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The Effect of Animál Disturbance on the Spatial Pattern and Dynamics of Leucobryum juniperoideum (Brid.) C. Muell

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Acta Acad. Paed. Agriensis, Sectio Biológiáé X X I V (2003) 201-213

The Effect of Animál Disturbance on the Spatial Pattern and Dynamics of Leucobryum juniperoideum (Brid.) C. Muell

Pénzes Kónya, E.

Botanical Department of Eszterházy College, H-3300 Eger Pf. 43.

konyaO ektf.hu

A b stra ct. In forest communities on radiolarian bedrock where the shrub layer is missing and the soil surface is very narrow the bryophyte and lichen species living in the ground appear with big dominance and have great importance forming a continuous cryptogamic layer there, bút the pattern of it is iníluenced mainly by the disturbance of wild animals. The dynamic of spatial pattern changes most directly in the cases of the dominant bryophyte species, one of which is Leucobryum juniperoideum in the examined area in the Bükk mountains.

Introduction

The forest communities growing on radiolarit bedrocks are special ha- bitats fór bryophyte species because the shrub layer is almost completely missing and the acidic soil and radiolarian chert bedrock provide favourable conditions fór many bryophyte species.They occur with great dominance and diversity in these areas where a bryofloristic examination was carried out. (Pénzes Kónya-Orbán 2000). One of these places has got a special im- portance, it can be found near Felsőtárkány, on the North Western slope of Csák-Pilis mountain. This community is Deschampsio-Fagetum, where somé perennial bryophyte species appear with great dominance: about 80 percent of the soil surface is covered by bryophytes (F ig.l).

The observation of the spatial pattern and the dynamics of bryophyte species has been carried out since 1999 in permanent quadrats and as it happened in the same way in other areas of the Bükk mountains, the gro- wing disturbance of wild animals can be observed among the vascular plánt species and fór bryophyte species, mainly by way of treading.

This forest habitat type with thin soil layer and with little number

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of shrubs and the density of the animals is emerging every year, wich is a disturbance danger fór plants.

Radiolarian bearing rocks are widely distributed in mountain ranges exposing geological units of oceanic affinities and radiolarites have special physical and chemical features which have been examined fór about 25 years (Racki-Cordey 2000) These rocks are prone to rubbling in a similar way as dolomites and may cause the fragmentation and the entire destruction of the vegetation close to the surface.

In the examined axea the number of species is low bút their absolute cover value of them is high. The dominant species of the sampling area is Leucobryum juniperoideum (Brid.) C. Muell which has been considered as a rare species in Hungary with one floristic data (Boros 1968, Orbán-Vajda 1983), bút several occurrences have been discovered recently (Pénzes Kónya 2003).

As the type of bedrock and the dominant bryophyte species are worth fór further examinations, the aim of the study is to discover and detect the degradation-regeneration processes during which the spatial pattern of Leucobryum juniperoideum changes as a consequence of the repeated and growing disturbance.

Materials and methods

12 permanent quadrats were chosen, the size of them are 30 X 30 cm, divided intő 10 X 10 cells. Four quadrats are touched with their one side, so they form sample blocks. The locality of blocks was chosen randomly.

The cover of bryophyte species was estimated in each cell using the following scale that consisted of three values. 1: The cover of the bryophyte species is less than 30% in the cell. 2: The cover of the bryophyte species is between 30% and 70% in one cell. 3: The cover of the bryophyte species is above 70% in the cell.

The cover data of the bryophyte species were recorded once a year.

The cover estimation values were analysed using spatial pattern analyses, the method was the Paired Quadrat Variance, PQV (Dalé 1999) as the spatial pattern and spatial distribution of bryophytes are close to the two- dimensional distributions and almost all of their growing forms are patchy in space, only the scale of pattern is different. In the method we applied it is persumed that the cover variance of the neighbouring cells is less than of those that are nőt neighbours (Dalé 1999). If there is any repeated spatial pattern in the data, the peaks of variance show the presence of patches at a given spatial scale which can be presented by diagramms. Another

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The Effect of Animál Disturbance on the Spatial Pattem .. . 203

type of examination was directed to the anatomical-morphological response of Leucobryum juniperoideum to the repeated and emerging disturbance of wild animals and to examine the regeneration capacity of the species.

