Combined effects of runoff and soil erodibility on available nitrogen losses from sloping farmland affected by agricultural practices

The susceptibility of purple soil and intensive tillage render the land prone to erosion under heavy precipitations in a sloping cropland in southwestern China. This study aimed to improve the evaluation of the potential benefits of surface protection tillage and organic matter addition to decreasing nutrient losses. A field plot experiment under natural rainfall conditions was conducted, which employed four management practices: conventional downslope tillage system as control (CK), contour tillage (CT) with organic matter addition (CT+OM), CT with wheat straw mulching (CT+SM), and CT combining straw mulching and organic matter addition (CT+OM+SM). Runoff depth, nutrient loads, and soil erodibility were used to estimate the effects of straw mulching and organic matter addition. Results indicated that the runoff depth under CK was largest during the experimental period, with an average of 16.91mm, and runoff coefficient average was 32%. Compared with CK, the runoff depth under CT+OM, CT+SM, and CT+OM+SM were reduced by 19%, 34%, and 50%, respectively. A significant difference in soil erodibility indicator among the four treatments was indicated (p<0.05); CK achieved the highest value, whereas CT+OM+SM obtained the least value. In addition, the contour cultivation (i.e., CT approaches) were more sustainable than the downslope tillage system (i.e., CK). Soil erodibility under CK was 9.83kgha−1mm−1. Meanwhile, soil erodibility under CT+OM, CT+SM, and CT+OM+SM were 8.49, 6.99, and 6.87kgha−1mm−1, respectively. These values were 14%, 29%, and 30% lower than that of CK, respectively. CK was more susceptible to accelerated erosion compared with the plots with a surface cover or organic addition. This greater erodibility resulted in higher runoff, sediment yield, and associated nutrient loss for CK. The runoff-associated nitrogen losses were mainly controlled by the runoff rate and soil erodibility (p<0.05). Variations in NO3−–N and NH4+–N concentration in runoff water were markedly affected by rainfall events and agricultural practice. A significant logarithmic correlation between NO3−–N load and runoff depth was identified. NO3−–N was proven to be the main form of inorganic nitrogen loss; therefore, fertilizer application of NO3−–N should be reduced in the purple soil region. Soil erodibility significantly influenced the available N losses (p<0.01), which was best described by a positive logarithmic correlation. Soil nutrient concentration also played an important role in nitrogen loss. However, further research is needed to understand the dynamic interactions between soil erodibility as well as soil and nutrient losses. Results indicated that surface protection by CT+OM+SM is one of the good management practices to reduce soil loss by water erosion in regions with intense agricultural activity.

[1]  K. Butterbach‐Bahl,et al.  Nitrate leaching, direct and indirect nitrous oxide fluxes from sloping cropland in the purple soil area, southwestern China. , 2012, Environmental pollution.

[2]  S. Tu,et al.  The effect of plant hedgerows on the spatial distribution of soil erosion and soil fertility on sloping farmland in the purple-soil area of China. , 2009 .

[3]  Nutrient Loss from an Agricultural Catchment and Landscape Modeling in Southeast China , 2003, Bulletin of environmental contamination and toxicology.

[4]  P. S. Miller,et al.  Impact of surface roughness and crusting on particle size distribution of edge-of-field sediments , 2008 .

[5]  Peter P. Motavalli,et al.  Nitrogen losses in runoff from three adjacent agricultural watersheds with claypan soils , 2006 .

[6]  J. Poesen,et al.  The effect of conservation tillage on runoff erosivity and soil erodibility during concentrated flow , 2008 .

[7]  E. Davidson,et al.  Managing nitrogen for sustainable development , 2015, Nature.

[8]  D. Pimentel,et al.  Environmental and Economic Costs of Soil Erosion and Conservation Benefits , 1995, Science.

[9]  Xing-xiu Yu,et al.  Impacts of surface runoff and sediment on nitrogen and phosphorus loss in red soil region of southern China , 2012, Environmental Earth Sciences.

[10]  Y. Lü,et al.  Assessing the soil erosion control service of ecosystems change in the Loess Plateau of China , 2011 .

[11]  M. Nearing,et al.  Handbook of erosion modelling. , 2011 .

[12]  David Pimentel,et al.  Ecology of Soil Erosion in Ecosystems , 1998, Ecosystems.

[13]  Bin Wang,et al.  Soil erodibility for water erosion: A perspective and Chinese experiences , 2013 .

[14]  C. Larson Climate change. Losing arable land, China faces stark choice: adapt or go hungry. , 2013, Science.

[15]  Peter Strauss,et al.  Conservation tillage practices in the alpine forelands of Austria — Are they effective? , 2016 .

[16]  Keli Zhang,et al.  Erodibility of agricultural soils on the Loess Plateau of China , 2004 .

[17]  J. Poesen,et al.  A robust algorithm for estimating soil erodibility in different climates , 2012 .

