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Our Approach to Delivering 
Successful Catchment Management 
Jenny Deakin & Donal Daly 
WFD Integration and Coordination Unit, EPA
Overview of Presentation 
• Our framework – Integrated Catchment 
Management (ICM) 
• Our Vision 
• Characterisation and catchments 
• Setting environmental objectives and goals 
• Identifying & evaluating management strategies 
• Designing our implementation programme 
• Producing the River Basin Management Plan
Our Framework - Integrated 
Catchment Management (ICM) 
 
Why use ICM as our framework? 
 
ICM provides a coherent basis for water resources 
management 
 
ICM includes ALL the relevant and essential 
elements 
 
Successful implementation of ICM  successful 
implementation of the WFD
The Vital Components of Integrated 
Catchment Management (ICM) 
 
Partnerships with local communities & citizen engagement 
 
“Bottom up” as well as “top down” approaches 
 
Linkages, cooperation & networks, while maintaining the good 
elements of silos. 
 
Emphasis on pollutant pathways and CSAs 
 
Seeing catchments in 3-D 
 
Consideration of “ecosystems”, geosystems and human-social 
systems in a holistic process 
 
A broader range of tools in the “toolkit” ranging in a continuum 
from local participation and partnership to enforcement
ICM 
Steps in the 
Integrated 
Catchment 
Management 
(ICM) Process 
(adapted from USEPA 
(2008) 
Step 1: Create & communicate a 
VISION 
Step 2: Build Partnerships 
Step 3: Characterise the 
catchment 
Step 4: Undertake Further 
Characterisation 
Step 5: Finalise goals 
Step 6: Identify & evaluate 
possible management strategies 
Step 7: Design an implementation 
programme 
Step 8: Implement the programme 
Step 9: Measure progress and 
make adjustments 
We do a lot of 
this already, 
but ………….
Step 1: Create & communicate a 
VISION 
ICM 
Steps in the 
Integrated 
Catchment 
Management 
(ICM) Process 
Our WFD I&C Unit Team Vision 
(adapted from USEPA 
(2008) 
“Working together to achieve healthy, 
resilient, productive and valued water 
resources, that support vibrant 
communities”.
ICM Step 2: Build Partnerships 
Steps in the 
Integrated 
Catchment 
Management 
(ICM) Process 
(adapted from USEPA 
(2008) Marie Archbold will 
outline our approach 
on this
Step 3: Characterise the 
catchment 
Step 4: Undertake Further 
Characterisation 
ICM 
Steps in the 
Integrated 
Catchment 
Management 
(ICM) Process 
(adapted from USEPA 
(2008)
Kilmaine Spring, Co. Mayo. 
Lough Guitane, Co Kerry. 
Doovilra strand, Killary Harbour, Co Galway. Source: Shane O’Boyle, EPA. 
Catchment characterisation 
(knowing and understanding our 
catchments) 
is the foundation of water 
resources management
Kilmaine Spring, Co. Mayo. 
In order to manage the water 
resources in a catchment, we must: 
UNDERSTAND (characterise) the 
movement and attenuation (where 
relevant) of water and pollutants along 
the pathways from the pressure to 
the receptor, 
UNDERSTAND the impacts, and 
UNDERSTAND the role of mitigation 
measures 
Lough Guitane, Co Kerry. 
Doovilra strand, Killary Harbour, Co Galway. Source: Shane O’Boyle, EPA.
And…, we can now do it really well (1) 
 Monitoring
And…, we can now do 
characterisation really well (2) 
 Licensing & Enforcement 
information, knowledge and 
expertise, especially locally
And…, we can now do it well (3) 
 Geoscientific and pathways 
information
Soils 
Source: Teagasc
Subsoils 
15 
Source: Teagasc
Subsoil 
Permeability 
Source: Geological Survey of Ireland
Bedrock 
Geology 
17 
Source: Geological Survey of Ireland
Aquifers 
Source: Geological Survey of Ireland
Groundwater 
Vulnerability 
Source: Geological Survey of Ireland
Pressures 
Houses with 
DWWTSs 
+ 
LPIS info 
+ 
UWWTP info 
Nutrient loads 
can be 
estimated 