Microscopic examinations were done and photographs were tElken about them.

Results

It can be observed ffom the results (Fig.2 a, b, c) that the number of bryophyte species is low, bút the relative percent cover of them is high, it is near 90—100% the dominant species of the areais Leucobryum juniperoideum and at the same time the changes of this species int he cover is the most intensive on the basis of the cover estimation in 12 quadrats in three years The other bryophyte species which occupy less space in the area have nőt as much changes in their cover values in the three years’ period.

If we observe the spatial distribution of Leucobryum juniperoideum du- ring three years (Fig.3) it can be seen írom the results of PQV pattem analysis that the cushion growing form which was the tipical spatial appe- arance of Leucobryum juniperoideum in the first year (smoothly repeated peaks in variance along distance scale, Fig.4), confused fór the third year, the cushions were fragmented which is manifested in the Httle peaks of the diagram of the third year. The disturbance of big wild animals and the extre- mely dry spring can be among the causes of this dynamics of the drastically changed spatial pattern of Leucobryum juniperoideum.

Considering the previous observations the assumption was that the absolute cover of L. juniperoideum slowly decreases, the big cushions are fragmented and the species is getting dangerously destroyed. Bút the rege- nerative capacity of the species provided another direction of the process of pattern dynamics.

The type of disturbance when big wild animals like deers and mouflons overturn whole cushions of Leucobryum juniperoideum, induces somé special morphological and anatomical processes. It seems at first sight that these cushions or fragments are entirely destroyed and dead, especially the ones turnéd to the soil surface with their top. If we examine them after somé weeks it can be observed that they are strongly connected to the ground.

Fig.4 and 5 shows the bottom and the top of these turnéd cushions. During the further regeneration processeses on the top side which was originally on the ground surface green, new leaves are developing while at the bottom of the cushion which was originally directed to the top leaves are getting yellowish-brown and rhizoids are growing to the soil surface.

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If we observe the morphological features during the regeneration pro- cesses of the turnéd cushions of Leucobryum juniperoideum on microscopical photographs (Fig.6) we can see special morphological processes during which apical rhizoids are growing from the leaf apex which are the formations of the green cells (Yamaguchi 1993) among the hyahne cells and when the cus- hion turns these rhizoids grow longer and thick. On the other side in the cells of old leaves protonema-like cell groups are growing and new leafy stems are formed (Fig.7). In many cases the taxa of Leucobryum form caducous lea- ves that function in asexual reproduction. These particular caducous leaves are defined as gemmae (Yamaguchi 1993). This type of regeneration process is getting faster in the rainy periods and it slows down in dry seasons. At this time the permanent disturbance and the rock fragmentation is very dangerous fór the dominant bryophyte species, Leucobryum juniperoideum, because the regeneration processes are slower than the intensity of the dis- turbance. Considering these results and the type of the special extended habitat of Leucobryum juniperoideum the area is worth to treat in a special conservational way as other forest communities on radiolarian bedrock in the Bükk mountains.

References

Bl a c k s t o c k, T . II. (1987): The Male Gametophores of Leucobryum glaucum (Hedw.) Angstr. and Leucobryum juniperoideum (Brid.) Muell. in two Welsh woodlands. J. Bryol. 14, 535-541.

Bo n n o t , E. (1964): Le Leucobryum juniperoideum (Brid.) C. Mull.

dans la brioflore francaise. Bull. Soc. Bot. Fr. 111: 151-164.

Bo r o s, Á . (1968): Bryogeographie und Bryoflora Ungarns. Akadémiai Kiadó, Budapest.

Ra c k i, G. h Co r d e y, F. (2000): Radiolarian paleoecology and radi- olarites: is the present the key to the pást?; Earth-Science Reviews, Vol. 52, pp. 83-120.

Da l é, M . T . (1999): Spatial Pattern Analysis in Plánt Ecology. Camb- ridge University Press.

Du r i n g, II. J. & Ll o r e t (1996): Permanent grid studies in bryophyte communities. J. Hattori Bot.Lab. N - 79., pp. 1-45.

