Skip to main content

Biophysical System Failure Pathways at the Regional Scale

  • Chapter
  • First Online:
Water Management in New Zealand's Canterbury Region

Part of the book series: Global Issues in Water Policy ((GLOB,volume 19))

  • 914 Accesses

Abstract

This chapter addresses water management failure pathways of climate change, and, the natural hazards of drought and floods. In terms of greenhouse gas emissions, the use of water for hydro-electric generation reduces New Zealand’s greenhouse gas emissions from energy compared to other developed countries. However, agriculture is the largest source producing 47.2% of total emissions, primarily from methane and nitrous oxide contributions. In addition, further forest clearance mainly for dairying is reducing greenhouse sinks.

Projected changes in climate have significant implications for water availability in Canterbury. Increased temperature increases the potential evapotranspiration deficit and therefore irrigation demand. Reduced winter rainfall on the Canterbury Plains reduces groundwater recharge and hence reduces flows in lowland streams. Reduced winter rainfall in the foothills reduces flow in foothill rivers. Increased rain on the Southern Alps but reduced snow means that while annual flow increases in alpine rivers, the peak flows shift from spring and summer towards winter and the reliability of supply for the irrigation season declines.

New Zealand’s response to climate change has been minimal with emissions continuing to increase. However, there are actions that could be taken through mitigation measures and offsets. Furthermore, better use could be made of economic instruments and environmental impact assessment procedures to manage emissions.

Drought can be defined in biophysical terms, i.e. meteorological and hydrological droughts but more relevant from a nested adaptive system perspective is the definition of agronomic drought because it focuses on damage from drought and can incorporate the socio-economic response. Drought adaptation responses are aligned with the sustainability approaches.

The case study of taking a resilience approach to management of the flood risk to Christchurch from the Waimakariri River is described. Rather than designing protection works for a flood of specific return period, the design incorporates the consequences of failure. A secondary stopbank system is provided to capture floodwaters if the primary system fails or is overtopped. The system also allows for return of floodwaters to the river. The international example of Hurricane Katrina and its flooding of New Orleans is also described. The inadequacies of the approach of designing just for a specific return period hazard has led the US Army Corps of Engineers to change to a comprehensive systems approach.

This is a preview of subscription content, log in via an institution to check access.

Access this chapter

Chapter
USD 29.95
Price excludes VAT (USA)
  • Available as PDF
  • Read on any device
  • Instant download
  • Own it forever
eBook
USD 129.00
Price excludes VAT (USA)
  • Available as EPUB and PDF
  • Read on any device
  • Instant download
  • Own it forever
Softcover Book
USD 169.99
Price excludes VAT (USA)
  • Compact, lightweight edition
  • Dispatched in 3 to 5 business days
  • Free shipping worldwide - see info
Hardcover Book
USD 169.99
Price excludes VAT (USA)
  • Durable hardcover edition
  • Dispatched in 3 to 5 business days
  • Free shipping worldwide - see info

Tax calculation will be finalised at checkout

Purchases are for personal use only

Institutional subscriptions

Notes

  1. 1.

    Typical figures for other developed countries are around 12%.

  2. 2.

    Temperature projections have been recently updated using the results of the IPCC Fifth Assessment Report (IPCC 2013). The ensemble average of projected changes in annual mean temperature between 1986–2005 and 2031–2050 for Canterbury vary from 0.7 °C to 1.0 °C for the four representative concentration pathways with a range from 0.4 °C to 1.6 °C. Projected increases for winter were slightly higher and spring slightly lower (Ministry for the Environment, 2016a, b, c).

  3. 3.

    A1B scenario is one of the Special Report on Emission Scenarios (Nakicenovic and Swart 2000). It assumes rapid economic growth and global population that peaks mid-century and declines thereafter, rapid introduction of new and more efficient technologies and a balance of fossil and non-fossil energy sources. This assumes a doubling of global emissions from 1990 to 2050 and declining thereafter.

  4. 4.

    Rainfall projections have been recently updated using the results of the IPCC Fifth Assessment Report (IPCC 2013). The ensemble average of projected changes in precipitation between 1986–2005 and 2031–2050 for Christchurch vary from 1 to 3% increase in summer and 0–4% decrease in winter, while for Tekapo in the Southern Alps it is 0–2% increase in summer and 6–11% increase in winter (Ministry for the Environment 2016c).