Source: An Post Geodirectory
Characterisation? 
1. Understanding water bodies 
 Physical, chemical and biological aspects 
 Functioning, ‘Source-pathway-receptor’ 
 Linkages with other water bodies 
 Impacts of human activities 
2. Assigning the level of risk (of not meeting WFD 
objectives), for the purposes of prioritising and 
targeting measures
Approach for 2nd RBMP Cycle 
 Characterisation will be a critical step in the WFD 
implementation process 
 Characterisation will be aligned more closely to 
influencing and targeting monitoring and measures 
 Analysis will be more robust based on the improved 
monitoring, pressures and geoscientific information 
 Will consider both protection and restoration 
objectives
Approach for 2nd RBMP Cycle 
• Groundwater and surface water body characterisation 
will be analogous and combined to encourage common 
understandings and approaches 
• Information from licensing and enforcement activities 
will be used to improve characterisation, via the EPA 
Informatics systems (source apportionment) 
• Greater use will be made of GIS and automation tools. 
Informatics systems are a crucial element of our work
Characterisation Approach 
Three TIERS of 
risk characterisation 
so that the level of assessment is 
commensurate with the risk posed
WFD Characterisation Tiers 
Screening 
At Risk’ 
bodies 
Risk WBs 
susceptible 
potential 
Susceptible areas 
significant 
issues, and 
specific measures 
Not At Risk 
Objectives met 
Increasing scale and level of detail 
Increasing focus on site specific supplementary 
measures, enforcement and engagement with 
landholders. Increasing resources 
What is the WB 
condition? Have 
significant pressures 
been mitigated? 
Where and why are 
the measures not 
working? 
What needs to be 
done to improve the 
situation? 
Status 
Capacity 
Trends 
Investigative monitoring, modelling 
Catchment walks, inspections 
Measures 
Additional measures 
Are the measures working and the objectives being met? 
If yes, continue surveillance and/or operational monitoring (status, 
trends, capacity) for next cycle. 
If not, further characterise and select new measures. Measures can be 
Surveillance and/or 
Operational 
Monitoring 
Increasing 
cost, 
resources, 
confidence 
Tier 1: Screening 
Tier 2: Susceptible 
areas, potential 
pressures 
Tier 3: Significant 
pressures, site specific 
measures
Tier 1 Risk Characterisation 
• Takes account of: 
– Existing status 
– Whether significant pressures have been mitigated or not 
– Trends in concentrations or ecological condition 
– The capacity of the water body to absorb extras pressures 
– The resilience and sensitivity of the associated aquatic 
ecosystems 
– The value of having a combined approach for 
characterisation of both SWBs and GWBs
Not at Risk 
0.035 mg/l P as P 
Good Status 
0.025 mg/l P as P 
0.035 mg/l P as P 
Trend
At risk 
0.035 mg/l P as P 
Good Status 
0.025 mg/l P as P 
0.035 mg/l P as P 
Trend
0.025 mg/l P as P 
Trend Good Status 
Review 
0.035 mg/l P as P 
0.025 mg/l P as P
Not at Risk Review
Not at Risk At Risk
Distance Assigning risk to threshold high 1 to prioritise measures 
Tier 1 screening for SW bodies 
Previous 
Reported 
Status3 
Significant 
pressures 
mitigated? 
Significant trend4 in 
concentration or 
ecological metric 
Distance to threshold low2 
Achieve Good 
status 
WFD Objectives WFD Objectives 
No 
deterioration 
of Status 
Objectives 
combined 5 - 
low capacity 
Achieve Good 
status 
No 
deterioration 
of Status 
Objectives 
combined - 
high capacity 
High Improving Not applicable Not at risk Not at risk Not applicable Not at risk Not at risk 
Yes None/stable/don't know Not applicable Review Review Not applicable Not at risk Not at risk 
Disimproving Not applicable Review Review Not applicable Review Review 
