Your search found 11 records
1 Trout, T.; Carter, D.; Sojka, B. 1994. Irrigation-induced soil erosion reduces yields and muddies rivers. Irrigation Journal, 44(1):8, 11-12.
Erosion ; Control methods ; Irrigation effects ; River basins ; Furrow irrigation / USA / Snake River
(Location: IWMI-HQ Call no: PER Record No: H014209)

2 Benjamin, L.; van Kirk, R. W. 1999. Assessing instream flows and reservoir operations on an eastern Idaho River. Journal of the American Water Resources Association, 35(4):899-909.
Reservoir operation ; Stream flow ; Water management ; Water rights ; Models / USA / Idaho River / Snake River / Island Park
(Location: IWMI-HQ Call no: PER Record No: H025126)

3 Papanicolaou, A. N.; Maxwell, A. R. 2000. Hydraulic performance of fish bypass-pools for irrigation diversion channels. Journal of Irrigation and Drainage Engineering, 126(5):314-321.
Irrigation management ; Open channels ; Design ; Rivers ; Fish ; Velocity ; Models ; Flow measurement / USA / Columbia River / Snake River / Salmon River
(Location: IWMI-HQ Call no: PER Record No: H026877)

4 Shallat, T. 2000. Ecology in policymaking: Water and the restoration of America's Snake River Plain. Water Policy, 2(4-5):327-341.
River basin development ; Ecology ; Policy making ; History / USA / Snake River / Idaho
(Location: IWMI-HQ Call no: PER Record No: H026956)

5 Ashraf, M. S.; Izadi, B.; King, B. A.; Neibling, H. 1999. Field evaluation of furrow irrigation performance, sediment loss, and bromide transport in a highly erosive silt loam soil. Journal of Soil and Water Conservation, 54(2):468-473.
Furrow irrigation ; Water quality ; Irrigation management ; Performance evaluation ; Models ; Erosion ; Soil properties / USA / Idaho / Snake River
(Location: IWMI-HQ Call no: P 5560 Record No: H027350)

6 Johnston, J. R.; Allen, R. G.; Anderson, S. S. (Eds.) 1999. River basin management to meet competing needs: Proceedings from the USCID Conference on Shared Rivers, Park City, Utah, October 28-31, 1998. Denver, CO, USA: USCID. vii, 312p.
River basins ; Dams ; Watershed management ; Water resource management ; Social participation ; International cooperation ; Canals ; Flood plains ; Flood control ; Models ; Networks ; Environmental sustainability / USA / Egypt / Canada / India / Europe / Elwha River / Kennebec River / Edwards Dam / Colorado River / Yakima River / Rio Grande River / Columbia River / Yampa River / Platte River / North Dakota / Sheyenne River / Sierra Nevada / San Joaquin / Glen Canyon Dam / Snake River / Nile River / Mackenzie River / Ganges / Danube River
(Location: IWMI-HQ Call no: 333.91 G000 JOH Record No: H028188)

7 Benjamin, L. 1999. Henry's Fork Watershed Council: Five years of learning to share a river. In Johnston, J. R.; Allen, R. G.; Anderson, S. S. (Eds.), River basin management to meet competing needs: Proceedings from the USCID Conference on Shared Rivers, Park City, Utah, October 28-31, 1998. Denver, CO, USA: USCID. pp.119-126.
Watershed management ; Institutions ; River basins ; Water management ; Organizations / USA / Snake River
(Location: IWMI-HQ Call no: 333.91 G000 JOH Record No: H028191)

8 Buchal, J. L. 1998. The great salmon hoax: An eyewitness account of the collapse of science and law and the triumph of politics in salmon recovery. Aurora, OR, USA: Iconoclast Publishing Company. 384p.
Fish ; Fisheries ; Rivers ; Dams ; Irrigation effects ; Ecosystems ; Environmental effects ; Legal aspects / USA / Snake River / Columbia Basin
(Location: IWMI-HQ Call no: 639.3 G430 BUC Record No: H037392)

