Nitrous oxide emission from N fertilizer and vinasse in sugarcane

Heitor Cantarella1, Késia Silva Lourenço1, Johnny R. Soares1, Janaína B. Carmo2, Andre C. Vitti3, Raffaella Rossetto3, Zaqueu F. Montezano1, Eiko E. Kuramae4

1 Agronomic Institute of Campinas, Av. Barao de Itapura 1487, Campinas, SP, 13020-902 Brazil, Email: cantarella@iac.sp.gov.br
2 Federal University of São Carlos, Rod. João Leme dos Santos, Sorocaba, SP, 18052-780, Brazil
3 APTA Regional, Piracicaba Research Pole, Piracicaba, SP, 13400-970, Brazil
4 Department of Microbial Ecology, Netherlands Institute of Ecology, Wageningen, 6708 PB, The Netherlands

Abstract

Nitrous oxide (N2O) emissions from nitrogen fertilizers may strongly affect the sustainability indicators of ethanol produced from sugarcane and there are evidences that the application of vinasse could enhance the emission of GHGs from N fertilizers. The strategy of separating the application of N fertilizer and vinasse in time was tested in three field experiments in Brazil. Vinasse – both regular and concentrated – was applied a) at the same time as the fertilizer, b) anticipated by one month or c) delayed by one month. Intense measurements of N2O emissions were carried out using static chambers. The N2O-N fertilizer emission factor (EF) varied from 0.08% to 0.52%, whereas the average EF of regular and concentrated vinasse were 0.68% and 0.33% respectively. Application of concentrated vinasse in the same day of the mineral N fertilization caused high N2O emissions than when the fertilizer was applied alone; simultaneous application of regular vinasse increased N2O emission in 2 out of 3 experiments. The strategy of anticipating or postponing the application of both regular and concentrated vinasse by about 30 days with respect to N fertilization in most cases granted lower N2O emissions.

Nitrous oxide emissions from wheat grown in a medium rainfall environment in SE Australia are low compared to overall nitrogen losses

Ashley Wallace1,4,5, Roger Armstrong1,2, Rob Harris3, Oxana Bellyaeva1, Peter Grace4, Clemens Scheer4

1 Department of Economic Development, Jobs, Transport and Resources, Private Bag 260, Horsham, Victoria, 3400.

2 Department of Animal, Plant and Soil Sciences, LaTrobe University, Bundoora, Victoria, 3086.

3 Formerly: Department of Economic Development, Jobs, Transport and Resources, Private Bag 105, Hamilton, Victoria, 3300.

4 Institute for Future Environments, Queensland University of Technology, Brisbane, Qld, 4000.

5 Corresponding author: ashley.wallace@ecodev.vic.gov.au

Abstract

Efficient management of nitrogen (N) is critical to the profitability and sustainability of agricultural systems. Losses of N can both reduce productivity and in the case of  nitrous oxide (N2O) emissions contribute to global warming and ozone depletion. The limited number of studies from medium rainfall cropping systems have indicated that N2O  losses tend to be low to moderate, but that there is the potential to reduce these losses through altered fertiliser management. This study investigated the magnitude of N2O flux from a medium rainfall cropping system in south eastern Australia and the potential to mitigate N2O losses through altered timing (at sowing compared with in-season) of N application and the use of both nitrification and urease inhibitors. This study also measured overall N fertiliser losses and crop productivity. Losses of N2O and overall fertiliser losses were measured using static chamber and 15N mass balance techniques respectively, as part of a field experiment conducted in the Victorian Wimmera during 2012. Cumulative N2O loss from sowing until harvest of the wheat crop amounted to between 75 and 270 g N2O-N/ha with  fertiliser application significantly increasing losses. In contrast, total losses of fertiliser N ranged from 7‑11 kg N/ha (14-22% of applied N), indicating that N2O losses were low in comparison to both crop requirements and overall N losses.

