Your search found 10 records
1 Burke, S.; Mulligan, M.; Thornes, J. B. 1999. Optimal irrigation efficiency for maximum plant productivity and minimum water loss. Agricultural Water Management, 40(2/3):377-391.
Irrigation efficiency ; Water loss ; Plant growth ; Models ; Hydrology ; Rain
(Location: IWMI-HQ Call no: PER Record No: H024402)

2 Cook, S.; Johnson, N.; Swallow, B.; Ravnburg, H.; Beaulieu, N.; Mulligan, M.; Schreier, H.; Valentin, C.; Wani, S. P.; Penning de Vries, F.; Sanz, N.; Gottriet, V.; Westermann, O. 2002. Multiple use of upper catchments: toward a research agenda for Subtheme Two of the Challenge Program on water and food. Challenge Program on Water and Food background paper 2. In CGIAR Challenge Program on Water and Food. Challenge Program on Water and Food: background papers to the full proposal. Colombo, Sri Lanka: CGIAR Challenge Program on Water and Food. pp.43-84.
Catchment areas ; Watershed management ; Agricultural research ; Research projects ; Poverty ; indicators ; Living conditions ; Water use ; Water quality ; Hydrology ; Water balance ; Conflict
(Location: IWMI HQ Call no: 333.91 G000 CGI Record No: H031288)

3 Mulligan, M.; Fisher, M.; Sharma, Bharat R.; Xu, Z. X.; Ringler, C.; Mahe, G.; Jarvis, A.; Ramirez, J.; Clanet, J.-C.; Ogilvie, A.; Ahmad, Mobin-ud-Din. 2011. The nature and impact of climate change in the Challenge Program on Water and Food (CPWF) basins. Water International, 36(1):96–124. (Special issue on "Water, food and poverty in river basins, Part 2: Cross-basin analysis and synthesis" with contributions by IWMI authors). [doi: https://doi.org/10.1080/02508060.2011.54340]
Water resource management ; Climate change ; River basins ; Food security ; Poverty ; Agricultural production ; Statistical methods / Africa / Asia / USA
(Location: IWMI HQ Call no: PER Record No: H043689)
https://vlibrary.iwmi.org/pdf/H043689.pdf
(1.47 MB)
In this article the authors assess the potential impacts of projected climate change on water, livelihoods and food security in the Basin Focal Project basins. The authors consider expected change within the context of recently observed climate variability in the basins to better understand the potential impact of expected change and the options available for adaptation. They use multi-global circulation model climate projections for the AR4 SRES A2a scenario, downscaled and extracted for each basin. They nd significant differences in the impacts (both positive and negative impacts) of climate change, between and within basins, but also nd large-scale uncertainty between climate models in the impact that is projected.

4 Mulligan, M.; Fisher, M.; Sharma, Bharat; Xu, Z. X.; Ringler, C.; Mahe, G.; Jarvis, A.; Ramirez, J.; Clanet, J.-C.; Ogilvie, A.; Ahmad, M. D. 2012. The nature and impact of climate change in the Challenge Program on Water and Food (CPWF) basins. In Fisher, M.; Cook, Simon (Eds.). Water, food and poverty in river basins: defining the limits. London, UK: Routledge. pp.334-362.
Climate change ; Temperature ; Precipitation ; Seasonality ; River basins ; Food security ; Flow discharge ; Water balance ; Agriculture ; Poverty ; Social aspects ; Living conditions ; Rain / Africa / Asia / South America / Limpopo River Basin / Niger River Basin / Nile River Basin / Volta River Basin / Ganges River Basin / Karkeheh River Basin / Mekong River Basin / Yellow River Basin / Andes River Basins
(Location: IWMI HQ Call no: IWMI Record No: H044850)
https://vlibrary.iwmi.org/pdf/H044850.pdf
(2.13 MB)

5 Mulligan, M.; Rubiano, J.; Hyman, G.; White, D.; Garcia, J.; Saravia, M.; Leon, J. G.; Selvaraj, J. J.; Guttierez, T.; Saenz-Cruz, L. L. 2012. The Andes basins: biophysical and developmental diversity in a climate of change. In Fisher, M.; Cook, Simon (Eds.). Water, food and poverty in river basins: defining the limits. London, UK: Routledge. pp.9-29.
River basins ; Climate change ; Economic aspects ; Social aspects ; Poverty ; Water availability ; Water productivity ; Water balance ; Rain ; Agricultural production ; Population growth / Venezuela / Colombia / Ecuador / Peru / Bolivia / Chile / Argentina / Andes Basins
(Location: IWMI HQ Record No: H044837)

