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European Union Water Initiative plus
for Eastern Partnership
© iStockphoto.com/ansonsaw
Support of Water Policy Reforms
towards Integrated Water Resources Management
WORKSHOP ON
ECOLOGICAL CLASSIFICATION
The role of physico-chemical parameters in the
WFD process
Karin Deutsch
Kyiv, 19-20 June 2018
European Union Water Initiative plus
for Eastern Partnership
© iStockphoto.com/ansonsaw
Physico-chemistry and WFD: Quality Element
Water Framework Directive, Annex V – Normative definitions:
Rivers
 Biological elements
 Composition and abundance of aquatic flora
 Composition and abundance of benthic invertebrate fauna
 Composition, abundance and age structure of fish fauna
 Chemical and physico-chemical elements supporting the biological
elements
 General conditions: Nutrients, oxygen balance, salinity, pH,
temperature, acid neutralization capacity
 Specific synthetic and non synthetic pollutants: National relevant
specific pollutants
 Hydromorphological elements supporting the biological elements
European Union Water Initiative plus
for Eastern Partnership
© iStockphoto.com/ansonsaw
Physico-chemical quality elements according to WFD
Water Framework Directive, Annex V (Normative definitions of ecological status classifications):
Definition of High, Good and Moderate Status for Physico-chemical Quality Elements of Rivers
Element High status Good status Moderate status
General
conditions
The value correspond totally or
near totally to undisturbed
conditions
Nutrient concentrations remain
within the range normally
associated with undisturbed
conditions
Levels of salinity, pH, oxygen
balance, acid neutralising
capacity and temperature do not
show signs of anthropogenic
disturbance and remain within the
range normally associated with
undisturbed conditions
Temperature, oxygen balance,
pH, acid neutralising capacity
and salinity do not reach levels
outside the range estalished so
as to ensure the functioning of
the type specific ecosystem
and the achievment of the
values specified for the
biological quality elements
Nutrient concentrations do not
exceed the levels established so
as to ensure the functioning of
the ecosystem and …….
Conditions consistent with the
achievement of the values
specified above for the
biological quality elements.
Specific
synthetic and
non-synthetic
pollutants
Concentration below zero and at
least below LOD of the most
advanced analytical techniques in
general use (standard methods
WFD)
Concentrations do not exceed
standards set in accordance with
Annex 5, 1.2.6
Conditions consistent with the
achievement of the values
specified above for the
biological quality elements.
European Union Water Initiative plus
for Eastern Partnership
© iStockphoto.com/ansonsaw
high ecological status good ecological status
WFD QUALITY ELEMENTS
Hydromorphology Biology Physico-Chemistry
Hydrology
Morphology
River continuity
Makroinvertebrates
Fish
Phytobenthos
Makrophytes
Pollutants
Non-synthetic
Synthetic
General
Parameters
Temp., pH,
O2, N, P etc.
chemical Status
Priority Substances
Ecological Status
ECOLOGICAL STATUS – RELEVANCE OF ELEMENTS FOR
STATUS ASSESSMENT
European Union Water Initiative plus
for Eastern Partnership
© iStockphoto.com/ansonsaw
HOW TO ESTABLISH RANGES AND
LEVELS
5
Type-specific values also for GPCQE
European Union Water Initiative plus
for Eastern Partnership
© iStockphoto.com/ansonsaw
GENERAL PHYSICO-CHEMICAL QUALITY
ELEMENTS (GPCQE)
Which parameters for the different quality elements?
