An Assessment of Water Resources in the Taiwan Strait Island Using the Water Poverty Index
Abstract
:1. Introduction
2. Development and Application of the WPI
2.1. Framework of the WPI
- (1)
- Water resources: Based on economic and calculated considerations, available water resources are usually estimated using post rainfall runoff and groundwater recharge (blue water);
- (2)
- Measure of access: In areas where access to water is difficult, the time it takes to fetch water is very important. During the dry season, rich or influential people can obtain sufficient water resources, while the poor can only find the water that is naturally available. People who have insufficient income often must choose between food or water, making their lives very difficult.
- (3)
- Water quality and change: Water quality is an indicator used to define environmental improvements. Changes in the water supply are often overlooked indicators, and, in developing countries, this impact factor can determine the uncertainty of the water supply in the region.
- (4)
- Water used for production or food: The United Nations only focuses on the water required for people’s livelihoods; however, the food manufacturing sector also uses a large amount of water (industries such as animal husbandry, agriculture, and manufacturing), which should be included in the calculation of the WPI.
- (5)
- Ability to manage water resources: the effective management of water resources is closely related to education and income levels and affects whether water resources can be effectively used and whether relevant units can properly resolve issues.
- (6)
- Environment: The improvement of water resources must not cause environmental damage, and environmental sustainability must be a priority. The areas of nature reserves, the popularizing rate of environmental information, and the special environmental features of each region should be discussed from this perspective.
- (7)
- Spatial scale: The state of water resources often changes with space. Sometimes, areas less than a few kilometers apart have different socio–economic features that affect their use of water resources. Therefore, spatial scale requires careful consideration to reflect the degree of discrepancy in regional water use.
2.2. Application of the WPI
2.3. Development of the WPI in Taiwan
2.4. Study area
- (1)
- Based on the framework of the WPI in Taiwan, to calculate the WPI in Kinmen;
- (2)
- Based on the calculation results of the WPI in Kinmen, compare the ranking with the WPI in Taiwan;
- (3)
- For influential indicators, use a time-series forecast by year to understand the changes in the WPI in Kinmen until 2030.
- (1)
- In the WPI, every component, second component, and indicator project can illustrate the water resource problems in Kinmen.
- (2)
- Different indicators have different calculation scales so that the differences between the indicators can be identified.
- (3)
- The indicator calculation results reflect the conditions of water resources in Kinmen.
2.5. Development of Water Resources in Kinmen
3. Research Method
3.1. The WPI Calculation Method
3.1.1. Transnational Application of the WPI
3.1.2. Development of Taiwan’s WPI
3.2. Time-Series Analysis
4. Research Results
4.1. Comparisons with Other Counties and Cities
- (1)
- The resource score: In situation 1, the total score of the Kinmen region was 0.621; thus, Kinmen was ranked 13th among all counties and cities. In situation 2, the total score of the Kinmen region was 0.619, ranking it 13th among all counties and cities. In both situations, Kinmen had the same rank.
- (2)
- The access score: In situation 1, the total score of the Kinmen region was 0.828, which ranked Kinmen 11th among all counties and cities. In situation 2, the total score of the Kinmen region was 0.838, ranking Kinmen 9th among all counties and cities. Kinmen’s ranking in situation 2 was more than that in situation 1.
- (3)
- The capacity score: In situation 1, the total score of the Kinmen region was 0.523, which ranked Kinmen 17th among all counties and cities. In situation 2, the total score of the Kinmen region was 0.522, ranking Kinmen 17th among all counties and cities. In these two situations, Kinmen had the same rank.
- (4)
- The use score: In situation 1, the total score of the Kinmen region was 0.532, ranking Kinmen 16th among all counties and cities. In situation 2, the total score of the Kinmen region was 0.547, which ranked Kinmen 15th among all counties and cities. Kinmen’s ranking in situation 2 was greater than that in situation 1.
- (5)
- The environment score: In situation 1, the total score of the Kinmen region was 0.809, ranking Kinmen first among all counties and cities. In situation 2, the total score of the Kinmen region was 0.799, which ranked Kinmen first among all counties and cities. In these two situations, Kinmen had the same rank.
