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Acta

Agrophysica,

2002, 229-235

SOME

ABIOTIC AND BIOTIC

FACTORS or

THE

SIX

LAKES

OF ŁĘCZNA-WŁODAWA

LAKELAND

(LUBLIN

POLESIE REGION)

IN

SUMMER PERIOD

A. Pasztaleniec, R. Mencfel

Department ofBolany and Hydrobiology, Catholic University

or

Lublin C.K. Norwid 4 str., 20·061 Lublin, Poland, e-mail: paszta@kul.lublin.pl

A b s I r a c t. Studics were carried out in six lakes locatcd within the Lęcz-oa-Wlodawa Lakeland (the Zagłębocze. the Czarne near SosIlowica, the Głębokie near Uscimów, fhe Rotczc, the

Sumin and the Długie) during the 5ummcr season (from Junc to August)

or

2001. Thcy involved

physico-chemical parameters (water transparency, conductivity, pH, oxygen saturation, tola1 phos-phorus and nitrogcn) and also biological ones (chlorophyll-a cOJlccntration, phytoplankton abundancc and structurc, lake ;nlo accounl domin:mt species and domination of higher taxa). Physical and ehemieal

faetors and the phytoplankton composilion of lakes usually confinn their trophie charaeter. The mesotro-phic Zaglęboeze lake was eharaclerised by a high Secchi dise (SD), low abundanee of phytoplankton and chlorophyłl-a valucs typieal of a low trophic status. Physieal and chemical walcr characteristics and ovcr 90010 domination of blue-green algae showed high trophy of the Czame lake near Sosnowica. In the shal-low, eutrophie lakes: the Rotcze, the Sumin and in the dystrophie the Długie lake high abundanee of phy-toplankton and ehlorophyll-a eoncentralion was also high diversity of species, was recorded. Stability ol'

characler ofthese lakcs was thus confinned. lllC highest concentration of nutrients and chlorophyll-a and high abundanec ofphytoplankton with law SD was recordcd in (he Głębokie lake near Uśeimów.

K e y wo r d s: lakes, summer physieal and chemieal factors, phytoplankton, biodiversity, the Lęezna-Włodawa Lakeland, Ihe Polesie Lubelskie Region

lNTRODUCTION

A hydrobiologieal eharaeteristic of lakes includcs physical, chemical and

bio-log

i

cal parameters.

The

basic, factors analysed

were

:

water transpareney as

mea-su red

by

a

Secchi dise

(SD), pH, conductivity and oxygen saturation in

the

water

eolumn. An important element

in the lakes deseription

is concentration of nutr

i

ents,

necessary

for the phy topIan kto n

growth.

Phosphoru

s

and nitrogen are such

ele-ments, They usually limit the

growth of algae and macrophytes.

In the natura l

l

akes ecosystems, a

l

gae are the producers in deep water. An assessment ofthe

lake

(2)

230 A. PASZTALENIEC, R. MENCFEL

trophic

status takes into account an abundance of summer phytoplankton and

espe-cially the structure of dominant species and domination of

higher

taxa. Another

biological

factor is concentration of chlorophyll-a

in

the water.

Chlorophyll-a

is

the

most

important photosynthetic

pigment

in the cells of ali groups of algae and

its

concentration can indieate phytoplankton biomass.

The

aim ofthe present work was to present a quantitative and qualitative

struc-ture of

the

planktonic algae

in

some ch os en lakes situated

in

the

Łęczna-

Wlodawa

Lakeland

again

st

the background ofphysical and ehemical factors.

STUDY AREA AND METHODS

Six

lakes located

within the

Łęezna-Wlodawa

Lakeland (Lublin Polesie

Re-gion) were seleeted for

the

present study: deep

lakes

-

the

Zaglęboeze

and the

Czarne

near

Sosnowica (n/S), and shallow

lakes

-

the

Glębokie near Uśeimów

(n/U), the

Roteze,

the Sumin and the

Dlugie

(Fig. I). The area and

depth

of the

lakes studied are

given

in Table l, together with their trophic cha rac

ter

[5].