• Nutrients,
• oxygen balance,
• salinity,
• pH,
• temperature,
• acid neutralization capacity
EU member states: large number of supportive physical and
chemical parameters are in use
Reflects the long tradition in use
6
European Union Water Initiative plus
for Eastern Partnership
© iStockphoto.com/ansonsaw
7
Lit: WFD CIS ECOSTAT WG A Report “Comparison of Environmental Quality Objectives, Threshold Values or
Water Quality Targets Set for the Demands of the European Water Framework Directive” (2012)
European Union Water Initiative plus
for Eastern Partnership
© iStockphoto.com/ansonsaw
PHYSICO-CHEMICAL QUALITY ELEMENTS
IN AUSTRIA
 General conditions (GPCP)
EQS/guiding values for 8 parameters – type-specific
 National relevant specific synthetic and non-
synthetic pollutants
EQS for 28 synthetic and 6 non-synthetic pollutants
European Union Water Initiative plus
for Eastern Partnership
© iStockphoto.com/ansonsaw
AUSTRIA: GPCQE – NUTRIENT PARAMETERS
Quality element
WFD
Austria
Parameter Biological
type
Legal
Implementation
General Nutrient
concentrati
ons
Phosphorus Running
water:
SRP
Bioregions +
Trophic Reference
Condition PHB
Quality Objective
Ordinance –
Ecological Status
of Surface
Waters (2010)
Lakes:
TP
13 Laketypes
Nitrogen Running
water:
Nitrate
Bioregions +
Saprobic
Reference
Condition MZB
Specific
pollutants
Nitrite Chloride-
classes
Quality Objective
Ordinance –
Chemical
Condition of
Surface Waters
(2006 idgF)
Ammonium pH +
Temperature
European Union Water Initiative plus
for Eastern Partnership
© iStockphoto.com/ansonsaw
GPCQE – HOW TO ESTABLISH
RANGES/VALUES
• Stepwise approach
• Basis:
• WFD compliant biological methods (EQR) for assess
different pressures
• biological data and
• physico-chemical data
• Statistical analysis
10
European Union Water Initiative plus
for Eastern Partnership
© iStockphoto.com/ansonsaw
EXAMPLE AUSTRIA
APPROACH FOR DERIVING QUALITY STANDARDS
Formulation of quality standards based on
 existing monitoring data for running waters of 240 sites
including reference sites for high and good status
 WFD typology
 assessment of biological quality elements with WFD
compliant methods
 Makroinvertebrates – saprobic index as indicator
for organic pollution
 Phytobenthos – trophic index as indicator for
nutrient pollution
European Union Water Initiative plus
for Eastern Partnership
© iStockphoto.com/ansonsaw
AUSTRIA - DATA PROCESSING/1
Parameter
High/good based on
PO4-P (SRP) Phytobenthos – Trophic index (TI)
NO3-N Macroinvertebrate – Saprobic index for high status
• Selection of most indicative biological element:
• Selection of relevant monitoring
sites :
Definition high and good for each
bioregion
 focus of the definition of boundary
values :selection of monitoring sites within
the range boundary - 0,125 TI/SI
European Union Water Initiative plus
for Eastern Partnership
© iStockphoto.com/ansonsaw
 Statistical data not available for all types
 Clusteranalysis identifies similar bioregions
  Expertjudgment
AUSTRIA - DATA PROCESSING/2
European Union Water Initiative plus
for Eastern Partnership
© iStockphoto.com/ansonsaw
AUSTRIA/ SRP - QUALITY STANDARDS
AND GUIDING VALUES
 Compliance checking - monthly data1 year - 90 percentile
PO4-P (mg/l)
Bioregion Trophic reference condition classes
ot
(oligotroph)
om
(oligo-mesotroph)
mt
(mesotroph)
me1
(meso-eutroph 1)
me2
(meso-eutroph2)
high good high good high good high good high good
Perzentil
90
Perzentil
90
Perzentil
90
Perzentil
90
Perzentil
90
Perzentil
90
Perzentil
90
Perzentil
90
Perzentil
90
Perzentil
90
AV 0,010 0,020 0,020 0,050
AM 0,010 0,020 0,030 0,060
BR 0,010 0,020 0,020 0,050 0,030 0,080
FH 0,070 0,200
FL 0,007 0,015 0,010 0,030 0,020 0,050
GF 0,050 0,090
GG 0,030 0,060 0,040 0,080 0,060 0,100
HV 0,007 0,015 0,010 0,030
IB 0,050 0,100 0,070 0,150
KH 0,007 0,015 0,020 0,040
KV 0,007 0,015 0,010 0,030
SA 0,007 0,015 0,010 0,030
UZA 0,007 0,015 0,010 0,030 0,020 0,050
VAV 0,010 0,030 0,020 0,050
VZA 0,007 0,015 0,010 0,040
European Union Water Initiative plus
for Eastern Partnership
© iStockphoto.com/ansonsaw
NEW! BEST PRACTICE GUIDE ON ESTABLISHING
NUTRIENT CONCENTRATIONS TO SUPPORT GOOD
ECOLOGICAL STATUS (2017)
Includes 3 approaches to setting these threshold concentrations:
• Regression analysis, using a continuous relationship between EQR
and nutrient concentration
• Categorical analysis, using the distribution of nutrient concentration
within biological classes
• Minimisation of mis-match of classifications for biology and nutrients
 choice of method depends upon a number of factors, including the
length of the gradient that available datasets cover and the statistical
strength of the relationship between the explanatory and response
variables.