- (6)
- An analysis of the overall scores and county and city rankings showed that, in situation 1, the total score of Kinmen was 0.663, which ranked Kinmen 10th among the 23 counties and cities, and, in situation 2, the total score of Kinmen was 0.664, which ranked Kinmen 9th among the 23 counties and cities.
4.2. Comparisons with Other Regions
- (1)
- In situation 1, Kinmen ranked last among the regions, including southern Taiwan, central Taiwan, northern Taiwan, eastern Taiwan, and Kinmen. In situation 2, Kinmen ranked the same. Figure 7 and Figure 8 compare Kinmen and the other regions of Taiwan in situations 1 and 2, respectively. In both figures, Taiwan is divided into four regions, namely north, central, south, and east, to facilitate its comparison with Kinmen.
- (2)
- Comparing the differences between each component of Kinmen in situations 1 and 2. Except for the capacity component in situation 2 (0.01), which was higher than that in situation 1, the other components in situation 1 were all higher than those in situation 2 by 0.01–0.03. Overall, no significant differences were observed in the WPI between situations 1 and 2.
4.3. The Future Development of the WPI of Kinmen
- (1)
- (2)
- Water popularization rate: According to estimations based on the WPI data, the water popularization rate in Kinmen will be reduced to approximately 95.3% because of the increase in the immigrant population by 2030 (Figure 10).
- (3)
- People over 15 years old according to their proportion of higher education: According to estimations based on the WPI data, the proportion of people over 15 years old with higher education in Kinmen will increase to approximately 56% by 2030 (Figure 11).
- (4)
- The average annual income per person: According to estimations based on the WPI data, the average annual income per person in Kinmen will increase to approximately 291,000 yuan/person by 2030 (Figure 12).
- (5)
- Daily livelihood water consumption per person: According to estimations based on the WPI data, the daily livelihood water consumption per person in Kinmen will be reduced to approximately 88.71 L/person by 2030 (Figure 13).
- (6)
- Water pipeline leakage rate: According to estimations based on the WPI data, the water pipeline leakage rate in Kinmen will be reduced to approximately 10.42% by 2030 (Figure 14).
- (7)
- Sewage sewer takeover rate: According to estimations based on the WPI data, the sewage sewer takeover rate in Kinmen will be approximately 63.9% by 2030 (Figure 15).
5. Conclusions and Suggestions
5.1. Conclusions
5.2. Policies and Suggestions
Author Contributions
Funding
Conflicts of Interest
References
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Component | Subcomponent |
---|---|
Resources | Internal volume of fresh water sources, foreign water, population. |
Access | Percentage of the population that can get clean water; percentage of the population that can use sanitary equipment, percentage of the population for whom irrigation is acceptable. |
Capacity | GDP Per Capita, under-five infant mortality, the proportion of education, Gini index (income distribution). |
Use | Daily water consumption, the proportion of industrial water and agricultural water. |
