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INDICATORS OF DYNAMICS
IN FISHERY RESOURCE
Indicators of dynamics in fishery resource
What are indicators?
 Indicators are data or combination of data collected and processes
for a clearly defined analytical or policy purpose.
 That purpose should be explicitly specified and taken into account
when interpreting the value of an indicator.
 Fisheries indicators should provide practical and cost-effective
means for the evaluation of the state and the development of
fisheries systems and the effects that policy changes have on those
systems.
 In considering the concept of indicators of sustainable
development, a necessary first step is to define the sustainable
development in the context of fisheries.
Indicators of dynamics in fishery resource conted….
What are indicators?
 Sustainable development is generally defined as being
development that meets the needs of the current generation without
compromising the ability of future generations to meet their own
needs.
 In the fisheries sector, the use of biological indicators in the
development of fisheries assessments and management plans has
been standard practice, in most OECD countries for many years.
 However relatively little attention has paid to the development of
economic and social indicators that serve to assess progress on
other aspects of sustainable development.
Indicators of dynamics in fishery resource conted….
What are indicators?
 With respect to criteria for success it has been found, both
theoretically and empirically that good indicators are easily
measured, cost effective to collect to calculate, and easily interpreted
( to avoid confusion about the state of the system they are
reflecting).
 Simple indicators are consistently found to out perform more
complex (model-dependent) indicators, which were sensitive to data
quality.
 There is consensus on the need for a suite rather than a single
indicator and on the types of indicators that perform well regardless
of system types.
 These indicators are:
Economic and Social Indicators
For the indicators to be effective and workable in assessing the economic and social
performance of fisheries, they should:
Have a clear policy relevance and in particular:
A. Provide balanced coverage of some of the key issues of common concern to
OECD countries, and reflect changes over time;
B. Be easy to interpret (that is, movements in each indicator should have clear
link to overall sustainability);
C. Allow comparisons across countries;
D. Lend themselves to being adapted to different national contexts, analysed at
different levels of aggregation and linked to more detailed indicator sets.
 Be analytically sound in technical and scientific terms, based on internationally
accepted standards and broadly accepted by stakeholders.
 Be based on data that are available, of known quality and regularly updated.
Economic and Social Indicators conted….
What are indicators used for ?
 The main purpose in developing a set of sustainability indicators is to
assist in assessing the performance of fisheries policy and
management and to stimulate action to better pursue to sustainability
objectives.
 This can occur in a number of areas. For example, indicators can be
used for ex-post evaluations of the impacts of management initiatives;
assessment of progress towards medium and/or long-term objectives;
and assessment of the impacts of fisheries.
 They can also enhance communication, transparency,
effectiveness and accountability in fisheries management.
Economic and Social Indicators conted….
What are indicators used for ?
 In this regard, indicators can be developed and reported at various
levels of aggregation- international, national, regional and local levels.
 Many of the environmental indicators for fisheries referred to above
are focused on the fishery level.
Other aggregates that are regularly reported, such as the
contribution of fisheries to exports, are reported at a national level.
 Yet others relate to fisheries that are managed regionally as
straddling and/or highly migratory stocks.
Biological indicators
Relative biomass:
 specifically of gelatinous zooplankton, cephalopods, small pelagic,
scanvengers, demersal fish, piscivores, top predators, and biogenic
habitat (cover forming species).
 Ease of sampling differs strongly between these groups (for
instance external bodies, such as NGOs, often monitor the
charismatic top predators, tourism can focus attention on coral reef
fishes, snapshots of mangrove forests and shallow benthic habitat
may be available from satellite images.
 It is possible to find proxies for even some of the most difficult
groups. For example, changes in relative biomass of gelatinous
zooplankton may be captured by frequency of bloom events, as this
is a much more easily obtainable statistic due to the ability to
generate it from expert information and fisher interviews.
Biological indicators conted….
