Your search found 25 records
1 ESCAP. 1993. Atlas of mineral resources of the ESCAP Region: Geology and mineral resources of Nepal - Explanatory brochure. Vol.9. Bangkok, Thailand: ESCAP. x, 107p.
(Location: IWMI-HQ Call no: 549 G726 ESC Record No: H013335)
(Location: IWMI-HQ Call no: P 3421 Record No: H013904)
(Location: IWMI-HQ Call no: 574.5 G744 SRI Record No: H012660)
(Location: IWMI-HQ Call no: 551.4 G000 CHO Record No: H014130)
5 Naidu, R.; Sumner, M. E.; Rengasamy, P. (Eds.) 1995. Australian sodic soils: Distribution, properties and management. East Melbourne, Victoria, Australia: CSIRO. viii, 351p.
(Location: IWMI-HQ Call no: 631.42 G922 NAI Record No: H017959)
6 ESCAP. 1995. Atlas of mineral resources of the ESCAP region. Volume II: Geology and mineral resources of Afghanistan. New York, NY, USA: UN. viii, 85p.
(Location: IWMI-HQ Call no: 333.85 G580 ESC Record No: H020115)
7 ESCAP. 1996. Atlas of mineral resources of the ESCAP Region: Volume 12 - Geology and mineral resources of Myanmar. New York, NY, USA: UN. xiii, 1939.
(Location: IWMI-HQ Call no: 333.85 G590 ESC Record No: H021151)
8 Kapoor, A. S. 1998. Rate of increase in ground water salinity due to irrigation with and without bio-drainage. Unpublished report. Indira Gandhi Nahar Board, Jaipur, India. 13p.
(Location: IWMI-HQ Call no: P 4884 Record No: H022635)
9 Whiteley, P.; Masayesva, V. 1998. The use and abuse of aquifers: Can the Hopi Indians survive multinational mining? In Donahue, J. M.; Johnston, B. R. (Eds.), Water, culture, and power: Local struggles in a global context. Washington, DC, USA: Island Press. pp.9-34.
(Location: IWMI-HQ Call no: 333.91 G000 DON Record No: H025728)
(Location: IWMI-HQ Call no: 912.13 G744 SOM Record No: H025758)
(Location: IWMI-HQ Call no: 631.7.6.3 G584 BAN Record No: H025807)
12 ESCAP. 2000. Atlas of mineral resources of the ESCAP Region: Volume 15 - Geology and mineral resources of Azerbaijan. New York, NY, USA: UN. ix, 216p.
(Location: IWMI-HQ Call no: 549 G867 ESC Record No: H027629)
(Location: IWMI-HQ Call no: 333 G744 SRI Record No: H029406)
14 Davy, J. 1821. An account of the interior of Ceylon and of its inhabitants with travels in that island. Dehiwala, Sri Lanka: Tisara. xxiv, 399p. (The Ceylon Historical Journal vol.16)
(Location: IWMI-HQ Call no: 910.4 G744 DAV Record No: H031431)
(Location: IWMI-HQ Call no: CD Col Record No: H031576)
16 Flint, L. E.; Selker, J. S. 2003. Use of porosity to estimate hydraulic properties of volcanic tuffs. Advances in Water Resources, 26(5):561-571.
(Location: IWMI-HQ Call no: PER Record No: H031992)
17 Nag, P. (Ed.) 2002. National atlas of India: Abridged edition (English) Kolkata, India: National Atlas and Thematic Mapping Organisation. 30p.
(Location: IWMI-HQ Call no: R 912 G635 NAG Record No: H032984)
18 Dinar, S. (Ed.) 2011. Beyond resource wars: scarcity, environmental degradation, and international cooperation. Cambridge, MA, USA: Massachusetts Institute of Technology (MIT). 335p. (Global Environmental Accord: Strategies for Sustainability and Institutional Innovation)
(Location: IWMI HQ Call no: 363.7 G000 DIN Record No: H043961)
(0.09 MB)
19 Rao, P. S.; Pant, D. C. 2014. Implications of labour migration and land use changes on food production in the peri-urban area of Rajsamand district of Rajasthan, India: a case study. In Maheshwari, B.; Purohit, R.; Malano, H.; Singh, V. P.; Amerasinghe, Priyanie. (Eds.). The security of water, food, energy and liveability of cities: challenges and opportunities for peri-urban futures. Dordrecht, Netherlands: Springer. pp.327-339. (Water Science and Technology Library Volume 71)
(Location: IWMI HQ Call no: IWMI Record No: H047044)
This study examines the situation of land utilization and migration of population from farming sector to marble sector of the district, and identifies the causes of reduction of crop productivity. To achieve these objectives the peri-urban area of Amet tehsil of Rajsamand district is the most affecting tehsil where marble industry has flourished strongly and substituting the agriculture industry causing reduction of crop and livestock production drastically over the period. Thus, Amet tehsil of Rajsamand district has been selected purposively for the study. For indepth study, a case study of ‘‘Jetpura Panchaayat’’ has been selected randomly. Besides, it is again important that this Panchaayat is growing for quartz production where 10–15 crusher plants are already established in the area. Primary data have been collected from pre-tested schedules and raw data have been analysed with the help of % and averages and conclusions have been drawn accordingly. It is concluded that land use pattern of the district is changing rapidly after the introduction of marble industry. The area under forest was decreasing from 24,663 hectares in 2001 to 23,214 hectares in 2010; this may be due to conversion of the area into nonforest purposes. Similarly, the area under non-agricultural use has been decreased from 1,27,697 hectares in 2001 to 1,85,439 hectares in 2010, which further strengthens the statement of introduction of marble industry. It is further clear from the results that productivity of all the crops have been on the decline over the study period and as such this has implication for food security in the region.
(Location: IWMI HQ Call no: e-copy only Record No: H047624)
(3.33 MB)
Phosphorus (P) is a critical, geographically concentrated, nonrenewable resource necessary to support global food production. In excess (e.g., due to runoff or wastewater discharges), P is also a primary cause of eutrophication. To reconcile the simultaneous shortage and overabundance of P, lost P flows must be recovered and reused, alongside improvements in P-use efficiency. While this motivation is increasingly being recognized, little P recovery is practiced today, as recovered P generally cannot compete with the relatively low cost of mined P. Therefore, P is often captured to prevent its release into the environment without beneficial recovery and reuse. However, additional incentives for P recovery emerge when accounting for the total value of P recovery. This article provides a comprehensive overview of the range of benefits of recovering P from waste streams, i.e., the total value of recovering P. This approach accounts for P products, as well as other assets that are associated with P and can be recovered in parallel, such as energy, nitrogen, metals and minerals, and water. Additionally, P recovery provides valuable services to society and the environment by protecting and improving environmental quality, enhancing efficiency of waste treatment facilities, and improving food security and social equity. The needs to make P recovery a reality are also discussed, including business models, bottlenecks, and policy and education strategies.
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