Foliar nitrogen dynamics of representative woody plants seedlings grown under elevated ozone with a free-air system

Cong Shi1, Fankang Meng1,2, Toshihiro Watanabe1, Fuyuki Satoh3, Takayoshi Koike1*

Graduate School of Agriculture, Hokkaido University, Sapporo 060-8689, Japan

  1. College of Life Science, Nankai University, Tianjin 300071, China
  2. Hokkaido University Forests, Sapporo 060-0809, Japan

*Corresponding author: Takayoshi Koike: tkoike@for.agr.hokudai.ac.jp

 

Abstract

To clarify effects of ozone (O3) on foliar nitrogen (N) contents dynamics in three representative woody plant seedlings: birch (Betula platyphylla var. japonica), oak (Quercus mongolica var. crispula), and beech (Fagus crenata) grown in elevated O3 (eO3), we investigated N contents in live and senescing leaves, the relation of N content differences and leaf mass per area (LMA) of each species. The 3 species seedlings were planted in a free-air O3 enrichment system for one growing season with 3 replicated plots exposed to the air or O3 at about 2.5 times the ambient. In our study, about 60 % of foliar N was retranslocated under eO3 conditions in birch; nearly 70 % of N in live leaves of oak was decreased by O3; and negative correlations were found between LMA and N at ambient. Based on the results, we discussed plausible understanding physiologically and biochemically to conclude that foliar N contents of birch is more sensitive than beech in response to O3, especially for the senescing leaves; on the other hand, LMA may be considered as an index parameter in speculation of the changes in foliar N contents at ambient O3 concentrations.

 

Setting and reaching institutional N Footprint reduction goals: a case study at the University of Virginia

Elizabeth S. Milo1, Elizabeth A. Castner1, Lia R.Cattaneo1, James N. Galloway1, Allison M. Leach2

1University of Virginia, 291 McCormick Rd, Charlottesville, VA, 22904 USA, esm9gq@virginia.edu

2University of New Hampshire, 131 Main Street, 107 Nesmith Hall, Durham, NH, 03824 USA

Abstract

Reactive nitrogen is both essential and detrimental to life on Earth. While nitrogen is a key component of protein, it is also a pollutant that can cause climate change, eutrophication, and more. The University of Virginia (UVA) is the only university that has approved a nitrogen footprint reduction goal. This goal was approved by UVA’s governing board in 2013 and aims to reduce the University’s nitrogen footprint by 25% below 2010 levels by 2025. Note that for this study, the boundaries of the N footprint calculation at UVA include on-campus university operations but excludes the food component of the universities’ health system.  UVA has calculated its footprint for 2010 and 2014 and will continue to complete a benchmark calculation every four years. The UVA N footprint group and the Office for Sustainability have determined a number of scenarios to reduce the University’s N footprint. Examples of these include implementing a Meatless Mondays program, composting all food waste at the University and switching from coal to natural gas at the heating plant. Since the 2010 baseline year, UVA’s N footprint has changed from a total of 403 to 393 MT N; the total reduction needs to be to 303 MT N. The decrease in the universities N footprint can be partially attributed to the decrease in coal use in the universities’ heating plant.   UVA hopes to serve as a model for other universities and institutions that want to reduce their environmental impact by setting and achieving N reduction goals.

Monitoring and modeling of nitrogen leaching caused by nitrogen fertilizer application to green tea fields in Japan

Yuhei Hirono1, Shigekazu Nakamura2, Tomohito Sano3, Kunihiko Nonaka3

1 National Agriculture and Food Research Organization, 2769, Kanaya-Shishidoi, Shimada, Shizuoka, 428-8501, Japan, E-mail: hirono@affrc.go.jp

2 Shizuoka Prefectural Research Institute of Agriculture and Forestry, Mobata, Shimizu, Shizuoka, 424-0101, Japan

3 National Agriculture and Food Research Organization, 2769, Kanaya-Shishidoi, Shimada, Shizuoka, 428-8501, Japan

Abstract

Large amounts of nitrogen fertilizer are required in the cultivation of tea (Camellia sinensis (L.)), relative to other crops, resulting in nitrate contamination of surrounding water systems and high rates of nitrous oxide emissions. In response to these problems, the amount of nitrogen fertilizer applied to tea fields in Japan has been decreased by the improvement of fertilizer application methods in recent years. In this study, we aimed to assess the changes in water quality due to the reduction of nitrogen input and determine the environmental response to improved fertilizer application methods in tea fields. First, we analyzed 21-year water quality monitoring data in an intensive tea-growing area in Japan. We found nitrate concentrations significantly decreased at most studied sites in water systems in the tea-growing area, indicating that water quality was improved by reducing nitrogen fertilizer application in tea fields. Second, we modeled nitrogen leaching from tea field soil based on the data obtained by lysimeter experiments. This showed that the calculated amounts of water and nitrogen leachate agreed well with the observed results.

