<p>Sa&nbsp; jedne&nbsp; strane&nbsp; se&nbsp; eksploatacija&nbsp; &scaron;ljunka&nbsp; navodi kao&nbsp; značajan&nbsp; ugrožavajući&nbsp; faktor&nbsp; sa&nbsp; velikim negativnim&nbsp; uticajem&nbsp; na&nbsp; vodena&nbsp; stani&scaron;ta&nbsp; i biodiverzitet,&nbsp; dok&nbsp; same&nbsp; &scaron;ljunkare&nbsp; mogu predstavljati&nbsp; vredne&nbsp; refugijume&nbsp; akavtičnog&nbsp; biodiverziteta.&nbsp; Osnovni&nbsp; cilj&nbsp; disertacije&nbsp; je određivanje&nbsp; najznačajnijih&nbsp; i&nbsp; relevantnih hidromorfolo&scaron;kih&nbsp; parametara&nbsp; koji&nbsp; utiču&nbsp; na strukturiranje&nbsp; makrofitskih&nbsp; zajednica&nbsp; u &scaron;ljunkarama&nbsp; duž&nbsp; plavnog&nbsp; područja&nbsp; reke&nbsp; Drine&nbsp; i određivanje&nbsp; korelacije&nbsp; između&nbsp; izdvojenih parametara&nbsp; i&nbsp; kvantitativnih&nbsp; indeksa&nbsp; makrofita.Istraživanje&nbsp; je&nbsp; vr&scaron;eno&nbsp; u&nbsp; toku&nbsp; letnjih&nbsp; meseci 2015, 2016, 2017 i 2018. godine na 18 &scaron;ljunkara (60 istraživačkih vegetacijskih sektora) u okviru tri&nbsp;&nbsp; eksploataciona&nbsp; polja&nbsp; u&nbsp; Crnoj&nbsp; Bari, Badovincima&nbsp; i&nbsp; Lipničkom&nbsp; &Scaron;oru&nbsp; i&nbsp; na&nbsp; četiri prirodna&nbsp; fluvijalna&nbsp; jezera&nbsp; (13&nbsp; istraživačkih vegetacijskih&nbsp; sektora)&nbsp; u&nbsp; plavnom&nbsp; području&nbsp; reke Drine.&nbsp; Makrofitska&nbsp; vegetacija&nbsp; je&nbsp; konstatovana na svih 18 istraţivanih &scaron;ljunkara, prikupljenih na tri eksploataciona polja (Badovinci, Crna Bara&nbsp; i<br />Lipniĉki &Scaron;or). Zabeležena je 31 biljna vrsta. Kao najučestalije,&nbsp; sa&nbsp; najvećom&nbsp; apsolutnom pokrovno&scaron;ću izdvojile su se vrste:&nbsp;<em> Potamogeton nodosus</em>&nbsp; Poiret,&nbsp; <em>Ceratophyllum&nbsp; demersum&nbsp; L subsp.&nbsp; demersum,&nbsp; Myriophyllum&nbsp; spicatum&nbsp; L,Najas&nbsp; marina&nbsp; L&nbsp; i&nbsp;&nbsp; Chara&nbsp; globularis&nbsp; Thuill&nbsp;</em> Na četiri prirodna fluvijalna jezera zabeleženo je 13 vrsta.&nbsp; Vrste&nbsp; <em>Vallisneria&nbsp; spiralis&nbsp; L,&nbsp; Elodea canadensis&nbsp; Michx,&nbsp; Callitriche&nbsp; palustris&nbsp; L, Potamogeton&nbsp; natans&nbsp; L&nbsp; i&nbsp; Nuphar&nbsp; lutea&nbsp; (L)&nbsp;</em> Sm izdvojile&nbsp; su&nbsp; se&nbsp; kao&nbsp; konstantne&nbsp; i&nbsp; dominantne. Vrednosti svih kvantitativnih indeksa makrofita,<br />značajno&nbsp; su&nbsp; veće&nbsp; za&nbsp; &scaron;ljunkare&nbsp; u&nbsp; poređenju&nbsp; sa prirodnim&nbsp; fluvijalnim&nbsp; jezerima&nbsp; na&nbsp; nivouLEAFPACS&nbsp; sektora.&nbsp; Na&nbsp; istraživanim &scaron;ljunkarama,&nbsp; analizom&nbsp; klasterovanja&nbsp; je<br />izdvojeno&nbsp; 13&nbsp; vegetacijskih&nbsp; grupa&nbsp; (VG):&nbsp; VG1<em> Ceratophyllum&nbsp; demersum</em>,&nbsp; VG2&nbsp; <em>Ceratophyllum demersum&nbsp; -&nbsp; Valisneria&nbsp; spiralis</em>,&nbsp; VG3&nbsp; <em>Chara contraria,</em>&nbsp; VG4&nbsp; <em>Chara</em>&nbsp; <em>globularis,</em>&nbsp; VG5&nbsp; <em>Elodea canadensis,</em>&nbsp; VG6&nbsp; <em>Elodea&nbsp; nuttallii</em>,&nbsp; VG7&nbsp; <em>Najas marina</em>,&nbsp; VG8&nbsp; <em>Najas&nbsp; minor,</em>&nbsp; VG9&nbsp; <em>Nitellopsis obtusa</em>,&nbsp; VG10&nbsp;<em> Nuphar&nbsp; lutea</em>,&nbsp; VG11 <em>Potamogeton&nbsp; nodosus</em>,&nbsp; VG12&nbsp;<em> Potamogeton natans&nbsp;</em> i&nbsp;&nbsp; VG13&nbsp; <em>Potamogeton&nbsp; pectinatus</em>.