DSD-INT 2014 - Symposium 'Water Quality and Ecological modelling' - Optimisation of the Nutrient Reduction Strategy in the North Sea, Ronald van Dokkum, WVL and Tineke Troost, Deltares
The document discusses optimizing nutrient reduction strategies for the North Sea. It describes an integrated modeling approach that labels nutrients by source and tracks their fate and transport throughout the system. A composition matrix is developed from the labeling results. An optimization technique, like linear programming, is then applied to determine the optimal set of river load reductions needed to meet nutrient concentration targets throughout the North Sea. The approach finds required reductions in a target-oriented way rather than through traditional scenario-based modeling of changes to individual sources.
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Mark Killar, Western Pennsylvania Conservancy, “Sewickley Creek Cost/Benefit ...Michael Hewitt, GISP
Throughout Pennsylvania, many non-profit organizations have developed restoration plans for AMD impaired watersheds. To secure federal AML funding through Pennsylvania’s Abandoned Mine Reclamation Program and with other federal programs, those plans must include a cost/benefits analysis to assure that funds from the program are spent wisely. In an effort to assist in the development of a cost/benefit analysis for AMD projects being proposed for a qualified hydrologic unit watershed, Western Pennsylvania Conservancy worked with Hedin Environmental, through a technical assistance grant provided by Trout Unlimited’s Eastern Abandoned Mines Program, to develop a treatment cost calculator, which could compare costs on a variety of AMD treatment types. This presentation will demonstrate how it was used to develop a cost/benefit analysis for priority AMD discharges within the Sewickley Creek watershed in Westmoreland County.
La gestió i l'eficiència dels aiguamolls artificials del Delta de l'EbreICGCat
Presentació realitzada per Carles Ibáñez (IRTA) a la jornada "La lluita contra el canvi climàtic al Delta de l'Ebre: mesures d'adaptació i mitigació" (25/05/2018)
Big CInema Data: Analysing global cinema showtimesDeb Verhoeven
Looking at cinema exhibition and distribution at an international scale requires data beyond broad aggregates, it requires data that is specific to individual films and cinema venues in order to appreciate the intricate temporal and geographic aspects of flow and patterns. The Kinomatics Project has tracked the global flow of individual film screenings (down to date and time) for over 54,000 films for 30,000 venues throughout 48 countries internationally.
This presentation will highlight the importance of global scale analysis and data through three case studies. The first will track the spatial and temporal relationships of The Hobbit: an unexpected journey, highlighting the complexities of international cinema enterprises and the subtleties of contemporary releasing strategies. The second explores the relationship between remittance flows and the movement of film around the globe with a focus on Bollywood films. The thrid test dyadic relationships between countries. This presentation will introduce some methods for analysing and visualising data used in the three case studies.
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DSD-INT 2014 - Symposium 'Water Quality and Ecological modelling' - Optimisation of the Nutrient Reduction Strategy in the North Sea, Ronald van Dokkum, WVL and Tineke Troost, Deltares
1. DSD-INT 2014: 3 November 2014
Optimisation of the nutrient reduction strategy for the North Sea
IenM/RWS WVL : Ronald van Dokkum Deltares: Tineke Troost , Hans Los, Jan v. Beek, Christophe Thiange, Marc Weeber, Joost v.d Roovaart, Sibren Loos
5. Nitrogen targets (winterconc DIN mg/l)
In case of overlapping targets the most strict of the two is considered
5
Offshore targets (OSPAR)
Coastal targets (WFD)
6. 6
Project objective
• Starting point: Several areas with present nutrient concentrations
• Desired end point: target nutrient concentrations
• Potential Measures: River load reductions
Objective: To find the optimal set of river load reductions to meet all targets
8. 8
Modeling approach
due to:
-Transboundary transport of nutrients
-Biogeochemical processes
-Limiting factors may vary (e.g. nitrate, phosphate, light)
Relative reduction (%) in chlorophyll concentration following 50% river loads reduction
Non-linear response of the ecosystem to reduced river loads
10. 10
biogeochemical processes: Delft3D-WAQ
•N, P, Si, plankton, detritus , O2
•4 functional groups: diatoms, flagellates, dinoflagelates, Phaeocystis
•3 phenotypes adapted to environmental conditions (light, N, P limitation)
•Nutrient uptake, respiration, mortality + ‘grazing’
•Decay in water & sediments, nitrification, denitrification: parameterised
•O2 production, consumption, reareation
•Light extinction (CDOM, SPM, algae, detritus)
(see e.g. Los & Wijsman, JMS, 2007)
AlgaePNCNNH4-NNO3-NPPO4-PDetritus PNCsettlingsettlingrespirationphotosynthesisNutrientmineralisationmineralisationmetabolismmortalityDOproductionconsumptionreaerationDetritus in SedimentC N P SiSiSiN2 denitrificationmineralisation& nitrificationautolysisSiconsumptionnitrificationGrazersgrazinggrazingoxygen consumptionbiodepositionAIPadsorptionMicrophytobenthosC N P SiAIP in sedimentsettlingmortalityphotosynthesis
11. How to determine required nutrient reductions
Traditional approach (source oriented)
•Change some forcings (river loads)
•Rerun several times (scenarios)
•Look at difference between scenarios and base case
11
?
Current situation
Desired end point
12. How to determine required nutrient reductions
12
Alternative approach (target oriented)
1. Labelling: follow fate and transport of all nutrients
2. Set up composition matrix
3. Apply optimization technique
Current situation
Desired end point
13. Step 1. Labelling nutrients
13
• Labeling the nutrients when they enter the system and following
them throughout time and space
FR
BE
NL2
NL1
GM
UK1
UK2
Atlantic
Channel
Atm
Dep
NH4
NH4r
flux
shadow flux
NH4r / NH4 x flux
16. Step 3: Optimisation (2 x 2 example)
Ems
Rhine
Reduction
goal
GC1
0.10 * f1
0.12 * f2
≥
0.08
NLC2
0.00 * f1
0.33 * f2
≥
0.13
1.00 * f1
0.00 * f2
≤
0.85
0.00 * f1
1.00 * f2
≤
0.85
16
Goal: Find set of reduction factors f1 and f2 which will achieve the targets and be as cheap as possible
Cost function
10 * f1
100 * f2
Optimal reduction f1 = 0.33, f2 = 0.4
18. Nitrogen targets (winterconc DIN mg/l)
In case of overlapping targets the most strict of the two is considered
18
Offshore targets (OSPAR)
Coastal targets (WFD)
19. Target concentrations
0
0.5
1
1.5
2
2.5
3
Current
Target
Winterconcentrations of DIN (mg/l)
• only the most strict targets per area are shown;
• the WFD-target for the Ems-Dollard estuary is 1.33 mg/l
19
30. Conclusions
Optimisation method is a quick and powerful tool to:
•optimise nutrient reductions
•check consistency and attainability of targets
•facilitate discussions between stakeholders
30