No or Improving Not applicable Not at risk Not at risk Not applicable Not at risk Not at risk 
Don't know None/stable/don't know Not applicable Review Review Not applicable Not at risk Not at risk 
Disimproving Not applicable At risk At risk Not applicable At risk At risk 
Good Improving Not at risk Not at risk Not at risk Not at risk Not at risk Not at risk 
Yes None/stable/don't know Not at risk Review Review Not at risk Not at risk Not at risk 
Disimproving Not at risk Review Review Not at risk Review Review 
No or Improving Not at risk Not at risk Not at risk Not at risk Not at risk Not at risk 
Don't know None/stable/don't know Not at risk Review Review Not at risk Not at risk Not at risk 
Disimproving Review At risk At risk Review At risk At risk 
Moderate Improving Review Not at risk Review Review Not at risk Review 
Yes None/stable/don't know At risk Review At risk At risk Not at risk At risk 
Disimproving At risk Review At risk At risk Review At risk 
No or Improving Review Not at risk Review Review Not at risk Review 
Don't know None/stable/don't know At risk Review At risk At risk Not at risk At risk 
Disimproving At risk At risk At risk At risk At risk At risk 
Poor Improving At risk Not at risk At risk At risk Not at risk At risk 
Yes None/stable/don't know At risk Review At risk At risk Not at risk At risk 
Disimproving At risk Review At risk At risk Review At risk 
No or Improving At risk Not at risk At risk At risk Not at risk At risk 
Don't know None/stable/don't know At risk Review At risk At risk Not at risk At risk 
Disimproving At risk At risk At risk At risk At risk At risk 
Bad Improving At risk Not at risk At risk At risk Not at risk At risk 
Yes None/stable/don't know At risk Review At risk At risk Not at risk At risk 
Disimproving At risk Review At risk At risk Review At risk 
No or Improving At risk Not at risk At risk At risk Not at risk At risk 
Don't know None/stable/don't know At risk Review At risk At risk Not at risk At risk 
Disimproving At risk At risk At risk At risk At risk At risk
Groundwater body risk 
Assigning risk to prioritise measures 
GW bodies Tier 1 screening 
Previous 
Significant 
reported 
pressures 
Status 
mitigated? 
Significant trend in 
concentration or level 
Achieve Good 
status 
Distance Distance to threshold low to threshold high 
WFD Objectives WFD Objectives 
No 
deterioration 
Reverse 
upward trend 
Objectives 
combined - 
low capacity 
Achieve Good 
status 
No 
deterioration 
Reverse 
upward trend 
Objectives 
combined - 
high capacity 
Good Improving Not at risk Not at risk Not at risk Not at risk Not at risk Not at risk Not at risk Not at risk 
Yes None/stable/don't know Not at risk Review Not at risk Review Not at risk Not at risk Not at risk Not at risk 
Disimproving Not at risk Review Review Review Not at risk Review Review Review 
No or Improving Not at risk Not at risk Not at risk Not at risk Not at risk Not at risk Not at risk Not at risk 
Don't know None/stable/don't know Not at risk Review Not at risk Review Not at risk Not at risk Not at risk Not at risk 
Disimproving Review At risk At risk At risk Review At risk At risk At risk 
Poor Improving Review Not at risk Not at risk Review Review Not at risk Not at risk Review 
Yes None/stable/don't know At risk Review Not at risk At risk At risk Not at risk Not at risk At risk 
Disimproving At risk Review Review At risk At risk Review Review At risk 
No or Improving Review Not at risk Not at risk Review Review Not at risk Not at risk Review 
Don't know None/stable/don't know At risk Review Not at risk At risk At risk Not at risk Not at risk At risk 
Disimproving At risk At risk At risk At risk At risk At risk At risk At risk
Tier 2 Risk Characterisation 
Undertaken on “At Risk” WBs and “Review” WBs 
 