  5. 5.

    A2 scenario assumes a heterogeneous world, increasing global population, regionally oriented economic development and slower technological change compared to other scenarios. This assumes a doubling of emissions from 1990 to 2040 and ongoing increases to 2100 (Nakicenovic and Swart 2000).

  6. 6.

    A1FI scenario is one of the Special Report on Emission Scenarios (Nakicenovic and Swart 2000). It assumes rapid economic growth and global population that peaks mid-century and declines thereafter, rapid introduction of new and more efficient technologies with a technological emphasis on fossil-intensive sources.

  7. 7.

    B1 scenario is one of the Special Report on Emission Scenarios (Nakicenovic and Swart 2000). It is based on a convergent world with the global population, that peaks in mid-century and declines thereafter, as in the A1 scenarios, but with rapid change in economic structures toward a service and information economy, with reductions in material intensity and the introduction of clean and resource-efficient technologies. The emphasis is on global solutions to economic, social and environmental sustainability, including improved equity, but without additional climate initiatives.

  8. 8.

    Greenhouse gas emissions have been specifically excluded from consideration by local government authorities in the consenting process (New Zealand’s impact assessment process). This was on the basis that there would be a national approach through a National Environmental Standard (NES). However, no NES has been promulgated.

  9. 9.

    The example shows the importance of considering multiple failure pathways . DCD is effective in reducing nitrous emissions (contributing to addressing failure pathway 9 of climate change ) and in reducing nitrate leaching (contributing to addressing failure pathway 2 of environmental impacts). However, there is no standard for DCD residue in food products (related to failure pathway 6 – the disease pathway ) so when traces were found in milk products its use has been stopped (based on failure pathway 8 – collapse of trade network).

  10. 10.

    Note that this is the natural geomorphological process that created the Canterbury Plains. Deposition of shingle and sediment in river channels gradually raises the elevation of the channel bed and reduces the flow capacity of the channel. A flood flow leads to overflow to what had become a flood plain at a lower elevation and the formation of a new channel. The process is then repeated eventually forming a shingle and sediment plain.

References

  • Burton, R., & Peoples, S. (2008). Learning from past adaptations to extreme climatic events: A case study of drought. Dunedin: AgResearch.

    Google Scholar 

  • Chapin, F., Kofinas, G., & Folke, C. (2009). Principles of ecosystem stewardship: Resilience-based natural resource management in a changing world. New York: Springer.

    Google Scholar 

  • Chinn, T. (1996). New Zealand glacier responses to climate change of the past century. New Zealand Journal of Geology and Geophysics, 39(3), 415–428.

    Article  CAS  Google Scholar 

  • DairyNZ. (2013). New Zealand dairy statistics 2012–13. Hamilton: DairyNZ.

    Google Scholar 

  • De Klein, C., Monaghan, R., Ledgard, S., & Shepherd, M. (2010). A system’s perspective on the effectiveness of measures to mitigate the environmental impacts of nitrogen losses from pastoral dairy farming. Paper presented at the proceedings of the 4th Australasian Dairy Science Symposium.

    Google Scholar 

  • Di, H., & Cameron, K. (2004). Treating grazed pasture soil with a nitrification inhibitor, eco-n™, to decrease nitrate leaching in a deep sandy soil under spray irrigation – a lysimeter study. New Zealand Journal of Agricultural Research, 47(3), 351–361.

    Article  CAS  Google Scholar 

  • Di, H., Cameron, K., & Sherlock, K. (2007). Comparison of the effectiveness of a nitrification inhibitor, dicyandiamide, in reducing nitrous oxide emissions in four different soils under different climate and management conditions. Soil Use and Management, 23(1), 1–9.

    Article  Google Scholar 

  • Editor. (2011, September 20). Farmers must share burden on emissions. The Herald.

    Google Scholar 

  • Environmental Protection Authority. (1998). Guidance statement no. 12: Minimising greenhouse gas emissions. Perth: Environmental Protection Authority.

    Google Scholar 

  • Environmental Protection Authority. (1999). Bulletin 931 Murrin Murrin Nickel-Cobalt Project Stage 2 expansion, 60km east of Leonora: Report and recommendations of the Environmental Protection Authority. Perth: Environmental Protection Authority.

