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ACTIVITIES (Europe). . This is PAGE 1. (of 4 Pages) of a special Web-published Version of sub-Project Documentation, last revised on 16 February 2009. The Main un-edited Project-level Documentation is available in hardcopy form for Project Research Assistants and other Authorized Users. |
. Project Title [GB] :.."A JOINT STRATEGY FOR THE PROTECTION OF THE ENDANGERED UNDERGROUND ENDEM Proteus anguinus AND ITS NATURAL KARST HABITAT IN THE TREBIŠNJICA RIVER VALLEY" Eastern Herzegovina, Bosnia & Herzegovina. Project Title [BiH-Lat] :.."ZAJEDNIČKA STRATEGIJA ZA ZAŠTITU UGROŽENOG PODZEMNOG ENDEM ČOVJEČJA RIBICA (Proteus anguinus) I NJEZINOG PRIRODNOG KRŠKOG STANIŠTA U DOLINI RIJEKA TREBIŠNJICA." Istočna Hercegovina, Bosna i Hercegovina. Project Title [BiH-Cyr] :.."ЗАЈЕДНИЧКА СТРАТЕГИЈА ЗА ЗАШТИТЕ УГРОЖЕНОГ ПОДЗЕМНОГ ЕНДЕМА ЧОВЈЕЧИЈА РИБИЦА (Proteus anguinus) И ЊЕГОВОГ ПРИРОДНОГ КРШКОГ СТАНИШТА У ДОЛИНИ РИЈЕКЕ ТРЕБИШЊИЦЕ." Источна Херцеговина, Босна и Херцеговина. |
| Sub-Project
Vrelo "Oko" (Zasad) - Webpage Contents for PAGE 1..."Introductory
Information, Background Notes and Proposals" :
.....Sect. 1....Site Location. .....Sect. 2....General Description and Historical Overview. .....Sect. 3....Karst Hydrology. .....Sect. 4....Karst Water Quality Monitoring, Species Sightings Records & Habitat Suitability. .....Sect. 5....Importance of the Site as a Habitat & Special Importance to the Project's Aims. .....Sect. 6....General Site Condition. .....Sect. 7....Incorporation of the Location into a Proteus anguinus Habitat Restoration Project, May 2003. .....Sect. 8....A Proteus Habitat Conservation Plan for the Vrelo "Oko" (Zasad) Location. .....Sect. 9....General Notes Relating to the On-going Physico-Chemical and Micro-Biological Qualities of the Karst Water in Vrelo "Oko" (Zasad). .....Sect. 10...The Vrelo "Oko" (Zasad) Conduit Aquifer Cave System. .....Sect. 11...A Proteus Habitat Site Protection & Preservation Plan for the Vrelo "Oko" (Zasad) Location. .....Sect. 12...Notes on the Austro-Hungarian Heritage at Vrelo "Oko" (Zasad). .....Sect. 13...Notes on the Collection and Disposal of Waste Within the Trebinje Municipality. .....Sect. 14...Bibliography. Click on the underlined Links.above to move down to the Sections quickly. |
Speleološko Društvo "Zelena Brda", Trebinje, RS-BiH - Спелеолошко Друштво "Зелена Брда", Требиње, РС-БиХ. . .Sub-Project Title :...ВРЕЛО "ОКО", (Засад), Требињско Поље - VRELO "OKO", (Zasad), Trebinjsko Polje. THE RESTORATION OF THE VRELO "OKO" (ZASAD) PROTEUS ANGUINUS HABITAT LOCATION. Page 1. Introductory Information, Background Notes and Proposals. Page 2...Habitat Restoration Programme Illustrated Progress Reports. Progress with Phased Action Plan - Part 1. (Phase 1.) "The Permanent Removal of the encroaching and structurally-damaging bush and tree growth". Page 3. Habitat Restoration Programme Illustrated Progress Reports. Progress with Phased Action Plan - Part 1. (Phase 2.) "The Permanent Removal of all Dumped Waste Materials from the Site". Page 4. Habitat Restoration Programme Illustrated Progress Reports. Progress with Phased Action Plan - Part 1. (Phase 3.) "Reconstruction of the Masonry Infrastructure". (The Web-published version of this Document does not contain Karst Water Physico-Chemical Analysis Data, Bacteriological Reports or Species Sightings Records.) .Operational
Progress Reports by B. Lewarne, Honorary Science Officer.
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| 1...SITE
LOCATION :
There are many karst springs within the Balkans which have the name "Oko". The word "Oko" means "eye" and refers to the circular appearance of such locations when seen from a great distance, especially when they contain static or overflowing water. Within the Society's Website pages, we always clearly identify the location of the "Oko" to which we are referring. This
location is in the eastern end of Popovo Polje, at the western end of its
geomorphological sub-division of Trebinjsko Polje, within the Trebinje
Region / Trebinje Municipality of the "Republika Srpska" territory of Bosnia
& Herzegovina.