To identify what pressure is causing the WBs to be “At 
Risk”. (The “WHAT” question). 
 
To locate the Critical Source Area (CSA), i.e., the areas 
contributing more pollutants than other parts. (The 
“WHERE” question). 
 
Uses the Pathways Project tools, load apportionment 
techniques, other modelling tools, LA input
Receptor 
Poorly productive aquifer 
(70% of country) 
Free-draining soils & subsoils
Receptor 
Characterisation 
Helps decide “what” and “where” 
and “how”. 
PO4 CSA 
Poorly productive aquifer 
(70% of country) 
PO4 CSA
Receptor 
Characterisation 
Helps decide “what” and “where” 
and “how”. 
Poorly productive aquifer 
(70% of country) 
measures 
measures 
Knowing and 
understanding (i.e., 
characterising) the 
pathway is vital
Source: Jenny Deakin Mattock catchment 
Pollution Impact 
Potential (PIP) Maps 
Nitrate to GW 
Nuenna catchment 
Nitrate to GW
Tier 3 Risk Characterisation 
• Further investigates the CSAs from the Tier 2 
assessment. 
• Site specific investigations, such as catchment 
walks, investigative monitoring, licence reviews, 
compliance checks, etc. 
• Use of modelled scenarios using CMSTs, etc. 
• Identifies significant pressures, i.e. those 
causing the impact that need mitigation.
Characterisation Timelines 
Characterisation 
process 
Start Finish 
Tier 1 Now Q2 2015 
Tier 2 mid 2015 Q2 2016 
Tier 3 Q4 2015 Ongoing 
SWMI and Article 5 reports by Q4 2015 
Draft RBMPs by Q4 2016 
Final RBMPs by Q4 2017
Benefits 
• Links existing and new knowledge in a structured, 
holistic way for multiple purposes 
• Provides a means of focussing work already being 
carried out across a number of agencies 
Input and contribution 
from others is essential 
• Integrates assessments for all water body types 
• Uses an automated risk based approach in Tier 1 – 
reduced time, repeatable, defensible 
• Helps prioritise areas/issues for measures and 
monitoring 
• Supports SWMI, Article 5 reports and RMBPs
A word on catchments and scale … 
What is a catchment? 
The catchment is the appropriate 
land-based organising unit for 
water management 
A basic tenet of catchment 
Demo outside! 
 It is a coherent topographically-based 
management is that feature 
what happens in 
one part of the catchment, as an 
interconnected system, affects people 
 It is defined by the natural hydrology and 
hydrogeology 
 
 and It environments ‘connects’ all relevant in other elements, 
parts. 
including pressures, receptors and the 
people living there. 
 Communities can relate to it. 
(Everyone lives in a catchment!)
Water Body (WB) Scale 
 WBs are the water features referred to in the WFD 
 We have to report on WBs to the COM 
 Tier 1 characterisation 
(Risk screening on water bodies into: ‘at risk’, ‘not at risk’ and ‘review’) 
 Range in size from a few km long (rivers) 
to 100s km2 in size (groundwater) 
 However: 
 Numerous (~5000) in total for 2nd cycle 
 Minimal integration of WB types 
 Not suitable for assessing PoMs properly
Sub-catchment Scale 
(the scale for local involvement) 
 Approx. 100 km2 each (~700) 
 Tier 2 & Tier 3 
characterisation (All WBS ‘at risk’ 
aggregated into sub-catchments for 
more detailed assessment.) 
 Catchment walks 
 Modelling (e.g., CCT) 
 Investigative monitoring 
 Involve stakeholders 
 Measure results
N 
Bad status 
Poor status 
Moderate status 
Group and 
public 
groundwater 
supplies 
Sub-catchment (Tullamore River) scale = where (the real) work is 
undertaken 
WWTP 
Groundwater water 
body boundary 
Hydrometric 
Station
Catchment Scale 
(Water Management Units) 
 100s km2 (46 in RoI) 
 “From the mountains to the sea” 
 Integrate WB types 
 Evaluate issues 
 Prioritise measures 
 Organise delivery 
 Reports and plans
ICM - Step 5: 
Set Overall Goals 
 Objectives & targets need to be set to guide 
the process, taking account of: 
 WFD (and all associated Directives) & Drinking Water 
Directive requirements. 
 Standards & thresholds in Irish regulations. 
 Requirements of sensitive ecosystems 
 Risk and status results, incl. load apportionment 
 Lag times for reductions in nutrient removal from 
soils and subsoils. 
47
ICM - Step 6: Identification & Evaluation 
of Possible Management Strategies 
 Evaluate existing measures 
 Review other potential mitigation measures 
 Take account of main pollution sources, 
impacts and pathways, including critical source 
areas (CSAs) 
 Stakeholder input critical 
 Develop and rank the measures needed 
48
ICM - Step 7: Design an 
Implementation Programme (1) 
 EPA will lead/facilitate this. But, LA ++ input essential 
 Includes: 
 Local community awareness and engagement process 
 Outputs of characterisation 
 Analysis of FH2020 implications 
 Climate change adaptation measures 
 Ecological flows & levels (E-flows & E-levels) 
 Resilience & sensitivity of ecosystems 
 Modelling as a means of evaluating management strategies 
 Linkages with physical planning 
 Review and amendment, as necessary, of the monitoring 
programme 
49
ICM - Step 7: Design an 
Implementation Programme (2) 
Includes: 
This one will be 
challenging/difficult 
Measures analysis 
Economic analysis 
 Finalisation of objectives 
 Selection of final management strategies 
Measures – what & where 
Implementation schedule 
 Provision of training, technical assistance and 
follow-up support 
50
ICM - Step 8: Implement the 
Programme 
Template River Basin Management Plan 
(RBMP) by EPA 
Completion of plan by WFD Offices/LAs 
Measures – what & where 
Implementation schedule 
Approval by DEHLG/Minister 
Reporting to the Commission by EPA 
51
ICM – Step 9: Measure Progress & 
Make Adjustments 
Analyse trends and outcomes 
Give feedback to stakeholders 
Make adjustments, as necessary 
Commence the 3rd cycle work! 
52
53 
Four Final Summary Thoughts 
1. Catchments, connecting all 
relevant elements 
2. Hard work 
3. Working together
“It’s people who save 
rivers, not plans ……” 
(quote from: “Saving Eden: A Manifesto”)