The physico-chemical and biological factors were studied during the

summer

period

from

Jun

e to

August in 200

I,

once a

month.

The

results

presented

in

this

work are arithmetic averages of these three

measurements.

Sampling for analyses

was carried out

in

the pelagie zone. A sampler of

the

Ruttner type with a capacity

of 2

dm

3

was used. Water from the stratified

lakes

was sam pled as a colleetive

sample

from three

depths in the epilimnion

layer. Water

of

the

shallow

lakes

was

taken from a depth of about

I m.

Conduetivity and pH we re

measured

using

a

(3)

ABIOTIC AND BIOTIC FACTORS

or

THE SIX LAKES 231 T a b I e l. Morphologicaland trophie characteristics oflhe lakes according to Radwan and Komijó\V (5]

L.ke Surface area (ha) Maximum depth Trophic status (m)

the Zagłębocze 84.7 25.0 mesotrophic

the Czame near Sosnowica 38.8 15.6 eutrophic

the Głębokie near Uścimów 20.5 7.1 eutrophic

the Rolcze 42.7 4.3 eutrophic

the Sumin 91.5 6.5 eutrophic

the Długie 28.4 1.3 dystrophic

cond

uctivity

meter and pH-meter

,

respectively. At the

same

time,

visibi

lit

y

was

meas

ured

in wat er using a Secchi disc. Mea

s

urement

s

of oxygenation were

made

at

depth intervals

of

one meter

with an aid or a

WTW

OX

I

96

oxymeter. Chem

i

cal

wate

r analyses was carried

out according

to

s

tandard

methods

de

scr

ibed

by

H

er-manowicz [I]

.

Analyses or chlorophyll-a always began on the day

or sample collection,

1-2

dm

3

of water was filtered through

a

Whatman GF

/C g

lass

-

fibre filter

and

the

residue

was

then

homogenized and

extracted

wi

th boiling

90% ethanol

[4].

Meas-urements of light absorption at the

wavelengths or 665 and

750

nm were carried

out with a

Beckman DU 640B

spectrophotometer. The

final

concentration of chlo

-rophyll-a

p

e

r

dm

3

of

water

was calculated using

a

Lor

e

n

z

form

ula

[8].

The

number of phytop

l

ankton was determined wit h

an

inverted microscope by

Uter-m6

hl

method. Species diversity was

ca

l

culated on

the

basis of

a

num ber of

"indi-vi

duals" according to an

equations

b

y

Shannon

and

Weaver

[7] w

ith

logarithm

of

the

2

(H')

base and a Lloyd and Ghelardi

[3]

-

index

of eveness (e).

RESULTS

The

lakes

studied varied in respect

of

the parameters

analysed.

The

thermal-oxygen

stratification was formed durin

g

the

summer season

in the deep

,

dimictic

th

e

Zagłębocze

lake

and

the Czarne lake near

Sosnowica and also

in

the shallow

the

Glębokie

lake

.

The

waters

of these lak

es

showed oxygen depletion

in the

hy-polim

nion

.

Other lakes were well

oxygenized in

the

whole water column (Tab

l

e

2).

Phys

i

ca

l

parameters

showed similar

i

t

i

es

in term

s

of pH and conductivity,

pH

was

al

k

al

ine

(from 8.4

to 9.2) and the level

of

mineralization

was

low (conductivity

values

varied from

154

to 469

JlS

cm-I).