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Photo VOZ 1.1..Illustrates the neo-circular top of the masonry shaft-lining protruding above the flood-water issuing from Vrelo "Oko", within the water-overflow-containment canal, at Zasad. The view is taken looking upstream during the month of March, 2002. (Photo : B. Lewarne, 01 March 2002.) |
Illustrates the position of the neo-circular top of the masonry shaft-lining of Vrelo "Oko" protruding above the polje floor, within its canal at Zasad. The aerial view was taken for the Society by one of our local contacts, Mr Zoran Petrović, who has taken up the activity of para-gliding. The view was recorded in the late afternoon of 03 November 2005. A closer view of the Vrelo "Oko" surface shaft in Photo 1.0B. below visibly indicates the position of the water within the karst conduit aquifer. Because of the visible karst water level down within the shaft and by virtue of there being no overflowing water from Vrelo "Oko", the karst groundwater conditions between here and Ljubomirsko Polje can be said to be at medium to low levels. Vrelo "Oko" (Zasad) is a karst window. . Photo
VOZ 1.0B..(left)
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Photo VOZ 1.2..Illustrates the location of Vrelo "Oko", in greater environmental context at Zasad. Note the waste materials lining the floor of the water-overflow-containment canal. The view is taken looking upstream during the month of March, 2002. (Photo : B. Lewarne, 01 March 2002.) |
Photo VOZ 1.3..Illustrates the location of Vrelo "Oko", at the foot of Brda Ilino at Zasad. The proximity of a large cluster of foul-water drains and sewers will affect the water-quality in Vrelo "Oko". The view is taken looking upstream during the month of March, 2002. (Photo : B. Lewarne, 01 March 2002.) |
Photo VOZ 1.4..Illustrates a contextual view of the water-overflow-containment canal. A series of regularly positioned indents on the top of the protruding shaft structure indicates anchor points for a former metal grille, which has now been removed. The view is taken looking downstream during the month of March, 2002. (Photo : B. Lewarne, 01 March 2002.) |
Photo VOZ 2.1..Illustrates the general problem of plant growth, even in March. Note the identical modern construction of the Vrelo "Oko" shaft collar and the adjacent canal walls. (Photo : B. Lewarne, 01 March 2002.) |
| 3...KARST
HYDROLOGY :
. .....3.1...Functionality : This is an allogenic or "B-Type" spring, which has a large difference between Qmin and Qmax. As of yet, we have no actual flow data. The surrounding images below show the karst spring both in overflow condition and completely without water. There is a permanent water flow in the cave passages below, hence, Qminshould not be regarded as being zero. We also have reason to believe that this site is actually an estavelle but that its ponor mode of functionality is prevented by the hydro-melioration infrastructure on the surface, notably the canal and its downstream-end weir, which prevents back-flow during post high-water conditions from both the polje-floor and the Trebišnjica River into the entrance shaft. Underground at the bottom of the stone-lined shaft, we may also discover a purpose-built masonry structure designed to impound the permanent underground flow in order to maintain a useful minimum level of water for utilization. . .....3.2...Hydrological Connections : During low flow conditions, the water supply is fed by percolation from the hinterland. At high water and in overflowing condition, direct connections have been proven with the ponors in Ljubomirsko Polje :- - Sodium fluorescein dye-testing investigations were carried out in this area by the Energoinvest Company of Sarajevo for the HET Co. between the years 1956-1964. [We have been trying to locate the archive records of the work of the Energoinvest Company, thus far without any success.] If it is eventually proven that the site is an estavelle, a programme of dye-testing will be undertaken to establish the down-stream hydrological connection(s), if we cannot locate the record of any such work having been done previously. . [Return to Top of Page.] |
.. Photo VOZ 3.1..Illustrates the location under zero flow conditions, in July 2004. (Photo : B. Lewarne, 08 July 2004.) |
Photo VOZ 3.3..Illustrates a rapidly rising water level from a zero point, in September 2003. (Photo : B. Lewarne, 11 September 2003.) |
Photo VOZ 3.2. Illustrating water-output under low flow conditions, in March 2002. (Photo : B. Lewarne, 01 March 2002.) |
| 4....KARST
WATER QUALITY MONITORING, SPECIES SIGHTINGS RECORDS AND HABITAT SUITABILITY
:
.....4.1...Karst Water Physico-Chemical Quality : This location is being monitored for its water quality, the results of which are entered into the Project's Karst Water Quality Database. Photo VOZ 3.2. above indicates chemical analysts D. Banjak and D. Janković testing the water output of Vrelo "Oko" for the very first time at this former Proteus Habitat, on 01 March 2002. . .....4.2...Karst Water Bacteriological Quality : This location had its first sample extracted for Bacteriological Examination at the time of the first appearance of water in the vertical shaft in the Autumn / Winter of 2004. . .....4.3...Species Sightings : This location is on the "Čučković List" - but until September 2006., this was only as a former.Proteus Habitat because the animal had not been recorded at this site since before 1960. . .....4.4...Habitat : - 01 March 2002 - 2006 : The current and on-going condition of this site is not conducive to it being a healthy aquatic habitat for Proteus anguinus or any other hypogean faunal species. It is very badly polluted and contaminated. - September 2006 to the present day : The site is now a recovered active hypogean habitat, due to the removal of all localised pollution and contamination sources. It is now a re-confirmed Proteus anguinus Habitat Location. . [Return to Top of Page.] |
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| 5....IMPORTANCE
OF THE SITE AS A PROTEUS HABITAT AND ITS SPECIAL LOCATIONAL IMPORTANCE
TO THE PROJECT'S AIMS :
The site was once recognized as being a habitat for Proteus anguinus. Čučković reported in the 1960's that the site was disappearing under accumulating rubbish. The site is especially important to restore as a viable Proteus habitat in view of its convenient and close proximity to the headquarters of the Speleološko Društvo "Zelena Brda" and to the administrative and political centres of the Municipality. Experimental scientific procedures would be easy and convenient to undertake and the location would be eminently suitable for a long-term karst hydrological data series to be initiated. Its convenient geographical location and its comparative smallness in size also favours the initiation of a Site Conservation Management Plan, which could be regularly monitored and maintained at very low cost and without the problems of time and fuel costs associated with more distant and remote locations. The location easily lends itself to being developed as an example and a "demonstration site" of how to conserve and preserve a typical Proteus Habitat and in this aspect has great potential. |
. CURRENTLY CONFIRMED STATUS OF THIS HABITAT (2009 onwards) : Active Hypogean Habitat. . [Previous Status - 2007-2008 : Active and Recovering.] [Previous Status - 2005-2006 : Recovering.] [Previous Status - 1968-2004 : Sterile (unreservedly).] |
| 6.
GENERAL SITE CONDITION :
. .....6.1...01 March 2002 : Since the facility was built, its structural integrity has been generally well maintained, probably due more to the high quality of the original engineering than to subsequent preventative maintenance!! The scenario as at 01 March 2002 reflected that of the past 40+ years and was one of disuse, disrepair and general mis-management -or rather lack of management- whereby, in the absence of a viable Municipal Waste Regulation Authority, the surrounding population use the circular shaft as a dumping site for general household and industrial refuse. The prevailing Municipal conditions in the post-Bosnian War Period from the 1990's did nothing other than exacerbate the situation, where other priorities were perceived to be more important than maintaining a clean environment and clean natural water supplies. . During our visit at this time, it was very late winter and the location was overflowing with water. It was not possible to see down the entrance shaft under these conditions. Additionally, the offending tree and bush growth within the location had not yet begun their seasonal leaf-growth. . However, it was possible to see the surface outlet canal, which leads the overflowing water during the wet season directly to the main channel of the Trebišnjica River. The canal was in a very good structural condition but was scattered with a variety of domestic and industrial refuse, as is illustrated in.Photo. VOZ 1.2. at the top of this page. This added to the general sense of environmental neglect which pervaded the area. . [Return to Top of Page.] |
Photo VOZ 6.1..Illustrates the prevailing overgrown conditions, in August 2002. (Photo : L. Satterley, 07 August 2002.) |
Photo VOZ 6.2...Illustrates the surface of the dumped waste in the shaft of Vrelo "Oko", in August 2002. Note the wide variety of waste materials, including the lead-acid car battery. (Photo : B. Lewarne, 07 August 2002.) |
6.
