Upload
others
View
2
Download
0
Embed Size (px)
Citation preview
Developing Biological tools 55
p g gin Lake Ohrid according to
the Water Frameworkthe Water Framework Directive
1Lirika KUPE; 2Suzana PATCEVA; 2Tatjana LOSHKOSKA
1 AGRICULTURAL UNIVERSITY OF TIRANA.
2 HYDROBIOLOGICAL INSTITUT OF OHRID
OUTLINE OF THE PRESENTATION
Introduction (Working group and Lake
Ohrid).)
Aims of the study.
Sampling, dynamic frequency
Biological approach based on WFD (Waterg pp (
Framework Directive).
W t l ifi ti b d i EU di tiWater classification based in EU directive.
WFD classification
Results and Discussion
Working Group in Project.
Lake Lake OhridOhrid
Is the deepest lake in
B lkBalkan.
The deepest point is
289 m and the average 289 m and the average
deepness is about 164
meters.meters.
The maximum width
is 14,8 km.,
The maximum length
is 30,8 km.
Station Code of station
Time of sampling
Method of sampling
DoganaTushemisht
AR3D July 2010 Periphyton from stons
P d 2 ANR5PG2 J l 2010 P i h t f
Station Code of station
Time of sampling
Method of sampling
Tushemisht - Drilon
ANR7T July 2011
Periphyton from stones
Pogradec 2 ANR5PG2 July 2010 Periphyton from stones
Udënisht ANR3U July 2010 Periphyton from stons
Piskupat (near the rock)
AR2 July 2010 Periphyton from stones
Pogradeci- Vërdovë
ANR6PG1 July 2011
Periphyton from stones
Mëmëlisht- train station
ANR4M July 2011
Periphyton from stones
the rock) stones
Lini-village ANR1L July 2010 Periphyton from stons
Radozda MRR July 2010 Periphyton from stones
station Piskupat ANR2P July
2011 Periphyton from stones
Cape of Lini
AR1L July 2011
Periphyton from stones
Kalishta MRK July Periphyton from stones
Struga MNRS July 2010 Periphyton from stones
Sateska river MNRSR July 2010 Periphyton from stones
Kalishta MRK July 2011
Periphyton from stones
AutocampAs
MNRA July 2011
Periphyton from stones
Koselska MNRK July 2011
Periphyton from stones
Grashnica MNRG July 2010 Periphyton from stones
Ohrid bay MNRZ July 2010 Periphyton from stones
H.Metropol MNRM July 2010 Periphyton from
2011 stonesBlato MNRB July
2011 Periphyton from stones
Rachanska
MNRRR July 2011
Periphyton from stones
Pestani MNRP July Periphyton from p y p ystones
Hotel Park MRP July 2010 Periphyton from stones
Velidab MRV July 2010 Periphyton from stones
Pestani MNRP July 2011
Periphyton from stones
Sv.Zaum MRZ July 2011
Periphyton from stones
Veljapesh MRVL July 2011
Periphyton from stonesTrpejca MNRT-
non reference
July 2010 Periphyton from stones
Cherava river MNRCR July 2010 Periphyton from stones
2011 stonesTrpejca MRT-
referenceJuly 2011
Periphyton from stones
Sv.Naum MNRSN July 2011
Periphyton from stones
LINI (Ohrid Lake)
Udenisht
Memelisht
Aims of StudyAims of StudyKnowledge of the diatom algae insediments of Lake Ohrid.
Evaluation of Lake Ohrid Biodiversity.
Calculation of the trophic and saprobicindexindex.
Human impact in Lake Ohrid during thep glast years.
Data processing based on ENSISprogram.
FIELD SAMPLING IN LAKE OHRID DURING 2010
Dogana Tushemisht (AR3D)Pogradec 2 (ANR5PG2)
Samples were collected only at 0.5m depth.
Udënisht (ANR3U)Piskupat (near the rock)(AR2)
Lini-village (ANR1L)
0.5m depth.