Biomass ratios: The rapidity with which leaving materials can be
replaced itself is measured by biomass ratio. In particular the biomass
ratios of piscivore: planktivore (PS:ZP), pelagic: demersal (P:D) and
infauna: epifauna. The last of these is probably not feasible in data
poor situations, but the other two can be done.
Size spectra: which give an indication of perturbation in system
structure (using the slope of the curve), but can also highlight changes
in system productivity (via the intercept).
Maximum (or mean) length: This indicator is observed to work in
practice even if simple rules of thumb regarding are used. Caution is
needed regarding market driven changing in preferred sizes, however.
Biological indicators conted….
Total fisheries removals: (catch + bycatch + discards):
This indicator considers the total biomass removed from the system
versus what is left cycling in the system. While similar in concept to the
widely used comparison of primary production vs. removals from the
system, there is concern that it will not be suitable for data poor and
dispersed small scale fisheries due to the lack of data on removals let
alone discards.
Diversity: (counts of species):
It remains an informative and fundamental piece of information about
the system. Alternative measures of diversity or system structure may
need to be considered too, depending on which operating model is
used or what empirical data is available.
Biological indicators conted….
Diversity: (counts of species):
One possibility is considering the value of changes in species-area
curves (e.g. the slope and asymptote of the curve) through time (or
spatially if under a perturbation gradient). It is likely that some simple
or ordinal data can be collected on this from the fishers themselves
given that they are acutely aware of what they catch. Looking at
changes in these ranking could be highly informative.
Size at maturity (weight and length):
It is a strong means of detecting change in the system and stock
structure. It may be too difficult to use in data poor situations.
Biological indicators conted….
Biophysical (Chlorophyll a, temperature, dissolved inorganic
nitrogen, and level of contaminants):
These may be drawn from water quality monitoring programs or
remotely sensed data sets, but are needed even if they aren’t
already being collected as they are means of teasing out causation.
Indicators respond to any system change, including those caused by
sectors other than fisheries, so any information that helps elucidate
causation is extremely helpful.
While all of these indicators are not equally easily calculated in data
poor situations, they are a good “straw-man” to start testing
indicators for such fisheries in this study.
Biological indicators conted….
Biophysical (Chlorophyll a, temperature, dissolved inorganic nitrogen,
and level of contaminants):
It is critical that a suite of indicators, which are not all highly correlated,
is used;
 Multiple time and space scales are spanned by the data sets.IT is also
critical that data include species that:
 Are directly impacted
 Have high turnover rates, which may provide a noisy but early
warning;
 Define the habitat, as these often have a disproportionate or keystone
role in the system; and are from the upper trophic level, which are
typically both vulnerable in their own right due to their life history
Fisheries Indicators and data sources
Statistical information needed are:
A - TAC, Quotas, by species,
B - Quantity and value of landings, by species
C - Employment (total; full and part-time; male/female; capture
fisheries/aquaculture/ processing industry)
D - Fleet capacity (number of boats, by length or by GT/GRT)
E - Quantity and value of aquaculture production by species,
F - Recreational fisheries (estimates concerning the production
and the number of people involved),
Fisheries Indicators and data sources conted….
Statistical information needed are:
G - Trade in fish and fish products (by main species and main
partners).
H - Government financial transfers relating to the marine capture,
aquaculture and processing sectors.
J - Status of fish stock
In broad terms, the PSR framework to aims to identify the pressure
on the environment from human and economic activities, which
lead to changes in the state or environmental conditions that prevail
as a result of that pressure, and may provoke responses by society
to change the pressures and the state of the environment.
Fisheries Indicators and data sources conted….
Source: “Economic and Social Sustainability Indicators for
Fisheries” study
References
FAO (1999), Indicators for Sustainable Development of Marine
Capture Fisheries, Technical Guidelines for Responsible Fisheries
No. 8, Rome.
Hilborn, R. and C.J. Walters (1992), Quantitative Fisheries Stock
Assessment: Choice, Dynamics and Uncertainty, Chapman and
Hall, New York.