• Excel and R-based statistical “toolkits” are provided
15
European Union Water Initiative plus
for Eastern Partnership
© iStockphoto.com/ansonsaw
BEST PRACTICE GUIDANCE/TOOLKIT (V6)
EXAMPLE AUSTRIA PHB-TYPE ME2
16
Categorical methods (Log transformed nutrient conc.)
Ave adj
class
quartiles
Ave adj
class
median
75th
quartile
class
minimise
mis-match
Good/Mod 99 87,73 122,90 130,00
High/Good 53,52 59,90 48,63 50,00
Best Practice Guide on establishing nutrient concentrations to support good ecological status
Geoff Phillips, Martyn Kelly, Heliana Teixeira, Fuensanta Salas, Gary Free, Wera Leujak, Anne Lyche Solheim, Gábor
Várbíró; Final draft, December 2017
European Union Water Initiative plus
for Eastern Partnership
© iStockphoto.com/ansonsaw
ASSESSMENT OF ECOLOGICAL STATUS/1
General chemical and physico-chemical elements
 Assessment of ecological status requires biological and
chemical data
 Mismatch Biology and general chemical and physico-chemical
elements
 High status: Worst case
 Good status: Assessment follows the biological results
(intercalibration)
 Consistent mismatch in one type for good/moderate –
checking procedure (CIS-Guidance 13)
European Union Water Initiative plus
for Eastern Partnership
© iStockphoto.com/ansonsaw
CHECKING PROCEDURE 1
Is the level or range for GPCQE more stringent than required?
CIS Guidance No. 13
European Union Water Initiative plus
for Eastern Partnership
© iStockphoto.com/ansonsaw
CHECKING PROCEDURE 2
19
Is the level or range for GPCQE insufficiently stringent than required?
European Union Water Initiative plus
for Eastern Partnership
© iStockphoto.com/ansonsaw
ASSESSMENT OF ECOLOGICAL STATUS/3
… nevertheless it is important
• uncertainty can be reduce by using adequate data sets
and categorising water bodies into similar types,
• but the complexity of the ecological interactions involved
will always result in a variation in the relative biological
status
• challenges by multiple stressors
20
European Union Water Initiative plus
for Eastern Partnership
© iStockphoto.com/ansonsaw
AUSTRIA – COMPARISON OF BIOLOGICAL
AND GPCQE ASSESSMENT
21
Compliancematrix statusclassification
GPCQE total (worst case BSB5, DOC, O2, PO4-P, NO3-N) / Biology
total(worst case MZB + PHB)
equal different
European Union Water Initiative plus
for Eastern Partnership
© iStockphoto.com/ansonsaw
PHYSICO-CHEMICAL ASSESSMENT RELEVANT
FOR …
Typology
Pressure &impact
analysis
Development of
status classification
Water body
delineation
Programme of
measures
Monitoring
Gap-Analysis
Design of appropriate
restoration measure
Risk analysis
European Union Water Initiative plus
for Eastern Partnership
© iStockphoto.com/ansonsaw
PHYSICO-CHEMICAL STANDARDS AND
ASSESSMENT ARE RELEVANT FOR …
• Managing the risk of adverse ecological impacts: Where rivers
are already adversely affected, e.g. phosphorus standards can
indicate the likely degree to which phosphorus concentrations
would need to be reduced (e.g. by reducing concentrations in
discharges) to improve ecological quality.
• Permitting new discharges - standards can indicate whether or
not the river is likely to be able to accommodate the additional
inputs without significant risk of adverse ecological effects –
combined approach!
• Evaluation of measures
• Risk analysis and planning of operational monitoring
23
European Union Water Initiative plus
for Eastern Partnership
© iStockphoto.com/ansonsaw
 CIS Guidance Document No 13 (2005):
Overall Approach to the Classification of Ecological Status and
Ecological Potential
 Best Practice Guide on establishing nutrient concentrations to
support good ecological status (2017)
Geoff Phillips, Martyn Kelly, Heliana Teixeira, Fuensanta Salas,
Gary Free, Wera Leujak, Anne Lyche Solheim, Gábor Várbíró;
Final draft, December 2017
LITERATURE
24
European Union Water Initiative plus
for Eastern Partnership
© iStockphoto.com/ansonsaw
Thank you for attention !
