Pollution control cost valuation for Scheldt watershed contamination - - PowerPoint PPT Presentation

pollution control cost valuation for scheldt watershed
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Pollution control cost valuation for Scheldt watershed contamination - - PowerPoint PPT Presentation

Pollution control cost valuation for Scheldt watershed contamination Audrey Polard ULB-CEESE-Brussels 8th Word Wide Workshop for Young Environmental Scientists, 2 5 June 2009 Plan DPSIR approach Estimation of the cost of each


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Pollution control cost valuation for Scheldt watershed contamination

Audrey Polard ULB-CEESE-Brussels

8th Word Wide Workshop for Young Environmental Scientists, 2‐5 June 2009

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Plan

‐ DPSIR approach ‐ Estimation of the cost of each control pollution measure ‐ Estimation of the effectiveness of each control pollution measure ‐ Cost‐effectiveness ratio ‐ Conclusion

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Water Framework Directive (WFD) 2000/60/EC:

Context

Timothy project

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Study Area

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DPSIR

D : Driving forces P : Pressures S : State I : Impact R : Responses

D : Agriculture and Households

Diffuse sources (run‐off) Point sources (WWTP)

P : Nutrients : N and P S : High concentration in nutrients I : Eutrophication phenomena in Scheldt basin Emphasis on eutrophication of Belgian coastal waters (Southern North Sea) Nitrogen contamination of groundwater R : Nutrient reduction measures (scenarios)

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Smeets and Weterings, 1999

DPSIR

D : Driving forces P : Pressures S : State I : Impact R : Responses

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Eutrophication phenomena

Spring Phaeocystis foam : North Sea Belgian coastal zone Eutrophic river

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Nutrient reduction measures

Choice:

‐ Economic guidelines (Kranz et al., 2005; MVW, 2005; Interwies et al., 2004; Jacobsen, 2007; European Communities, 2003) ‐ Ease of “translation” into RIVERSTRAHLER model ‐ Political relevance ‐ Availability of data (cost and efficiency)

Households scenarios:

Upgrading of existing WWTP from secondary to tertiary treatment (N and P treatment) 1. WWTP > 500 000 IE 2. WWTP > 100 000 IE 3. WWTP > 20 000 IE 4. WWTP > 0 IE

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Households scenarios

Nutrient reduction measures

WWTP

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Nutrient reduction measures

Agricultural scenarios:

Focus on nitrogen reduction 1. Nitrogen fertilization reduction and catch crop introduction (AGRI 1)

  • 2. Conversion of fodder corn crop surfaces into meadow surfaces (AGRI

2)

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Nutrient reduction measures Effectiveness valuation:

Year of reference : 2000 1 . RIVERSTRAHLER parameter modifications STICS model : AGRI 1 Literature review : AGRI 2 and WWTP scenarios

  • 2. Running the RIVERSTRAHLER

model => Impact on N and P concentrations along the Scheldt basin

  • 3. RIVERSTRAHLER

results into the MIRO model => Impact on the occurrence of algal blooms in the Belgian coastal zone

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Nutrient reduction measures Effectiveness valuation:

RIVERSTRAHLER : river model

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Nutrient reduction measures Effectiveness valuation:

The STICS model

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Nutrient reduction measures Effectiveness valuation:

N reduction of the different measures in the Scheldt basin

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Households scenarios :

Two types of costs: ‐ Investment costs ‐ Additional costs of operating a tertiary treatment ⇒ Total annual cost Investment costs:

  • Highly variable but no cost data for each WWTP

Cost range applied according to : ‐ equipment already present in WWTP ‐ the age of the WWTP Experts information

  • Annualized with

AEC = [NPV * a] / [1 – (1 + a)‐D] AEC : Annual Equivalent Cost NPV : Net Investment Value a : discount rate : 5 % D : lifetime of the capital equipment : 20 year

Nutrient reduction measures Cost valuation

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Nutrient reduction measures Cost valuation

Households scenarios :

Additional costs of operating a tertiary treatment : N: ‐ Biological removal : 5 % P: ‐ Physico‐chemical removal: 2.5€/IE ‐ Biological removal : 0.5 €/IE

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Households scenarios :

Costs : existing Waste Water Treatment Plants not increase of collecting rate of sewage network Impossible to separate N and P investment costs – same infrastructures used in activated sludge treatment

Nutrient reduction measures Cost valuation

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Agricultural scenarios:

1. Nitrogen fertilization reduction and catch crop introduction

(AGRI 1)

Nutrient reduction measures Cost valuation

STICS Amount of N fertilizer N fertilizer cost (CF) Yield (Y) * Market price of crop (PM) I : no nitrogen fertilization reduction s : nitrogen fertilization reduction Unit Cost (€/ha) = ( (Yi * PM) – (Ys * PM) ) – (CFi – CFs) ‐Yield loss ‐ Fertilizer savings

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Agricultural scenarios:

1. Nitrogen fertilization reduction and catch crop introduction

(AGRI 1)

Unit cost for 3 crops (Lacroix et al., 2004) => 6 crops : own STICS simulations Total cost = Unit cost (€/ha) * Scheldt Basin crops surfaces (ha)

Nutrient reduction measures Cost valuation

Scheldt basin crops distribution

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Agricultural scenarios:

1. Nitrogen fertilization reduction and catch crop introduction

(AGRI 1)

Cost difference between i and s Different cost items such as: ‐ Farming cost of sowing, growing, cropping, burying ‐ Seeds and machinery i: soil not covered during winter s: catch crop introduction

Nutrient reduction measures Cost valuation

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Agricultural scenarios:

2. Conversion of fodder corn crop surfaces into meadow surfaces

(AGRI 2)

Gross Margin (GM) comparison

GM = p – Cv P ≠ ct Cf = ct => GM bs – GM AGRI 2 ≤

Nutrient reduction measures Cost valuation

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Nutrient reduction measures Cost valuation Agricultural scenarios:

2. Conversion of fodder corn crop surfaces into meadow surfaces

(AGRI 2)

No annual cost Although one‐off costs such as fencing grazed meadows

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Nutrient reduction measures Cost valuation

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Nutrient reduction measures Cost‐effectiveness ratio

Cost‐effectiveness ratio for N

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Nutrient reduction measures Cost‐effectiveness ratio Similar cost‐ratio in Atkins and Burdon, 2006, Nolte, 2007 for AGRI 1 measure Agricultural measures more cost‐effective

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Conclusion:

Nitrogen is still too high Slight decrease of coastal eutrophication phenomena => Go further in the effectiveness valuation of agricultural measures : AGRI 1 : New STICS simulations AGRI 2 : Decrease of cattle density and nitrate leaching reduction + decrease of exogenous N input N surplus : => Need to simulate other control pollution measures as such organic farming

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=> Compare eutrophication damage costs with pollution control costs

Conclusion:

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Thank you for your attention

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Nutrient reduction measures: Effectiveness valuation:

Source : Gaury, 1992

Nitrate leaching with different crops:

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Nutrient reduction measures: Effectiveness valuation:

Mean nitrate concentration below the rooting zone for several crop rotations with or without catch crops (calculated for a deep loamy soil)

Beaudoin et al., 2005

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Agricultural scenarios:

1. Nitrogen fertilization reduction and catch crop introduction

(AGRI 1)

Nutrient reduction measures Cost valuation

‐Yield loss

Different curve for each crop

Oe : Δ yield gain < Δ N fertilizer cost Op : max yield