Environment | Standard (Z) value of the water quality, water pressure, environmental laws and management, biodiversity, information technology capacity indicators in the environmental sustainability index architecture. |
Component | S1/S2 | Subcomponent | S1/S2 | Indicator | S1/S2 |
---|---|---|---|---|---|
Resources | 0.200/0.213 | Surface water | 0.066/0.072 | Amount of surface water resources per capita | 0.066/0.072 |
Groundwater | 0.066/0.072 | Amount of groundwater recharge per capita | 0.033/0.037 | ||
0.066/0.067 | Proportion of groundwater use and recharge amount | 0.066/0.035 | |||
Storage capacity | 0.066/0.067 | Effective capacity of reservoir per capita in area | 0.066/0.067 | ||
Access | 0.200/0.188 | Water used for people’s livelihoods | 0.066/0.072 | Installation popularity rate of household water pipelines | 0.033/0.037 |
Annual water rationing days of water use for people’s livelihood | 0.033/0.035 | ||||
industrial water | 0.066/0.059 | Water rationing, days of annual industrial water | 0.066/0.059 | ||
agricultural water | 0.066/0.057 | Proportion of irrigated area under arable land | 0.033/0.029 | ||
Cost of compensation for water rationing effect irrigation fallow | 0.033/0.028 | ||||
Capacity | 0.200/0.178 | Health | 0.050/0.050 | Infant mortality | 0.050/0.050 |
Education | 0.050/0.045 | Literacy rates for population over 15 years of age | 0.025/0.023 | ||
Proportion of people over 15 years of age received higher education | 0.025/0.022 | ||||
Consumption capacity | 0.050/0.040 | Average annual disposable income per person | 0.025/0.020 | ||
Engle coefficient | 0.025/0.019 | ||||
Investment in water | 0.050/0.045 | Proportion of investment funds for water resource construction in public fixed capital | 0.050/0.045 | ||
Use | 0.200/0.213 | Amount of water used for people’s livelihoods | 0.050/0.056 | Daily water consumption for people’s livelihoods per person | 0.050/0.056 |
Efficiency of water use | 0.050/0.057 | Economic efficiency of industrial water use | 0.017/0.020 | ||
Economic efficiency of water used in the service industry | 0.017/0.019 | ||||
Economic efficiency of agricultural water use | 0.017/0.019 | ||||
Cost | 0.050/0.049 | Cost of one cubic meter of running water | 0.050/0.049 | ||
Leakage | 0.050/0.051 | Leakage rate of water pipeline | 0.050/0.051 | ||
Environment | 0.200/0.213 | Landslide | 0.040/0.043 | Number of landslides declared per unit area | 0.040/0.043 |
Flood | 0.040/0.041 | Annual average number of casualties caused by floods in recent ten years | 0.020/0.020 | ||
Rainfall wet season and dry season ratio | 0.020/0.021 | ||||
Formation subsidence | 0.040/0.044 | Proportion of the area of continuous subsidence caused by the groundwater exceeding pumping | 0.040/0.044 | ||
Biological diversity | 0.040/0.037 | Proportion of forest cover | 0.013/0.013 | ||
Percentage of area of nature reserves | 0.013/0.012 | ||||
Proportion of species threatened by survival | 0.013/0.012 | ||||
Pollution | 0.040/0.048 | Proportion of being classified as heavily contaminated river sections | 0.020/0.023 | ||
Sewage sewer takeover rate | 0.020/0.025 |
Component | Resources | Access | Capacity | Use | Environment | WPI Total Score S1/S2 | Total Rank S1/S2 |
---|---|---|---|---|---|---|---|
County/City | S1/S2 | S1/S2 | S1/S2 | S1/S2 | S1/S2 | ||
Keelung City | 0.589/0.585 | 0.782/0.786 | 0.505/0.506 | 0.274/0.283 | 0.533/0.531 | 0.537/0.533 | 23/23 |
