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Brisbane, Australia | 20-24 October 2019
Development of a Dissolved Oxygen -Biochemical Oxygen Demand (DO-BOD) System Dynamics Model of Pasig River,
Philippines using STELLA
Engr. Eduardo Bornilla Jr.
Engr. Tolentino Moya, Ph.D.
Merliza Bonga
Brisbane, Australia | 20-24 October 2019
What’s important with DO and BOD?Dissolved Oxygen
- an essential element supporting the aquatic life
- provides the maximum information about water quality conditions (Ji, 2008)
Biochemical Oxygen Demand
- a measure of organic pollutants in the water
- amount of dissolved oxygen needed to break down organic matter in water
Polluted aquatic systems lead to reduction of dissolved oxygen. Further reductionto 2 – 3 mg/L DO concentration leads to a hypoxic condition or worse to anoxiccondition (0 mg/L DO) that results to altered breathing patterns or fish kills.
Brisbane, Australia | 20-24 October 2019
The Case of Pasig River System • Coastal estuarine
• Drains the Philippine National Capital Region
• Connects the Laguna Lake and Manila Bay
• Declared biologically dead in early 2000s (Gorme, et al. 2010)
Source: Pasig River Rehabilitation Commission (PRRC)
Laguna Lake
Manila Bay
Brisbane, Australia | 20-24 October 2019
Water Quality Standard
• BOD ≤ 7 mg/L
• DO ≥ 5 mg/L
Source: Pasig River Rehabilitation Commission (PRRC)
Annual Water Quality Data
Brisbane, Australia | 20-24 October 2019
Rationale behind the Pasig River ModelSituationer
• This model was an academic research project in partnership with PRRC for purposes of additional environmental management tool.
Main Objective
• develop a system dynamic model to understand the non-linear behavior of surface water dissolved oxygen (DO) and biochemical oxygen demand (BOD) over time as water moves downstream
Potential Applications
• reconstruct pollution transport and identify the hypoxia hot spots along the river channel
• estimate the BOD load contribution of the Pasig River watershed to Manila Bay
• estimate a daily allowable BOD load from Pasig River tributaries to attain Class C water
Brisbane, Australia | 20-24 October 2019
The River Water Quality ModelStreeter-Phelps Model
• pioneering river water quality model
• dissolved oxygen is consumed to degrade BOD in water
• mathematically describes the decrease in the DOconcentration by degradation of BOD along a stream
Source: nptel.ac.in
Aquatic hypoxia is a result of complex interactions of biogeochemicaland physical processes. The water quality is a set of parameters thatare mutually interrelated (Khalil et al. 2010) and these processes can becoupled (Jolankai 1997) based on interrelations.
Brisbane, Australia | 20-24 October 2019
• BOD decay
• K1 temperature correction
• Oxygen deficit equation
• Saturation equation of dissolved oxygen
• Reaeration coefficient
• Denitrification(Jolankai, 1997)
The equations can explain the non -linear DO and BOD interaction as water moves at a distance or downstream.
Modeling Equations
Brisbane, Australia | 20-24 October 2019
Overall STELLA Model Setup
Brisbane, Australia | 20-24 October 2019
• run and stop buttons
• f value and temp sliders
• background DO and BOD knobs
• graph and table
STELLA User Interface
Brisbane, Australia | 20-24 October 2019
Results: Sensitivity Analysis• to identify the important parameters
that affect the model results (Chapra, 1997) for DO and BOD
• done by varying each of the parameters by a set of percentage
• STELLA modeling platform has a built-in parameter perturbation technique for sensitivity analysis.
Brisbane, Australia | 20-24 October 2019
The parameters were set to: • 7 mg/L dissolved oxygen • 15 mg/L BOD• 2.5 f• 28°C water temperature
The model was run 5 times for 10 days at different parameter with fixed increment.
DO sensitivity to Temperature (20 to 32°C)
Sensitive where at higher temperatures can reach hypoxia and anoxia.
DO sensitivity to Depth (1 to 12 m)
Sensitive where at shallower depth, the faster the oxygen regeneration.
DO sensitivity to Velocity (0.1 to 1.5 m/s)
Highly sensitive where a slight increase in velocity delays the oxygen regeneration
BOD sensitivity to Temp (20 to 32°C)
A slight increase in water temperature does not affect much the rate of BOD decay.
Results: Sensitivity Analysis
Brisbane, Australia | 20-24 October 2019
Results: Preliminary Scenario Building
Dry Season (from Napindan Station)
• 32 °C, 1.2 f, 28 mg/L BOD, 5.1 mg/L DO
Wet Season (from Napindan Station)
• 23 °C, 2.3 f, 14 mg/L BOD, 6.8 mg/L DO
Anoxic condition is most probable during dry season at high temperature and slowriver velocity. Dissolved oxygen can regenerate faster during wet season.