Samples were collected in 15 collected in 15 localities (5 localities in
Tushemisht - Drilon (ANR7T)
Albanian part and 10 localities in Macedonian
Radozda (MRR); Struga (MNRS)Sateska river (MNRSR); Grashnica (MNRG)Ohrid bay (MNRZ); Hotel Metropol (MNRM)( )Pogradeci- Vërdovë (ANR6PG1)
Mëmëlisht- train station (ANR4M) Piskupat (ANR2P)
Macedonian part).
Samples were
Hotel Park (MRP); Velidab (MRV)Trpejca (MNRT-non reference); Cherava river (MNRCR)
Cape of Lini (AR1L) Samples were collected one time per year.
FIELD SAMPLING IN LAKE OHRID DURING 2011
Samples were
Dogana Tushemisht (ANR3D)Pogradec 2 (ANR5PG2)
Tushemisht - Drilon (ANR7T)Pogradeci- Vërdovë (ANR6PG1)
Mëmëlisht- train station (ANR4M)
collected only at 0.5m depth.
Udënisht (ANR3U)Piskupat (near the rock)(ANR2)
Lini-village (ANR1L)
Piskupat (ANR2P) Cape of Lini (AR1L) Samples were
collected in 15 localities (5 localities (5 localities in Albanian part
Kalishta (MRK); Autocamp As (MNRA) Koselska river (MNRK); Blato (MNRB)Rachanska river (MNRRR); Pestani ( )
and 10 localities in Macedonian (MNRP)
Sv.Zaum (MRZ); Veljapesh (MRVL); Trpejca (MRT-reference)St N (MNRSN)
Macedonian part).
Samples were St.Naum (MNRSN) Samples were collected one time per year.
Monitoring of fresh water with diatoms is based in two standards:
1. Standard EN 13946:2003, Water quality - Guidance standard
for the routine sampling and pre-treatment of benthic diatoms
from rivers. Establishes a method for the sampling and
laboratory preparation of benthic diatoms for water quality
assessments. Data produced by this method are suitable for
production of water quality indices based on the relativeproduction of water quality indices based on the relative
abundance of taxa. With appropriate modifications the method
can be applied to the study of benthic diatoms in lakes.
Monitoring of fresh water with diatoms is based in two standards:
2. Standard EN 14407:2004 Water quality. Guidance
standard for the identification, enumeration and
interpretation of benthic diatom samples from running
t Thi t d d t f id tifi ti dwaters. This standard covers aspects of identification and
enumeration of the relative abundance of diatom taxa on
prepared slides and of data interpretation relevant to
assessment of water quality.assessment of water quality.
BIOLOGICAL APPROACH
C ll t d i h ti i i l (Di t )Collected epiphytic microscopic algae (Diatoms).
Cleaning of diatom frustules: boiling with HClcc and g gH2SO4cc (Krammer & Lange-Bertalot, 1986-1991)
Microscopic slides: using Naphrax (index 1 71)Microscopic slides: using Naphrax (index 1.71)
Observed in an optic microscope, using 40X and 63X bj tiobjectives.
Determinations: Krammer & Lange-Bertalot (1986-1991) keys.
