TDA/SAP Methodology Training Course Module 2 Section 5
preynolds_blacksearecovery.ppt
1. Indicators to monitor theIndicators to monitor the
effect of nutrients within theeffect of nutrients within the
Black SeaBlack Sea
THE GLOBAL ENVIRONMENT
FACILITY
2. The Black Sea
..an endangered sea shared by
Bulgaria, Georgia, Romania,
Russia, Turkey & Ukraine
….a large basin
Inhabited by 160 million people
from 17 countries
3. GEF/UNDP Assistance to the Wider BlackGEF/UNDP Assistance to the Wider Black
Sea BasinSea Basin
The new GEF assistance is designed to address the three highestThe new GEF assistance is designed to address the three highest
priority transboundary problems of the Black Sea (namelypriority transboundary problems of the Black Sea (namely
eutrophication, discharge of toxic substances including oil, loss of criticaleutrophication, discharge of toxic substances including oil, loss of critical
benthic habitats and wetlands) and to highlight emerging onesbenthic habitats and wetlands) and to highlight emerging ones
Assistance is provided as three complementary components:Assistance is provided as three complementary components:
Two Regional Projects for the Black Sea and the Danube River BasinTwo Regional Projects for the Black Sea and the Danube River Basin
Black Sea project which will be implemented in two Phases betweenBlack Sea project which will be implemented in two Phases between
(2002- 2004) and (2004- 2006);(2002- 2004) and (2004- 2006);
A series of country-related investment projects executed through theA series of country-related investment projects executed through the
World Bank-GEF Nutrient Investment Facility;World Bank-GEF Nutrient Investment Facility;
Other GEF and donor interventions in the basin targeting reduction ofOther GEF and donor interventions in the basin targeting reduction of
nutrients/toxic pollutants and restoration of critical habitats.nutrients/toxic pollutants and restoration of critical habitats.
4. Eutrophication - SummaryEutrophication - Summary
Anthropogenic eutrophication is usually caused by nitrogen and/orAnthropogenic eutrophication is usually caused by nitrogen and/or
phosphate compounds either dumped at sea, discharged throughphosphate compounds either dumped at sea, discharged through
pipes, or lost to the marine environment via the atmosphere or runpipes, or lost to the marine environment via the atmosphere or run
off from land.off from land.
Nutrients act as "food" for phytoplankton (plant cells in the waterNutrients act as "food" for phytoplankton (plant cells in the water
column), capable of multiplying at an enormous rate, given sufficientcolumn), capable of multiplying at an enormous rate, given sufficient
food and light. This in turn causes a change in the planktonfood and light. This in turn causes a change in the plankton
population, a general increase in water turbidity and greaterpopulation, a general increase in water turbidity and greater
fluctuations in oxygen levels.fluctuations in oxygen levels.
As light is prevented from penetrating down, other organisms suchAs light is prevented from penetrating down, other organisms such
as sea weeds (algae) and sea grass can be adversely effected.as sea weeds (algae) and sea grass can be adversely effected.
Finally with little water movement and a high plankton mass,Finally with little water movement and a high plankton mass,
deoxygenation and mass death of organisms in the affected areadeoxygenation and mass death of organisms in the affected area
may be observedmay be observed
5. What to measure?What to measure?
Biota
(Phytoplankton,
macrophytes, benthic
algae, invertebrates,
fish etc.)
Firmly bound
particulate P
Mineral-forming reactions
Desorption
Firmly bound
sediment P
Desorption
P inputs
Slow
diffusion
Settlement/
resuspension
Uptake
Release
Wash-out
Uptake
Microbial
decomposition
Water
column
Sediment
Export from river reach
Diffusion
and flushing
Decomposition
Diffusion
Porewater P
Labile
sediment P
Labile
particulate P
Soluble P
Sediment organic
matter
Uptake/
decomposition
Bioturbation
Sediment infauna
Sorption/
desorption
6. Strategic Goals for Nutrients in the Black SeaStrategic Goals for Nutrients in the Black Sea
1.1. A long term goal of nutrient reduction to a level whichA long term goal of nutrient reduction to a level which
will allow the ecosystem to recover (1960s level);will allow the ecosystem to recover (1960s level);
2.2. An intermediate goal not to exceed levels of nutrientsAn intermediate goal not to exceed levels of nutrients
above levels encountered in 1997;above levels encountered in 1997;
3.3. To reach agreement on a common methodology for aTo reach agreement on a common methodology for a
monitoring approach;monitoring approach;
4.4. To further assess the nutrient input loads and theTo further assess the nutrient input loads and the
ecological status of the Black Sea and the Sea of Azovecological status of the Black Sea and the Sea of Azov
7. Areas of Impact of Nutrients in the Black SeaAreas of Impact of Nutrients in the Black Sea
The central part of the north-western shelfThe central part of the north-western shelf
biomass reduction of 10 million tons in Phyllophorabiomass reduction of 10 million tons in Phyllophora fieldfield fromfrom
1950 to 19901950 to 1990
Seasonal hypoxic zones in front of largest riversSeasonal hypoxic zones in front of largest rivers
biological loss ofbiological loss of 200 t per square kilometre of seabed.200 t per square kilometre of seabed.
