_1_2_7_44_1 e_1_2_7_46_1 e_1_2_7_27_1 Bolinder M.A. (e_1_2_7_10_1) 1998 Chardon W.J. (e_1_2_7_16_1) 1999 Schoumans O.F. (e_1_2_7_50_1) 2000 Breeuswma A. (e_1_2_7_12_1) 1992 e_1_2_7_30_1 e_1_2_7_53_1 Self‐Davis M.L. (e_1_2_7_51_1) e_1_2_7_32_1 e_1_2_7_55_1 Eliason R. (e_1_2_7_21_1) 2001 e_1_2_7_22_1 e_1_2_7_34_1 e_1_2_7_20_1 Breeuwsma A. (e_1_2_7_11_1) 1995 e_1_2_7_38_1 PSU (Pennsylvania State University) Agronomy Guide (e_1_2_7_47_1) 2000 USGS (e_1_2_7_72_1) 1999 Sims J.T. (e_1_2_7_61_1) 2000 |
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Version 8.0 ed year: 1998 ident: e_1_2_7_48_1 contributor: fullname: SAS Institute – volume-title: Handbook on reference methods for soil analysis year: 1999 ident: e_1_2_7_67_1 contributor: fullname: SPAC (Soil and Plant Analysis Council) – ident: e_1_2_7_58_1 doi: 10.2134/jpa1993.0501 – ident: e_1_2_7_75_1 doi: 10.2134/jeq2000.00472425002900010021x – ident: e_1_2_7_25_1 doi: 10.2134/jeq1995.00472425002400050018x – ident: e_1_2_7_18_1 doi: 10.2134/jeq2002.1471 – ident: e_1_2_7_53_1 – start-page: 82 volume-title: The quality of our nation's water: Nutrients and pesticides. Circ. No. 1225 year: 1999 ident: e_1_2_7_72_1 contributor: fullname: USGS – volume-title: Agron. Facts 40 year: 1997 ident: e_1_2_7_5_1 contributor: fullname: Beegle D. – volume-title: Interpretation of soil test results. Bull. 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Snippet | Laws and guidelines limiting P applications to cropland based on soil P exist in the Mid‐Atlantic USA because of water quality concerns. We evaluated Mehlich 3... Laws and guidelines limiting P applications to cropland based on soil P exist in the Mid-Atlantic USA because of water quality concerns. Sims et al evaluated... |
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SubjectTerms | Agricultural land Agricultural runoff Biological and medical sciences Crop yield Fundamental and applied biological sciences. Psychology Groundwater Leachates Leaching Natural resources Nonpoint source pollution Phosphorus Pollution Resource conservation Soil testing Soils Water quality |
Title | Evaluation of Mehlich 3 as an Agri‐Environmental Soil Phosphorus Test for the Mid‐Atlantic United States of America |
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