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Our approach to delivering sucessful catchment management - Jenny Deakin and Donal Daly

  • 1. Our Approach to Delivering Successful Catchment Management Jenny Deakin & Donal Daly WFD Integration and Coordination Unit, EPA
  • 2. Overview of Presentation • Our framework – Integrated Catchment Management (ICM) • Our Vision • Characterisation and catchments • Setting environmental objectives and goals • Identifying & evaluating management strategies • Designing our implementation programme • Producing the River Basin Management Plan
  • 3. Our Framework - Integrated Catchment Management (ICM)  Why use ICM as our framework?  ICM provides a coherent basis for water resources management  ICM includes ALL the relevant and essential elements  Successful implementation of ICM  successful implementation of the WFD
  • 4. The Vital Components of Integrated Catchment Management (ICM)  Partnerships with local communities & citizen engagement  “Bottom up” as well as “top down” approaches  Linkages, cooperation & networks, while maintaining the good elements of silos.  Emphasis on pollutant pathways and CSAs  Seeing catchments in 3-D  Consideration of “ecosystems”, geosystems and human-social systems in a holistic process  A broader range of tools in the “toolkit” ranging in a continuum from local participation and partnership to enforcement
  • 5. ICM Steps in the Integrated Catchment Management (ICM) Process (adapted from USEPA (2008) Step 1: Create & communicate a VISION Step 2: Build Partnerships Step 3: Characterise the catchment Step 4: Undertake Further Characterisation Step 5: Finalise goals Step 6: Identify & evaluate possible management strategies Step 7: Design an implementation programme Step 8: Implement the programme Step 9: Measure progress and make adjustments We do a lot of this already, but ………….
  • 6. Step 1: Create & communicate a VISION ICM Steps in the Integrated Catchment Management (ICM) Process Our WFD I&C Unit Team Vision (adapted from USEPA (2008) “Working together to achieve healthy, resilient, productive and valued water resources, that support vibrant communities”.
  • 7. ICM Step 2: Build Partnerships Steps in the Integrated Catchment Management (ICM) Process (adapted from USEPA (2008) Marie Archbold will outline our approach on this
  • 8. Step 3: Characterise the catchment Step 4: Undertake Further Characterisation ICM Steps in the Integrated Catchment Management (ICM) Process (adapted from USEPA (2008)
  • 9. Kilmaine Spring, Co. Mayo. Lough Guitane, Co Kerry. Doovilra strand, Killary Harbour, Co Galway. Source: Shane O’Boyle, EPA. Catchment characterisation (knowing and understanding our catchments) is the foundation of water resources management
  • 10. Kilmaine Spring, Co. Mayo. In order to manage the water resources in a catchment, we must: UNDERSTAND (characterise) the movement and attenuation (where relevant) of water and pollutants along the pathways from the pressure to the receptor, UNDERSTAND the impacts, and UNDERSTAND the role of mitigation measures Lough Guitane, Co Kerry. Doovilra strand, Killary Harbour, Co Galway. Source: Shane O’Boyle, EPA.
  • 11. And…, we can now do it really well (1)  Monitoring
  • 12. And…, we can now do characterisation really well (2)  Licensing & Enforcement information, knowledge and expertise, especially locally
  • 13. And…, we can now do it well (3)  Geoscientific and pathways information
  • 16. Subsoil Permeability Source: Geological Survey of Ireland
  • 17. Bedrock Geology 17 Source: Geological Survey of Ireland
  • 18. Aquifers Source: Geological Survey of Ireland
  • 19. Groundwater Vulnerability Source: Geological Survey of Ireland
  • 20. Pressures Houses with DWWTSs + LPIS info + UWWTP info Nutrient loads can be estimated Source: An Post Geodirectory
  • 21. Characterisation? 1. Understanding water bodies  Physical, chemical and biological aspects  Functioning, ‘Source-pathway-receptor’  Linkages with other water bodies  Impacts of human activities 2. Assigning the level of risk (of not meeting WFD objectives), for the purposes of prioritising and targeting measures