disappearance of large amounts of surface-living organisms ofdisappearance of large amounts of surface-living organisms of
both of marine and fresh-water originboth of marine and fresh-water origin
Rocky shoresRocky shores
disappearance ofdisappearance of epiphyte algae, invertebrates and fish.epiphyte algae, invertebrates and fish.
Sandy beachesSandy beaches
decrease of polychaetes and bivalvesdecrease of polychaetes and bivalves
The open coastal watersThe open coastal waters
increase in mass species of phytoplanktonincrease in mass species of phytoplankton
Coastal wetlandsCoastal wetlands
decrease of species and increase of hypoxiadecrease of species and increase of hypoxia
8. Criteria for the Choice of Environmental Status IndicatorsCriteria for the Choice of Environmental Status Indicators
CConsensusonsensus-- does everybody agree that “less is better”, or vice versa?does everybody agree that “less is better”, or vice versa?
RResponsiveness -esponsiveness - will we see comparable figures in the next 5 years? Howwill we see comparable figures in the next 5 years? How
quickly will changes be detected?quickly will changes be detected?
IIndependence of assumptions -ndependence of assumptions - could the value change drastically bycould the value change drastically by
fumbling with some assumptions?fumbling with some assumptions?
TTransparency -ransparency - can a layperson understand what’s happening? does thecan a layperson understand what’s happening? does the
indicator hide or reveal facts?indicator hide or reveal facts?
EExperiencexperience -- Is the technical capacity available in the region? Is there aIs the technical capacity available in the region? Is there a
significant variability in the historical measurements/significant variability in the historical measurements/
RResponsibility -esponsibility - does the indicator point at those who should be helddoes the indicator point at those who should be held
responsible?responsible?
IInternational standard –nternational standard – has the scientific community at least ring-tested thehas the scientific community at least ring-tested the
methodologymethodology
AAnalytical soundness -nalytical soundness - does the indicator measure the problem, or ratherdoes the indicator measure the problem, or rather
something else?something else?
9. Potential ES Indicators for the Black SeaPotential ES Indicators for the Black Sea
Chemical concentrations and loadings inChemical concentrations and loadings in
water and sedimentwater and sediment
Physical measurements – turbidity relatedPhysical measurements – turbidity related
Biological parametersBiological parameters
micro-algae, macro-algae and higher plantsmicro-algae, macro-algae and higher plants
InvertebratesInvertebrates
10. Potential ES Indicators for the Black SeaPotential ES Indicators for the Black Sea
Chemical loadings to the Black SeaChemical loadings to the Black Sea
TP, SRP, TN, TIN, Silicate, BODTP, SRP, TN, TIN, Silicate, BOD
• Frequency of measurements required is very high – weekly basisFrequency of measurements required is very high – weekly basis
• Continuous flow dataContinuous flow data
• Annual mean load with confidence limitsAnnual mean load with confidence limits
• Total nutrient input important to determine the potential bioavailable loadTotal nutrient input important to determine the potential bioavailable load
Chemical concentrations in water columnChemical concentrations in water column
Bioavailable nutrients (SRP, TIN) and BODBioavailable nutrients (SRP, TIN) and BOD
• Trend analysis must include confidence limitsTrend analysis must include confidence limits
• Winter monitoring for nutrients to remove seasonalityWinter monitoring for nutrients to remove seasonality
Chemical concentrations in sedimentChemical concentrations in sediment
Bioavailable nutrients (SRP, TIN) and BOD in interstitial waterBioavailable nutrients (SRP, TIN) and BOD in interstitial water
• Analysis at specific depths is important – diatoms versus macrophytesAnalysis at specific depths is important – diatoms versus macrophytes
Mineralisation, nitrification and denitrification ratesMineralisation, nitrification and denitrification rates
11. Potential ES Indicators for the Black SeaPotential ES Indicators for the Black Sea
Physical measurements – turbidity relatedPhysical measurements – turbidity related
Secchi discSecchi disc
• Measure of disappearance of discMeasure of disappearance of disc
• Cheap and simpleCheap and simple
Suspended solidsSuspended solids
• May be simple but prone to large variabilityMay be simple but prone to large variability