Karin Deutsch
karin.deutsch@bmnt.gv.at

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The role of physico-chemical parameters in the WFD process

  • 1. European Union Water Initiative plus for Eastern Partnership © iStockphoto.com/ansonsaw Support of Water Policy Reforms towards Integrated Water Resources Management WORKSHOP ON ECOLOGICAL CLASSIFICATION The role of physico-chemical parameters in the WFD process Karin Deutsch Kyiv, 19-20 June 2018
  • 2. European Union Water Initiative plus for Eastern Partnership © iStockphoto.com/ansonsaw Physico-chemistry and WFD: Quality Element Water Framework Directive, Annex V – Normative definitions: Rivers  Biological elements  Composition and abundance of aquatic flora  Composition and abundance of benthic invertebrate fauna  Composition, abundance and age structure of fish fauna  Chemical and physico-chemical elements supporting the biological elements  General conditions: Nutrients, oxygen balance, salinity, pH, temperature, acid neutralization capacity  Specific synthetic and non synthetic pollutants: National relevant specific pollutants  Hydromorphological elements supporting the biological elements
  • 3. European Union Water Initiative plus for Eastern Partnership © iStockphoto.com/ansonsaw Physico-chemical quality elements according to WFD Water Framework Directive, Annex V (Normative definitions of ecological status classifications): Definition of High, Good and Moderate Status for Physico-chemical Quality Elements of Rivers Element High status Good status Moderate status General conditions The value correspond totally or near totally to undisturbed conditions Nutrient concentrations remain within the range normally associated with undisturbed conditions Levels of salinity, pH, oxygen balance, acid neutralising capacity and temperature do not show signs of anthropogenic disturbance and remain within the range normally associated with undisturbed conditions Temperature, oxygen balance, pH, acid neutralising capacity and salinity do not reach levels outside the range estalished so as to ensure the functioning of the type specific ecosystem and the achievment of the values specified for the biological quality elements Nutrient concentrations do not exceed the levels established so as to ensure the functioning of the ecosystem and ……. Conditions consistent with the achievement of the values specified above for the biological quality elements. Specific synthetic and non-synthetic pollutants Concentration below zero and at least below LOD of the most advanced analytical techniques in general use (standard methods WFD) Concentrations do not exceed standards set in accordance with Annex 5, 1.2.6 Conditions consistent with the achievement of the values specified above for the biological quality elements.
  • 4. European Union Water Initiative plus for Eastern Partnership © iStockphoto.com/ansonsaw high ecological status good ecological status WFD QUALITY ELEMENTS Hydromorphology Biology Physico-Chemistry Hydrology Morphology River continuity Makroinvertebrates Fish Phytobenthos Makrophytes Pollutants Non-synthetic Synthetic General Parameters Temp., pH, O2, N, P etc. chemical Status Priority Substances Ecological Status ECOLOGICAL STATUS – RELEVANCE OF ELEMENTS FOR STATUS ASSESSMENT
  • 5. European Union Water Initiative plus for Eastern Partnership © iStockphoto.com/ansonsaw HOW TO ESTABLISH RANGES AND LEVELS 5 Type-specific values also for GPCQE
  • 6. European Union Water Initiative plus for Eastern Partnership © iStockphoto.com/ansonsaw GENERAL PHYSICO-CHEMICAL QUALITY ELEMENTS (GPCQE) Which parameters for the different quality elements? • Nutrients, • oxygen balance, • salinity, • pH, • temperature, • acid neutralization capacity EU member states: large number of supportive physical and chemical parameters are in use Reflects the long tradition in use 6
  • 7. European Union Water Initiative plus for Eastern Partnership © iStockphoto.com/ansonsaw 7 Lit: WFD CIS ECOSTAT WG A Report “Comparison of Environmental Quality Objectives, Threshold Values or Water Quality Targets Set for the Demands of the European Water Framework Directive” (2012)
