Transcript Slide 1

Fishes in Lakes Prespa and Ohrid
Threats and Conservation needs
Spase Shumka
Agricultural University of Tirana
[email protected]
Based on field surveys and observations on fishery and plankton, monitoring
data available, examining the extensive published record, conducting
interviews, we aim to:
1. assess threats to Lakes Ohrid and Prespa (endemic) biodiversity, in terms of
fishes.
2. summarize existing conservation activities and strategies, and
3. outline future conservation needs for Lakes Ohrid and Prespa in light of
national commitments to EU and other international binding documents and
species conservation.
In case of lakes Ohrid and Prespa, the species conservation cannot be achieved
without an integrated approach!
To that fact the fish’s conservation is an ecosystem approach rather than a species
oriented plan.
The threat assessment carried for this presenation is based on the guidelines provided by
both the International Union for Conservation of Nature (IUCN)
and the Global International Waters Assessment (GIWA). IUCN threat classes were
used, which 5 are primarily designed to assess key threats to species. They involve
past, ongoing and future threats, using a time frame of three generations or ten years,
whichever is the longer (not exceeding 100 years in the future) as required by the
Red List Criteria (IUCN Standards and Petitions Subcommittee, 2010). Environmental
impacts were assessed using the scoring scheme provided by GIWA, which is more
10 ecosystem oriented. Four impact scores ranging from 0 (no known impact) through
1 (slight impact), 2 (moderate impact) to 3 (severe impact) were used to quantify the
importance of each key issue.
Details on determining impact scores can be found in the GIWA Methodology handbook
for scaling and scoping (GIWA, 2001).
Conservation areas in the transboundary Ohrid
Prespa lakes region
Threat class
1. Households/Commercial
2. Agriculture/aquaculture
3. Energy production/mining
4. Transport/service corridors
5.Biological resources use
6. Human intrusion/disturbance
7. Natural system modifications
8. Invasive/other problematic species,
genes
9. Pollution
10. Geological events
11. Climate changes/severe weather
Key threat
1.1. Housing and urban araes
1.2. Commersial/industry
1.3. Tourism/recreation
2.1. Annual perrenials
2.2. Wood / pulp planrtaions
2.3. Livestock/Framing
2.4. Aquaculture
3.1.Oils/Gass
3.2. Mining/Quarrying
3.3. Renewable energy
4.1. Roads/railwayas
4.2.Utility/services
4.3.Shiping lines
4.4. Flight paths
5.1. Hunting/trapping tererstrial animals
5.2.Gathering terestrial plants
5.3. Logging/wood harvesting
5.4.Fishing/harvesting aquaric resources
6.1. Recreational activities
6.2. War, civil unrest/military excersises
6.3. Work and other activities
7.1. Dams/water management/use
7.2.Fire/fire supression
7.3. Other ecosystem modifications
8.1. Non native species
8.2. Problematic native species
Introduced genetical material
9.1. Domestic and urban pollution
9.2. Industrial/military effluents
9.3.Grabage/solid waste
9.4. Air-borne pollutants
9.5. Agriculture forestry effluents
9.6. Exces energy
10.1. Volcanous
10.2.earthquarks/tsunamis
10.3. Avallanches/lanslides
11.1. Habitat shifting/alteration
11.2. Droughts
11.3. Temperature extreme
Impact Ohrid
3
2
3
2
1
1
3
0
3
0
3
0
0
0
3
2
3
3
3
0
1
0
2
3
0
0
2
3
3
3
1
3
0
0
0
0
3
3
2
Mean impact Impact Prespa Mean impact
3 (2.66)
2
2
0
1
2 (1.75)
2
2
1
3
0
3
0
2
2
0
3
0
2
2
0
0
3 (2.75)
2
2 (2.25)
1
3
3
2
2
2
0
1
2.5
1
2.5
2
2
2
3 (2.6)
0
0
0
2 (2.25)
2
0
2
3
0
3
0
3
0
0
0
0
2
3
2
3
0
0
0
2 (2.33)
The common general threats to environment of the project area are as follows:
•Unsustainable use of natural resources, including all resources;
•Unsustainable management of forests and illegal logging;
•Practices of tree lopping, overgrazing;
•Inadequate river basin management affecting aquatic ecosystems,
•Loss, degradation and fragmentation of habitats due to urbanization and land development,
•Loss of native plant and animal species, both wild species and traditional breeds,
•Introduction of alien invasive species of flora and fauna into ecological system,
•Pressure of tourism on biodiversity of the mountain, coastal and marine ecosystems,
•Pollution of the environment by industrial and agricultural pollutants, and municipal waste,
•Insufficient law enforcement, in particular in physical planning and preventing illegal activities
threatening the state of environment and integrity of nature.
Ohrid
Origin
No.
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
26
27
28
29
30
31
32
33
34
35
36
37
38
39
Species
Anguilla anguilla*
Alburnoides prespensis
Alburnoides ohridanus
Alburnus belvica
Alburnus scoranza
Barbus prespensis
Barbus rebeli
Carassius gibelio
Chondrostoma prspense
Chondrostoma ohridanus
Cobitis meridionalis
Cobitis ohridana
Barbatula sturany
Cyprinus carpio
Gobio ohridanus
Ctenopharyngodon idella
Pachychilon pictum
Gambusia holbrooki
Hypophthalmichthys militrix
Lepomis gibbous
Pelasgus prespensis
Pelasgus minutus
Phoxinus limarieus
Pseudorasbora parva
Rhodeus amarus
Rutilus prespensis
Rutilus ohridanus
Salmo afelios
Salmo balkanicus
Salmo letnica
Salmo lumi
Salmo ohridanus
Salmo peristericus
Scardinus knezevici
Silurus glanis
Squalius prespensis
Squalius squalius
Tinca tinca
Telestes montenegrinus
Native
Lake
Prespa Lake
Origin
Native
Native
Native
Native
Native
Native
Native
Nonantive
Native
Native
Native
Native
Native
Nonnative
Native
Nonnative
IUCN
List
CR
VU
VU
CR
LC
VU
LC
Observed in
Berne
Albanian Albanian part
red Convention Red List of Lakes first
Annex
2007
time
Last 1996
LRcd
1973
VU
LC
VU
LC
LC
DD
VU
&
LRlc
Nonnative
Native
Nonnative
Nonnative
Nonnative
Native
Native
Native
Nonnative
Nonnative
Native
Native
Native
Native
Native
Native
Nonnative
Nonnative
Native
Nonnative
Native
Nonnative
Native
Native
Nonnative
Native
1979
LC
LRlc
2006
1979
1996
EN
DD
LC
VU
LC
LC
EN
DD
DD
DD
VU
EN
VU
LC
LC
LC
LC
1998
1992
VU
&
1982
1996
Last 1996
The species categories in Micro Prespa lake
Species composition in the stock catched
The differences among catches in Albania and Greece
The % fishes in catch at Macro Prespa
The mean CPUE for Macro Prespa lake
Prespa lake: The fish stock/h/m2/net
Matrix demand for Macro Prespa Lake to fulfill the EU WFD (S.Shumka, 2010)
What is needed in the current state?
(i) Additional elements ‘remediation’s’ in all lakes of concern;
(ii) Reduction of fertilizers/manures in all sides of littoral countries;
(iii) Small scale facility of water treatment in case of rural areas and high cost
when comes to apply the commercial treatments;
(iv) Habitat restoration;
(v) Cooperating with neighbors in Water Management practices and
vi) Respect ESPO convention in case of transboundary water bodies.