6 Mulligan, M.; Cruz, L. L. S.; Pena-Arancibia, J.; Pandey, B.; Mahe, G.; Fisher, M. 2012. Water availability and use across the Challenge Program on Water and Food (CPWF) basins. In Fisher, M.; Cook, Simon (Eds.). Water, food and poverty in river basins: defining the limits. London, UK: Routledge. pp.255-279.
Water availability ; Water resources ; Water demand ; Water supply ; Water use ; Water costs ; Water balance ; Water quality ; Rain ; River basins ; Population growth ; Climate change
(Location: IWMI HQ Call no: IWMI Record No: H044847)

7 Mulligan, M.. 2012. The water resource implications for and of FDI [Foreign Direct Investment] projects in Africa. In Allan, T.; Keulertz, M.; Sojamo, S.; Warner, J. (Eds.). Handbook of land and water grabs in Africa: foreign direct investment and food and water security. London, UK: Routledge. pp.384-405.
Water resources ; Water balance ; Water productivity ; Foreign investment ; Land use ; Indicators ; Vegetation ; Farmland ; Crop production ; Pastures ; Rangelands ; River basins ; Rain ; Risk analysis / Africa
(Location: IWMI HQ Call no: 333.91 G000 ALL Record No: H045690)

8 Peh, K. S.-H.; Thapa, I.; Basnyat, M.; Balmford, A.; Bhattarai, G. P.; Bradbury, R. B.; Brown, C.; Butchart, S. H. M.; Dhakal, M.; Gurung, H.; Hughes, F. M. R.; Mulligan, M.; Pandeya, B.; Stattersfield, A. J.; Thomas, D. H. L.; Walpole, M.; Merriman, J. C. 2016. Synergies between biodiversity conservation and ecosystem service provision: lessons on integrated ecosystem service valuation from a Himalayan protected area, Nepal. Ecosystem Services, 22(Part B):359-369. (Special issue: Integrated Valuation of Ecosystem Services: Challenges and Solutions). [doi: https://doi.org/10.1016/j.ecoser.2016.05.003]
Ecosystem services ; Biodiversity conservation ; Economic value ; Water quality ; Greenhouse gases ; Carbon ; Tourism ; Cost benefit analysis ; Land use ; Social aspects ; Valuation ; Assessment ; Decision making / Nepal / Himalayan Region / Shivapuri-Nagarjun National Park
(Location: IWMI HQ Call no: e-copy only Record No: H048023)
https://vlibrary.iwmi.org/pdf/H048023.pdf
(2.17 MB)
We utilised a practical approach to integrated ecosystem service valuation to inform decision-making at Shivapuri-Nagarjun National Park in Nepal. The Toolkit for Ecosystem Service Site-based Assessment (TESSA) was used to compare ecosystem services between two alternative states of the site (protection or lack of protection with consequent changed land use) to estimate the net consequences of protection. We estimated that lack of protection would have substantially reduced the annual ecosystem service flow, including a 74% reduction in the value of greenhouse gas sequestration, 60% reduction in carbon storage, 94% reduction in nature-based recreation, and 88% reduction in water quality. The net monetary benefit of the park was estimated at $11 million year-1. We conclude that: (1) simplified cost-benefit analysis between alternative states can be usefully employed to determine the ecosystem service consequences of land-use change, but monetary benefits should be subject to additional sensitivity analysis; (2) both biophysical indicators and monetary values can be standardised using rose plots, to illustrate the magnitude of synergies and trade-offs among the services; and (3) continued biodiversity protection measures can preserve carbon stock, although the benefit of doing so remains virtual unless an effective governance option is established to realise the monetary values.