&nbsp; Na prirodnim&nbsp; fluvijalnim&nbsp; jezerima&nbsp; konstatovane&nbsp; su četiri&nbsp; vegetacijske&nbsp; grupe:&nbsp; VG5&nbsp;<em> Elodea canadensis</em>,&nbsp; VG10&nbsp; <em>Nuphar&nbsp; lutea,</em>&nbsp; VG12<em> Potamogeton natans&nbsp;</em> i&nbsp; VG14&nbsp; <em>Typha latifolia</em>.&nbsp; Na osnovu izmerenih fizičko-hemijskih parametara,kvalitet vode u većini &scaron;ljunkara odgovara II klasi kvaliteta, na osnovu čega se mogu okarakterisati kao&nbsp; vodna&nbsp; tela&nbsp; sa&nbsp; dobrim&nbsp; i&nbsp; boljim&nbsp; ekolo&scaron;kim potencijalom. Sve &scaron;ljunkare i fluvijalna jezera se klasifikuju&nbsp; kao&nbsp; visoko&nbsp; alkalna.&nbsp; Kvalitet&nbsp; vode&nbsp; u prirodnim&nbsp; fluvijalnim&nbsp; jezerima&nbsp; odgovara&nbsp; III&nbsp; &ndash; IV&nbsp; klasi&nbsp; kvaliteta&nbsp; voda,&nbsp; pri&nbsp; čemu&nbsp; se&nbsp; mogu okarakterisati&nbsp; kao&nbsp; vodna&nbsp; tela&nbsp; sa&nbsp; slabim&nbsp; do umerenim&nbsp; ekolo&scaron;kim&nbsp; statusom.&nbsp; Značajno&nbsp; veće<br />vrednosti&nbsp; ukupnih&nbsp; suspendovanih&nbsp; materija, hemijske&nbsp; i&nbsp; biolo&scaron;ke&nbsp; potro&scaron;nje&nbsp; kiseonika, ukupnog&nbsp; organskog&nbsp; kiseonika&nbsp; i&nbsp; nitrata zabeležene su na prirodnim fluvijalnim jezerima u poređenju sa &scaron;ljunkarama. Izmerene vrednosti fizičko-hemijskih&nbsp; parametara&nbsp; ukazuju&nbsp; na mezotrofni&nbsp; karakter&nbsp; lokaliteta&nbsp; u&nbsp; Badovincima&nbsp; i mezo-eutrofni&nbsp; karakter&nbsp; lokaliteta&nbsp; u&nbsp; Lipničkom &Scaron;oru,&nbsp; dok&nbsp; se&nbsp; &scaron;ljunkare&nbsp; na&nbsp; teritoriji&nbsp; Crne&nbsp; Bare mogu&nbsp; okarakterisati&nbsp; kao&nbsp; eutrofna&nbsp; jezera.Vrednosti&nbsp; LHMS&nbsp; (modifikacionog)&nbsp; skora&nbsp; za &scaron;ljunkare kretale su se u rasponu od 9&nbsp; &ndash;&nbsp; 15, dok su vrednosti LHQA skora (stani&scaron;nog diverziteta) bile u rasponu izmeĊu 33&nbsp; &ndash;&nbsp; 44. Sliĉne vrednosti za&nbsp; LHQA&nbsp; skor&nbsp; su&nbsp; izraĉunate&nbsp; i&nbsp; za&nbsp; prirodna fluvijalna&nbsp; jezera&nbsp; (36&nbsp; &ndash;&nbsp; 49).&nbsp; MeĊutim,&nbsp; vrednosti<br />LHMS&nbsp; skora&nbsp; za&nbsp; prirodna&nbsp; fluvijalna&nbsp; jezera&nbsp; su znaĉajno&nbsp; veće&nbsp; u&nbsp; odnosu&nbsp; na&nbsp; vrednosti&nbsp; LHMS skora za &scaron;ljunkare. Ovi podaci ukazuju na manje prisustvo&nbsp; antropogenog&nbsp; pritiska&nbsp; na&nbsp; &scaron;ljunkarama u poređenju sa prirodnim fluvijalnim jezerima uistraţivanom&nbsp; podruĉju.&nbsp; Fizičko -hemijski&nbsp; i hidromorfolo&scaron;ki&nbsp; parametri&nbsp; zajedno&nbsp; su&nbsp; objasnili 57.07&nbsp; %&nbsp; od&nbsp; ukupne&nbsp; varijanse&nbsp; vegetacijskih podataka,&nbsp; sa&nbsp; 16.57&nbsp; %&nbsp; deljenog&nbsp; efekta.&nbsp; Fizičkohemijski&nbsp; parametri&nbsp; kvaliteta&nbsp; vode&nbsp; objasnili&nbsp; su 17.02&nbsp; %&nbsp; varijabilnosti&nbsp; u&nbsp; strukturi&nbsp; makrofitske vegetacije.&nbsp; Kao&nbsp; najsignifikantniji&nbsp; parametri<br />izdvojili&nbsp; su&nbsp; se:&nbsp; saturacija&nbsp; vode&nbsp; kiseonikom,ukupni&nbsp; organski&nbsp; ugljenik,&nbsp; povr&scaron;inski&nbsp; aktivne materije, temperatura, elektroprovodljivost, pH i ukpni&nbsp; alkalitet.