  • 22. Approach for 2nd RBMP Cycle  Characterisation will be a critical step in the WFD implementation process  Characterisation will be aligned more closely to influencing and targeting monitoring and measures  Analysis will be more robust based on the improved monitoring, pressures and geoscientific information  Will consider both protection and restoration objectives
  • 23. Approach for 2nd RBMP Cycle • Groundwater and surface water body characterisation will be analogous and combined to encourage common understandings and approaches • Information from licensing and enforcement activities will be used to improve characterisation, via the EPA Informatics systems (source apportionment) • Greater use will be made of GIS and automation tools. Informatics systems are a crucial element of our work
  • 24. Characterisation Approach Three TIERS of risk characterisation so that the level of assessment is commensurate with the risk posed
  • 25. WFD Characterisation Tiers Screening At Risk’ bodies Risk WBs susceptible potential Susceptible areas significant issues, and specific measures Not At Risk Objectives met Increasing scale and level of detail Increasing focus on site specific supplementary measures, enforcement and engagement with landholders. Increasing resources What is the WB condition? Have significant pressures been mitigated? Where and why are the measures not working? What needs to be done to improve the situation? Status Capacity Trends Investigative monitoring, modelling Catchment walks, inspections Measures Additional measures Are the measures working and the objectives being met? If yes, continue surveillance and/or operational monitoring (status, trends, capacity) for next cycle. If not, further characterise and select new measures. Measures can be Surveillance and/or Operational Monitoring Increasing cost, resources, confidence Tier 1: Screening Tier 2: Susceptible areas, potential pressures Tier 3: Significant pressures, site specific measures
  • 26. Tier 1 Risk Characterisation • Takes account of: – Existing status – Whether significant pressures have been mitigated or not – Trends in concentrations or ecological condition – The capacity of the water body to absorb extras pressures – The resilience and sensitivity of the associated aquatic ecosystems – The value of having a combined approach for characterisation of both SWBs and GWBs
  • 27. Not at Risk 0.035 mg/l P as P Good Status 0.025 mg/l P as P 0.035 mg/l P as P Trend
  • 28. At risk 0.035 mg/l P as P Good Status 0.025 mg/l P as P 0.035 mg/l P as P Trend
  • 29. 0.025 mg/l P as P Trend Good Status Review 0.035 mg/l P as P 0.025 mg/l P as P
  • 30. Not at Risk Review
  • 31. Not at Risk At Risk
  • 32. Distance Assigning risk to threshold high 1 to prioritise measures Tier 1 screening for SW bodies Previous Reported Status3 Significant pressures mitigated? Significant trend4 in concentration or ecological metric Distance to threshold low2 Achieve Good status WFD Objectives WFD Objectives No deterioration of Status Objectives combined 5 - low capacity Achieve Good status No deterioration of Status Objectives combined - high capacity High Improving Not applicable Not at risk Not at risk Not applicable Not at risk Not at risk Yes None/stable/don't know Not applicable Review Review Not applicable Not at risk Not at risk Disimproving Not applicable Review Review Not applicable Review Review No or Improving Not applicable Not at risk Not at risk Not applicable Not at risk Not at risk Don't know None/stable/don't know Not applicable Review Review Not applicable Not at risk Not at risk Disimproving Not applicable At risk At risk Not applicable At risk At risk Good Improving Not at risk Not at risk Not at risk Not at risk Not at risk Not at risk Yes None/stable/don't know Not at risk Review Review Not at risk Not at risk Not at risk Disimproving Not at risk Review Review Not at risk Review Review No or Improving Not at risk Not at risk Not at risk Not at risk Not at risk Not at risk Don't know None/stable/don't know Not at risk Review Review Not at risk Not at risk Not at risk Disimproving Review At risk At risk Review At risk At risk Moderate Improving Review Not at risk Review Review Not at risk Review Yes None/stable/don't know At risk Review At risk At risk Not at risk At risk Disimproving At risk Review At risk At risk Review At risk No or Improving Review Not at risk Review Review Not at risk Review