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Frontiers of Engineering Management

ISSN 2095-7513

ISSN 2096-0255(Online)

CN 10-1205/N

Postal Subscription Code 80-905

Front. Eng    2022, Vol. 9 Issue (2) : 257-267    https://doi.org/10.1007/s42524-020-0144-y
RESEARCH ARTICLE
An evaluation model of water-saving reconstruction projects based on resource value flows
Runwen JIANG1, Xiaohong CHEN2, Lingchu ZHAO1, Zhifang ZHOU3, Tao ZHANG4()
1. Central South University, Changsha 410083, China
2. Collaborative Innovation Center of Resource-conserving & Environment-friendly Society and Ecological Civilization, Central South University, Changsha 410083, China; Mobile E-business 2011 Collaborative Innovation Center of Hunan Province, Hunan University of Technology and Business, Changsha 410205, China
3. Collaborative Innovation Center of Resource-conserving & Environment-friendly Society and Ecological Civilization, Central South University, Changsha 410083, China
4. Loughborough University London, London E20 3BS, UK
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Abstract

Due to uncertainties in water supply, there is growing demand for water resource management in enterprises. In this study, we evaluated the effects of companies’ water-saving reconstruction projects. We used Hina Advanced Materials Company as a case to construct an investment decision model to (1) calculate the internal and external costs of water resources based on circular economic value analysis theory, and (2) locate the level of water resources circulation. We adopted gray situation decision analysis to identify the typical problems that occur in water resource utilization. Moreover, we demonstrated optimization plans for different potential improvements, thereby providing guidance and references for water resource cost management and the comprehensive optimization of environmental benefits. We concluded that the circulation economic value analysis model can effectively display the flow and amount of value derived from water resource flows, thereby providing guidance and suggestions for optimizing water resource flows.

