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Living Water Exchange: Promoting Nutrient Reduction Best Practices in the CEE DREPR Regional Conference: Lessoned Learned and Next Steps in Agriculture Pollution Reduction in Danube Black Sea basin
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Living Water Exchange: Promoting NutrientReduction Best Practices in the CEE

DREPR Regional Conference:Lessoned Learned and Next Steps in AgriculturePollution Reduction in Danube Black Sea basin

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• Perspective/overview• Challenges

• What is a best practice?

• Demonstration outcomes• Discussion

– How to replicate & scale-up?

About Today

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Lessons

• Manure handling/householdwaste

• NM plans – incremental• Agricultural high school

• Permitting process

• Constructed wetlands

• ICPDR coordination/jointmeasures

• Data collection

• Constructed wetlands• SWG – rural networks

• Industrial treatment

• WW & sanitation

• Farmer & community

Conference Practices/Lessons Thus far

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• 500 million small farms globally of 2 hectares or less

Perspectives

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• 15 years of GEF, WB, other investments

• Agriculture issues (which the experience of the Danube hasshown) contribute majority share of N

• Improved best management practices (BMPs) proven to reduceN & P (by limiting application of fertilizer & better handling of

manure, etc.)

• Challenge: There is a need to collect, analyze and 

replicate BMPs in a systematic way.

Why Is This Important:

The CEE/EECCA Body of Work

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Geographic Scope

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• Reduce nutrientloading

• Link to GEF/WBprojects in theregion

• Ensure sustainableBMPS

• Build a model forfunding andreplication in theCEE

GEF System

• StrongerInternational legalframeworks on NR

• Codes of conduct

• Linking to otherglobal NR projects &BMPs

Inventory BMPs Demonstrations ImplementEffectively

AchieveImpact

GEF & World Bank NR 

Projects in the CEE

Global Perspective

• Key markets/regions

• Lessons & successes

• Leverage resources& data

Practices

• BAP

• Manure management

• Knowledge building

• Wetlands restorationPartnerships

• USG

• EU

• Other donors

• Implementingorganizations

Wetlands

Restoration &Innovative NR 

Practices

CapacityBuilding

Partnerships

BAP Projects

System Oversight

• Consistentengagement inproject progress

Measurement

• Consistent Use ofMonitoring andEvaluationFramework

Sustainability

• Ensure results within10 month period

Effective

Communication• Engage interested

partners, currentprojects

20102009

A Framework for Action

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• Several scientific reviews released in 2008-10

• Number of cases doubled every 10 years starting in 1960s

• Up to 1969 there were 60 cases reported

Coastal Hypoxia

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• 1980s had explosive increase in the number of hypoxicsystems.

• Number of cases was 275 by 1989.

Coastal Hypoxia

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• By 1990s most estuarine and marine systems close topopulation centers had reports of hypoxia or anoxia.

• Number of cases is now >500.

? ??

Coastal Hypoxia

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From: Dumont, et al. 2005 GBC

Fertilizer

Manure

AtmosphericDeposition

Sewage

2-fixation

Fertilizer

Manure

N2-fixation

Sewage

Impacts on Watersheds:DIN Export Variation in Dominant Source

(Single largest source)

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Source: http://maps.grida.no/go/graphic/ratio-of-wastewater-treatment 

Global Ratio of Wastewater Treatment

Global Ratio of Wastewater

Treatment

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Sample Sources/Danube-Black Sea

Nitrogen Phosphorus

12%

27%

9%

7%

13%

10%

7%

15%

12%

27%

9%

7%

13%

10%

7%

15%

 

40%

19%

4%

9%

28%

 

40%

19%

4%

9%

28%

WWTP Urban systems

Background

Manure & fertilizer

NHy agricultural areasNOx agricultural areas

NHy other areaNOx other area

WWTPWWTP Urban systemsUrban systems

BackgroundBackground

Manure & fertilizerManure & fertilizer

NHy agricultural areasNHy agricultural areasNOx agricultural areasNOx agricultural areas

NHy other areaNHy other areaNOx other areaNOx other area

WWTP Urban systems

Background

Agricultural land-use

Other sources

WWTP Urban systems

Background

Agricultural land-use

Other sources

WWTPWWTP Urban systemsUrban systems

BackgroundBackground

Agricultural land-useAgricultural land-use

Other sourcesOther sources

758 kt of N/year 68 kt of P/year

The most dominant pathways from diffuse pollution into the surface water:

For N: groundwaterFor P: erosion

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Long-term Discharges of N & P into

the Black Sea

0

100

200

300

400

500

600

  1   9   5   5

  1   9   6   0

  1   9   6   5

  1   9   7   0

  1   9   7   5

  1   9   8   0

  1   9   8   5

  1   9   9   0

  1   9   9   5

   2   0   0   0

   2   0   0   5

   D   I   N    l  o

  a   d   i  n   k   t   /

0

5

10

15

20

25

30

35

40

  1   9   5   5

  1   9   6   0

  1   9   6   5

  1   9   7   0

  1   9   7   5

  1   9   8   0

  1   9   8   5

  1   9   9   0

  1   9   9   5

   2   0   0   0

   2   0   0   5

   T   P    l  o

  a   d   i  n

   k   t   /  y

Nitrogen Phosphorus

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Initial Inventory:

Nutrient Relevant Projects By Region

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Initial Inventory: Scope of Investment

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Core Investment: Investment Fund for

Nutrient Reduction

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Sample Impact: Investment Fund for

Nutrient Reduction

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Challenge: Ad Hoc Results

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• Challenges to nutrient reduction best practiceimplementation:

1. Focus on centralized solutions for WW in particular iscostly

2. Lack of baseline data from diffuse pollution sources

3. Difficult to receive buy-in from farmers

4. Balance between development & pollution reduction

5. Resistance to innovative financing instruments

6. Costs are challenging to understand

Key Messages

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Pollution

Prevention

Process

Management

Facility

Management

On-site

Treatment

Off-site

Remediation

NutrientBalancing NutrientUse Efficiency FieldManagement In-fieldTreatment Edge of FieldManagement

FeedManagement

Nutrient ratereduction

NutrientManagement

Precision Ag

ConservationTillage

ErosionControl

Cover Crops

Soil PRemediation

RiparianBuffers

WetlandTreatment

Industrial Pollution Control Systems Approach

Agricultural Nutrient Pollution Control Systems Approach

Examples of Agricultural Nutrient Pollution Control System Practices

T Simpson, 1-2008

Context: What is a Best Practice

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Best Practices

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Slide 24

0

1000

2000

3000

4000

5000

6000

0 500 1000 1500 2000

reduction in nitrogen loss

(thousand tonnes)

   c

   o

   s

   t

   e

   r 

   u

   n    i   t

    $

    /   t   o

   n

   n

   e

fertilizer reduction

wetland res toration

Comparison of Nitrogen ReductionStrategies

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Size People Capacity Average

Cost

Small < 10,000 < 1 MGD $1.5 M to

$2 M

Medium >10,000,< 100,000

1 to 5 MGD $2 M to$15 M

Large >100,000 5 to 20 MGD $15 M to$100 M

Sample conventional optionsSample decentralized options

8,000 GPD Natural WWT

$3 per gal packaged system

Best Practice Samples:

WW Technology Deployment

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Best Practice Samples

Display of N statusIndex of growing

plants and N

Fertilizer Need for

top-dressing basedon algorithms &

computations

Capacitybuilding throughcommunities ofpractice

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• Organic matterincrease– C:N ratio

• Soil structureimprovement

• Atmospheric

nitrogen fixation

Benefits of No-Till Cropping Systems

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• Decreased soil erosion

• Decreased soil compaction

• Increased aggregate stability

• Increased water infiltration• Decreased surface crusting

• Decreased weed competition

Benefits of Cover Crops

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INI Visualization Cockpit

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Project BMP Name Definition

Baltic A dedicated teamfor outreach to

farmers

The establishment of a local projectimplementation team to work with farms and

to implement agro-environmental investments.Anatolia Centralized

compostingOn-farm composting vs. burying/re-use ofresources

DRP Livestock density Density should correspond to N contentmaximum of 170 kg /ha with trading of excess

manure

DRP Modeling MONERIS nutrient model was adapted to theDanube River Basin and became the de factostandard for estimating loads.

DRP Manure handling Manure should not be spread between October

and March

Poland Nutrient useefficiency

Reduce fertilizer application rate, “decisionfarming”, nutrient management plans

Hungary Wetlands

restoration

Enhancement of the nutrient trapping capacity

Sample BMP Database

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Best Practice Database

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Best Practice Database

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Demonstrations Country Costs

Constructed Wetland forNutrient Reductions in the

Waters of Tirana River

Albania US $38,569

The Decrease of WaterPollution Sources in Prut RiverBasin through the Promotionand Implementation of theBest Agricultural Practices

Moldova US $55,200

Cleaning up the Lake Celije

from nutrients and sediments Serbia US $19,342

Best Practices of FertilizersReduction from AgriculturalLands in Upper Tisza Basin Ukraine US $34,000

On-the-Ground Demonstrations

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Questions for Discussion

• What are key nutrient problems/challenges (agriculture,detergents, wastewater, etc)?

• What are the current legal/regulatory drivers/frameworks fornutrient pollution control/reduction?

• Is there baseline data of current nutrient loads? What are they?

What are the sources?• What are the current nutrient reduction

projects/approaches/practices/ interventions and how much isbeing invested?

• What are the barriers to implementation?• What have been the outcomes/quantitative results?

• What are the gaps?

• What might be a strategy to address these gaps?

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Chuck ChaitovitzGlobal Environment & Technology Foundation

703-379-2713

[email protected]://nutrient-bestpractices.iwlearn.org/

Contact Information


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