Full text: Resource and environmental monitoring (A)

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IAPRS & SIS, Vol.34, Part 7, “Resource and Environmental Monitoring”, Hyderabad, India,2002 
order to identify the stakeholders using the resource. The steps 
that follow guide the user to think in a systematic way to 
formulate land use policies and to compare the impacts of 
different strategies. 
2.4 Interactive specification of Objectives and Criteria 
The DSS through its interface, allows the user to interactively 
formulate objectives and select the criteria which will allow the 
strategies to be evaluated in more specific and quantitative 
terms. The user is allowed to select the criteria that can be 
actually computed through the computational framework. 
  
  
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Figure 2. Link between the conceptual framework and 
computational framework 
The overall objective of the study is to “optimize use of land 
resources for shrimp-paddy cultivation within the study area”. 
In order to achieve this ultimate objective, the user can 
concentrate on some or all of the criteria listed in Table 1 that 
are elaborations of the three national policy objectives of 
‘economic growth’, ‘social well-being’ and ‘environmental 
integrity’ in accordance with the Fifth Five Year Plan (FFYP, 
1997). 
25 Scenarios or exogenous developments 
In this DSS, four different fresh water flows or discharges from 
the Gorai River are presented as possible scenarios (0 m3/sec, 
60 m3/sec, 100 m3/sec and 150 m3/sec) The water 
management options, which may establish these different 
flows, are considered to be outside management control and as 
such would be an exogenous development. The user may select 
one of the four scenarios to evaluate the impacts of different 
strategies. Increased fresh water flow from the Gorai River 
would push down the salinity frontiers in the study area and 
may result in more land being profitable for paddy cultivation 
or the cultivation of Golda shrimp instead of Bagda shrimp. 
Depending on the freshwater flow, areas under the different 
salinity classes would change and the impact of the land use 
policy on the criteria would vary. Hence, the analysis would 
show how the impact of a strategy changes with the Gorai flow 
scenario. 
2.6 Interactive specification of strategies or 
management options 
The strategies considered in the context of this study restrict . 
paddy and shrimp cultivation to specific areas. One strategy is 
to allocate land to different production regimes. This is done as 
presented in Table 2. The table shows the base case (1999) 
landuse under each salinity regime. The user can interactively 
change the allocations in percentages. A strategy that intends to 
maximize agricultural production can, for example, bring all the 
suitable lands under paddy cultivation by replacing any existing 
shrimp cultivation as shown in Table 3, and making landuse 
allocation as per Table 4. A balanced land use, on the other 
hand, may include allocations such as that shown in Table 4. 
All the Aman-Boro land is shifted to Golda-Boro land use in 
order to increase shrimp production, thereby reducing paddy 
production. In order to somewhat mitigate this effect, all the 
Bagda-Bagda land, which is environmentally damaging, may 
be shifted to the Bagda-Aman regime. The Aman floodplain is 
kept as it is in order to retain the capture fisheries production. 
  
Economic growth 
  
Regional income 
Foreign currency earning 
Employment 
Net economic return 
Sum of wages, profit and land rent received by the region. 
Foreign currency income of the country from shrimp export. 
Total employment (male and female) generated in the region. 
Gross return less total cost. It is an indicator of economic efficiency. 
  
Social well-being 
  
Nutrition 
Sanitation 
Education 
Housing 
Public health 
Unskilled job opportunities 
Female work opportunities 
Access to common 
properties 
Access to small holdings 
Nutrition value of total rice paddy and fish production. 
Degree of access to fresh water on the surface. 
Opportunities for education resulting from different types of production activities. 
Vulnerability of housing structures under the different types of inundation required for different types of production 
activities. 
Degree of risk of the population from exposure to inundated conditions. 
Total job opportunities for unskilled labor in the study area. 
Total job opportunities for women in the study area. 
Degree of access to floodplain fishing and grazing areas. Aman floodplain provides the maximum access to such 
activities. 
Degree of access for small land holding operations under different crop production regimes. Area under paddy 
production provides the most access for such operations. 
  
Environmental Integrity 
  
  
Aquatic bio-diversity 
Terrestrial bio-diversity 
Mangrove bio-diversity 
Soil condition 
Groundwater salinity 
Health of aquatic eco-system of the region. Area of rivers, beels or waterbodies and floodplains in different salinity 
regimes are influencing factors. Aquatic bio-diversity is best in the mid salinity regime. 
Health of terrestrial eco-system. Area of vegetation (settlement and others) is indicative of terrestrial eco-system. 
Terrestrial eco-system is the most productive in fresh water, or lowest (<5ppt) salinity regime. 
Areas of mangrove multiplied by weights, which varies according to salinity. Mangrove is the most productive in the 
5-10ppt salinity range. 
Deterioration of soil productivity resulting from different production regimes. It depends upon area under bagda 
production and salinity. 
Threat to coastal aquifers. Depends upon area under Boro production, which uses groundwater as irrigation water. 
  
Table 1. List of criteria 
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