PRESENTATION TITLE Presented by: Name Surname Directorate Date Classification Of Water Resources and Determination of the Comprehensive Reserve and Resource.

Slides:



Advertisements
Similar presentations
Template: Making Effective Presentation about Your Evidence-based Health Promotion Program This template is intended for you to adapt to your own program.
Advertisements

Outcomes of The Living Murray Icon Sites Application Project Stuart Little Project Officer, The Living Murray Environmental Monitoring eWater CRC Participants.
ECOLOGICAL CONSEQUENCES Presented by: Delana Louw (Rivers for Africa) 3 April 2014.
DWA CORPORATE IDENTITY Presented by: Johan Maree Deputy Director: Media Production 12 December 2012 RESOURCE QUALITY OBJECTIVES: USER WATER QUALITY TWG.
TITLE OF PROJECT PROPOSAL NUMBER Principal Investigator PI’s Organization ESTCP Selection Meeting DATE.
Recommendations to Inform Development of a Climate Change Adaptation Strategy for the Lake Watershed Climate Change Adaptation Strategy for the Lake Simcoe.
Ramsar Convention on Wetlands ( Ramsar Convention on Wetlands ( Convention on Wetlands “The conservation and wise use of.
National Freshwater Ecosystem Priority Areas Project (NFEPA)
Future Research NeedsWorld Heritage and Climate Change World Heritage and Climate Change - Future Research Needs Bastian Bomhard World Heritage Officer.
UGDIE KICK-OFF MEETING F-MAN 1 ΑΝΝΕΧ 1-A by UGDIE.
Community Planning Training 1-1. Community Plan Implementation Training 1- Community Planning Training 1-3.
DWA CORPORATE IDENTITY Presented by: Johan Maree Deputy Director: Media Production 12 December 2012 MVOTI TO UMZIMKULU CLASSIFICATION STUDY PSC Overview.
Water Management System - WMS What is the Water Management System? The Water Management System is a computer system designed to support the water resource.
COORDINATED WATERBIRD COUNTS. Coordinated Waterbird Counts (CWAC) CWAC started in 1992 with 45 sites counted in South Africa Currently there are 645 wetlands.
Integrated Catchment Management Key Elements - Julie Burke.
Funded by the Government of Alberta Ecosystem Services and Conservation Offsets April 24 th, 2012.
National Reserve System and non-marine aquatic ecosystems Presented by: Tim Bond Science Coordinator National Reserve System Section.
Jan 2005 Kissimmee Basin Projects Jan Kissimmee Basin Projects Kissimmee River Restoration Project (KRR) Kissimmee Chain of Lakes Long Term Management.
DETERMINATION OF WATER RESOURCE CLASSES AND ASSOCIATED RESOURCE QUALITY OBJECTIVES IN THE INKOMATI WMA PUBLIC MEETING Date: 12 JUNE 2013 Time: 09:00 Venue:
IW: LEARN Case study:The Mekong Wetlands Biodiversity Programme Peter-John Meynell UNDP Team Leader 20 November 2004.
HYDROLOGY AND ECOLOGY. HYDROLOGY WATER QUALITY HYDRAULICS GEOMORPHOLOGY ECOLOGY SOCIO/ECONOMICS RESEARCHTEACHINGPOLICYCONSULTANCY VERTICAL INTEGRATION.
Daniel Baláž, Ján Černecký State Nature Conservancy of the Slovak Republic Nature Conservation and River Monitoring in Slovakia.
Classification of water resources and and Resource Quality Objectives in the Inkomati Catchment Methodology to way up the level of protection against water.
Watershed Assessment and Planning. Review Watershed Hydrology Watershed Hydrology Watershed Characteristics and Processes Watershed Characteristics and.
LETABA ECOSYSTEM SERVICES CONSEQUENCES OF SCENARIOS Presented by: Greg Huggins Nomad 03 April 2014.
Desktop Analysis Used To: Identify areas that meet certain criteria (e.g. contig forest 50 acres+, id gaps as well, or set lower value in urban area) Identify.
 Aldo Leopold’s Game Management - cornerstone text for U.S. federal wildlife agencies - three necessities for free-ranging wildlife: food, water, and.
PRESENTATION TITLE Presented by: Name Surname Directorate Date Classification, Reserve & RQO determination of water resources in the Mvoti to Umzimkulu.
Implementation of the Water Resources Classification System and Determination of the Resource Quality Objectives for Significant Water Resources in the.
FSC Issues and studies. HJ van Hensbergen Wildhorus Limited.
PRESENTATION TITLE Presented by: Name Surname Directorate Date CLASSIFICATION OF SIGNIFICANT WATER RESOURCES IN THE MVOTI TO UMZIMKULU WATER MANAGEMENT.
DWA CORPORATE IDENTITY Presented by: Johan Maree Deputy Director: Media Production 12 December 2012 MVOTI TO UMZIMKULU NWRCS WATER QUALITY: CONSEQUENCES.