9 Anderson, J. L.; Hilborn, R.W.; Lackey, R. T.; Ludwig, D. 2003. Watershed restoration: adaptive decision making in the face of uncertainty. In Wissmar, R. C.; Bisson, P. A. (Eds.). Strategies for restoring river ecosystems: sources of variability and uncertainty in natural and managed systems. Bethesda, MD, USA: American Fisheries Society. pp.203-232.
Watershed management ; Decision making ; Decision support systems ; Rivers ; Fish ; Habitats / USA / Cedar River / Columbia River / Snake River
(Location: IWMI-HQ Call no: 333.9162153 G430 WIS Record No: H040917)
https://vlibrary.iwmi.org/pdf/H040917.pdf

10 Bennett, A.; Nijssen, B.; Ou, G.; Clark, M.; Nearing, G. 2019. Quantifying Process Connectivity With Transfer Entropy in Hydrologic Models. Water Resources Research, 55(6):4613-4629. [doi: https://doi.org/10.1029/2018WR024555]
Hydrology ; Models ; River basins ; Runoff ; Water balance ; Information transfer ; Precipitation ; Mountains / USA / Canada / Columbia River Basin / Snake River / Willamette River / Olympic Mountains / Canadian Rockies
(Location: IWMI HQ Call no: e-copy only Record No: H049255)
https://vlibrary.iwmi.org/pdf/H049255.pdf
(2.36 MB)
Quantifying the behavior and performance of hydrologic models is an important aspect of understanding the underlying hydrologic systems. We argue that classical error measures do not offer a complete picture for building this understanding. This study demonstrates how the information theoretic measure known as transfer entropy can be used to quantify the active transfer of information between hydrologic processes at various timescales and facilitate further understanding of the behavior of these systems. To build a better understanding of the differences in dynamics, we compare model instances of the Structure for Unifying Multiple Modeling Alternatives (SUMMA), the Variable Infiltration Capacity (VIC) model, and the Precipitation Runoff Modeling System (PRMS) across a variety of hydrologic regimes in the Columbia River Basin in the Pacific Northwest of North America. Our results show differences in the runoff of the SUMMA instance compared to the other two models in several of our study locations. In the Snake River region, SUMMA runoff was primarily snowmelt driven, while VIC and PRMS runoff was primarily influenced by precipitation and evapotranspiration. In the Olympic mountains, evapotranspiration interacted with the other water balance variables much differently in PRMS than in VIC and SUMMA. In the Willamette River, all three models had similar process networks at the daily time scale but showed differences in information transfer at the monthly timescale. Additionally, we find that all three models have similar connectivity between evapotranspiration and soil moisture. Analyzing information transfers to runoff at daily and monthly time steps shows how processes can operate on different timescales. By comparing information transfer with correlations, we show how transfer entropy provides a complementary picture of model behavior.

11 Williams, P.; Kliskey, A. A.; Cronan, D.; Trammell, E. J.; de Haro-Martí, M. E.; Wilson, J. 2023. Constructing futures, enhancing solutions: stakeholder-driven scenario development and system modeling for climate-change challenges. Frontiers in Environmental Science, 11:1055547. [doi: https://doi.org/10.3389/fenvs.2023.1055547]
Climate change ; Stakeholders ; Uncertainty ; Energy ; Water quality ; Farmland ; Aquifers ; Models / United States of America / Idaho / Magic Valley / Twin Falls / Snake River
(Location: IWMI HQ Call no: e-copy only Record No: H051778)
https://www.frontiersin.org/articles/10.3389/fenvs.2023.1055547/pdf
https://vlibrary.iwmi.org/pdf/H051778.pdf
(1.74 MB) (1.74 MB)
Finding effective and practical solutions to climate change challenges in food-energy-water systems requires the integration of experts in local/regional social and biophysical systems, and these are commonly local community members. In the Magic Valley, Idaho we investigated the tensions between water used for energy and to irrigate cropland for food production, as well as, strategies for protecting water quantity and quality. Incorporating stakeholders with long-standing expertise allows the development of solutions to these challenges that are locally and regionally practical and consistent with the values of the social system into which they are incorporated. We describe a stakeholder-driven process used in a case study in the Magic Valley that incorporated local experts to develop plausible future scenarios, identify drivers of change, vet impact and hydrological modeling and map areas of change. The process described allowed stakeholders to envision alternative futures in their region, leading to development of enhanced context and place-based solutions and an anticipated time line for adoption of those solutions. The solutions developed by the stakeholders have been applied across many geographic areas. The described process can also be applied across a broad range of geographic levels. Most importantly, stakeholders should be involved in anticipating solutions and solution timing to the differing challenges posed by each scenario.

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