  • 8. European Union Water Initiative plus for Eastern Partnership © iStockphoto.com/ansonsaw PHYSICO-CHEMICAL QUALITY ELEMENTS IN AUSTRIA  General conditions (GPCP) EQS/guiding values for 8 parameters – type-specific  National relevant specific synthetic and non- synthetic pollutants EQS for 28 synthetic and 6 non-synthetic pollutants
  • 9. European Union Water Initiative plus for Eastern Partnership © iStockphoto.com/ansonsaw AUSTRIA: GPCQE – NUTRIENT PARAMETERS Quality element WFD Austria Parameter Biological type Legal Implementation General Nutrient concentrati ons Phosphorus Running water: SRP Bioregions + Trophic Reference Condition PHB Quality Objective Ordinance – Ecological Status of Surface Waters (2010) Lakes: TP 13 Laketypes Nitrogen Running water: Nitrate Bioregions + Saprobic Reference Condition MZB Specific pollutants Nitrite Chloride- classes Quality Objective Ordinance – Chemical Condition of Surface Waters (2006 idgF) Ammonium pH + Temperature
  • 10. European Union Water Initiative plus for Eastern Partnership © iStockphoto.com/ansonsaw GPCQE – HOW TO ESTABLISH RANGES/VALUES • Stepwise approach • Basis: • WFD compliant biological methods (EQR) for assess different pressures • biological data and • physico-chemical data • Statistical analysis 10
  • 11. European Union Water Initiative plus for Eastern Partnership © iStockphoto.com/ansonsaw EXAMPLE AUSTRIA APPROACH FOR DERIVING QUALITY STANDARDS Formulation of quality standards based on  existing monitoring data for running waters of 240 sites including reference sites for high and good status  WFD typology  assessment of biological quality elements with WFD compliant methods  Makroinvertebrates – saprobic index as indicator for organic pollution  Phytobenthos – trophic index as indicator for nutrient pollution
  • 12. European Union Water Initiative plus for Eastern Partnership © iStockphoto.com/ansonsaw AUSTRIA - DATA PROCESSING/1 Parameter High/good based on PO4-P (SRP) Phytobenthos – Trophic index (TI) NO3-N Macroinvertebrate – Saprobic index for high status • Selection of most indicative biological element: • Selection of relevant monitoring sites : Definition high and good for each bioregion  focus of the definition of boundary values :selection of monitoring sites within the range boundary - 0,125 TI/SI
  • 13. European Union Water Initiative plus for Eastern Partnership © iStockphoto.com/ansonsaw  Statistical data not available for all types  Clusteranalysis identifies similar bioregions   Expertjudgment AUSTRIA - DATA PROCESSING/2
  • 14. European Union Water Initiative plus for Eastern Partnership © iStockphoto.com/ansonsaw AUSTRIA/ SRP - QUALITY STANDARDS AND GUIDING VALUES  Compliance checking - monthly data1 year - 90 percentile PO4-P (mg/l) Bioregion Trophic reference condition classes ot (oligotroph) om (oligo-mesotroph) mt (mesotroph) me1 (meso-eutroph 1) me2 (meso-eutroph2) high good high good high good high good high good Perzentil 90 Perzentil 90 Perzentil 90 Perzentil 90 Perzentil 90 Perzentil 90 Perzentil 90 Perzentil 90 Perzentil 90 Perzentil 90 AV 0,010 0,020 0,020 0,050 AM 0,010 0,020 0,030 0,060 BR 0,010 0,020 0,020 0,050 0,030 0,080 FH 0,070 0,200 FL 0,007 0,015 0,010 0,030 0,020 0,050 GF 0,050 0,090 GG 0,030 0,060 0,040 0,080 0,060 0,100 HV 0,007 0,015 0,010 0,030 IB 0,050 0,100 0,070 0,150 KH 0,007 0,015 0,020 0,040 KV 0,007 0,015 0,010 0,030 SA 0,007 0,015 0,010 0,030 UZA 0,007 0,015 0,010 0,030 0,020 0,050 VAV 0,010 0,030 0,020 0,050 VZA 0,007 0,015 0,010 0,040
  • 15. European Union Water Initiative plus for Eastern Partnership © iStockphoto.com/ansonsaw NEW! BEST PRACTICE GUIDE ON ESTABLISHING NUTRIENT CONCENTRATIONS TO SUPPORT GOOD ECOLOGICAL STATUS (2017) Includes 3 approaches to setting these threshold concentrations: • Regression analysis, using a continuous relationship between EQR and nutrient concentration • Categorical analysis, using the distribution of nutrient concentration within biological classes • Minimisation of mis-match of classifications for biology and nutrients  choice of method depends upon a number of factors, including the length of the gradient that available datasets cover and the statistical strength of the relationship between the explanatory and response variables. • Excel and R-based statistical “toolkits” are provided 15