Indicators_of_dynamics_in_fishery_resource_7.ppt

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Indicators_of_dynamics_in_fishery_resource_7.ppt

  • 1. INDICATORS OF DYNAMICS IN FISHERY RESOURCE
  • 2. Indicators of dynamics in fishery resource What are indicators?  Indicators are data or combination of data collected and processes for a clearly defined analytical or policy purpose.  That purpose should be explicitly specified and taken into account when interpreting the value of an indicator.  Fisheries indicators should provide practical and cost-effective means for the evaluation of the state and the development of fisheries systems and the effects that policy changes have on those systems.  In considering the concept of indicators of sustainable development, a necessary first step is to define the sustainable development in the context of fisheries.
  • 3. Indicators of dynamics in fishery resource conted…. What are indicators?  Sustainable development is generally defined as being development that meets the needs of the current generation without compromising the ability of future generations to meet their own needs.  In the fisheries sector, the use of biological indicators in the development of fisheries assessments and management plans has been standard practice, in most OECD countries for many years.  However relatively little attention has paid to the development of economic and social indicators that serve to assess progress on other aspects of sustainable development.
  • 4. Indicators of dynamics in fishery resource conted…. What are indicators?  With respect to criteria for success it has been found, both theoretically and empirically that good indicators are easily measured, cost effective to collect to calculate, and easily interpreted ( to avoid confusion about the state of the system they are reflecting).  Simple indicators are consistently found to out perform more complex (model-dependent) indicators, which were sensitive to data quality.  There is consensus on the need for a suite rather than a single indicator and on the types of indicators that perform well regardless of system types.  These indicators are:
  • 5. Economic and Social Indicators For the indicators to be effective and workable in assessing the economic and social performance of fisheries, they should: Have a clear policy relevance and in particular: A. Provide balanced coverage of some of the key issues of common concern to OECD countries, and reflect changes over time; B. Be easy to interpret (that is, movements in each indicator should have clear link to overall sustainability); C. Allow comparisons across countries; D. Lend themselves to being adapted to different national contexts, analysed at different levels of aggregation and linked to more detailed indicator sets.  Be analytically sound in technical and scientific terms, based on internationally accepted standards and broadly accepted by stakeholders.  Be based on data that are available, of known quality and regularly updated.
  • 6. Economic and Social Indicators conted…. What are indicators used for ?  The main purpose in developing a set of sustainability indicators is to assist in assessing the performance of fisheries policy and management and to stimulate action to better pursue to sustainability objectives.  This can occur in a number of areas. For example, indicators can be used for ex-post evaluations of the impacts of management initiatives; assessment of progress towards medium and/or long-term objectives; and assessment of the impacts of fisheries.  They can also enhance communication, transparency, effectiveness and accountability in fisheries management.
  • 7. Economic and Social Indicators conted…. What are indicators used for ?  In this regard, indicators can be developed and reported at various levels of aggregation- international, national, regional and local levels.  Many of the environmental indicators for fisheries referred to above are focused on the fishery level. Other aggregates that are regularly reported, such as the contribution of fisheries to exports, are reported at a national level.  Yet others relate to fisheries that are managed regionally as straddling and/or highly migratory stocks.
  • 8. Biological indicators Relative biomass:  specifically of gelatinous zooplankton, cephalopods, small pelagic, scanvengers, demersal fish, piscivores, top predators, and biogenic habitat (cover forming species).  Ease of sampling differs strongly between these groups (for instance external bodies, such as NGOs, often monitor the charismatic top predators, tourism can focus attention on coral reef fishes, snapshots of mangrove forests and shallow benthic habitat may be available from satellite images.  It is possible to find proxies for even some of the most difficult groups. For example, changes in relative biomass of gelatinous zooplankton may be captured by frequency of bloom events, as this is a much more easily obtainable statistic due to the ability to generate it from expert information and fisher interviews.