1 Raising of Kouga Dam: Improved Desktop Analysis Preliminary findings.
1. THE IMPLEMENTATION OF THE WATER RESOURCES CLASSIFICATION SYSTEM AND DETERMINATION OF THE RESOURCE QUALITY OBJECTIVES FOR THE SIGNIFICANT WATER RESOURCES.
Cécile BONINO-Pilot Wildlife Estates Spa August 2007 Wildlife Estates Darius Movaghar (ELO) WE Plenary Session - 2 September 2009 Delphine Dupeux.
TECHNICAL MEETING ON RESERVE DETERMINATION TOTAL OUTFLOW STRATEGY:WWT Venue: NATIONAL TREASURY Date: 24 JUNE 2014 Time: 10:00 – 16:30.
Using EoH tools to identify values and threats to those values (tools 1 and 2)
Rapid Bioassessment Protocols for low gradient streams) for species richness, composition and pollution tolerance, as well as a composite benthic macroinvertebrate.
“The minimum flow for a given watercourse shall be the limit at which further withdrawals would be significantly harmful to the water resources or ecology.
January 27, 2011 Summary Background on Delta Flow and Habitat Relationships Delta Stewardship Council Presentation by the Independent Consultant.
PRESENTATION TITLE Presented by: Name Surname Directorate Date Classification, Reserve & RQO determination of water resources in the Mvoti to Umzimkulu.
The current state-of-play – protected areas Existing protected areas are not sufficiently comprehensive or adequate to achieve conservation targets. The.
DWA CORPORATE IDENTITY Presented by: Johan Maree Deputy Director: Media Production 12 December 2012 MVOTI TO UMZIMKULU CLASSIFICATION STUDY Technical Working.
Starter: Look at the photograph. This is the site for a proposed coal mine, providing essential fuel for the community. In pairs: Discuss whether you think.
Healthy Schools. The Strategic Aims of the Healthy Schools Programme: To support children and young people in developing healthy behaviours To help raise.
Atmospheric Research Characterising Climate Risks Breakout Workshop Presentation Roger N. Jones CSIRO Atmospheric Research.
1 The Future Role of the Food and Veterinary Office M.C. Gaynor, Director, FVO EUROPEAN COMMISSION HEALTH & CONSUMER PROTECTION DIRECTORATE-GENERAL Directorate.
DWA CORPORATE IDENTITY Presented by: Johan Maree Deputy Director: Media Production 12 December 2012 MVOTI TO UMZIMKULU NWRCS MVOTI & MKOMAZI RIVER ECOLOGICAL.
PRESENTATION TITLE Presented by: Name Surname Directorate Date Classification, Reserve & RQO determination of water resources in the Mvoti to Umzimkulu.
Biodiversity Health Index Main Streams for Life John MacKinnon UNDP consultant June 2012.
Classification of water resources and determination of the comprehensive reserve and Resource Quality Objectives in the Mvoti to Umzimkulu Water Management.
Implementation of the Water Resources Classification System and Determination of the Resource Quality Objectives for Significant Water Resources in the.
RESERVE DETERMINATION STUDIES FOR SELECTED SURFACE WATER, GROUNDWATER, ESTUARIES AND WETLANDS IN THE GOURITZ WMA – PSC MEETING NO 1 OVERVIEW OF THE RESERVE.
EWR SUMMARY Presented by: Delana Louw Rivers for Africa 31 October 2013.
PRESENTATION TITLE Presented by: Name Surname Directorate Date Classification, Reserve & RQO determination of water resources in the Mvoti to Umzimkulu.
FROM SCENARIOS TO MANAGEMENT CLASSES: ECOLOGICAL COMPONENT DEMONSTRATION Presented by: Delana Louw (Rivers for Africa) 26 November 2013.
Environmental Flow Instream Flow “Environmental flow” is the term for the amount of water needed in a watercourse to maintain healthy, natural ecosystems.
1 Gouritz WMA Study: Wetlands Mark Rountree Fluvius Environmental Consulting
IWRM in SA: Where are the law suits? The Association for Water and Rural Development Ramin Pejan Dr. Sharon Pollard.
PNAMP Monitoring Terminology Data Dictionary The meta data file provides a better explanation of the project’s intent. The estuary work group is still.
Principal Investigator ESTCP Selection Meeting
International Water Quality Guidelines for Ecosystems
Principal Investigator ESTCP Selection Meeting
Presenter: Christi Melendez, RN, CPHQ
Climate Change Dr Mark Rehfisch Director of Development
LIFE and the implementation of the Water Framework Directive
CIS Working Group 2A ECOSTAT SCG Meeting in Brussels
Marine Strategy Coordination Group 14 November 2011, Brussels
Environmental Priorities Environmental Impact Assessment
Presentation transcript:

PRESENTATION TITLE Presented by: Name Surname Directorate Date Classification Of Water Resources and Determination of the Comprehensive Reserve and Resource Quality Objectives in the Mvoti To Umzimkulu Water Management Area DRAFT WETLAND RQOs Presented by: Mark Rountree 24 March 2015

Wetlands in the Mvoti WMA Wetland RQOs in the Mvoti WMA There are many thousands of wetlands in the Mvoti WMA (Nel et al. 2011), including two Ramsar wetlands (Ntsikeni wetland & Mngeni sponge). Activities in and around all wetlands are subject to authorisations under the National Water Act. The DWS evaluates proposed developments through the WULA system. RQOs are a set of narrative and/or numerical management objectives defined for water resources. These set the objectives for the desired condition of the resource and can be used to guide the evaluation of WULAs. Verified baseline information is required to set a RQO. BACKGROUND

DWS and Wetlands Wetland RQOs in the Mvoti WMA The DWS’s National Water Resource Strategy (DWA, 2013) provides for two key aspects related to the management of wetlands, namely to 1.address proactively, as well as remedially, the loss and degradation of wetlands and 2.maintain healthy, functional ecosystems. In addition to the NWRS, the DWS’s National Wetland Position Paper (in prep) has proposed an objective that there be no net loss of wetland ecosystem functions in South Africa. The draft RQOs for the wetlands of the Mvoti WMA attempt to adhere to the objectives for wetlands proposed by these two national strategy documents. BACKGROUND

Levels of RQOs Wetland RQOs in the Mvoti WMA Three levels of RQO’s have been identified for wetlands: - Level 3 RQOs for priority wetlands (individual high priority wetlands) - Level 2 RQOs for high priority catchments (average wetland EIS is moderate, high or very high) - Level 1 RQOs for all other wetlands, and potential FEPAs APPROACH

Level 1 RQOs for priority individual wetlands Wetland RQOs in the Mvoti WMA In 2012 each sub-quaternary catchment was assessed to identify large (level 1) FEPA wetlands which were directly dependent on river flows. These were prioritised in the identification of key hotspots for the selection of river EWR sites Hotspots used in the IUAs and analysis of scenarios for the WMA None of the flow scenarios impacts upon wetlands. However, many impacts upon wetlands are non-flow related APPROACH

Level 1 RQOs for priority individual wetlands Wetland RQOs in the Mvoti WMA Regardless of river flow dependence, other priority wetlands (Ramsar sites, Important Birding Areas and priority Ezemvelo KZN wildlife wetland monitoring sites) were also identified. Of these, 4 high priority sites (including the two RAMSAR sites) had existing monitoring (EcoStatus) data which allowed for the generation of specific RQOs. The four high priority wetlands in the Mvoti WMA were: Ntsikeni wetland (a Ramsar wetland) Mgeni sponge (a Ramsar wetland) The Mvoti vlei (priority KZN Ezemvelo monitoring site), and The Swamp (priority KZN Ezemvelo wetland monitoring site). APPROACH

Level 2 RQOs for priority catchments (1) Wetland RQOs in the Mvoti WMA There are many thousands of wetlands in the Mvoti and it is unrealistic to try to define or monitor specific RQOs for each individual wetland. Moreover, there was no widespread EcoStatus (baseline condition) information of the wetlands. In 2012 a desktop assessment to estimate the EIS of wetlands per quaternary catchment was undertaken to provide some indication of priority wetland catchments within the WMA. These desktop data identified priority wetland catchments – those with moderate, high or very high EIS. APPROACH