&nbsp; Hidromorfolo&scaron;ki&nbsp; parametri&nbsp; su objasnili&nbsp; 23.48&nbsp; %&nbsp; varijabilnosti&nbsp; u&nbsp; strukturi makrofitske&nbsp; vegetacije.&nbsp; Kao&nbsp; najsignifikantnije varijable,&nbsp; izdvojile&nbsp; su&nbsp; se:&nbsp; struktura&nbsp; vegetacije&nbsp; u priobalnoj&nbsp; zoni,&nbsp; diverzitet&nbsp; prirodnih&nbsp; tipova stani&scaron;ta&nbsp; priobalne&nbsp; zone,&nbsp; prirodnost&nbsp; obale, diverzitet&nbsp; prirodnog&nbsp; supstrata&nbsp; litorala,masimalna dubina &scaron;ljunkara, povr&scaron;ina &scaron;ljunkara,indeks relativne dubine, udaljenost &scaron;ljunkara od glavnog&nbsp; reĉnog&nbsp; toka&nbsp; i&nbsp; starost&nbsp; &scaron;ljunkara. Hidrolo&scaron;ki&nbsp; parametri&nbsp; su&nbsp; objasnili&nbsp; 8.38&nbsp; % varijabilnosti u strukturi&nbsp; makrofitske vegetacije. Kao&nbsp; najsignifikantnije&nbsp; varijable,&nbsp; izdvojile&nbsp; su&nbsp; se broj plavnih talasa u vegetacionoj sezoni tokom godine u kojoj je vr&scaron;eno uzorkovanje vegetacije i broj plavnih talasa u prolećnom periodu za sve četiri&nbsp; godine.&nbsp; Ovi&nbsp; rezultati&nbsp; potvrđuju&nbsp; direktni destruktivni&nbsp; uticaj&nbsp; plavnih&nbsp; talasa&nbsp; na&nbsp; vodenu vegetaciju u vegetacionoj sezoni, kao i indirektni uticaj prolećnih poplava, usled uticaja na trofički status&nbsp; vode.&nbsp; Sumarno,&nbsp; &scaron;ljunkare&nbsp; u&nbsp; plavnom području&nbsp; reke&nbsp; Drine&nbsp; predstavljaju&nbsp; optimalno stani&scaron;te&nbsp; za&nbsp; razvoj&nbsp; retke&nbsp; i&nbsp; ugroţene&nbsp; makrofitske flore.&nbsp; Od&nbsp; ukupnog&nbsp; broja&nbsp; zabeleženih&nbsp; vrsta makrofita,&nbsp; 30&nbsp; %&nbsp; se&nbsp; kategori&scaron;e&nbsp; kao&nbsp; za&scaron;tićeno&nbsp; ili ugroženo na nacionalnom nivou.&nbsp; Značajno veće vrednosti&nbsp; konzervacionih&nbsp; indeksa&nbsp; ustanovljene su&nbsp; za&nbsp; &scaron;ljunkare&nbsp; u&nbsp; poređenju&nbsp; sa&nbsp; prirodnim fluvijalnim jezerima, &scaron;to ukazuje na njihov visok ekolo&scaron;ki&nbsp; potencijal.&nbsp; Ustanovljen&nbsp; je&nbsp; visok diverzitet&nbsp; prioritetnih&nbsp; tipova&nbsp; akvatiĉnih&nbsp; stani&scaron;ta prema&nbsp; Pravilniku&nbsp; o&nbsp; kriterijumima&nbsp; za&nbsp; izdvajanje tipova&nbsp; stani&scaron;ta,&nbsp; o&nbsp; tipovima&nbsp; stani&scaron;ta,&nbsp; osetljivim, ugroženim,&nbsp; retkim&nbsp; i&nbsp; za&nbsp; za&scaron;titu&nbsp; prioritetnim tipovima&nbsp; stani&scaron;ta&nbsp; i&nbsp; o&nbsp; merama&nbsp; za&scaron;tite&nbsp; za&nbsp; njihovo očuvanje, Aneksu I, Direktive Evropske unije oza&scaron;titi&nbsp; prirodnih&nbsp; stani&scaron;ta&nbsp; i&nbsp; divlje&nbsp; flore&nbsp; i&nbsp; faune (Natura&nbsp; 2000),&nbsp; Rezoluciji&nbsp; br.&nbsp; 4&nbsp; Konvencije&nbsp; o očuvanju&nbsp; evropske&nbsp; divlje&nbsp; flore&nbsp; i&nbsp; faune&nbsp; i prirodnih&nbsp; stani&scaron;ta (EMERALD)&nbsp; i&nbsp; Evropskoj crvenoj&nbsp; listi&nbsp; stani&scaron;ta.