The Secchi disk visibilit

y

was varied

in

the individual

l

akes,

in direct relation

to

biological

factors,

mainl

y

phytoplankton

(4)

232 A. PASZTALENTEC, R. MENCFEL

T a b I c 2. Physico-chemical factors in the water ofthe lakes studied

Lakes

Physico-chemical the Zaglę- the Czarne the Glę- the Rotczc the Sum in the Długie factors bocze n/S bokie n/U

SD (m) 3.2 0.7 0.6 1.9 0.9 0.9 pH 8.4 9.2 9.0 9.0 8.7 9.2 Conductivity (~S cm") 282 470 348 188 413 154 02 (%) surface 102 132 108 120 114 127 02 (%) hypolimnion 3.3 0.7 0.7 112 95 127 Ntol (J-lg dm -3) 460 997 1443 1175 809 123 PIOI (~lg dm -3} 107 197 202 65 67 76

Zaglęboeze

l

a

k

e

,

at the same

time

,

a

low

num ber of algae

plankton

oeeurred

(be-low

400

indiv. '10

3

dm-

3)

and the lowe

s

t

ehlorophyll-a

eoncentration (in

the

epilimnion water 8.5

~g

dm-

3)

on

ave

ra

g

e

.

The remaining

chlorophyll-a

concen-tration below

10

~g

dm-

3

is

charaeteristie of

deep, dimictie lakes

in

other region

s

of

Poland

[2].

In

spite

ofthe low

phytoplankton abundance great speeies

diver

si

t

y

(as expressed

b

y

a

Shannon

-

We

ave

r index)

and

its

evenness was

found

(Table 3).

The

seco

nd lake in

size

-

the Czarne near Sosnowica, was characterized

b

y

different

values of

the parameters

studied. Visibility of

0.7

m only,

very

high

abundance of

algae in the pelagial layer

(23

.

95

indiv

..

10

6

dm

-3)

and high values

of

chlorophyll-a

(50

~g

dm -3) were observed. The lotal amount of phosphorus in

Ihe

surfaee

water was

197

~g

dm-

3

Aeeording to

Zdanowski

[10],

such

high

va-lues

of

phosphorus

are

typieal of high trophy in lakes. High fertility was

con

-firmed by the phytoplankton

struelure

dominated

by

filamentous blue-green

T a b I c 3. Mean numbers (N) of phytoplankton and chlorophyl1-a concentration (ChI), mean values or

Diversity Indcx (H') and Evenness (e) ofphytoplankton and dominated spccies in the lakes studied

N ChI Percen

-Lakes N 103 dm-3 (J.tgdm-3) e li' Dominaled species tage of

dom

ina-tion

Ihe Zagłębocze 379.1 8.5 0.7 2.6 Gomphosphaeria pl/silla 58

Ihe Czarne n/S. 23952.8 50.2 0.3 0.8 Limnothrix plane/onica 85

the Glębokie nlU. 1583.2 91.7 0.7 3.3 Ceratium hirundinella 39 Closterilflll dianae 14

Ihe Rotcze 677.6 17.2 0.5 4.6 Crypromonas sp. 19

Ihe Sumin 1009.5 55.0 0.8 3.4 Tetraiidron minimum

Ihe Długie 1147.1 25.1 0.7 2.9 Scenedesmus quadricauda 18

(5)

ABIOTIC AND B10TIC FACTORS OF THE SIX LAKES 233

[J]

Cyanoprokaryota

§

Oinophyceae ~ Cryptophyceae

D

Bacillariophyceae

o

Chlorophyta .Others

Zagłeboc.te Czarne near Głebokie near Rolcze Sumin Długie

~ UscimOw

Fig. 2. Percenlage shares oftaxonomic groups in the total numbers ofphytoplankton in studied lakes

algae

(Fig.

2):

Limnothrix planetonica,

L.

redekei and Planktothrix aghardii (with

the

predominance

of

L.

planclonica), species

typical of advanced eutrophy

[6].

Studies

on

the Czarne Lake near Sosnowica were

conducted

in the

sixties

by

Wo-jciechowski [9]. Great diversity of the

phytoplankton species and

twice

greater

water transparency nowadays was then

noted.

