Effect of Long-Term Annual Application of Biosolids on Soil Properties, Phosphorus, and Metals
The USEPA Part 503 rule did not directly specify the amount of sludge-borne P that can be applied but allowed application rates based on the recommended N requirement of a crop. Monitoring of long-term application of biosolids is important to protect both soil and water quality. Biosolids and ammoni...
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Published in: | Soil Science Society of America journal Vol. 72; no. 1; pp. 73 - 82 |
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Abstract | The USEPA Part 503 rule did not directly specify the amount of sludge-borne P that can be applied but allowed application rates based on the recommended N requirement of a crop. Monitoring of long-term application of biosolids is important to protect both soil and water quality. Biosolids and ammonium nitrate were annually applied for 13 yr to winter wheat at six plant available N (PAN) rates: 0, 45, 90, 180, 269, 536 kg N ha-1 yr-1. Biosolids application did not increase soil pH but increased levels of total C, total N, NH4-N, NO3-N, and electrical conductivity (EC). Soil concentrations of Cd, Cu, Pb, Mo, and Zn were greater in biosolid-treated plots but were <24% of their respective cumulative pollutant loading rates. Application of biosolids increased plant micronutrient B, Cu, Fe, and Zn concentrations. The addition of biosolids to the Norge soil (fine-silty, mixed, active, thermic Udic Paleustoll) increased Mehlich 3 plant available P (M3P) and water soluble P (WSP) and these P levels were well correlated with biosolids application rate. Application of biosolids at rates of >or= 2 times the recommended agronomic rate of 90 kg PAN ha-1 resulted in M3P concentrations that exceeded an environmental threshold of 200 mg kg-1 established by the USDA-NRCS for the land application of manures in Oklahoma non-nutrient limited watersheds. Significant relationships were found between the ammonium oxalate P saturation index (PSI(ox)) and M3P as well as between PSI(ox) and WSP. It appears the repeated long-term application of biosolids above the N agronomic rate should be avoided and application should be based on other criteria such as an agronomic P threshold, an environmental P threshold, or a P site index. |
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AbstractList | The USEPA Part 503 rule did not directly specify the amount of sludge-borne P that can be applied but allowed application rates based on the recommended N requirement of a crop. Monitoring of long-term application of biosolids is important to protect both soil and water quality. Biosolids and ammonium nitrate were annually applied for 13 yr to winter wheat at six plant available N (PAN) rates: 0, 45, 90, 180, 269, 536 kg N ha^sup -1^ yr^sup -1^. Biosolids application did not increase soil pH but increased levels of total C, total N, NH^sub 4^-N, NO^sub 3^-N, and electrical conductivity (EC). Soil concentrations of Cd, Cu, Pb, Mo, and Zn were greater in biosolid-treated plots but were <24% of their respective cumulative pollutant loading rates. Application of biosolids increased plant micronutrient B, Cu, Fe, and Zn concentrations. The addition of biosolids to the Norge soil (fine-silty, mixed, active, thermic Udic Paleustoll) increased Mehlich 3 plant available P (M3P) and water soluble P (WSP) and these P levels were well correlated with biosolids application rate. Application of biosolids at rates of ≥2 times the recommended agronomic rate of 90 kg PAN ha^sup -1^ resulted in M3P concentrations that exceeded an environmental threshold of 200 mg kg^sup -1^ established by the USDA-NRCS for the land application of manures in Oklahoma non-nutrient limited watersheds. Significant relationships were found between the ammonium oxalate P saturation index (PSI^sub ox^) and M3P as well as between PSI^sub ox^ and WSP. It appears the repeated long-term application of biosolids above the N agronomic rate should be avoided and application should be based on other criteria such as an agronomic P threshold, an environmental P threshold, or a P site index. [PUBLICATION ABSTRACT] The USEPA Part 503 rule did not directly specify the amount of sludge‐borne P that can be applied but allowed application rates based on the recommended N requirement of a crop. Monitoring of long‐term application of biosolids is important to protect both soil and water quality. Biosolids and ammonium nitrate were annually applied for 13 yr to winter wheat at six plant available N (PAN) rates: 0, 45, 90, 180, 269, 536 kg N ha −1 yr −1 Biosolids