&nbsp; Vrednosti&nbsp; izdvojenih atributa&nbsp; &scaron;ljunkara&nbsp; mogli&nbsp; bi&nbsp; se&nbsp; iskoristiti&nbsp; u procesu&nbsp; ranog&nbsp; planiranja&nbsp; i&nbsp; projektovanja eksploatacionih&nbsp; polja&nbsp; u&nbsp; plavnom&nbsp; području&nbsp; reke Drine&nbsp; i&nbsp; na&nbsp; drugim,&nbsp; sličnim&nbsp; lokalitetima. Generalna preporuka je da se dva tipa &scaron;ljunkara kreiraju&nbsp; u&nbsp; okviru&nbsp; jednog&nbsp; eksploatacionog&nbsp; polja. Prvi&nbsp; tip,&nbsp; odnosno&nbsp; &scaron;ljunkare&nbsp; koje&nbsp; bi&nbsp; podržavale pionirsku&nbsp; vegetaciju&nbsp; pr&scaron;ljenčica&nbsp; trebale&nbsp; bi&nbsp; da budu locirane na razdaljini do 100 m od glavnog rečnog&nbsp; toka,&nbsp; povr&scaron;ine&nbsp; do&nbsp; 1000&nbsp; m 2 i&nbsp; da&nbsp; imaju vrednost indeksa relativne dubine &gt; 5 %. Drugi tip&nbsp; &scaron;ljunkara&nbsp; koje&nbsp; bi&nbsp; podržavale&nbsp; vegetaciju karakterističnu&nbsp; za&nbsp; nizijska&nbsp; fluvijalna&nbsp; jezera trebale bi da budu locirane na razdaljani od oko 300 m od glavnog rečnog toka, dubine 3&nbsp; &ndash;&nbsp; 4&nbsp; m (najmanje 2 m), povr&scaron;ine između 10000 i 20000 m ²(najmanje&nbsp; 4000&nbsp; m² ),&nbsp; različitih&nbsp; vrednosti indeksa relativne dubine, ali&nbsp; ne preko 5 %. Sva eksploataciona&nbsp; polja&nbsp; bi&nbsp; trebalo&nbsp; isplanirati&nbsp; i isprojektovati&nbsp; kako&nbsp; bi&nbsp; se&nbsp; minimizirao&nbsp; uticaj&nbsp; na priobalnu&nbsp; i&nbsp; obalnu&nbsp; zonu.&nbsp; Pridržavanjem&nbsp; datih smernica&nbsp; povećao&nbsp; bi&nbsp; se&nbsp; diverzitet&nbsp; i&nbsp; kvalitet stani&scaron;ta,&nbsp; kao&nbsp; i&nbsp; konzervacioni&nbsp; potencijal &scaron;ljunkara. Kreiranjem &scaron;ljunkara na naĉin kao &scaron;to je predloženo u ovoj disertaciji omogućila bi se spontana&nbsp; rekultivacija&nbsp; eksploatacionih polja,odnosno&nbsp; remedijacija&nbsp; u&nbsp; cilju&nbsp; pobolj&scaron;anja kvaliteta vode i renaturalizacija stani&scaron;ta, čime bi se&nbsp; znatno&nbsp; smanjili,&nbsp; ili&nbsp; u&nbsp; potpunosti&nbsp; eliminisali, tro&scaron;kovi tehničke rekultivacije terena.</p> / <p>Gravel pit lakes in the river floodplains represent a kind of ecological paradox. Gravel exploitation was recognised&nbsp; as&nbsp; important&nbsp; factor&nbsp; significantlyaffecting&nbsp; aquatic&nbsp; habitats&nbsp; and&nbsp; biodiversity.&nbsp; On the&nbsp; other&nbsp; hand,&nbsp; gravel&nbsp; pit&nbsp; lakes&nbsp; are&nbsp; valuable biodiversity&nbsp; refugiums,&nbsp; potentially&nbsp; supporting rarae&nbsp; species&nbsp; and&nbsp; habitats.&nbsp; The&nbsp; aim&nbsp; of&nbsp; this dissertation&nbsp; was&nbsp; to&nbsp; determine&nbsp; the&nbsp; most significant&nbsp; and&nbsp; relevant&nbsp; hydromorphological parameters&nbsp; in&nbsp; structuring&nbsp; macrophyte assemblages&nbsp; in gravel pit&nbsp; lakes along the Drina River floodplain and to determine the correlation between&nbsp; selected&nbsp; parameters&nbsp; and&nbsp; macrophyte quantitative&nbsp; indices.&nbsp; The&nbsp; research&nbsp; was&nbsp; carried out at the 18 gravel pit lakes (60 survey sectors) in&nbsp; Crna&nbsp; Bara,&nbsp; Badovinci&nbsp; and&nbsp; Lipnicki&nbsp; Sor&nbsp; and four natural fluvial lakes (13 survey sectors), in the&nbsp; Drina&nbsp; River&nbsp; floodplain&nbsp; during&nbsp; the&nbsp; summer months&nbsp; of&nbsp; 2015,&nbsp; 2016,&nbsp; 2017&nbsp; and&nbsp; 2018.Macrophyte&nbsp; vegetation&nbsp; was&nbsp; recorded&nbsp; in&nbsp; all&nbsp; 18 gravel pit lakes, in total supporting 31 taxa.&nbsp; The most&nbsp; abundant&nbsp; species,&nbsp; with&nbsp; highest&nbsp; tot al&nbsp; cover value&nbsp; were <em>Potamogeton</em>&nbsp; <em>nodosus,Ceratophyllum&nbsp;</em> demersum&nbsp; subsp.