[18]  T. C. Daniel,et al.  Effects of pine straw harvesting on quantity and quality of surface runoff , 2004 .

[19]  Zongxue Xu,et al.  Role of soil erodibility in affecting available nitrogen and phosphorus losses under simulated rainfall , 2014 .

[20]  Xinyu Zhu,et al.  Diversity and abundance of soil fauna as influenced by long-term fertilization in cropland of purple soil, China , 2015 .

[21]  De-ti Xie,et al.  Anthropic pedogenesis of purple rock fragments in Sichuan Basin, China , 2006 .

[22]  Zhanbin Li,et al.  Soil erodibility, microbial biomass, and physical–chemical property changes during long-term natural vegetation restoration: a case study in the Loess Plateau, China , 2010, Ecological Research.

[23]  Jing-zhu Zhao,et al.  Effects of hydrological processes on nitrogen loss in purple soil , 2007 .

[24]  A. Cerda,et al.  Soil water erosion on road embankments in eastern Spain. , 2007, The Science of the total environment.

[25]  Joe M. Bradford,et al.  Analyses of Slope and Runoff Factors Based on the WEPP Erosion Model , 1993 .

[26]  J. O. Erhabor,et al.  Estimating soil erodibility from microtopographic features of erosion by rain under selected cropping systems and management practices in Mhong Chun Yen Village, northern Thailand. , 2011 .

[27]  Xie Hong Nitrogen balance of agro-ecosystem in a typical watershed in the hilly area of central Sichuan Basin , 2006 .

[28]  Kristof Van Oost,et al.  The impact of agricultural soil erosion on biogeochemical cycling , 2010 .

[29]  G.-H. Zhang,et al.  Effects of vegetation cover and rainfall intensity on sediment-associated nitrogen and phosphorus losses and particle size composition on the Loess Plateau , 2011, Journal of Soil and Water Conservation.

[30]  L. Gang Characteristics of runoff generation and its numerical simulation of surface flow in hilly area with purple soil under convetional tillage systems , 2002 .

[31]  Ramesh P. Rudra,et al.  SEASONAL VARIATION OF ERODIBILITY INDICES BASED ON SHEAR STRENGTH AND AGGREGATE STABILITY IN SOME ONTARIO SOILS , 1988 .

[32]  S. Ng,et al.  Effects of hedgerows on sediment erosion in Three Gorges Dam Area, China , 2008 .

[33]  Li Zhanbin,et al.  Effects of mulching and nitrogen on soil temperature, water content, nitrate-N content and maize yield in the Loess Plateau of China , 2015 .

[34]  S. Sadeghi,et al.  Straw Mulching Effect on Splash Erosion, Runoff, and Sediment Yield from Eroded Plots , 2013 .

[35]  A. Cerdà The influence of aspect and vegetation on seasonal changes in erosion under rainfall simulation on a clay soil in Spain , 1998 .

[36]  L. Owens,et al.  Effect of No‐Till and Extended Rotation on Nutrient Losses in Surface Runoff , 2013 .

[37]  D. Marx,et al.  Nutrient losses in runoff from feedlot surfaces as affected by unconsolidated surface materials , 2012, Journal of Soil and Water Conservation.

[38]  Yi Liu,et al.  Runoff and nutrient losses in citrus orchards on sloping land subjected to different surface mulching practices in the Danjiangkou Reservoir area of China , 2012 .

[39]  R. Reeder,et al.  No-till: plenty of positives. , 2010 .

[40]  M. A. Casermeiro,et al.  Influence of scrubs on runoff and sediment loss in soils of Mediterranean climate , 2004 .

[41]  R. Lal Soil conservation and ecosystem services , 2014, International Soil and Water Conservation Research.

[42]  Mark A. Nearing,et al.  Runoff, erosion, and nutrient losses from compost and mulch blankets under simulated rainfall , 2004 .

[43]  M. Tiscareño-López,et al.  NITROGEN AND ORGANIC MATTER LOSSES IN NO‐TILL CORN CROPPING SYSTEMS 1 , 2004 .

[44]  M. Bodí,et al.  Soil and water losses from new citrus orchards growing on sloped soils in the western Mediterranean basin , 2009 .

[45]  L. D. Norton,et al.  Polyacrylamide soil amendment effects on runoff and sediment yield on steep slopes: Part I. Simulated rainfall conditions , 2002 .

[46]  Fan Li-li Effects of Farming Practices on Soil Erosion and Nutrient Loss in the Three-George Reservoir Area. , 2007 .

[47]  Z. Shangguan,et al.  Runoff hydraulic characteristics and sediment generation in sloped grassplots under simulated rainfall conditions , 2006 .

[48]  José A. Martínez-Casasnovas,et al.  Nutrient losses by runoff in vineyards of the Mediterranean Alt Penedès region (NE Spain) , 2006 .