    Google Scholar 

  • Environmental Protection Authority. (2000). Bulletin 985 proposed gas to synthetic hydrocarbons plant, Burrup Peninsula, Western Australia: Report and recommendations of the Environmental Protection Authority. Perth: Environmental Protection Authority.

    Google Scholar 

  • Environmental Protection Authority. (2009). Gorgon gas development revised and expanded proposal: Barrow Island nature reserve: Report and recommendations of the Environmental Protection Authority. Perth: Environmental Protection Authority.

    Google Scholar 

  • Environmental Protection Authority. (2015). Environmental Protection Bulletin No. 24 greenhouse gas emissions and consideration of projected climate change impacts in the EIA process. Perth: Environmental Protection Authority.

    Google Scholar 

  • IPCC. (2013). The physical science basis: Contribution of Working Group 1 to the Fifth assessment report of the Intergovernmental Panel on Climate Change. Cambridge/New York.

    Google Scholar 

  • Ledgard, S., Judge, A., Smeaton, D., & Boyes, M. (2010). Greenhouse gas emissions from Rotorua dairy farms: Summary report. Hamilton: AgResearch.

    Google Scholar 

  • Livestock Improvement Corporation. (2008). New Zealand dairy statistics 2007–08. Hamilton: Livestock Improvement Corporation.

    Google Scholar 

  • Lopez, J. (2006a). The multiple lines of defense strategy to sustain coastal Louisiana. Lake Pontchartrain Basin Foundation.

    Google Scholar 

  • Lopez, J. (2006b). Overview of multiple lines of defense strategy to sustain coastal Louisiana. Lake Pontchartrain Basin Foundation & Coalition to Restore Coastal Louisiana. http://www.mlods.org/images/web_MLODS_overview.pdf

  • Lopez, J. (2009). The multiple lines of defense strategy to sustain coastal Louisiana. Journal of Coastal Research (Special Issue 54):186–197.

    Google Scholar 

  • Manly, B. (2013). 2012 deforestaion survey. Wellington: Ministry for Primary Industries.

    Google Scholar 

  • Mason, E., & Ledgard, S. (2013). Making your farm greenhouse gas neutral. www.forestry.ac.nz/euan/carbonStockUnits.htm. Accessed 29 Dec 2013.

  • McLaren, R., & Cameron, K. (1996). Soil science: Sustainable production and environmental protection (2nd ed.). Melburne: Oxford University Press.

    Google Scholar 

  • McLeman, R., Mayo, D., Strebeck, E., & Smit, B. (2008). Drought adaptation in rural eastern Oklahoma in the 1930s: Lessons for climate change adaptation. Mitigation and Adaptation Strategies for Global Change, 13, 379–400. https://doi.org/10.1007/s11027-007-9118-1.

    Article  Google Scholar 

  • Ministry for Primary Industries. (2013). National exotic forest description as at 1 April 2012. Wellington: Ministry for Primary Industries.

    Google Scholar 

  • Ministry for the Environment. (2008). Climate change effects and impacts assessment: A guidance manual for Local Goverment in New Zealand (2nd ed.). Wellington: Ministry for the Environment.

    Google Scholar 

  • Ministry for the Environment. (2013). New Zealand’s greenhouse gas inventory 1990–2011. Wellington: Ministry for the Environment.

    Google Scholar 

  • Ministry for the Environment. (2016a). New Zealand’s greenhouse gas inventory 1990–2014. Ministry for the Environment. https://www.mfe.govt.nz/sites/default/files/media/Climate%20Change/greenhouse-gas-inventory-snapshot-2016.pdf

  • Ministry for the Environment. (2016b). The New Zealand emissions trading scheme evaluation 2016. Wellington: Ministry for the Environment.

    Google Scholar 

  • Ministry for the Environment. (2016c). Climate change projections for New Zealand: Atmospheric projections based on simulations undertaken for the IPCC 5th assessment. Wellington: Ministry for the Environment.

    Google Scholar 

  • Ministry of Agriculture and Forestry. (2004). A national exotic forest description as at 1 April 2003. Wellington: Ministry of Agriculture and Forestry.

    Google Scholar 

  • Ministry of Agriculture and Forestry. (2009). Drought guide: Drought definition, recognition and assistance measures. http://maxa.maf.govt.nz/mafnet/rural-nz/adverse-events/droughts/drought-guide.pdf

  • Ministry of Economic Development. (2013). Energy in New Zealand. Wellington: Ministry of Economic Development.