The

Glębokie

Lake near

Uścimów

was characterized

by

the highest

physico-chemical values

among

all studied reservoirs, i.e., a high level of total nitrogen

,

and

phosphorus as

well

as by a very low Secchi disk

visibility (Table

I).

The

chl

o-rophyll-a concentration reached as much as 90 fIg dm

-3

(Table 3) and

exceeded

the

values characteristic of

advanced eutrophy in

lakes

[2].

An abundance of phy

to-plankton was dominated by one Dinophyceae species Ceratium hirundinella

(

Table

3).

Thr

ee

of the

lakes

studied,

the

Rotcze,

the Sumin and

th

e

Długie,

are

shallow

and

polimictic

with different character

of the

catchment areas: agricultural

and

recreationał

in the case of

the Rotcze

and the Sum in; forest and peat-bog in th

e

case ofthe

Długie.

Co

ncentration

oftotal

phosphorus

(TP) in

alł

above-mentioned

lakes

was

not

very high and reached about 70 fIg dm

-3

Concentrations of

chloro-phyłl-a

values ranged from 17

to

55 fIg dm-

3

At

the

same time, a

high

percenta

ge

share ofphytoplankton

had

green algae and blue

-green algae. Biodiversity

indi

ces,

i.e.: Shannon-Weaver and evenness were

high

in alllakes oflhis gro up

(Table 3).

Among

the

lakes studied, a

relativeły

high

water transparenc

y

was

in

th

e

Rotcze

łake

(SD=I.9

m) and

in

the

Długie łake

wherc lighr

always

reach

e

d

the

(6)

234 A. PASZTALENTEC, R. MENCFEL

bottom

(SD=0.9 m). In

this

latter lake, maerophytes

we

re

a

frequent

oeeurrenee.

They

eould

absorb and aeeumulate

biogenies

elements and

limit

the growth of

al-gae.

Values

of

the parameters

studied indieated asimila

r,

temperate

eutrophie

character of

these lakes.

CONCLUSION

Physieal and

ehem

ieal

faetors

and

the

phytoplankton eomposition of

lakes

stud

ied

usually

eonfirmed their

trophie

eharaeter.

The mesotrophie lake

Zagłęboeze

was eharaeterised

by

a

high

SD, low abundanee

of phytoplankton

and

ehlorophyll-a values typieal of a

low trophie

status. Another

deep lake the

Czarne

near

Sosnowica showed

a high trophy

of

its

water eonfirmed

by

a great

predomi-nanee

or

filamentous

blue-green algae.

In

the shallow, eutrophie lakes:

Roteze

,

Sumin and in the

dystrophic

the

Długie

lakc a

high

abundanee or

phytoplankton

and a

high

ehlorophyll-a eoneentration was reeorded.

However, rather high

biodi-versity ean

indieate

stability of

these lakes. The highest

concentration or

nutrients

and chlorophyl

l-a and a

high

abundanee of phytoplankton with

low SD

was

re-eorded

in

the

Głębokie

lake near

Uśeimów.

REFERENCES

I. HcrnlO1nowicz '''., Oorożańska W., Dojlido J" Koziol"owski 8.: Physical and chemical study

ofwater and sewage (in Polish). Arkady, Warszmva, 556,1976.

2. Hillbricht-Ilkowska A., Kajak Z.: Parametcrs and indicatol's lIscful for control fllnctiol1;11 Jnd

slructural chan ges in lakcs ecosyslems during cUlrophicalion (in Polish) [In:] Lakes ccosyslems

monitoring. red. A. Hillbrichl-lIkowsb. Ossolineum. Wroc1aw, 23-45, 1986.

3. Lloyd M. Gheraldi J.: A table for calcu1:J.ting the cquitability componcnt of specics diversity, 1.

Anim. 8col. 33: 217-225, 1964.