  • 9. Biological indicators conted…. Biomass ratios: The rapidity with which leaving materials can be replaced itself is measured by biomass ratio. In particular the biomass ratios of piscivore: planktivore (PS:ZP), pelagic: demersal (P:D) and infauna: epifauna. The last of these is probably not feasible in data poor situations, but the other two can be done. Size spectra: which give an indication of perturbation in system structure (using the slope of the curve), but can also highlight changes in system productivity (via the intercept). Maximum (or mean) length: This indicator is observed to work in practice even if simple rules of thumb regarding are used. Caution is needed regarding market driven changing in preferred sizes, however.
  • 10. Biological indicators conted…. Total fisheries removals: (catch + bycatch + discards): This indicator considers the total biomass removed from the system versus what is left cycling in the system. While similar in concept to the widely used comparison of primary production vs. removals from the system, there is concern that it will not be suitable for data poor and dispersed small scale fisheries due to the lack of data on removals let alone discards. Diversity: (counts of species): It remains an informative and fundamental piece of information about the system. Alternative measures of diversity or system structure may need to be considered too, depending on which operating model is used or what empirical data is available.
  • 11. Biological indicators conted…. Diversity: (counts of species): One possibility is considering the value of changes in species-area curves (e.g. the slope and asymptote of the curve) through time (or spatially if under a perturbation gradient). It is likely that some simple or ordinal data can be collected on this from the fishers themselves given that they are acutely aware of what they catch. Looking at changes in these ranking could be highly informative. Size at maturity (weight and length): It is a strong means of detecting change in the system and stock structure. It may be too difficult to use in data poor situations.
  • 12. Biological indicators conted…. Biophysical (Chlorophyll a, temperature, dissolved inorganic nitrogen, and level of contaminants): These may be drawn from water quality monitoring programs or remotely sensed data sets, but are needed even if they aren’t already being collected as they are means of teasing out causation. Indicators respond to any system change, including those caused by sectors other than fisheries, so any information that helps elucidate causation is extremely helpful. While all of these indicators are not equally easily calculated in data poor situations, they are a good “straw-man” to start testing indicators for such fisheries in this study.
  • 13. Biological indicators conted…. Biophysical (Chlorophyll a, temperature, dissolved inorganic nitrogen, and level of contaminants): It is critical that a suite of indicators, which are not all highly correlated, is used;  Multiple time and space scales are spanned by the data sets.IT is also critical that data include species that:  Are directly impacted  Have high turnover rates, which may provide a noisy but early warning;  Define the habitat, as these often have a disproportionate or keystone role in the system; and are from the upper trophic level, which are typically both vulnerable in their own right due to their life history
  • 14. Fisheries Indicators and data sources Statistical information needed are: A - TAC, Quotas, by species, B - Quantity and value of landings, by species C - Employment (total; full and part-time; male/female; capture fisheries/aquaculture/ processing industry) D - Fleet capacity (number of boats, by length or by GT/GRT) E - Quantity and value of aquaculture production by species, F - Recreational fisheries (estimates concerning the production and the number of people involved),
  • 15. Fisheries Indicators and data sources conted…. Statistical information needed are: G - Trade in fish and fish products (by main species and main partners). H - Government financial transfers relating to the marine capture, aquaculture and processing sectors. J - Status of fish stock In broad terms, the PSR framework to aims to identify the pressure on the environment from human and economic activities, which lead to changes in the state or environmental conditions that prevail as a result of that pressure, and may provoke responses by society to change the pressures and the state of the environment.
  • 16. Fisheries Indicators and data sources conted…. Source: “Economic and Social Sustainability Indicators for Fisheries” study References FAO (1999), Indicators for Sustainable Development of Marine Capture Fisheries, Technical Guidelines for Responsible Fisheries No. 8, Rome. Hilborn, R. and C.J. Walters (1992), Quantitative Fisheries Stock Assessment: Choice, Dynamics and Uncertainty, Chapman and Hall, New York.