Measure of scattered or adsorbed lightMeasure of scattered or adsorbed light
12. The Process of Adoption of ES IndicatorsThe Process of Adoption of ES Indicators
Biological parameters – micro-algaeBiological parameters – micro-algae
Primary productivityPrimary productivity
• Measured asMeasured as tonne C/ha/yeartonne C/ha/year
Standing crop -micro-algal biomassStanding crop -micro-algal biomass
• measured as Chlorophyll-a contentmeasured as Chlorophyll-a content
• Sampling may miss bloomSampling may miss bloom
Community compositionCommunity composition
• The development of an index or the identification of indicatorThe development of an index or the identification of indicator
species may be best represented only on a single communityspecies may be best represented only on a single community
13. The Process of Adoption of ES IndicatorsThe Process of Adoption of ES Indicators
Biological parameters – macro-algae and higher plantsBiological parameters – macro-algae and higher plants
Maximum depth of colonisationMaximum depth of colonisation
• Offers three major advantages over conventional Secchi depth orOffers three major advantages over conventional Secchi depth or
suspended solids monitoring:suspended solids monitoring:
It provides an integrated measure of turbidity over time - perhaps 6It provides an integrated measure of turbidity over time - perhaps 6
months-2 years.months-2 years.
It provides a genuine measure of the depth of the euphotic zone, notIt provides a genuine measure of the depth of the euphotic zone, not
simply a measure of water clarity at a particular depth within the watersimply a measure of water clarity at a particular depth within the water
column.column.
It is much more ecologically relevant.It is much more ecologically relevant.
Biomass and productivityBiomass and productivity
• Possible problems with storm damage.Possible problems with storm damage.
• number of samples required to detect a significant change innumber of samples required to detect a significant change in
biomass over, say, 5 years,biomass over, say, 5 years,
14. The Process of Adoption of ES IndicatorsThe Process of Adoption of ES Indicators
Invertebrates – sediment infaunaInvertebrates – sediment infauna
To be used for monitoring medium-long termTo be used for monitoring medium-long term
(>5 years) recovery of the Black Sea.(>5 years) recovery of the Black Sea.
Must use harmonized monitoring protocolMust use harmonized monitoring protocol
The sediment should also be analysed forThe sediment should also be analysed for
toxicants (organic and inorganic), particle sizetoxicants (organic and inorganic), particle size
analysis and total organic carbon, in additionanalysis and total organic carbon, in addition
to water column salinity.to water column salinity.
15. Implementation in the Black Sea RegionImplementation in the Black Sea Region
1.1. Proposal of ES indicators for consultation with the Black SeaProposal of ES indicators for consultation with the Black Sea
Commission’s Advisory groups – Key group: pollution monitoringCommission’s Advisory groups – Key group: pollution monitoring
and assessmentand assessment
2.2. Consultation with the ICPDR and the Black Sea Commission JointConsultation with the ICPDR and the Black Sea Commission Joint
Technical Working GroupTechnical Working Group
3.3. Integrate feedback on criteria and weightingIntegrate feedback on criteria and weighting
4.4. Prioritisation of indicatorsPrioritisation of indicators
5.5. Submission to the Black Sea Commission for reviewSubmission to the Black Sea Commission for review
6.6. Undertake pilot monitoring programmeUndertake pilot monitoring programme
1.1. - include training, QA/QC and inter-comparison exercise- include training, QA/QC and inter-comparison exercise
2.2. - agree sampling sites- agree sampling sites
7.7. Collect baseline dataCollect baseline data
8.8. Include ES indicators into the Black Sea Integrated PollutionInclude ES indicators into the Black Sea Integrated Pollution
Monitoring and Assessment Programme (BSIPMAP)Monitoring and Assessment Programme (BSIPMAP)
16. Where are we likely to encounter delayWhere are we likely to encounter delay
Agreement of the scientific communityAgreement of the scientific community
Combat with a proactive approachCombat with a proactive approach
Limit the input of non-relevant advisoryLimit the input of non-relevant advisory
groupsgroups
Quality control – validity of dataQuality control – validity of data
SamplingSampling
AnalysisAnalysis
Procedures for assessment of dataProcedures for assessment of data
17. Thank you for your attentionThank you for your attention