&nbsp; demersum,<em> Myriophyllum&nbsp; spicatum,&nbsp;</em> <em>Najas&nbsp; marina&nbsp;</em> and<em> Chara&nbsp; globularis</em>.&nbsp; Fluvial&nbsp; lakes&nbsp; supported&nbsp; 13 macrophyte&nbsp; taxa&nbsp; with&nbsp;<em> Vallisneria&nbsp; spiralis, Elodea&nbsp; canadensis,&nbsp; Callitriche&nbsp; palustris,Potamogeton&nbsp;</em> <em>natans&nbsp;</em> and&nbsp;<em> Nuphar&nbsp; lutea</em>&nbsp; as constant and dominant&nbsp; species.&nbsp; The values of all macrophyte&nbsp; quantitative&nbsp; indices&nbsp; found&nbsp; to&nbsp; be significantly&nbsp; higher&nbsp; in&nbsp; the&nbsp; gravel&nbsp; pit&nbsp; lakes compared&nbsp; to&nbsp; the&nbsp; fluvial&nbsp; ones.&nbsp; The&nbsp; cluster analysis&nbsp; revealed&nbsp; 14&nbsp; aquatic&nbsp; vegetation&nbsp; groups (VG).&nbsp; At&nbsp; 16&nbsp; out&nbsp; of&nbsp; 18&nbsp; gravel&nbsp; pit&nbsp; lakes&nbsp; 13 vegetation&nbsp; groups&nbsp; were&nbsp; revealed:&nbsp; VG1<em>Ceratophyllum&nbsp; demersum</em>,&nbsp; VG2&nbsp; <em>Ceratophyllum demersum- Valisneria&nbsp; spiralis</em>,&nbsp; VG3&nbsp;<em> Chara contraria</em>,&nbsp; VG4&nbsp; <em>Chara&nbsp; globularis</em>,&nbsp; VG5&nbsp;<em> Elodea&nbsp; canadensis,</em>&nbsp; VG6&nbsp;<em> Elodea&nbsp; nuttallii,</em>&nbsp; VG7&nbsp; <em>Najas marina,&nbsp;</em> VG8&nbsp;<em> Najas&nbsp; minor,</em>&nbsp; VG9&nbsp; <em>Nitellopsis obtusa</em>,&nbsp; VG10&nbsp; <em>Nuphar&nbsp; lutea,</em>&nbsp; VG11 <em>Potamogeton&nbsp; nodosus</em>,&nbsp; VG12&nbsp; <em>Potamogeton natans,</em> VG13&nbsp;<em> Potamogeton pectinatus</em>), Natural fluvial&nbsp; lakes&nbsp; supported&nbsp; 4&nbsp; vegetation&nbsp; groups: VG5&nbsp; <em>Elodea&nbsp; canadensis</em>,&nbsp; VG10&nbsp; <em>Nuphar&nbsp; lutea</em>, VG12&nbsp; <em>Potamogeton&nbsp; natans&nbsp;</em> and&nbsp; VG14&nbsp;<em> Typha latifolia</em>.&nbsp; All&nbsp; gravel&nbsp; pit&nbsp; lakes&nbsp; can&nbsp; be characterized&nbsp; as&nbsp; water&nbsp; bodies&nbsp; with&nbsp; good&nbsp; to maximal&nbsp; ecological&nbsp; potential,&nbsp; while&nbsp; all&nbsp; the fluvial ones can be characterized as water bidies with&nbsp; poor&nbsp; to&nbsp; moderate&nbsp; ecological&nbsp; status.&nbsp; The values&nbsp; of&nbsp; total&nbsp; suspended&nbsp; supstances,&nbsp; chemical and&nbsp; biological&nbsp; oxygen&nbsp; demand,&nbsp; total&nbsp; organic carbon&nbsp; and&nbsp; nitrates&nbsp; were&nbsp; significantly&nbsp; higher&nbsp; in the natural&nbsp; fluvial&nbsp; lakes compared to the gravel pit&nbsp; ones.&nbsp; Measured&nbsp; level&nbsp; of&nbsp; physico-chemical parameters&nbsp; indicating&nbsp; mesotrophic&nbsp; character&nbsp; of gravel&nbsp; pit&nbsp; lakes&nbsp; in&nbsp; Badovinci&nbsp; and&nbsp; mesoeutrophic&nbsp; in&nbsp; Lipnicki&nbsp; Sor,&nbsp; while&nbsp; all&nbsp; the&nbsp; gravel pits&nbsp; in&nbsp; Crna&nbsp; Bara&nbsp; could&nbsp; be&nbsp; characterized&nbsp; as eutrophic.&nbsp; Similar&nbsp; range&nbsp; values&nbsp; were&nbsp; calculated for&nbsp; LHQA&nbsp; for&nbsp; gravel&nbsp; pit&nbsp; and&nbsp; fluvial&nbsp; lakes&nbsp; (36 &ndash; 49). However, natural lakes&nbsp; showed significantly higher&nbsp; values&nbsp; for&nbsp; LHMS&nbsp; score.&nbsp; The&nbsp; above mentioned,&nbsp; indicates&nbsp; higher&nbsp; anthropogenic pressures&nbsp; on&nbsp; natural&nbsp; fluvial&nbsp; lakes&nbsp; compared&nbsp; to gravel&nbsp; pit&nbsp; ones.