Level 2 RQOs for priority catchments (2) Wetland RQOs in the Mvoti WMA These data provide an indication of catchments with important (moderate or higher EIS) wetlands. APPROACH Ramsar wetland Priority Ezemvelo KZN Wildlife wetland

Level 2 RQOs for priority catchments (3) Wetland RQOs in the Mvoti WMA For the priority catchments (moderate, high or very high EIS), an average PES category was determined A variety of within-wetland and catchment landuse activities and condition scored to estimate PES Small sample size of field data (n=8), but good correlation between desktop assessed and field verified scores (R 2 = 0.866). APPROACH

Level 2 RQOs for priority catchments (4) Wetland RQOs in the Mvoti WMA Baseline PES for priority catchments (moderate, high or very high EIS) APPROACH

Level 3 RQOs for general wetlands and other FEPAs Wetland RQOs in the Mvoti WMA For all wetlands within the WMA (including non-priority catchments), ecosystem services of wetlands must be maintained (objective of the DWS’s Wetland Position Paper). Across the WMA, FEPA wetlands (desktop estimates of potential priortity wetlands) are present. Level 1 RQOs relating to FEPA wetlands have been set in the event that data (verification) on specific wetlands becomes available in the future. These RQOs aim to maintain the TARGET (or achieve, if Target is higher than PES) the EC of the wetland for water quantity, quality, habitat and key biota components. APPROACH

Priority wetland: Mngeni Sponge (RAMSAR) Wetland RQOs in the Mvoti WMA LEVEL 3 RQOs Mgeni sponge (Ramsar wetland) IUA and SQComponentSub-component RQO Indicator Numerical MRU uMnA ( U2 0A ) Water availabilityHydrology PES is a C and must be maintained or improved. Wetland hydrology score. Detailed assessment of wetland hydrology using a PES tool at years intervals. Habitat Geomorphology PES is an A and must be maintained or improved. Wetland geomorphology score. Geomorphology module of a wetland PES tool at year intervals. General vegetation PES is a C and must be maintained or improved. Wetland vegetation score: assessment of vegetation using a wetland PES tool at year intervals. PES overall PES is a C and must be maintained or improved. Wetland PES assessment tool at year intervals. BiotaWattled cranes Presence of at least 5 breeding pairs of wattled crane and breeding success. The number of breeding pairs of wattled crane.

Priority wetland: Ntsikeni wetland (RAMSAR) Wetland RQOs in the Mvoti WMA LEVEL 3 RQOs Ntsikeni wetland (Ramsar wetland) IUA and SQ ComponentSub-component RQO Indicator Numerical Ru Mz8 ( T51H-04846) Water availabilityHydrology PES is an A and must be maintained or improved. Wetland hydrology score. Detailed assessment of wetland hydrology using a PES tool at years intervals. Habitat Geomorphology PES is an A and must be maintained or improved. Wetland geomorphology score. Geomorphology module of a wetland PES tool at year intervals. General vegetation PES is a B and must be maintained or improved. Wetland vegetation score: assessment of vegetation using a wetland PES tool at year intervals. PES overall PES is an A and must be maintained or improved. Wetland PES assessment tool at year intervals. Biota Wattled cranes Presence of at least 3 breeding pairs of wattled crane and breeding success. The number of breeding pairs of wattled crane (baseline of 2014). European Bittern Annual presence of European Bitterns. Annual presence of European Bittern migrants (sighted or indicated from call).

Priority wetlands: The Swamp Wetland RQOs in the Mvoti WMA LEVEL 3 RQOs The Swamp (priority KZN Ezemvelo wetland monitoring site) IUA and SQ ComponentSub-component RQO Indicator Numerical RU Mz4 (T51E-04478) Water availabilityHydrology PES is a D and must be maintained or improved. Wetland hydrology score. Detailed assessment of wetland hydrology using a PES tool at years intervals. Habitat Geomorphology PES is a C and must be maintained or improved. Wetland geomorphology score. Geomorphology module of a wetland PES tool at 3-5 year intervals. General vegetation PES is a C and must be maintained or improved. Wetland vegetation score: assessment of vegetation using a wetland PES tool at 3 -5 year intervals. PES overall PES is a C and must be maintained or improved. Wetland PES assessment tool at year intervals. Biota (key vegetation species) Cyperus marginatus vegetation Current areas are not known, but should not reduce more than 20% below baseline. Area of vegetation type at year intervals.