Extending “SafeGauge for Nutrients” to high rainfall cropping in Australia

Kirsten Barlow1, Thabo Thayalakumaran2, Philip Moody3

1 Agriculture Victoria, DEDJTR,124 Chiltern Valley Road, Rutherglen, Victoria, 3685, Kirsten.Barlow@ecodev.vic.gov.au

2 Agriculture Victoria, DEDJTR, 32 Lincoln Square North, Carlton, Victoria, 3053

3 Department of Science, Information Technology and Innovation, Brisbane, Queensland, 4000

Abstract

As agricultural systems continue to intensify there is a need for farmers and farm advisors to understand how soil, climate and management interact to affect nitrogen (N) losses at the paddock scale. Computer-based decision support tools have been widely used to build farm advisors’ capacity to understand the risks of N losses to the environment. However, existing tools often only provide an average annual risk of nitrogen loss from a paddock, even though nitrogen export is dependent on daily interactions between soil water content, water movement through deep drainage and runoff pathways and N availability. In this paper we present the design of a decision support tool for high rainfall cropping systems building on SafeGauge for Nutrients (developed for the sugarcane industry in Queensland, Australia). This tool (SG_Grains), allows users to define the system including location, cropping season, soil type and management decisions (e.g. fertiliser rate and timing, cultivation, stubble management). Information on management practices is combined with relevant modelled daily crop growth, soil water, drainage and runoff sourced from a library of simulation runs for various soil types and climates. Taking account of  N uptake and cycling, the daily nitrogen balance and risks of nitrogen losses via the various pathways are calculated. The risks are then modified to account for differences in slope and paddock position in the landscape. The results are presented as a risk gauge for all three loss pathways (runoff, leaching and denitrification), as well as a summary report on nitrogen input/output balance for the selected paddock. SG_Grains will be used as part of the training for advisors within the Fertcare Program, allowing the investigation of how management affects the risk of N export through various pathways.

Nitrogen Budget on Township Scale in North China Plain

Xinsheng NIUa  Baojing GUb  Xiaotang JUc[1]

a Qu Zhou Experimental Station, China Agricultural University, Quzhou 057250, PR China.

b Department of Land Management, Zhejiang University, Hangzhou 310058, PR China.

c College of Resources and Environmental Sciences, China Agricultural University, Beijing 100193, PR China.

Abstract

To find out the critical problems of reactive nitrogen (Nr) on township scale and ascertain Nr flows in basic agricultural farming unit, we carried out a research of Nr budget at the township scale in North China Plain (NCP). Results showed that chemical N fertilizer dominants the Nr imported into a town, which was concerning with complex economic, social and conventional issues. Low Nr using efficiency in cropland subsystem was found in ecotone of agriculture-animal husbandry due to natural condition dependent and meteorological changes adaptive crop. Environmental Nr loads mainly derived from cropland subsystem due to excessive N fertilizer application and irrational applying universally used in NCP. Thus, application rates of N fertilizer synchronized to demand of crop and alternatives of scientific and advanced application measurements were necessary. Huge losses of Nr during storage of human feaces and manure due to inaccessible to treatment facilities and ignoring the rational management on wastes should be given a priority consideration. The extension of new extensive technologies of livestock husbandry for achieving higher converting ratio of feed and provided with facilities of treating manure with great efforts seem necessity especially in ecotone of agriculture-animal husbandry.

Integrating nitrogen footprints across scales: from institution to watershed

Elizabeth A. Castner1, Allison Leach2, Beth McGee3, James N. Galloway4

1 University of Virginia, Charlottesville, VA, 22903, www.N-print.org, eac6e@virginia.edu

2 University of New Hampshire, Durham, NH

3Chesapeake Bay Foundation, Annapolis, MD

4 University of Virginia, Charlottesville, VA

Abstract

Nitrogen footprints provide an important link between the body of work concerning human alteration of the global nitrogen cycle and the actions that can be taken by individuals, institutions, and policy-makers. The nitrogen footprints calculated for institutions of higher education serve as a link between research, education, and management. The research component demonstrates which activities of the institution contribute most heavily to nitrogen pollution in the form of a data-intensive sustainability metric, which in turn is used to educate the community and promote management strategies that reduce the institution’s impact. Nitrogen footprints for individuals also serve as education and management tools, and can be applied in regions where nitrogen pollution has the most effect. A nitrogen footprint calculation tool for residents of the Chesapeake Bay watershed (USA) aims to teach users how their actions impact water quality in the bay and suggests actions that individuals can employ to reduce their impact. In both institutional and individual N footprints, the most important sector is food production. Broad changes in consumption patterns have the most potential for reduction. The Nitrogen Footprint Network addresses the needs of multiple communities at different scales, and data collected from novel footprint calculations for institutions and individuals informs how best to reduce their N pollution.