&nbsp; Physico-chemical&nbsp; and hydromorphological&nbsp; parameters&nbsp; together explained&nbsp; about&nbsp; 57&nbsp; %&nbsp; of&nbsp; the&nbsp; total&nbsp; variance&nbsp; of macrophyte&nbsp; assemblages&nbsp; with&nbsp; 16.57&nbsp; %&nbsp; of&nbsp; the shared effect. After accounting for the effects of physico-chemical&nbsp; parameters&nbsp; (17.02&nbsp; %), hydromorphological&nbsp; variables&nbsp; explained&nbsp; around 23 % of the total variance.&nbsp; The most significant water&nbsp; quality variables&nbsp; were: oxygen saturation, total&nbsp; organic&nbsp; carbon,&nbsp; surfactants, ,electroconductivity,&nbsp; pH&nbsp; and total alkalinity. The The most significant hydromorphology&nbsp; variables for&nbsp; structuring&nbsp; macrophyte&nbsp; assemblages&nbsp; were: riparian&nbsp; vegetation&nbsp; structural&nbsp; complexity, diversity&nbsp; of&nbsp; natural&nbsp; landcover&nbsp; types&nbsp; in&nbsp; riparianzone, shore structural habitat&nbsp; diversity, diversity of&nbsp; natural littoral zone, maximal&nbsp; lake depth, lake surface&nbsp; area,&nbsp; relative&nbsp; depth&nbsp; ratio,&nbsp; lake&nbsp; distance from&nbsp; r iver&nbsp; main&nbsp; channel&nbsp; and&nbsp; lake&nbsp;&nbsp; age.Hydrologycal parameters were explained 8.38 % of&nbsp; variance&nbsp; in&nbsp; structuring&nbsp; macrophyte assemblages.&nbsp; The&nbsp; most&nbsp; significant&nbsp; hydrology variables&nbsp; were&nbsp; the&nbsp; number&nbsp; of&nbsp; floods&nbsp; in vegetation&nbsp; season&nbsp; in&nbsp; first&nbsp; year&nbsp; when&nbsp; vegetation was sampled, and the number of spring floods in all four research years. These results&nbsp;&nbsp; confirm the direct destructive influence of summer floods&nbsp; on aquatic vegetation, as&nbsp;&nbsp; well as the indirect impact of&nbsp; spring&nbsp; floods,&nbsp; due&nbsp; to&nbsp; the&nbsp; impact&nbsp; on&nbsp; trophic status&nbsp; of&nbsp; water.&nbsp; Gravel&nbsp; pit&nbsp; lakes&nbsp; in&nbsp; te&nbsp; Drina River floodplain&nbsp; represent an optimal habitat&nbsp;&nbsp; for rare&nbsp; and&nbsp; threatened&nbsp; macrophyte&nbsp; flora.&nbsp; Of&nbsp; the total&nbsp; macrophyte&nbsp; species&nbsp; recorded,&nbsp; 30&nbsp; %&nbsp; were categorized&nbsp; as&nbsp; protected&nbsp; or threatened.&nbsp; At&nbsp; least one&nbsp; strictly&nbsp; protected,&nbsp; protected&nbsp; or&nbsp; threatened species&nbsp; was&nbsp; recorded&nbsp; in&nbsp; each&nbsp; gravel&nbsp; pit&nbsp; lake. Significantly&nbsp; higher&nbsp; values&nbsp; of&nbsp; conservation indices&nbsp; (C&nbsp; and&nbsp; Csp&nbsp; score)&nbsp; found&nbsp; to&nbsp; be significantly&nbsp; higher&nbsp; in&nbsp; the&nbsp; gravel&nbsp; pit&nbsp; lakes compared&nbsp; to&nbsp; the&nbsp; fluvial&nbsp; ones.&nbsp; High&nbsp; habitat diversity&nbsp; and&nbsp; conservation&nbsp; value&nbsp; of&nbsp; the&nbsp; sites have&nbsp; been&nbsp; recorded&nbsp; according&nbsp; to&nbsp; the&nbsp; National Rulebook,&nbsp; Annex&nbsp; I&nbsp; of&nbsp; Habitats&nbsp; Directive (NATURA 2000), Resolution&nbsp; no. 4 of the Bern Convention (EMERALD) and the European Red List&nbsp; of&nbsp; Habitats.