  • 16. European Union Water Initiative plus for Eastern Partnership © iStockphoto.com/ansonsaw BEST PRACTICE GUIDANCE/TOOLKIT (V6) EXAMPLE AUSTRIA PHB-TYPE ME2 16 Categorical methods (Log transformed nutrient conc.) Ave adj class quartiles Ave adj class median 75th quartile class minimise mis-match Good/Mod 99 87,73 122,90 130,00 High/Good 53,52 59,90 48,63 50,00 Best Practice Guide on establishing nutrient concentrations to support good ecological status Geoff Phillips, Martyn Kelly, Heliana Teixeira, Fuensanta Salas, Gary Free, Wera Leujak, Anne Lyche Solheim, Gábor Várbíró; Final draft, December 2017
  • 17. European Union Water Initiative plus for Eastern Partnership © iStockphoto.com/ansonsaw ASSESSMENT OF ECOLOGICAL STATUS/1 General chemical and physico-chemical elements  Assessment of ecological status requires biological and chemical data  Mismatch Biology and general chemical and physico-chemical elements  High status: Worst case  Good status: Assessment follows the biological results (intercalibration)  Consistent mismatch in one type for good/moderate – checking procedure (CIS-Guidance 13)
  • 18. European Union Water Initiative plus for Eastern Partnership © iStockphoto.com/ansonsaw CHECKING PROCEDURE 1 Is the level or range for GPCQE more stringent than required? CIS Guidance No. 13
  • 19. European Union Water Initiative plus for Eastern Partnership © iStockphoto.com/ansonsaw CHECKING PROCEDURE 2 19 Is the level or range for GPCQE insufficiently stringent than required?
  • 20. European Union Water Initiative plus for Eastern Partnership © iStockphoto.com/ansonsaw ASSESSMENT OF ECOLOGICAL STATUS/3 … nevertheless it is important • uncertainty can be reduce by using adequate data sets and categorising water bodies into similar types, • but the complexity of the ecological interactions involved will always result in a variation in the relative biological status • challenges by multiple stressors 20
  • 21. European Union Water Initiative plus for Eastern Partnership © iStockphoto.com/ansonsaw AUSTRIA – COMPARISON OF BIOLOGICAL AND GPCQE ASSESSMENT 21 Compliancematrix statusclassification GPCQE total (worst case BSB5, DOC, O2, PO4-P, NO3-N) / Biology total(worst case MZB + PHB) equal different
  • 22. European Union Water Initiative plus for Eastern Partnership © iStockphoto.com/ansonsaw PHYSICO-CHEMICAL ASSESSMENT RELEVANT FOR … Typology Pressure &impact analysis Development of status classification Water body delineation Programme of measures Monitoring Gap-Analysis Design of appropriate restoration measure Risk analysis
  • 23. European Union Water Initiative plus for Eastern Partnership © iStockphoto.com/ansonsaw PHYSICO-CHEMICAL STANDARDS AND ASSESSMENT ARE RELEVANT FOR … • Managing the risk of adverse ecological impacts: Where rivers are already adversely affected, e.g. phosphorus standards can indicate the likely degree to which phosphorus concentrations would need to be reduced (e.g. by reducing concentrations in discharges) to improve ecological quality. • Permitting new discharges - standards can indicate whether or not the river is likely to be able to accommodate the additional inputs without significant risk of adverse ecological effects – combined approach! • Evaluation of measures • Risk analysis and planning of operational monitoring 23
  • 24. European Union Water Initiative plus for Eastern Partnership © iStockphoto.com/ansonsaw  CIS Guidance Document No 13 (2005): Overall Approach to the Classification of Ecological Status and Ecological Potential  Best Practice Guide on establishing nutrient concentrations to support good ecological status (2017) Geoff Phillips, Martyn Kelly, Heliana Teixeira, Fuensanta Salas, Gary Free, Wera Leujak, Anne Lyche Solheim, Gábor Várbíró; Final draft, December 2017 LITERATURE 24
  • 25. European Union Water Initiative plus for Eastern Partnership © iStockphoto.com/ansonsaw Thank you for attention ! Karin Deutsch karin.deutsch@bmnt.gv.at