Taipei County | 0.633/0.628 | 0.810/0.813 | 0.624/0.628 | 0.535/0.523 | 0.755/0.749 | 0.671/0.666 | 7/8 |
Taipei City | 0.614/0.610 | 0.825/0.828 | 0.762/0.758 | 0.506/0.495 | 0.644/0.634 | 0.670/0.658 | 9/12 |
Taoyuan County | 0.637/0.633 | 0.736/0.749 | 0.510/0.504 | 0.663/0.652 | 0.760/0.755 | 0.661/0.662 | 12/10 |
Hsinchu County | 0.691/0.688 | 0.629/0.614 | 0.614/0.620 | 0.634/0.626 | 0.786/0.779 | 0.671/0.669 | 7/7 |
Hsinchu City | 0.612/0.608 | 0.759/0.744 | 0.610/0.609 | 0.777/0.777 | 0.780/0.777 | 0.708/0.705 | 2/3 |
Miaoli County | 0.830/0.828 | 0.732/0.717 | 0.749/0.756 | 0.679/0.673 | 0.778/0.767 | 0.754/0.749 | 1/1 |
Taichung County | 0.741/0.737 | 0.842/0.837 | 0.499/0.497 | 0.459/0.455 | 0.777/0.769 | 0.663/0.660 | 10/11 |
Taichung City | 0.432/0.428 | 0.925/0.921 | 0.580/0.578 | 0.400/0.394 | 0.719/0.716 | 0.611/0.601 | 21/21 |
Nantou County | 0.790/0.786 | 0.778/0.776 | 0.533/0.538 | 0.571/0.573 | 0.782/0.770 | 0.691/0.692 | 4/4 |
Changhua County | 0.588/0.589 | 0.886/0.881 | 0.507/0.513 | 0.662/0.667 | 0.490/0.487 | 0.627/0.625 | 18/17 |
Yunlin County | 0.666/0.671 | 0.890/0.886 | 0.602/0.610 | 0.623/0.621 | 0.364/0.355 | 0.629/0.623 | 17/18 |
Chiayi County | 0.730/0.734 | 0.841/0.839 | 0.584/0.586 | 0.658/0.658 | 0.573/0.562 | 0.677/0.675 | 6/6 |
Chiayi City | 0.392/0.392 | 0.829/0.832 | 0.631/0.638 | 0.653/0.653 | 0.700/0.698 | 0.641/0.638 | 16/15 |
Tainan County | 0.584/0.586 | 0.853/0.853 | 0.565/0.568 | 0.742/0.736 | 0.530/0.519 | 0.655/0.650 | 13/13 |
Tainan City | 0.500/0.500 | 0.875/0.875 | 0.610/0.616 | 0.749/0.744 | 0.533/0.534 | 0.653/0.650 | 14/14 |
Kaohsiung County | 0.572/0.573 | 0.828/0.826 | 0.477/0.476 | 0.527/0.520 | 0.718/0.707 | 0.624/0.620 | 19/19 |
Kaohsiung County | 0.278/0.279 | 0.945/0.939 | 0.574/0.575 | 0.607/0.604 | 0.688/0.701 | 0.618/0.613 | 20/20 |
Pingtung County | 0.688/0.691 | 0.744/0.729 | 0.563/0.564 | 0.651/0.650 | 0.744/0.735 | 0.678/0.676 | 5/5 |
Taitung County | 0.647/0.644 | 0.790/0.786 | 0.500/0.492 | 0.251/0.262 | 0.728/0.720 | 0.583/0.579 | 22/22 |
Hualien County | 0.760/0.759 | 0.793/0.786 | 0.623/0.615 | 0.239/0.245 | 0.749/0.740 | 0.633/0.626 | 15/16 |
Yilan County | 0.826/0.825 | 0.882/0.874 | 0.555/0.557 | 0.594/0.596 | 0.684/0.681 | 0.708/0.708 | 2/2 |
Kinmen County | 0.621/0.619 | 0.828/0.838 | 0.523/0.522 | 0.532/0.547 | 0.809/0.799 | 0.663/0.664 | 10/9 |
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Chen, T.-T.; Hsu, W.-L.; Chen, W.-K. An Assessment of Water Resources in the Taiwan Strait Island Using the Water Poverty Index. Sustainability 2020, 12, 2351. https://doi.org/10.3390/su12062351
Chen T-T, Hsu W-L, Chen W-K. An Assessment of Water Resources in the Taiwan Strait Island Using the Water Poverty Index. Sustainability. 2020; 12(6):2351. https://doi.org/10.3390/su12062351
Chicago/Turabian StyleChen, Tung-Tsan, Wei-Ling Hsu, and Wen-Kuang Chen. 2020. "An Assessment of Water Resources in the Taiwan Strait Island Using the Water Poverty Index" Sustainability 12, no. 6: 2351. https://doi.org/10.3390/su12062351
APA StyleChen, T. -T., Hsu, W. -L., & Chen, W. -K. (2020). An Assessment of Water Resources in the Taiwan Strait Island Using the Water Poverty Index. Sustainability, 12(6), 2351. https://doi.org/10.3390/su12062351