9 Matthews, N.; Dalton, J.; Matthews, J.; Barclay, H.; Barron, J.; Garrick, D.; Gordon, L.; Huq, S.; Isman, T.; McCornick, P.; Meghji, A.; Mirumachi, N.; Moosa, S.; Mulligan, M.; Noble, A.; Petryniak, O.; Pittock, J.; Queiroz, C.; Ringler, C.; Smith, Mark; Turner, C.; Vora, S.; Whiting, L. 2022. Elevating the role of water resilience in food system dialogues. Water Security, 17:100126. [doi: https://doi.org/10.1016/j.wasec.2022.100126]
Food systems ; Water management ; Resilience ; Water governance ; Water systems ; Innovation ; Decision making ; Participation ; Policies ; Water resources ; Climate change ; Ecosystems ; Learning ; Information dissemination
(Location: IWMI HQ Call no: e-copy only Record No: H051489)
https://www.sciencedirect.com/science/article/pii/S2468312422000177/pdfft?md5=925a0cf228e088fef886a408882c02f5&pid=1-s2.0-S2468312422000177-main.pdf
https://vlibrary.iwmi.org/pdf/H051489.pdf
(0.54 MB) (551 KB)
Ensuring resilient food systems and sustainable healthy diets for all requires much higher water use, however, water resources are finite, geographically dispersed, volatile under climate change, and required for other vital functions including ecosystems and the services they provide. Good governance for resilient water resources is a necessary precursor to deciding on solutions, sourcing finance, and delivering infrastructure. Six attributes that together provide a foundation for good governance to reduce future water risks to food systems are proposed. These attributes dovetail in their dual focus on incorporating adaptive learning and new knowledge, and adopting the types of governance systems required for water resilient food systems. The attributes are also founded in the need to greater recognise the role natural, healthy ecosystems play in food systems. The attributes are listed below and are grounded in scientific evidence and the diverse collective experience and expertise of stakeholders working across the science-policy interface: Adopting interconnected systems thinking that embraces the complexity of how we produce, distribute, and add value to food including harnessing the experience and expertise of stakeholders s; adopting multi-level inclusive governance and supporting inclusive participation; enabling continual innovation, new knowledge and learning, and information dissemination; incorporating diversity and redundancy for resilience to shocks; ensuring system preparedness to shocks; and planning for the long term. This will require food and water systems to pro-actively work together toward a socially and environmentally just space that considers the water and food needs of people, the ecosystems that underpin our food systems, and broader energy and equity concerns.

10 Correa, A.; Forero, J.; Renau, J. M.; Lizarazo, I.; Mulligan, M.; Codato, D. 2023. Advancing spatial decision-making in a transboundary catchment through multidimensional ecosystem services assessment. Ecosystem Services, 64:101554. [doi: https://doi.org/10.1016/j.ecoser.2023.101554]
(Location: IWMI HQ Call no: e-copy only Record No: H052388)
https://vlibrary.iwmi.org/pdf/H052388.pdf
(24.80 MB)
Global change has led to significant impacts on ecosystem services, posing a threat to the livelihoods of local communities worldwide. It is essential to assess these services to integrate them into regional planning, and policy design. We conduct ecosystem services assessments to inform spatial decision-making in a transboundary catchment. We focus on Mira-Mataje (11617 km2) transboundary catchment as an example of a natural unit, rich in natural resources that hosts an important cultural heritage of Indigenous and Afro-descendant ethnic groups.
We utilize three dimensions to evaluate ecosystem services: Firstly, the monetary dimension; secondly, the biophysical relevance, including current pressures and future threats; and thirdly, the social dimension. We combine globally available economic and remotely sensed datasets with the spatial ecosystem services modeling and mapping tool, Co$tingNature, and local knowledge and worldviews from community leaders.
Our results show that the total valuation of ecosystem services in the catchment is USD 2013344397 per year, with pixel values ranging from 3.7 to 4905783. High values concentrated near cities and main roads. We found that monetary values and current pressures on ecosystems services are correlated to total potential services for the entire catchment (-0.58 and -0.4 respectively). In addition, with our multidimensional assessment, we distinguish areas that require different types of management due to their specificities. For instance, the Awá territories hosts the largest total potential services, and will face greater threats in the future. This demonstrates the community's capacity to maintain the natural resources, but a more efficient control of illegal and unsustainable external activities is necessary. Afro-descendant territories on the highlands show overexploitation of its natural resources. Territories and land ownership must be recognized and to promote the transition to sustainable production. We provide advances in the research on the services valuation for potential integration into differentiated regional planning and sustainable policies.

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