scholarly journals Can application of liquid dairy manure onto no-tillage oxisols reduce runoff, sediment, phosphorus, and nitrogen losses over 9 years of natural rainfall?

Geoderma ◽  
2022 ◽  
Vol 405 ◽  
pp. 115406
Author(s):  
Nerilde Favaretto ◽  
Verediana Fernanda Cherobim ◽  
Fabiana de Medeiros Silveira ◽  
Adriana Timofiecsyk ◽  
Rebert Skalitz ◽  
...  
2008 ◽  
Vol 16 (4) ◽  
pp. 285-293 ◽  
Author(s):  
Khalil Tubail ◽  
Liming Chen ◽  
Frederick C. Michel ◽  
Harold M. Keener ◽  
Jerome F. Rigot ◽  
...  

2008 ◽  
Vol 98 (2) ◽  
pp. 187-199 ◽  
Author(s):  
M.S. Mkhabela ◽  
A. Madani ◽  
R. Gordon ◽  
D. Burton ◽  
D. Cudmore ◽  
...  

2017 ◽  
Vol 184 ◽  
pp. 96-103 ◽  
Author(s):  
Verediana Fernanda Cherobim ◽  
Chi-Hua Huang ◽  
Nerilde Favaretto

Soil Research ◽  
2021 ◽  
Author(s):  
Gabriel Barth ◽  
Lenir Fátima Gotz ◽  
Nerilde Favaretto ◽  
Volnei Pauletti

1999 ◽  
Vol 31 (1) ◽  
pp. 149-159 ◽  
Author(s):  
Laura S. VanDyke ◽  
Darrell J. Bosch ◽  
James W. Pease

AbstractThe effects of considering variable within-farm soil runoff and leaching potential on costs of reducing nitrogen losses are analyzed for a Virginia dairy. Manure applications may cause nitrogen losses through runoff and leaching because of factors such as uncertain nitrogen mineralization. Farmers can reduce nitrogen control costs by applying manure on soils with less nitrogen loss potential. Ignoring within-farm soil variability may result in overstating the farm's costs of reducing nitrogen losses.


2012 ◽  
Vol 2012 ◽  
pp. 1-9 ◽  
Author(s):  
N. E. Hansen ◽  
D. M. Vietor ◽  
C. L. Munster ◽  
R. H. White ◽  
T. L. Provin

Composted organic materials used to stabilize roadside embankments in Texas promote rapid revegetation of soils disturbed by construction activities. Yet, adding compost to soil may increase total and soluble plant nutrients available for loss in runoff water. Composted municipal biosolids and dairy manure products were applied to soils in Texas according to prescribed Texas Department of Transportation specifications for stabilizing roadside soils. The specifications included a method for incorporating compost into soils prior to seeding or applying a compost and woodchip mix over a disturbed soil and then seeding. Applying compost and woodchips over the soil surface limited sediment losses (14 to 32 fold decrease) compared to incorporating compost into the soil. Yet, the greatest total phosphorus and nitrogen losses in runoff water occurred from soils where the compost and woodchip mix was applied. The greatest losses of soluble phosphorus also occurred when the compost and woodchip mix was applied. In contrast, nitrate-nitrogen losses in runoff were similar when compost was incorporated in the soil or applied in the woodchip mix. Compost source affected the nutrient losses in runoff. While the composted municipal biosolids added greater nutrient loads to the soil, less nutrient loss in runoff occurred.


2009 ◽  
Vol 38 (6) ◽  
pp. 2438-2448 ◽  
Author(s):  
Alexander N. Hristov ◽  
Shah Zaman ◽  
Mike Vander Pol ◽  
Pius Ndegwa ◽  
Larry Campbell ◽  
...  

2016 ◽  
Vol 45 (6) ◽  
pp. 1829-1837 ◽  
Author(s):  
Emily A. Schwager ◽  
Andrew C. VanderZaag ◽  
Claudia Wagner-Riddle ◽  
Anna Crolla ◽  
Chris Kinsley ◽  
...  

2014 ◽  
Vol 38 (6) ◽  
pp. 1918-1928 ◽  
Author(s):  
Ildegardis Bertol ◽  
Fabrício Tondello Barbosa ◽  
Álvaro Luiz Mafra ◽  
Murilo Córdova Flores

The action of rain and surface runoff together are the active agents of water erosion, and further influences are the soil type, terrain, soil cover, soil management, and conservation practices. Soil water erosion is low in the no-tillage management system, being influenced by the amount and form of lime and fertilizer application to the soil, among other factors. The aim was to evaluate the effect of the form of liming, the quantity and management of fertilizer application on the soil and water losses by erosion under natural rainfall. The study was carried out between 2003 and 2013 on a Humic Dystrupept soil, with the following treatments: T1 - cultivation with liming and corrective fertilizer incorporated into the soil in the first year, and with 100 % annual maintenance fertilization of P and K; T2 - surface liming and corrective fertilization distributed over five years, and with 75 % annual maintenance fertilization of P and K; T3 - surface liming and corrective fertilization distributed over three years, and with 50 % annual maintenance fertilization of P and K; T4 - surface liming and corrective fertilization distributed over two years, and with 25 % annual maintenance fertilization of P and K; T5 - fallow soil, without liming or fertilization. In the rotation the crops black oat (Avena strigosa ), soybean (Glycine max ), common vetch (Vicia sativa ), maize (Zea mays ), fodder radish (Raphanus sativus ), and black beans (Phaseolus vulgaris ). The split application of lime and mineral fertilizer to the soil surface in a no-tillage system over three and five years, results in better control of soil losses than when split in two years. The increase in the amount of fertilizer applied to the soil surface under no-tillage cultivation increases phytomass production and reduces soil loss by water erosion. Water losses in treatments under no-tillage cultivation were low in all crop cycles, with a similar behavior as soil losses.


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