NBudget: A simple tool for farmers and advisors for N management in Australia’s northern grain cropping

David Herridge1

1 School of Environmental and Rural Science, University of New England, Armidale, NSW, 2351, www.une.edu.au, david.herridge@une.edu.au

Abstract

Effective management of plant-available nitrogen (N) by farmers will generally have beneficial productivity, economic and environmental consequences. The reality is that farmers may be unsure of plant-avalable N levels in cropping soils at sowing and by necessity make decisions about how much fertiliser N to apply with limited information about soil N supply. NBudget is an excel-based decision-support (DS) tool developed to assist farmers/advisors in Australia’s northern grains region estimate (i) plant-available soil N and water levels pre-sowing, (ii) target yields, (iii) fertiliser N requirements for cereals and oilseed crops and (iv) N2 fixation by legumes. NBudget does not rely on soil testing either for nitrate-N, organic carbon or water. Rather, the tool relies on rainfall data plus basic descriptions of soil texture and fertility, tillage practice, information about the previous two years paddock use plus rules-of-thumb values and stand-alone or linked algorithms. Winter and summer versions of NBudget cover the major crops of the region. Groundtruthing of NBudget against three independent data sets (n=55) indicated generally close agreement between measured and predicted values for sowing soil nitrate (r2=0.76). A limitation of the tool is that it does not account for denitrification losses of soil N. The usefulness of NBudget would be enhanced by transforming the current Excel-based tool to a stand-alone app or web-based tool.

Quantifying the supply of plant-available nitrogen from dairy effluents to grow crops

Johnstone P1, Norris M1, Houlbrooke D2, Dexter M2, Sharp J3, Selbie D2, Hedderley D4

1The New Zealand Institute for Plant & Food Research Limited, Havelock North, 4130

2AgResearch Limited, Hamilton, 3214

3The New Zealand Institute for Plant & Food Research Limited, Lincoln, 7608

4The New Zealand Institute for Plant & Food Research Limited, Palmerston North, 4442

Email: Paul.Johnstone@plantandfood.co.nz

Abstract

The use of dairy effluent to grow forage and arable crops represents an opportunity to more sustainably reuse shed, feed pad and barn nutrients that are generated from intensive dairy systems. To do so in a profitable and low risk manner requires an understanding of the effect of effluent characteristics on nutrient supply patterns, including both the quantum of release and rate of release. Between 2014 and 2016 we have conducted several assays to investigate the nitrogen (N) supplying power of dairy effluents and link this to effluent characteristics measured at the time of application. This paper reports on Assay 1 where we quantified release patterns for five slurry and six solid dairy effluents collected from commercial farms in the Waikato region of New Zealand. These effluents were applied to a single, low N (0.36 % total N) soil at a target application rate of 100 kg N/ha and subsequently incubated in 500 ml units at 20°C and 90% of field capacity for 182 days. Units were leached a total of 15 times during the assay and the drainage water characterised for inorganic N levels. Estimates of N supply were calculated, corrected for background N supply from a non- effluent control, and relationships with a wide range of effluent characteristics assessed. The assay showed that the pattern and magnitude of N supply across slurry and solid effluent treatments varied considerably, consistent with the large variation in effluent characteristics. Strong positive correlations were found between the water-soluble N and carbon (C) effluent characteristics and the rate of N supply in the first month after effluent addition. There were few clear correlations between effluent characteristics and the rate of N supply during the later stages of the assay (112-182 days). At the end of the assay (182 days), final N supply for respective slurry and solid effluents ranged from 3.7 to 74.2 % and 1.5 to 34.3 % of total effluent N applied. Net N supply values which adjusted for inorganic N in the effluents at application (expressed as either a percentage of total N or organic N) were positive for seven of the eleven treatments (three slurries and four solids) indicating a net N mineralisation effect and negative for the remaining four (two slurries and two solids), indicating a net N immobilisation effect. Work is ongoing to identify the causes of the large variation in N supply.

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