4. Nusch E. A.: Comparison of different methods for chlorophyll and pheopigmcnt dctcmlination,

Arch. Hydrobiol. Beih. Ergebn. Limnol., 14, 14-36, 1980.

5. Radwan S., Kornijów R.: Hydrobiologieal featlll'es oJ' łakes nowadays status <Ind currents ol'

changes (in Polish). In: Lęczna-Wlodaw3 Lakes. Nalurals Monography (Red: M. Harasimiuk, Z. MichaJczyk. M. Turczyński), Biblioteb Monitoringu Środowisb, Lublin. 129-144. 1998.

6. ReynoJds C.S.: What factors influence the speeies composition of phyloplankton in lakes

ar

different trophie status? Hydrobiologia 369/370, 11-26, 1998.

7. Shannon C.E., Wcaver W.: The Mathematical Theory of Communication, University of Ill i-Ilois Prcss, Urbana IL, 117, 1949.

8. Vollcnwcidcr R.A.: A Manual to Mcthods for Measuring Primal)' Production in Aquatie

Envi-ronmcnts, Blackwcll, Oxford-Edinburg, 213. 1969.

9. Wojciechowski J.: Periodie differcnccs of phytoplankton in Sosnowica Lakes (in Polish).

(7)

ABIOTIC AND BIOTIC FACTORS

or

THE SIX LAKES 235

10. Zdanowski B.: Ecological characteristic of lakes in north-eastern Poland vcrSLJS thcir trophic

gradient: UL Chemistry ofthe waleT in 41 lakes, Pol. J. Eco!., 287-307,1983.

WYBRANE CZYNNIKI ABIOTYCZNE I I3IOTYCZNE SZEŚCIU JEZIOR

POJEZIERZA ŁĘCZYŃSKO-WŁODAWSKIEGO (POLESIE LUBELSKIE)

W OKRESIE LETNIM

A. Pasz/ateniec, R. Mencjet

Katedra Botaniki i Hydrobiologii, Katolicki Uniwersytet Lubelski

uL

e.K.

Norwida 4, 20-061 Lublin, Polska, e-mail: paszla@kul.Jublin.pl

S t r e s z c z e n i e. Badania sześciu jezior Pojezierza Lęczyńsko-Włodawskiego (Zagłębocze,

Czarne Sosnowickic, Głębokie Uścimowskic, Rotcze. Sum in i Długie) przeprowadzono w okresie

letnim (czerwiec-sierpień) roku 2001. Wybrane jeziora cechowala odmienna morfometria i status

troficzny. Oznaczono parametry fizyczno-chemiczne (SD, pH, kondukcja, natlenienie. koncentracja

pierwiastków biogennych) i biologiczne (stężenie chlorofilu-a oraz liczebność i struktura jakościowa

fitoplanktonu z uwzględnieniem gatunków i grup dominujących).

Czynniki fizyczno-chemiczne i struktura fitoplanktonu na ogól potwierdzały typ troficzny

badanych jezior. Mczotroficzne jezioro Zagłębocze charakteryzowało się wysokim SD, niską

liczebnością glonów i wartościami chlorofilu-a typowymi dla jezior o niskiej trofii.

Fizyczno-chemiczne właściwości wody oraz ponad 90-cio procentowa dominacja sinic wskazują na wysoką

żyzność jeziora Czarne Sosnowickic. W plytkich jeziorach eutroficznych Rotczc, Sumin i w

dystro-ficzym jeziorze D/ugie stwierdzono wysokie liczebności fitoplanktonu i stężenia chlorofilu-a, przy

czym duża różnorodność gatunkowa może świadczyć o stabilności tych zbiorników. Najwyższe

stężenia biogenów i chlorofilu-a, a także dużą liczebność glonów planktonowych i niskie SD

stwierdzono w jeziorze Głębokie.

S / o w a k l li C Z o w e: jeziora, letni fitoplankton, czynniki fizyko-chemiczne,

Cytaty

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