&nbsp; Values&nbsp; of&nbsp; selected&nbsp; lake attributes can be used for early-design phases of future&nbsp; gravel&nbsp; extraction&nbsp; in&nbsp; the&nbsp; Drina&nbsp; River floodplain&nbsp; area,&nbsp; and&nbsp; in&nbsp; other&nbsp; similar&nbsp; sites. Therefore,&nbsp; general&nbsp; recommendations&nbsp; are&nbsp; that two gravel pit types should be excavated within the&nbsp; single&nbsp; extraction&nbsp; area&nbsp; in&nbsp; order&nbsp; to&nbsp; support pioneering charophyte vegetation and vegetation of typical eutrophic lowland floodplain lakes as well.&nbsp; The&nbsp; first&nbsp; hydromorphological&nbsp; lake&nbsp; type, suitable&nbsp; for&nbsp; stonewort&nbsp; species,&nbsp; should&nbsp; be excavated up to 100 m from river main channel, saving&nbsp; a&nbsp; surface&nbsp; area&nbsp; up&nbsp; to&nbsp; 1000&nbsp; m 2 and&nbsp; a relative depth ratio &gt; 5 %. The second gravel pit type&nbsp; should&nbsp; be&nbsp; located&nbsp; about&nbsp; 300&nbsp; m&nbsp; from&nbsp; river main channel, with preferable maximal depth inrange&nbsp; 3&ndash;4&nbsp; m&nbsp; (at&nbsp; least&nbsp; 2&nbsp; m&nbsp; depth),&nbsp; and&nbsp; a&nbsp; lake surface area between 10000 m 2 and 20000 m 2 (at least&nbsp; 4000&nbsp; m 2 ).&nbsp; Relative&nbsp; depth&nbsp; ratio&nbsp; may&nbsp; vary, but should be less than 5 %. Generally, all sites should&nbsp; be&nbsp; designed&nbsp; with&nbsp; the&nbsp; minimal&nbsp; impact to the&nbsp; riparian&nbsp; and&nbsp; shore&nbsp; zones.&nbsp; These&nbsp; proposed measures&nbsp; would&nbsp; considerably&nbsp; increase&nbsp; lake habitat diversity and their conservation potential. Creating&nbsp; gravel&nbsp; pit&nbsp; lakes&nbsp; as&nbsp; proposed&nbsp; in&nbsp; this dissertation&nbsp;&nbsp;&nbsp; would&nbsp; allow&nbsp; spontaneous recultivation&nbsp; of&nbsp; exploitation&nbsp; fields,&nbsp; remediation in&nbsp; order&nbsp; to&nbsp; improve&nbsp; water&nbsp; quality&nbsp; and renaturalization&nbsp; of&nbsp; habitats,&nbsp; which&nbsp; will significantly reduce, or completely eliminate, the costs of terrain technical recultivation.</p>

Anthropogenic lakes constitute a significant part of the Czech countryside water component which has not been given sufficient attention so far. The presented thesis deals with the assessment of variability of physico-chemical properties of water in 30 selected pit lakes in order to identify specific features associated with quarrying of different mineral raw materials, basin morphometry and trophic level of the lakes affecting the quality of accumulated water. In the second part of the thesis the author deals with the comprehensive limnological study of the Hromnické Lake with extreme water chemism resulting from excavation of pyritic shales and focuses on the phenomenon of meromixis especially. The results are based on the evaluation of physical properties of water in the lake vertical profile (temperature, conductivity, dissolved oxygen, pH, transparency and colour) and chemical analyzes of water samples collected from the surface and bottom of the lakes during the four seasons in 2003-07 (determination of Ca, Mg, Na, K, Nammon., NO3 - , SO4 2- , Cl- and alkalinity), including determination of chlorophyll-a. In the case study of the Hromnické Lake conducted in 2010-11, the analysis of hydrological regime of the lake, determination of PO4 3- , TOC, selected metals (Fe, Mn, Al, Zn, Ni, Cu, Co,...