application did not increase soil pH but increased levels of total C, total N, NH 4 –N, NO 3 –N, and electrical conductivity (EC). Soil concentrations of Cd, Cu, Pb, Mo, and Zn were greater in biosolid‐treated plots but were <24% of their respective cumulative pollutant loading rates. Application of biosolids increased plant micronutrient B, Cu, Fe, and Zn concentrations. The addition of biosolids to the Norge soil (fine‐silty, mixed, active, thermic Udic Paleustoll) increased Mehlich 3 plant available P (M3P) and water soluble P (WSP) and these P levels were well correlated with biosolids application rate. Application of biosolids at rates of ≥2 times the recommended agronomic rate of 90 kg PAN ha −1 resulted in M3P concentrations that exceeded an environmental threshold of 200 mg kg −1 established by the USDA‐NRCS for the land application of manures in Oklahoma non‐nutrient limited watersheds. Significant relationships were found between the ammonium oxalate P saturation index (PSI ox ) and M3P as well as between PSI ox and WSP. It appears the repeated long‐term application of biosolids above the N agronomic rate should be avoided and application should be based on other criteria such as an agronomic P threshold, an environmental P threshold, or a P site index. The USEPA Part 503 rule did not directly specify the amount of sludge‐borne P that can be applied but allowed application rates based on the recommended N requirement of a crop. Monitoring of long‐term application of biosolids is important to protect both soil and water quality. Biosolids and ammonium nitrate were annually applied for 13 yr to winter wheat at six plant available N (PAN) rates: 0, 45, 90, 180, 269, 536 kg N ha−1 yr−1 Biosolids application did not increase soil pH but increased levels of total C, total N, NH4–N, NO3–N, and electrical conductivity (EC). Soil concentrations of Cd, Cu, Pb, Mo, and Zn were greater in biosolid‐treated plots but were <24% of their respective cumulative pollutant loading rates. Application of biosolids increased plant micronutrient B, Cu, Fe, and Zn concentrations. The addition of biosolids to the Norge soil (fine‐silty, mixed, active, thermic Udic Paleustoll) increased Mehlich 3 plant available P (M3P) and water soluble P (WSP) and these P levels were well correlated with biosolids application rate. Application of biosolids at rates of ≥2 times the recommended agronomic rate of 90 kg PAN ha−1 resulted in M3P concentrations that exceeded an environmental threshold of 200 mg kg−1 established by the USDA‐NRCS for the land application of manures in Oklahoma non‐nutrient limited watersheds. Significant relationships were found between the ammonium oxalate P saturation index (PSIox) and M3P as well as between PSIox and WSP. It appears the repeated long‐term application of biosolids above the N agronomic rate should be avoided and application should be based on other criteria such as an agronomic P threshold, an environmental P threshold, or a P site index. The USEPA Part 503 rule did not directly specify the amount of sludge-borne P that can be applied but allowed application rates based on the recommended N requirement of a crop. Monitoring of long-term application of biosolids is important to protect both soil and water quality. Biosolids and ammonium nitrate were annually applied for 13 yr to winter wheat at six plant available N (PAN) rates: 0, 45, 90, 180, 269, 536 kg N ha-1 yr-1. Biosolids application did not increase soil pH but increased levels of total C, total N, NH4-N, NO3-N, and electrical conductivity (EC). Soil concentrations of Cd, Cu, Pb, Mo, and Zn were greater in biosolid-treated plots but were <24% of their respective cumulative pollutant loading rates. Application of biosolids increased plant micronutrient B, Cu, Fe, and Zn concentrations. The addition of biosolids to the Norge soil (fine-silty, mixed, active, thermic Udic Paleustoll) increased Mehlich 3 plant available P (M3P) and water soluble P (WSP) and these P levels were well correlated with biosolids application rate. Application of biosolids at rates of >or= 2 times the recommended agronomic rate of 90 kg PAN ha-1 resulted in M3P concentrations that exceeded an environmental threshold of 200 mg kg-1 established by the USDA-NRCS for the land application of manures in Oklahoma non-nutrient limited watersheds. Significant relationships were found between the ammonium oxalate P saturation index (PSI(ox)) and M3P as well as between PSI(ox) and WSP. It appears the repeated long-term application of biosolids above the N agronomic rate should be avoided and application should be based on other criteria