More than 400 valves were counted (with confidenceMore than 400 valves were counted (with confidence 95 %)
ECOLOGY OF WATERECOLOGY OF WATER
n
Diversity index: Shannon &Weaver (1949)
n
iii ppH
12
' log
C l l t T hi di t Id B d i R tt t l 1997
ii
n
i HGTW
Calculate Trophic diatom Idex: Based in Rott et al., 1997
n
iii
iDIA
HGTI
1
1 Is in correlation with inorganic matter in water
n
HGS
Calculate Saprobic Index: Based in Rott et al., 1999
n
iii
iii
i
HG
HGSSI
1
1 Is in correlation with organic matter in water
Trophic value
Trophic class
Concentration of total phosphorus (mg/l)Mean year Extrem
valueCorrelation between Trophic value
WATER CLASSIFICATION
≤ 1,0 ultraoligotroph
< 0,005 < 0,010
1,1 -1,3 oligotroph < 0,010 < 0,020
1 4 1 5 li 0 010 0 050
Correlation between Trophic value, Trophic class and concentration of total phosphorus, by Rott at al. 1997
1,4 - 1,5 oligo-mesotroph
0,010 -0,020
< 0,050
1,6 - 1,8 mesotroph < 0,030 < 0,100
1,9 - 2,2 meso- 0,030 - < 0,150
Saprobic value
Saprobic class
, ,eutroph
,0,050
,
2,3 - 2,6 eutroph 0,030 -0,100
< 0,250
2,7 - 3,1 eu- > 0,100 > 0,650
1,0 - <1,5 oligosaprob
1,5 - <1,8 Oligosaprob to-mesosaprob2,7 3,1 eu
polytroph> 0,100 > 0,650
3,2 - 3,4 polytroph 0,250 -0,650
> 0,650
> 3 4 poly > 0 650 > 0 650
1,8 - <2,3 -mesosaprob
2,3 -<2,7 -mesosaprob to-mesosaprob> 3,4 poly-
hypertroph> 0,650 > 0,650 -mesosaprob
2,7 - <3,2 -mesosaprob
3,2 - <3,5 -mesosaprob toCorrelation between Saprobic value and polisaprob
3,5 - <4,0 polisaprob
Correlation between Saprobic value and Saprobic class, by Rott at al. 1999
RESULTS AND DISCUSSIONLake Ohrid represents a unique ecosystem from
diatoms.
Most of the species in Ohrid Lake areMost of the species in Ohrid Lake areOLIGOTROPHIC like as :Gomphonemalateripuncatatum, Diploneis ovalis, Nitzschiadenticula, Achnanthes minutissima, Cymbellamicrocephala, Navicula cryptotenella,Nit hi t t G hNitzschia angustata, Gomphonematruncatum, G. parvulum, G.intricatumvar pumilum Fragilaria capucina Fragilariavar.pumilum, Fragilaria capucina, Fragilariavirescens, F. bicapitata, etc. This specieswere widespread in: Cape of Lini (AR1L),p p ( ),Dogana-Tushemisht (AR3D), Hotel Park(MRP),St.Zaum (MRZ), Radozda (MRR).
RESULTS AND DISCUSSION
Other species of highest vitality in strongerMESOTROPHIC TO EUTROPHIC waters wereobserved, like: Amphora pediculus, Cocconeispediculus, Cymbella minuta, Diatoma vulgaris var.vulgaris Epithemia adnata E sorex Gomphonemavulgaris, Epithemia adnata, E. sorex, Gomphonemapumilum, G. olivaceum, Gyrosigma accuminatum, N.menisculus var. grunowii, Navicula reinhardtii,Nit hi di i tNitzschia dissipata.
Rhoicosphaenia abbreviata etc., were found inp ,Piskupat near the rock (AR2) , Udenisht (ANR3U ),Piskupat (ANR2P ), Memelisht (ANR4M ), Ohrid bay(MNRZ ) Peshtani (MNRP ) Kalishta (MRK )(MNRZ ), Peshtani (MNRP ), Kalishta (MRK ).
RESULTS AND DISCUSSION
Despite some Poly-hypertrophicspecies of diatoms like as: Amphoraspecies of diatoms like as: Amphoralybica, Cymatopleura solea, Fragilariaulna Gomphonema parvulum Nitzchiaulna, Gomphonema parvulum, Nitzchiapalea, etc. have been observed inepiphytes samples of Lini villageepiphytes samples of Lini-village(ANR1L), Grashnica (MNRG), and rarelyin Pogradeci town (ANR5PG2) in Lakein Pogradeci-town (ANR5PG2) in LakeOhrid but there were not morewidespreadwidespread.