Don't know None/stable/don't know At risk Review At risk At risk Not at risk At risk Disimproving At risk At risk At risk At risk At risk At risk Poor Improving At risk Not at risk At risk At risk Not at risk At risk Yes None/stable/don't know At risk Review At risk At risk Not at risk At risk Disimproving At risk Review At risk At risk Review At risk No or Improving At risk Not at risk At risk At risk Not at risk At risk Don't know None/stable/don't know At risk Review At risk At risk Not at risk At risk Disimproving At risk At risk At risk At risk At risk At risk Bad Improving At risk Not at risk At risk At risk Not at risk At risk Yes None/stable/don't know At risk Review At risk At risk Not at risk At risk Disimproving At risk Review At risk At risk Review At risk No or Improving At risk Not at risk At risk At risk Not at risk At risk Don't know None/stable/don't know At risk Review At risk At risk Not at risk At risk Disimproving At risk At risk At risk At risk At risk At risk
  • 33. Groundwater body risk Assigning risk to prioritise measures GW bodies Tier 1 screening Previous Significant reported pressures Status mitigated? Significant trend in concentration or level Achieve Good status Distance Distance to threshold low to threshold high WFD Objectives WFD Objectives No deterioration Reverse upward trend Objectives combined - low capacity Achieve Good status No deterioration Reverse upward trend Objectives combined - high capacity Good Improving Not at risk Not at risk Not at risk Not at risk Not at risk Not at risk Not at risk Not at risk Yes None/stable/don't know Not at risk Review Not at risk Review Not at risk Not at risk Not at risk Not at risk Disimproving Not at risk Review Review Review Not at risk Review Review Review No or Improving Not at risk Not at risk Not at risk Not at risk Not at risk Not at risk Not at risk Not at risk Don't know None/stable/don't know Not at risk Review Not at risk Review Not at risk Not at risk Not at risk Not at risk Disimproving Review At risk At risk At risk Review At risk At risk At risk Poor Improving Review Not at risk Not at risk Review Review Not at risk Not at risk Review Yes None/stable/don't know At risk Review Not at risk At risk At risk Not at risk Not at risk At risk Disimproving At risk Review Review At risk At risk Review Review At risk No or Improving Review Not at risk Not at risk Review Review Not at risk Not at risk Review Don't know None/stable/don't know At risk Review Not at risk At risk At risk Not at risk Not at risk At risk Disimproving At risk At risk At risk At risk At risk At risk At risk At risk
  • 34. Tier 2 Risk Characterisation Undertaken on “At Risk” WBs and “Review” WBs  To identify what pressure is causing the WBs to be “At Risk”. (The “WHAT” question).  To locate the Critical Source Area (CSA), i.e., the areas contributing more pollutants than other parts. (The “WHERE” question).  Uses the Pathways Project tools, load apportionment techniques, other modelling tools, LA input
  • 35. Receptor Poorly productive aquifer (70% of country) Free-draining soils & subsoils
  • 36. Receptor Characterisation Helps decide “what” and “where” and “how”. PO4 CSA Poorly productive aquifer (70% of country) PO4 CSA
  • 37. Receptor Characterisation Helps decide “what” and “where” and “how”. Poorly productive aquifer (70% of country) measures measures Knowing and understanding (i.e., characterising) the pathway is vital
  • 38. Source: Jenny Deakin Mattock catchment Pollution Impact Potential (PIP) Maps Nitrate to GW Nuenna catchment Nitrate to GW
  • 39. Tier 3 Risk Characterisation • Further investigates the CSAs from the Tier 2 assessment. • Site specific investigations, such as catchment walks, investigative monitoring, licence reviews, compliance checks, etc. • Use of modelled scenarios using CMSTs, etc. • Identifies significant pressures, i.e. those causing the impact that need mitigation.
  • 40. Characterisation Timelines Characterisation process Start Finish Tier 1 Now Q2 2015 Tier 2 mid 2015 Q2 2016 Tier 3 Q4 2015 Ongoing SWMI and Article 5 reports by Q4 2015 Draft RBMPs by Q4 2016 Final RBMPs by Q4 2017