such as an agronomic P threshold, an environmental P threshold, or a P site index. , The USEPA Part 503 rule did not directly specify the amount of sludge- borne P that can be applied but allowed application rates based on the recommended N requirement of a crop. Monitoring of long-term application of biosolids is important to protect both soil and water quality. Biosolids and ammonium nitrate were annually applied for 13 yr to winter wheat at six plant available N (PAN) rates: 0, 45, 90, 180, 269, 536 kg N ha super(-1) yr super(-1). Biosolids application did not increase soil pH but increased levels of total C, total N, NH sub(4)-N, NO sub(3)-N, and electrical conductivity (EC). Soil concentrations of Cd, Cu, Pb, Mo, and Zn were greater in biosolid-treated plots but were <24% of their respective cumulative pollutant loading rates. Application of biosolids increased plant micronutrient B, Cu, Fe, and Zn concentrations. The addition of biosolids to the Norge soil (fine-silty, mixed, active, thermic Udic Paleustoll) increased Mehlich 3 plant available P (M3P) and water soluble P (WSP) and these P levels were well correlated with biosolids application rate. Application of biosolids at rates of =>2 times the recommended agronomic rate of 90 kg PAN ha super(-1) resulted in M3P concentrations that exceeded an environmental threshold of 200 mg kg super(-1) established by the USDA-NRCS for the land application of manures in Oklahoma non-nutrient limited watersheds. Significant relationships were found between the ammonium oxalate P saturation index (PSI sub(ox)) and M3P as well as between PSI sub(ox) and WSP. It appears the repeated long-term application of biosolids above the N agronomic rate should be avoided and application should be based on other criteria such as an agronomic P threshold, an environmental P threshold, or a P site index. The effects of long-term annual application of biosolids on soil properties, phosphorous (P), and metals were investigated. It was shown that the long-term application of biosolids using a nitrogen (N)-based approach increased soil P above crop production needs. It appeared that the application of biosolids above N agronomics rate should be regulated based on other criteria namely agronomic P threshold, an environmental P threshold, or a P site index. The rates applied ranged from 50 to 600% of the recommended agronomic rate. Soil pH was not changed by the application of biosolids but the application of ammonium nitrate significantly decreased soil pH. Soil electrical conductivity (EC) was increased at the two greatest rates of biosolids application but was not high enough to affect wheat yields. |
Author | Zazulak, A Payton, M.E Zhou, D Raun, W.R Zhang, H Schroder, J.L Basta, N |
Author_xml | – sequence: 1 fullname: Schroder, J.L – sequence: 2 fullname: Zhang, H – sequence: 3 fullname: Zhou, D – sequence: 4 fullname: Basta, N – sequence: 5 fullname: Raun, W.R – sequence: 6 fullname: Payton, M.E – sequence: 7 fullname: Zazulak, A |
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Snippet | The USEPA Part 503 rule did not directly specify the amount of sludge-borne P that can be applied but allowed application rates based on the recommended N... The USEPA Part 503 rule did not directly specify the amount of sludge‐borne P that can be applied but allowed application rates based on the recommended N... The effects of long-term annual application of biosolids on soil properties, phosphorous (P), and metals were investigated. It was shown that the long-term... , The USEPA Part 503 rule did not directly specify the amount of sludge- borne P that can be applied but allowed application rates based on the recommended N... |
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SubjectTerms | agricultural soils Agronomy. Soil science and plant productions Ammonium Ammonium nitrate application rate Biological and medical sciences Biosolids chemical concentration Earth sciences Earth, ocean, space environmental fate Exact sciences and technology fertilizer application Fertilizers Fundamental and applied biological sciences. Psychology heavy metals Loam soils Manures Metals Moisture content nitrogen phosphorus phosphorus satural index Pollution load R&D Research & development Saturation index Sludge soil nutrients Soil pH Soil properties soil salinity Soil science Soils Surficial geology trace element fertilizers Triticum aestivum wastewater wastewater treatment Water quality Winter wheat |
Title | Effect of Long-Term Annual Application of Biosolids on Soil Properties, Phosphorus, and Metals |
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