1- Cyclotella ocellata; 2-Stephanodiscus hantzchii .3-M l i i 4Melosira varians 4-Diatoma vulgaris 5-Cocconeis placentula 6-Fragilaria capucina Fragilaria capucina var. vauscheria 7-Cocconeis pediculus; 8-Cymbella microcephala; 9-Cymbella minuta; 10- Amphora inariensis ; 11-Navicula Navicula menisculus; 12-Gomphonema olivaceum; 14-Gomphonema truncatum; 15-Amphora lybicia; 16- Nitzschia palea; 17- Gomphonema tergestinum; 18-tergestinum; 18-Navicula cryptotenella
The most widespread Centric DiatomsDiatoms
16.8
12.6
14.0
15.4
8.4
9.8
11.2
4.2
5.6
7.0
Cyclotella ocellata
0.0
1.4
2.8
Melosira varians
Pograd
ec
Dog
ana
Ude
nish
t
Piskup
at Lin
Rado
zda
Struga
Sateska river
Grash
nica
Ohrid bay
H.M
etropo
l
Hotel Park
Velidab
Trpe
jca
Che
rava river
C l t ll ll t thCyclotella ocellata were the most widespread species in Lake Ohrid .
The most widespread Pennat DiatomsDiatoms
27.328.329.330.331.3
Cocconeispediculus
21.322.323.324.325.326.327.3
Fragilariavirescens
14 315.316.317.318.319.320.3
Amphora
Cymatopleura soela
Cymbella minuta
8.39.310.311.312.313.314.3 Amphora
ovalis
Fragilaria capucina
Navicula radiosa
Cymbella elogenisis
1 32.33.34.35.36.37.3
Roicosphaeniaabbreviata
Gomphonema olivaceumEpithemia adnata
G transsylvanicum
0.31.3 G. transsylvanicum
Number of species during July 2010
The poorest stations in species were: Udënishti, Lini-village, Velidab, Trpejca.
The high number of species were found in Sateska river (more over 40 species), Grashnica, Radozda, Cherava river, Dogana etc.
Velidab
Trpejca
Cherava river
Grashnica
Ohrid bay
H.Metropol
Hotel Park
Radozda
Struga
Sateska river
Grashnica
Dogana (Tushemisht)
Udenisht
Piskupat (Rock)
Lin
0 5 10 15 20 25 30 35 40 45
Pogradec 2
Number of species,N: 500
Diversity Index during July 2010Higher diversity values were observed in Pogradeci 2, Sateska river (about 1.30),Grashnica, Trpejca, Cherava river, Hotel park, Struga, etc.
Low values of Diversity index (H') were the result of a small number of genera anda high abundance of a few common species. Which were observed in: Ohrid bay(under 1.00), Udenisht, Velidab etc.
Cherava river
Oh id b
H.Metropol
Hotel Park
Velidab
Trpejca
Radozda
Struga
Sateska river
Grashnica
Ohrid bay
Dogana
Udenisht
Piskupat
Lin
Radozda
0.00 0.20 0.40 0.60 0.80 1.00 1.20 1.40
Pogradec 2
Diversity index, H':
Number of species during July 2011
The poorest stations in species were: Peshtani, Tushemishti, St. Zaum, Lini, etc.
The high number of species were found in: Auto camp As (More over 40 species), Rachanska river, Koselska river, Kalishta, Blato, Pogradec 1, Piskupat (near the rock), Memelisht, St. Naum and Trpejca.
Trpejca
St. Naum
Rachanska river
Pestani
St. Zaum
Veljapesh
p j
Kalishta
As
Koselska river
Blato
Piskupat
Tushemisht (Dogana)
Memelisht (Train station)
Cape of Lini
0 5 10 15 20 25 30 35 40 45
Pogradec 1 (Verdove)
Number of species,N: 500
Diversity Index during July 2011
Higher diversity values were observed in Rachanska, As, Koselska (about 1.40),Veljapesh, St. Naum, Trpejca, Pogradec 1, Tushemisht, Memelisht (about 1.30).