Keywords value flow analysis      ternary materials enterprises      grey situation decision analysis      water resources     
Corresponding Author(s): Tao ZHANG   
Just Accepted Date: 29 September 2020   Online First Date: 23 November 2020    Issue Date: 25 May 2022
 Cite this article:   
Runwen JIANG,Xiaohong CHEN,Lingchu ZHAO, et al. An evaluation model of water-saving reconstruction projects based on resource value flows[J]. Front. Eng, 2022, 9(2): 257-267.
 URL:  
https://academic.hep.com.cn/fem/EN/10.1007/s42524-020-0144-y
https://academic.hep.com.cn/fem/EN/Y2022/V9/I2/257
Goal layer Criterion layer Weight Index layers Weight
Water resource value flow evaluation index (H) Water input (C1) 0.413 Sales water cost rate 0.462
Fresh water consumption per unit product 0.203
Cycle water consumption per unit product 0.203
Wastewater treatment cost per unit product 0.132
Water recycling (C2) 0.260 Water resource cost loss rate 0.388
Water recycling rate 0.214
Ratio of internal resource value to external environmental damage 0.274
Ammonia wastewater treatment rate 0.124
Water output (C3) 0.327 Ammonia emissions per unit product 0.218
Ammonia wastewater discharge per unit product 0.380
Chemical oxygen demand emissions per unit product 0.152
External damage value per unit product 0.175
Total nitrogen emissions per unit product 0.075
Tab.1  Quantitative index system for water resource value flow evaluation in the ternary materials industry
Resource flow efficiency level Comprehensive evaluation score Resource flow efficiency
I 0.80 to 1.00 Consistent with international advanced standards
II 0.60 to 0.80 Consistent with domestic advanced standards
III 0.40 to 0.60 Met the basic domestic standards
IV Below 0.40 Failed to meet basic domestic standards
Tab.2  Ternary materials industry resource flow efficiency evaluation level
Validity index Specific indicators Weight Extremum
Comprehensive economic utility indicators A A1: Total investment 0.0893 Minimal
A2: Economic benefits 0.0954 Maximal
A3: Annual operating cost 0.0659 Minimal
A4: Added value output efficiency 0.0686 Maximal
Resource flow indicators B B1: Water resource cost loss rate 0.0995 Minimal
B2: Water recycling rate 0.0680 Maximal
B3: Change rate of wastewater treatment cost 0.0955 Minimal
B4: Change rate of internal resource value flow 0.1246 Minimal
Social environmental benefit indicators C C1: Change rate of ammonia nitride emissions 0.1182 Minimal
C2: Change rate of exhaust gas damage value 0.0304 Minimal
C3: Change rate of external damage per unit output 0.0593 Minimal
C4: Change rate of wastewater discharge 0.0752 Minimal
Tab.3  Optimization of water resource value flow index and weight allocation in ternary materials industry
Fig.1  Water resource transfer balance graph of Hina.
Stage Internal water loss cost External environmental damage cost
Item Value flow cost (yuan) Proportion Value flow cost (yuan) Proportion
Synthesis reaction Positive products 3671931 77.90% 523865 32.92%
Negative products 1041715 22.10%
Total 4713646 100%
Water filtration Positive products 4963938 57.07% 917713 57.66%
Negative products 3734043 42.93%
Total 8697981 100%
Dry sieving Positive products 3409800 68.69% 149967 9.42%
Negative products 1554241 31.31%%
Total 4964041 100%
Tab.4  Two-dimensional accounting summary of Hina’s water resource internal and external cost
Project b1 b2 b3 b4
Internal economic benefits 518946 -406956 558182 763166
External economic benefits 111339 475105 447321 -128362
Tab.5  Comprehensive cost-efficiency of different options (unit: yuan)
Projects b1 b2 b3 b4
Comprehensive economic utility indicators A A1: Total investment (yuan) 5460000 3900000 9620000 1560000
A2: Economic benefits (yuan) 518946 -406956 558182 763166
A3: Annual operating cost (yuan) 273127 27307 1740172 280319
A4: Added value output efficiency 0 0.24 0 1.56
Resource flow indicators B B1: Water resource cost loss rate (%) 60.42 45.63 40.35 64.32
B2: Water recycling rate (%) 72.64 84.62 88.65 67.52
B3: Change rate of wastewater treatment cost (%) -10.15 0 -48.75 -34.95
B4: Change rate of internal resource value flow (%) -7.60 6.59 -8.69 -9.53
Social environmental benefit indicators C C1: Change rate of ammonia nitride emissions (%) -16.50 -35.60 -58.69 -19.65
C2: Change rate of exhaust gas damage value (%) -0.94 -31.00 -1.96 45.63
C3: Change rate of external damage per unit output (%) -7.00 -29.85 -28.11 8.07
C4: Change rate of wastewater discharge (%) -39.15 -46.85 -55.63 0
Tab.6  Target effects of the different reconstruction projects in Hina
Projects b1 b2 b3 b4
Comprehensive economic utility indicators A A1: Total investment 0.71 1.00 0.41 0.25
A2: Economic benefits 0.33 0 0.35 1.00
A3: Annual operating cost 0.10 1.00 0.02 0.10
A4: Added value output efficiency 0 0.15 0 1.00
Resource flow indicators B B1: Water resource cost loss rate 0.67 0.88 1.00 0.63
B2: Water recycling rate 0.82 0.95 1.00 0.76
B3: Change rate of wastewater treatment cost 0.21 0 1.00 0.74
B4: Change rate of internal resource value flow 0.80 0 0.91 1.00
Social environmental benefit indicators C C1: Change rate of ammonia nitride emissions 0.28 0.61 1.00 0.33
C2: Change rate of exhaust gas damage value 0.03 1.00 0.06 0
C3: Change rate of external damage per unit output 0.23 1.00 0.94 0
C4: Change rate of wastewater discharge 0.70 0.84 1.00 0
Tab.7  Performance measurement of the different reconstruction projects in Hina
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