Brisbane, Australia | 20-24 October 2019
Further Development: Segmentation
The boundary conditions will be based on the distance of each confluence point from Laguna Lake (0 km).
North Bank Tributary Distance (km)Laguna Lake 0Ilugin Creek 3.86729Marikina River 6.69536Pineda Creek 8.39455
Buayang Bato Creek 9.11592San Juan River 16.7557Estero de Valencia 18.77561Estero de Sampaloc 19.24824Esterdo de Uli Uli 19.51631
Estero de San Miguel 21.41272Estero de la Reina 21.89083
Estero de Binondo 22.47864Manila Bay 25.90958
South Bank Tributary Distance (km)Laguna Lake -0.15Daang Paa Creek 5.18223Pateros-Taguig River 6.64688
Guadalupe Nuevo Creek 9.27288
Balisampan Creek 10.02217Estero de Santa Clara 13.01583Estero de Pandacan B 16.61422Estero de Pandacan A 18.63983Estero de Santibanez 20.00717
Estero de Paco 20.21842Estero de Tanque 20.31066Estero de Balete 20.6049Manila Bay 25.10755
Brisbane, Australia | 20-24 October 2019
Further Development• Initial BOD and DO condition:
0 km at Laguna Lake
• After transport of x1 km (t1), simulated BOD and DO will be the new boundary conditions
• General dilution equations apply at 21 confluence points until the water mass reaches Manila Bay
Brisbane, Australia | 20-24 October 2019
Future Works: Calibration and Validation• Calibration is required to “tune”
the model to fit a data set.
• Which data set from the water quality data?• 2016 and 2017 monthly water
quality data will be used for calibration
• For validation, the comparison of simulation results to 2018 actual water quality data.
Sample Output
Brisbane, Australia | 20-24 October 2019
Challenges, Opportunities and ConclusionModeling Challenges
• Pasig River is tidally-influenced (Tamura, et al. 2000)
• Consistency and availability of water quality data
• Limited hydrologic data; latest data is dated September 2009
• Technical skills of modeler and model users
Modeling Opportunities
• Can be a science-based tool for managing the Pasig River
• Replicable to other river systems
Conclusion
• It is possible to develop a simple model to help us understand the dynamics of a river system.
Brisbane, Australia | 20-24 October 2019
Major References and AcknowledgementChapra, S. C. (1997). Surface water quality modeling. In Surface water quality modeling.WCB/McGraw-Hill.
Ford, F. A. (1999). Modeling the environment: an introduction to system dynamics models ofenvironmental systems. Island Press.
Gorme, J. B., Maniquiz, M. C., Song, P., & Kim, L. H. (2010). The water quality of the PasigRiver in the City of Manila, Philippines: current status, management and futurerecovery. Environmental Engineering Research, 15(3), 173-179.
Jacinto, G. S., Sotto, L. P. A., Senal, M. I. S., San Diego-McGlone, M. L., Escobar, M. T. L.,Amano, A., & Miller, T. W. (2011). Hypoxia in Manila Bay, Philippines during the northeastmonsoon. Marine pollution bulletin, 63(5), 243-248.
Ji, Z. G. (2008). Hydrodynamics and water quality: modeling rivers, lakes, and estuaries. JohnWiley & Sons.
Jolankai, G. (1997). Basic river water quality models: Computer aided Learning (CAL)programme on water quality modelling (WQMCAL versión 1.1). In Technical documents inhydrology (No. 13). Unesco.
Khalil, B., Ouarda, T. B. M. J., St-Hilaire, A., & Chebana, F. (2010). A statistical approach forthe rationalization of water quality indicators in surface water quality monitoringnetworks. Journal of Hydrology, 386(1), 173-185.
Tamura, H., K. Nadaoka, E.C. Paringit, F.P. Siringan, G..Q. Tabios, C.L. Villanoy, A.C. Blanco, J.Kubota and H.Yagi (2003). Field survey on hydrodynamics and water quality in Manila Bayand Laguna Lake. Proc. Sympo. Environmental Issues Related to Infrastructure Development,JSPS Core Univ. Program on Env. Eng., 81-93.
• University of the Philippines• The Marine Science Institute• Institute of Environmental
Science and Meteorology
• Pasig River Rehabilitation Commission
• Philippine Young Water Professionals
• International RiverFoundation
Brisbane, Australia | 20-24 October 2019