Low values of Diversity index (H') were the result of a small number of genera and aLow values of Diversity index (H ) were the result of a small number of genera and ahigh abundance of a few common species. Which were observed in: Blato and St. Zaum(about 1.00).
St. Naum
Pestani
St. Zaum
Veljapesh
Trpejca
As
Koselska river
Blato
Rachanska river
Tushemisht (Dogana)
Memelisht (Train …
Cape of Lini
Kalishta
0.00 0.20 0.40 0.60 0.80 1.00 1.20 1.40
Pogradec 1 (Verdove)
Piskupat
Diversity index, H':
TIDIA in Ohrid Lake during 2010The water qulaity in Ohrid Lake, based in TIDIA: Trophic value ranged from oligo-mesotrophicq y , p g g pto eutrophic. Dogana (1.5), Udenishti (1.7) and Velidab (1.8) ranged from oligo-mesotrophic tomesotrophic. More of station ranged from mesotrophic to meso-eutrophic. Only Lini-village, Grashnica and Ohrid bay ranged from mesotrophic to eutrophic.
2 5
3.02.7 2.7
2.4
Eutroph
2.0
2.5 2.3
1.7
1.9 1.9
2.1
2.0
4
2.02.1
1.8
2.2 2.2
Mesotroph
Meso-eutroph
1.0
1.51.5
Oligotroph
Oligo-mesotroph
0.5
TIDIA (2010)
TIDIA in Ohrid Lake during 2011
The water quality in Ohrid lake, based in TIDIA, trophic value ranged from oligo-mesotrophicq y , , p g g pto eutrophic. St. Zaum (1.5), Piskupati (1.8) and Tushemishti (1.8) ranged from oligo-mesotrophic to mesotrophic. More of station renged from mesotrophic to meso-eutrophic.Only Rachanska (2.6) Pogradeci town and St. Naum ranged from mesotrophic to eutrophic.
2 5
3.0
2.62.5
Eutroph
2.0
2.5 2.3
1.8 1.8
2.12.3 2.3 2.3
2.1 2.22.3
1 5
2.12.2
Mesotroph
Meso-eutroph
1.0
1.51.5
Oligotroph
Oligo-mesotroph
0.5
TIDIA (2011)
Saprobic Index during 2010
The water quality in Ohrid Lake based on SI, were classified from Oligosaprobic (HotelP k d D ) t Oli bi (R d d Pi k t S t k i H t lPark and Dogana) to Oligo - - mesosaprobic (Radozda, Piskupat, Sateska river, HotelMetropol, Velidab and Trpejca). Only Pogradec 2, Hudenisht, Piskupat, Grashnica andOhrid Bay were classified from Oligo-β-mesosaprobic to -mesosaprobic, which show aslightly pollution.
mesosaprob (1 8 2 3)
1.9
2.0
Oli b
-mesosaprob (1.8-2.3)
1 5
1.6
1.7
1.8
Oli b (1 1 5)
Oligo--mesosaprob (1.5-1.8)
1.2
1.3
1.4
1.5 Oligosaprob (1 – 1.5)
1.0
1.1
SI (2010)
Saprobic Index during 2011The water quality Ohrid Lake based in SI, was classified from Oligosaprobic(St. Zaum approximately 1.4) to Oligo - - mesosaprobic (Cape ofLini, Veljapesh, Trpejca, St. Naum) and other station ranged from Oligo--mesosaprobic to -mesosaprobic.
-mesosaprob (1.8-2.3)
1 7
1.9
2.1
Oligosaprob- mesosaprob1.5-1.8)
1.3
1.5
1.7
Oligosaprob (1-1.5)
0.7
0.9
1.1
0.5
SI (2011)
Data processing based in ENSIS program - (TIDIA).