  • 41. Benefits • Links existing and new knowledge in a structured, holistic way for multiple purposes • Provides a means of focussing work already being carried out across a number of agencies Input and contribution from others is essential • Integrates assessments for all water body types • Uses an automated risk based approach in Tier 1 – reduced time, repeatable, defensible • Helps prioritise areas/issues for measures and monitoring • Supports SWMI, Article 5 reports and RMBPs
  • 42. A word on catchments and scale … What is a catchment? The catchment is the appropriate land-based organising unit for water management A basic tenet of catchment Demo outside!  It is a coherent topographically-based management is that feature what happens in one part of the catchment, as an interconnected system, affects people  It is defined by the natural hydrology and hydrogeology   and It environments ‘connects’ all relevant in other elements, parts. including pressures, receptors and the people living there.  Communities can relate to it. (Everyone lives in a catchment!)
  • 43. Water Body (WB) Scale  WBs are the water features referred to in the WFD  We have to report on WBs to the COM  Tier 1 characterisation (Risk screening on water bodies into: ‘at risk’, ‘not at risk’ and ‘review’)  Range in size from a few km long (rivers) to 100s km2 in size (groundwater)  However:  Numerous (~5000) in total for 2nd cycle  Minimal integration of WB types  Not suitable for assessing PoMs properly
  • 44. Sub-catchment Scale (the scale for local involvement)  Approx. 100 km2 each (~700)  Tier 2 & Tier 3 characterisation (All WBS ‘at risk’ aggregated into sub-catchments for more detailed assessment.)  Catchment walks  Modelling (e.g., CCT)  Investigative monitoring  Involve stakeholders  Measure results
  • 45. N Bad status Poor status Moderate status Group and public groundwater supplies Sub-catchment (Tullamore River) scale = where (the real) work is undertaken WWTP Groundwater water body boundary Hydrometric Station
  • 46. Catchment Scale (Water Management Units)  100s km2 (46 in RoI)  “From the mountains to the sea”  Integrate WB types  Evaluate issues  Prioritise measures  Organise delivery  Reports and plans
  • 47. ICM - Step 5: Set Overall Goals  Objectives & targets need to be set to guide the process, taking account of:  WFD (and all associated Directives) & Drinking Water Directive requirements.  Standards & thresholds in Irish regulations.  Requirements of sensitive ecosystems  Risk and status results, incl. load apportionment  Lag times for reductions in nutrient removal from soils and subsoils. 47
  • 48. ICM - Step 6: Identification & Evaluation of Possible Management Strategies  Evaluate existing measures  Review other potential mitigation measures  Take account of main pollution sources, impacts and pathways, including critical source areas (CSAs)  Stakeholder input critical  Develop and rank the measures needed 48
  • 49. ICM - Step 7: Design an Implementation Programme (1)  EPA will lead/facilitate this. But, LA ++ input essential  Includes:  Local community awareness and engagement process  Outputs of characterisation  Analysis of FH2020 implications  Climate change adaptation measures  Ecological flows & levels (E-flows & E-levels)  Resilience & sensitivity of ecosystems  Modelling as a means of evaluating management strategies  Linkages with physical planning  Review and amendment, as necessary, of the monitoring programme 49
  • 50. ICM - Step 7: Design an Implementation Programme (2) Includes: This one will be challenging/difficult Measures analysis Economic analysis  Finalisation of objectives  Selection of final management strategies Measures – what & where Implementation schedule  Provision of training, technical assistance and follow-up support 50
  • 51. ICM - Step 8: Implement the Programme Template River Basin Management Plan (RBMP) by EPA Completion of plan by WFD Offices/LAs Measures – what & where Implementation schedule Approval by DEHLG/Minister Reporting to the Commission by EPA 51
  • 52. ICM – Step 9: Measure Progress & Make Adjustments Analyse trends and outcomes Give feedback to stakeholders Make adjustments, as necessary Commence the 3rd cycle work! 52
  • 53. 53 Four Final Summary Thoughts 1. Catchments, connecting all relevant elements 2. Hard work 3. Working together
  • 54. “It’s people who save rivers, not plans ……” (quote from: “Saving Eden: A Manifesto”)