Priority wetlands: Mvoti Vlei Wetland RQOs in the Mvoti WMA LEVEL 3 RQOs The Mvoti vlei (priority KZN Ezemvelo monitoring site) IUA and SQ ComponentSub-component RQO Indicator Numerical MRU Mvoti A ( U40A ) Water availabilityHydrology PES is an E and must be maintained or improved. Wetland hydrology score. Detailed assessment of wetland hydrology using a PES tool at years intervals. Habitat Geomorphology PES is an A and must be maintained. Wetland geomorphology score. Geomorphology module of a wetland PES tool at 3-5 year intervals. General vegetation PES is a D and must be maintained or improved. Wetland vegetation score: assessment of vegetation using a wetland PES tool at 3 -5 year intervals. PES overall PES is a D and must be maintained or improved. Wetland PES assessment tool at year intervals.

Priority catchments (moderate, high or very high EIS) Wetland RQOs in the Mvoti WMA The RQOs identified for wetlands in priority catchments aim to maintain the average condition of the wetlands (Target is PES). LEVEL 2 RQOs

Priority catchments (moderate, high or very high EIS) Wetland RQOs in the Mvoti WMA LEVEL 2 RQOs IUA Applicable wetlands Component RQO IndicatorReference Descriptive All All wetlands within quaternary catchments which have moderate, high or very high EIS Habitat The TARGET EC of the wetlands in a catchment must be maintained. The average PES of the quaternary catchment NWRS

All wetlands and wetland FEPAs Wetland RQOs in the Mvoti WMA LEVEL 1 RQOs IUA Applicable wetlands Component RQO IndicatorReference Descriptive All All wetlands within the WMA Ecosystem Services The ecosystem services of wetlands in a catchment must be maintained. Hectare equivalents (PES x area) can be taken as a coarse indicator of ecosystem services. The National Wetland Position Paper (in prep), For FEPAs: - Flow and inundation regime must maintain wetland FEPAs in target EC - Water quality must be sufficient to maintain wetland FEPAs in target EC - Species diversity and health of boita should be maintained (includes the feeding, breeding and movement of fauna and flora) - Specific Baseline and Target EC of FEPAs are not verified - Assessment of the current condition and presence/count of significant biota is recommended. - Numerical RQO criteria should equate to the current condition and/or presence (or counts) of key species

RQOs for priority catchments (FEPAs within priority catchments) Wetland RQOs in the Mvoti WMA RQOs FOR WETLANDS IUA Applicable wetlands Component RQO IndicatorReference DescriptiveNumerical All Validated wetland FEPAs in a good condition (A – B EC) Water Quality Water quality must maintain wetland FEPAs in good condition. FEPA wetlands have not been verified, and EWRs and PES for these wetlands have yet to be determined. Water quality is sufficient to maintain the current PES. National Freshwater Ecosystem Priority Areas (Driver et al., 2011). Validated wetland FEPAs in a modified condition (C - F EC) Water quality is sufficient to achieve the REC.

RQOs for priority catchments (FEPAs within priority catchments) Wetland RQOs in the Mvoti WMA RQOs FOR WETLANDS IUA Applicable wetlands Component RQO IndicatorReference DescriptiveNumerical All Validated wetland FEPAs in a good condition (A – B EC) Habitat and biota Species diversity and health of biotic communities supported by wetland FEPAs should be maintained. This includes the feeding, breeding and movement of fauna and flora. PES of all the wetlands is unknown. An assessment of the current condition and presence/count of significant biota is required to develop numerical targets. The numerical criteria should equate to the current condition of the wetlands and/or presence (or counts) of key species within them. Habitat condition is sufficient to maintain the current PES. National Freshwater Ecosystem Priority Areas (Driver et al., 2011). Validated wetland FEPAs in a modified condition (C - F EC) Habitat condition is sufficient to achieve the REC.

Summary Wetland RQOs in the Mvoti WMA Available data has been used to set RQOs for high priority individual wetlands in the Mvoti WMA For the remaining thousands of wetlands where baseline data are not available per wetland, quaternary-scale RQOs have been set for priority catchments (where wetland EIS is moderate, high or very high). A variety of recommendations, organised according to impact types, are provided which could be used as guidelines or WULA conditions to enable the RQOs to be achieved. RQOs FOR WETLANDS