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E-raamat: Human Acceleration of the Nitrogen Cycle: Managing Risks and Uncertainty

  • Formaat: PDF+DRM
  • Sari: OECD Report Series
  • Ilmumisaeg: 15-Feb-2019
  • Kirjastus: IWA Publishing
  • Keel: eng
  • ISBN-13: 9781789060447
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  • Formaat: PDF+DRM
  • Sari: OECD Report Series
  • Ilmumisaeg: 15-Feb-2019
  • Kirjastus: IWA Publishing
  • Keel: eng
  • ISBN-13: 9781789060447

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This publication examines the risks associated with the release of excessive nitrogen into the environment (climate change, depletion of the ozone layer, air pollution, water pollution, loss of biodiversity, deterioration of soil quality). The report also examines the uncertainty associated with the ability of nitrogen to move from one ecosystem to another and cause "cascading effects". In addition to better management of nitrogen risks at the local level, there is a need to consider the global risks associated with the continued increase in nitrous oxide concentrations and to prevent excess nitrogen in all its forms by developing cost-effective strategies for all its sources. Other than the reduction of nitrogen pollution, this report provides guidance on the use of nitrogen policy instruments and how to ensure coherence with objectives such as food security, energy security and environmental objectives.
Foreword 3(2)
Acknowledgements 5(8)
Abbreviations 13(4)
Executive summary 17(2)
Chapter 1 Why does nitrogen matter?
19(22)
1.1 A doubling of global nitrogen fixation since pre-industrial time
20(1)
1.2 An essential nutrient, but a potential pollutant
21(1)
1.3 Nitrogen has multiple sources
22(2)
1.4 Multiple pathways
24(6)
1.4.1 Air
24(1)
1.4.2 Greenhouse balance and ozone layer
25(1)
1.4.3 Water
26(2)
1.4.4 Ecosystems and biodiversity
28(1)
1.4.5 Soil
29(1)
1.5 And multiple impacts
30(3)
1.5.1 Air quality
30(1)
1.5.2 Greenhouse balance and ozone layer
31(1)
1.5.3 Water quality
31(1)
1.5.4 Ecosystems and biodiversity
32(1)
1.5.5 Soil quality
33(1)
1.6 The "nitrogen cascade"
33(8)
Notes
36(2)
References
38(3)
Chapter 2 Proposed approach to address nitrogen pollution
41(30)
2.1 The risk approach
43(13)
2.1.1 The different nitrogen risks
43(1)
2.1.2 Deepening pathway analysis to better manage risks of nitrogen pollution
44(10)
2.1.3 Feasibility of the risk approach
54(1)
2.1.4 The case of nitrous oxide (N2O)
55(1)
2.2 The "precautionary" approach
56(15)
Notes
65(2)
References
67(4)
Chapter 3 Examples of impact-pathway analysis and its translation into policy-making
71(26)
3.1 Case study 1: Impact-Pathway Analysis (IPA) and air pollution
72(8)
3.1.1 Urban air pollution
72(2)
3.1.2 Eutrophication of terrestrial ecosystems
74(1)
3.1.3 Policy relevance of IPA for air pollution risk management
75(5)
3.2 Case study 2: Impact-Pathway Analysis (IPA) and water pollution
80(17)
3.2.1 Coastal water pollution
80(3)
3.2.2 Lake water pollution
83(2)
3.2.3 Groundwater contamination
85(3)
3.2.4 Policy relevance of IPA for water pollution risk management
88(4)
Notes
92(2)
References
94(3)
Chapter 4 The unintended consequences on the nitrogen cycle of conservation practises in agriculture
97(22)
4.1 Managing nitrogen for agriculture and the environment
98(1)
4.2 Nitrogen pathways in crop production
99(1)
4.3 Nitrogen pathways in animal production
100(1)
4.4 Conservation practices and the nitrogen cycle
101(5)
4.4.1 Nutrient management
102(1)
4.4.2 Tillage
103(1)
4.4.3 Cover crops
104(1)
4.4.4 Filter strips
104(1)
4.4.5 Restored wetlands
104(1)
4.4.6 Field drainage
104(1)
4.4.7 Chemical additions to manure
105(1)
4.4.8 Tank covers
105(1)
4.4.9 Slurry lagoon covers
105(1)
4.4.10 Manure incorporation and injection
105(1)
4.5 Changing nutrient management on cropland may result in environmental trade-offs
106(2)
4.5.1 NRCS Conservation Effects Assessment Project
107(1)
4.6 Water-air trade-offs in manure management
108(1)
4.7 Nitrous oxide (N2O) management practices
109(1)
4.8 Summary, conclusions and areas for further analysis
110(9)
Notes
112(1)
References
113(6)
Chapter 5 Criteria to guide nitrogen policy making
119(18)
5.1 Policy coherence
120(4)
5.2 The effectiveness, efficiency and feasibility of policy instruments
124(5)
5.2.1 A typology of policy instruments
124(2)
5.2.2 Effectiveness, efficiency and feasibility criteria
126(3)
5.3 Unintended effects related to the nitrogen cascade
129(8)
Notes
132(1)
References
133(4)
Chapter 6 An assessment of the effectiveness, efficiency and feasibility of nitrogen policy instruments
137(28)
6.1 Key findings
138(8)
6.2 Case studies of policy instruments
146(19)
6.2.1 The Swedish refund emission payment for nitrogen oxides (NOx): a combination of environmentally related tax and public financial support (PFS)
146(1)
6.2.2 Selected instrument combinations of relevance to nitrogen pollution
147(4)
6.2.3 The Greater Miami Watershed Trading Programme: an example of tradable permit system (TPS)
151(1)
6.2.4 Japan's automobile `nitrogen oxides (NOx) law': an example of direct environmental regulation (DER)
152(2)
6.2.5 Pennsylvania's Resource Enhancement and Protection Programme: an example of public financial support (PFS)
154(1)
6.2.6 The Agriculture and Environment Programme for Vittel area: an example of payment for ecosystem services (PES)
154(1)
6.2.7 Australia's `FERTCARE': an example of information measure
155(2)
6.2.8 Chesapeake 2000 Programme: an example of voluntary scheme
157(2)
Notes
159(2)
References
161(4)
Annex A Basic facts on nitrogen
165(7)
A.1 The nitrogen cycle
165(1)
A.2 The nitrogen problem in brief
166(1)
A.3 Supplementary information on nitrogen impacts
167(5)
A.3.1 Air quality
167(2)
A.3.2 Greenhouse balance
169(1)
A.3.3 Water quality
169(1)
A.3.4 Ecosystems and biodiversity
170(2)
Notes 172(1)
References 173