Or b á n, S.& Va j d a, L. (1983): Magyarország mohaflórájának kézi- könyve. Akadémiai Kiadó, Budapest.

P Én z e s nÉ Ko n y a, E.& Or b á n, S. (1998): A Bükk hegység radiolarit alapkőzetű területeinek mohaflórája. Kitabelia, Vol. 3. N - 2., pp. 357-358.

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The Effect of Animál Disturbance on the Spatial Pattem. .. 205

P Én z e s nÉ Ko n y a, E. & Or b á n, S. (2000): A Bükk hegység radiolarit alapkőzetű területeinek mohaflórája II. Kitaibelia Vol. 5. N - 1., pp. 125-130.

P Én z e s nÉ Ko n y a, E. (2003): A Leucobryum juniperoideum (Brid.) C. Muell. új hazai előfordulásai. Kitaibelia (in print).

Pi l o u s, Z. (1962): Das Moos Leucobryum juniperoideum (Brid.) C.

Müll. In Európa. Preslia 34: 159-175.

Sm i t h, A. J. E. (1978): The Moss Flóra of Britain and Ireland. Camb- ridge University Press.

Ya ma g u c i i i, T. (1993): A Revision of the Genus Leucobryum (Musci) in Asia. J. Hattori Bot. Láb. N- 73: 1-123.

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F ig .l The community Deschampsio-Fagetum vvith the great dominance of Leu- cobryum juniperoideum.

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The Effect of Animál Disturbance on the Spatial Pattern 207

Leucobryum juniperoideum 1999

sample quadrats

Polytrichum formosum 1999

sample quadrats

Dicranum scoparium

1999 Hypnum cupressiforme

1999

sample quadrats

Fig.2a

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Leucobryum juniperoideum

2000 Polytrichum formosum

2000

90

sample quadrats

■B «

o g9 x)

-Q q

Dicranum scoparium 2000

A ío

| & 40

c u in

Hypnum cupressiforme 2000

I 5 6 7 B 9 10 11 12

sample quadrats

Fig.2b

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The EfFect of Animál Disturbance on the Spatial Pattem .. 209

Leucobiyum juniperoideum

2001 Polytrichiim formosum

100

2001

•> 50 o ? S) u 60 í 2 30

if í r

pC °

P

20 110

i i . i i i

0 1 2 3 4 5 6 7 8 9 10 11 12 sample quadrats

Dicranum scoparium 2001

Hypnuin cupressiforme 2001

|00

Ü - (U 90

o « 0 ü 70

u. ° -n ífl ^ --- --- u, ° Hí -rt 60

3 1* J0 ' 3 3 J0

C 8 M - ^ 8 30

| ° » [S ° *

M 1 0 --- --- m--- H to

a - f l - ■ f l I . . a

1 2 3 4 3 6 7 8 9 10 11 J2 1 2 3 4 5 6 7 8 9 10 II 12

aample quadrats sample quadrats

Fig.2c

Fig.2 a, b, c The results of the cover estimation of bryophyte species during three years in the permanent quadrats.

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The variogram of Leucobryum juniperoideum

0 J---,--- ■ ■ - — i--- .— r--- ,--- .

1 2 3 4 5 6 7 8 9

Spatial scale (the numbers mean the distance o f cells)

F ig.3 The result of the spatial pattern analysis (P Q V ) of Leucobryum juniperoi- deum in a permanent quadrat on the basis of three years.

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The Effect öf Animál Disturbance on the Spatial P attem .. . 211

Fig.4 The original top of the turnéd cushion of L eu cobryum juniperoideum There are many rhizoids growing to the surface among the leaves in order to fix this side to the ground.

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Fig.5 The original bottom of tlie turnéd cushion. New branchlets are growing up írom the old, brownish leaves.

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The Effect of Animál Disturbance on the Spatial Pattern.. . 213

Fig.6 The rhizoids growing from the leaf apex of L. juniperoideum.

Fig.7 Protonema-like cell groups are developing in the leaf cells tovvard the upper side of the cushion, It can be probably the start of the development of caducous leaves.

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