    Google Scholar 

  • Mullen, B., Porteus, A., Wratt, D., & Hollis, M. (2005). Changes in drought risk with climate change. NIWA Client Report WLG 2005–23. Wellingtion: NIWA.

    Google Scholar 

  • Nakicenovic, N., & Swart, R. (2000). Special report on emission scenarios: A special report of Working Group III of International Panel on Climate Change. Cambridge/New York: Cambridge University Press.

    Google Scholar 

  • O’Donnell, L. (2007). Climate change: An analysis of the policy considerations for climate change for the review of the Canterbury Regional Policy Statement. Christchurch: Environment Canterbury.

    Google Scholar 

  • Parliamentary Commissioner for the Environment. (2016). Climate change and agriculture: Understanding the biological greenhouse gases. Wellington: Parliamentary Commissioner for the Environment.

    Google Scholar 

  • Renwick, J. (2015). Updated: NZ climate target announced – Expert reaction. http://www.sciencemediacentre.co.nz/2015/07/07/nz-climate-target-announced-expert-reaction/

  • Smeaton, D., Cox, T., Kerr, S., & Dynes, R. (2011). Relationships between farm productivity, profitability, N leaching and GHG emissions: A modelling approach. Proceedings of the New Zealand Grassland Association, 73, 57–62.

    Google Scholar 

  • Srinivasan, M., & Duncan, M. (2012). Droughts and irrigation reliability: An investigation of a river-based scheme in New Zealand. Journal of the Irrigation and Drainage Engineering, 138(1), 80–89.

    Article  Google Scholar 

  • Srinivasan, M., Schmidt, J., Poyck, S., & Hreinsan, E. (2011). Irrigation reliability under climate change scenarios: A modelling investigation in a river-based irrigation scheme in New Zealand. Journal of the American Water Resources Association, 47(6), 1261–1274.

    Article  Google Scholar 

  • Stehlik, D. (2003). Australian drought as lived experience: Social and community impacts. In E. Butterill & M. Fisher (Eds.), Beyond drought: People, policy and perspectives (pp. 87–108). Collinwood: CSIRO Publishing.

    Google Scholar 

  • Sustainability Council of New Zealand. (2015). New Zealand’s climate change: Targets, projections and liabilities. http://www.sustainabilitynz.org/nzs-climate-change-targets-projections-and-liabilities/

  • US Army Corps of Engineers. (2006a). Corps hurricane response: Task Force Hope Status Report, Sept 1 2006. New Orleans: US Army Corps of Engineers Mississippi Valley Division.

    Google Scholar 

  • US Army Corps of Engineers. (2006b). Performance evaluation of the New Orleans and Southeast Louisiana hurricane protection system: Draft final report of the Interagency Performance Evaluation Task Force Vol 1 executive summary and overview. New Orleans: US Army Corps of Engineers.

    Google Scholar 

  • US Army Corps of Engineers. (2009). Louisiana Coastal Protection and Restoration (LACPR): Final technical report. New Orleans: USACE New Orleans District.

    Google Scholar 

  • US Army Corps of Engineers. (2014). Hurricane & storm damage risk reduction system. New Orleans District: USACE http://www.mvn.usace.army.mil/Missions/HSDRRS.aspx. Accessed 14 Jan 2014.

  • Western Australia Environmental Protection Authority. (2002). Guidance statement for mininmising greenhouse gas emissions. Perth: WA EPA.

    Google Scholar 

  • Zammit, C., & Woods, R. (2011). Projected climate and river flow for the Waimakariri catchment for 2040s and 2090s. Christchurch: NIWA.

    Google Scholar 

Download references

Author information

Authors and Affiliations

Authors

Rights and permissions

Reprints and permissions

Copyright information

© 2018 Springer Science+Business Media B.V.

About this chapter

Check for updates. Verify currency and authenticity via CrossMark

Cite this chapter

Jenkins, B.R. (2018). Biophysical System Failure Pathways at the Regional Scale. In: Water Management in New Zealand's Canterbury Region. Global Issues in Water Policy, vol 19. Springer, Dordrecht. https://doi.org/10.1007/978-94-024-1213-0_7

Download citation

Publish with us

Policies and ethics