Value of Trophic Index Trophic Classes
≤ 1,0 ultraoligotroph
1,1 -1,3 oligotroph, , g p
1,4 - 1,5 oligo-mesotroph1,6 - 1,8 mesotroph
1,9 - 2,2 meso-eutroph2 3 2 6 e troph2,3 - 2,6 eutroph
2,7 - 3,1 eu-polytroph3,2 - 3,4 polytroph
> 3,4 poly-hypertroph, p y yp p
2 sampling sites wereoligo-mesotroph.4 sampling sites were
t hmeso-troph.13 sampling sites weremeso-eutroph.9 sampling sites were
t heutroph.2 sampling sites were eu-politroph.
Data processing based in ENSIS program - SI
Value of SI Saprobic Classes
1,0 - <1,5 oligosaprob
1,5 - <1,8 Oligosaprob - βmesosaprob
1,8 - <2,3 β mesosaprob
2,3 -<2,7 β mesosaprob -αmesosaprob1 sampling sites were
Oligosaprob.
2,7 - <3,2 α mesosaprob
3,2 - <3,5 α mesosaprob -li b
10 sampling sites were Oligo--mesosaprob.
polisaprob19 sapmling sites were -mesosaprob.
Data processing based in ENSIS program - SI
Nitzchia palea is pthe most abundant species in the locality of Grasnica.
Fragilariai i th virescens is the
most abundant species in the localities Park andlocalities Park andSt. Zaum.
The total The total Phosphorous is the highest in the locality of OhridBay.
CONCLUSION
Littoral habitats in Lake Ohrid belonging toan environment oligotrophic or mesotrophican environment oligotrophic or mesotrophicrepresented by species such as: Cyclotellaocellata, Achnanthes minutissima and A.,biasolettiana, Fragilaria capucina,Gomphonema pumilum, G. olivaceum, etc.Al h th i th t d i tAlso has other species that dominateeutrophic habitats such as: Amphorapediculus Cocconeis pediculus Cymbellapediculus, Cocconeis pediculus, Cymbellaminuta, Gomphonema minutum, Nitzschiadissipata, but there were not morep ,widespread in all sampling sites.
CONCLUSION
Trophic diatom index ranged from 1.5 (mesotrophic)in Dogana (AR3D), Udënishti (ANR3U), St. Zaum(MRZ) to 2.7 (eupolitroph) in Lini-village (ANR1L) andGrashnica (MNRG).
Saprobic index ranged from 1.4 (oligosaprobic) and1.6 (oligo- β-mesosaprobic), in St. Zaum (MRZ),Dogana (AR3D) Cape of Lini (AR1L); to 2 0 or 2 1 (βDogana (AR3D), Cape of Lini (AR1L); to 2.0 or 2.1 (β-mesosaprobic), in Lini-village (ANR1L).
The water of Lake Ohrid near Pogradeci town andGrashnica were dominated by Amphora lybica,Cymatopleura solea, Fragilaria ulna, Naviculay p , g ,cuspidata, Nitzschia palea, Gophonema parvulum(which considered as Polytrophic species).
CONCLUSION
Composition of diatoms show a slightelypollution with organic matter (oligo-β-mesosaprobic to β-mesosaprobic) and moderatemesosaprobic to β mesosaprobic) and moderatepolluted with inorganic matter (mesotrophic),exception of Lini-village and Grashnica is verypolluted (polytrophic)polluted (polytrophic).
As above, in all sampling stations nutrients werelower than the EC guide values for surface water.High values of nutrients were measured in Lini-village (ANR1L) and Pogradeci town nearvillage (ANR1L) and Pogradeci town nearEnkeleana Hotel (ANR6PG1).
The diatom index has an advantage of a shortThe diatom index has an advantage of a short-term indicator and furthermore, the samples canbe easily collected compare with other analyses.
ACKNOWLEDGEMENTS
In occasion, we express our
gratitude especially to thanks thegratitude especially to thanks the
Norwegian Ministry of ForeignNorwegian Ministry of Foreign
Affairs for financial support.
THANK YOU!THANK YOU!БЛАГОДАРАМ!БЛАГОДАРАМ!FALEMINDERIT!FALEMINDERIT!