This work applies advanced sampling (mark-release-recapture) and comparative approaches addressing the patterns in composition, structure and variability of larval trematode communities in three species of gastropod molluscs (Lymnaea stagnalis, Planorbarius corneus and Radix auricularia) at two nested scales of community organisation in typical Central European eutrophic environments. Hypothesis-testing with the application of null-model analyses, logistic regression modelling and multivariate randomisation techniques, revealed determinants of transmission rates, levels of infection and community structure in freshwater snail hosts in Central Europe and elucidated the mechanisms linking the spatial and temporal environmental variability with the action of complex community assembly rules in freshwater pulmonate snails.

Activity of enzymes was investigated in the soils of Norway spruce forests in the Bohemian Forest. The aim of the study was the determintation of the impact of temperature and plants dominant in understorey on the activity of extracellular enzymes in the soils in the watershed of Plešné and Čertovo Lake. The measurement of enzymes activities was conducted using the fluorometric method with model substrates.

Phosphorus is frequently a limiting factor for phytoplankton in freshwater ecosystems, because algae and cyanobacteria are able to incorporate it only in a dissolved inorganic form. Phytoplankton evolved several mechanisms to overcome phosphorus limitation. One of them is the production of extracellular phosphatases. These enzymes are excreted on the surface of cells or released to the environment. They hydrolyze organic molecules containing phosphorus, which can be then incorporated by cells. This mechanism can influence the competitiveness of algae living in environments that are characterised by long-term phosphorus limitation (that is caused e.g. by the effect of low pH). In this study the influence of phosphorus concentration and form on extracellular phosphatase activity under laboratory conditions was investigated. The two experimental strains of the genus Coccomyxa (Chlorophyta) were isolated from acidified localities with different phosphorus availability  Plešné Lake and Hromnické Lake. Extracellular phosphatase activity on a single-cell level was measured using the FLEA technique and fluorescence microscopy. The FLEA technique allows direct visualization of phosphatases on the cell surface by incubating the samples with the artificial substrate ELF® 97 phosphate. Extracellular...

The aim of urban concept is cadastral area of Brno – Holásky. This area is designated area for development in spatial plan for the city of Brno. Area is designated for housing, social care and education. The area has size of 42ha and it is defined by the railway in the east. From the south hit is V Aleji and U potoka street. The border continues along road towards shopping mall Olympia. The west border is consists by Holásky lakes. In the north the border goes through structure between V Aleji street and Ledárenská street. The area is relatively attractive mainly due the close connection nature sight Holásky lakes. Also interesting is location within the city of Brno. Altough the area is located outside the larger city center, there is a good accessibility to the center. The new residential housing area provides space for approximately 1400 inhabitants. The structure and vertical articulation is based on response of the surrounding buildings. The V Aleji street defines an axis that helps to create new space for central square. Another axis it the road from the V Aleji street towards Holasky lakes. This is major line connecting residential area and the surrounding with the area of lakes. This street also devide the area into two parts. Right part, northern, consisting with coherent block with dimension of 200x300 metres. Outside part of the block consists of blocks of flats. The inner part is filled with family houses and public space belonging to blocks of flats. Part of the block is also elderly house. The left, southern, part concludes the L shape block of current housing. Again the edge of block is formed by blocks of flats and family houses in inner part. At the end of the axis heading to Holasky lakes is kindergarten in direct relation to natural park. Next to the Holásky lakes there will be space for sports and recreation. Will include beach volley, football and wooden pier on lake. In this part also will starts cycling path to the city center. Stationar