GENERAL SITE CONDITION (continued) :
. .....6.2...07 August 2002 : The situation at the Site on 07 August of 2002 was very different to that of 5 months previous. In the intervening period, the karst water-level had retreated to its normal summer position down in the karst underground, leaving the location high and dry. However, we now faced a different barrier preventing easy access down into the Site. A profuse wall of dead and living foliage, tree roots and branches seemed to fill the entire shaft. Couple this with the most appalling stench arising from the damp depths! Photo VOZ 6.1. immediately above, shows the location to be in a disgraceful condition, heavily overgrown and filled with rubbish to within 5.4 metres (17.7 feet) of the top wall of the shaft. This situation was by no means unique to the locale but was ubiquitous throughout the Municipality at the time. Čučković reports that it was in a similar condition in the 1960's and was full of rubbish even at that time. . In addition, the stone-built infrastructure of the karst spring was under threat by the unchecked establishment and growth of small trees and bushes within the circular vertical shaft structure, see Photo VOZ 6.1. immediately above. The root development of the flora is developing within the mortared joints of the masonry and causing some localised structural damage and displacement of large masonry blocks, as is clearly indicated in Photo. VOZ 3.1. above. . .....6.3...After May 2003 : The condition of the Site after inclusion in the Habitat Restoration Programme is reported upon in the various progress reports detailed elsewhere in the Vrelo "Oko" (Zasad) Webpages.. |
Photo VOZ 6.3....Illustrating in greater detail the surface of the dumped waste in the shaft of Vrelo "Oko", in August 2002. (Photo : B. Lewarne, 07 August 2002.) |
Photo VOZ 6.4....Illustrating in greater detail the surface of the dumped waste in the shaft of Vrelo "Oko", in August 2002. (Photo : B. Lewarne, 07 August 2002.) |
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HABITAT RESTORATION PROJECT, May 2003. Rather than just passively monitoring the site, this would commit us to a programme of activity to restore the location to a pristine condition that would once again support a Proteus Habitat. The incorporation was formally activated in May 2003 with the completion of a formal Habitat Restoration Programme Document for Vrelo "Oko" (Zasad) and it was planned to begin work on restoring the site during the Society's brief visit to Trebinje in early September 2003. Specific details of the Progress
of the Habitat Restoration Programme are given in the other Webpages
dedicated to this sub-Project.
VRELO "OKO", (Zasad), - A Proteus anguinus HABITAT RESTORATION PROGRAMME. 7.1. Proposal : To restore the Vrelo "Oko" former Proteus anguinus Habitat Location to its original, physically clean and safe condition, to prevent further localised contamination of the clean underground karst-water supply and thus to encourage the return of various Hypogean Faunal species, including Proteus anguinus, to a viable aquatic habitat. . 7.2. A Phased Approach in Restoring the Habitat Location : The historical background, natural karst functionality and utilitarian use of this site is documented elsewhere in this Webpage. The four principal concerns in this project of Site and Habitat Restoration are, in order of priority :- i)..Permanent removal of the encroaching and structurally-damaging bush and tree growth; ii)..Permanent removal of all dumped waste materials from the site; iii)..Condition and Stability of the man-made masonry infrastructure and the necessary reconstruction work required to restore it to a structurally-safe condition for the long-term future; iv)..Initial restoration of the chemical and biological purity of the aquatic environment. For the purposes of public and institutional education, an additional aspect is necessary at all stages :- v)..To record the Restoration Project at various stages in film and digital photographic formats. Considerations which, for practical purposes, take us beyond the initial Restoration and Clean-up Stage, will be included in a PROTEUS HABITAT CONSERVATION PLAN. The practical details and associated problems of each of the above four priorities are dealt with in the Action Plan below. . 7.3. Phased Action Plan & Time-scale : .....7.3.1. Voluntary Labour and Available Manpower Resources : The Habitat Restoration Project is a purely Voluntary Sector activity and, as such, will benefit from having the necessary manual-labour aspect free of costs. Although this aspect of the Project is not labour-intensive, there remains the underlying associated problem of manpower availability. We propose to undertake and co-ordinate the majority of the phased programme of works when there is an unusually large number of available local and international speleologists converging on Trebinje during specific months of each year. Any additional input to the Project must be co-ordinated at a local level by the Speleološko društvo "Zelena Brda". As of July 2004, various ideas on progressing this latter point are being considered locally. .....7.3.2. Site Accessibility : There is the additional situation that this hydrologically-active location is only "water-free" within the entrance shaft for the summer months. . .....7.3.3. Phased Action Plan, Part 1. (PHASE 1.) ....."The Permanent Removal of the encroaching and structurally-damaging bush and tree growth" : Prevailing Situation as of 07 August 2002 : The site is totally overgrown within the structure by long-established trees and bushes. Many new tree saplings are also establishing their roots. All such growth is centred on the cracks and crevices in between the blocks of stone constituting the stone-lined infrastructure, which is being damaged and displaced as the root growth increases. There is additional root damage by sapling growth on the outside of the structure at ground-level. Some small-scale work was undertaken to start clearing a route through the undergrowth and thick vegetation, so that a structural survey could be undertaken, a photographic record of the waste dump inside could be taken and the Site generally assessed as a possible Restoration Project. Action Plan : To remove 100% of all tree and bush growth by cutting it down and physically removing all accessible roots, so as to facilitate ease of access into the shaft for the removal of the rubbish from the shaft in Phase 2. of the clearance work. Clearance should also be done around the outside perimeter of the stone containment structure. Complete removal of all root growth may take persistent efforts over several years to fully achieve. All such "green waste" should be burned at the surface nearby. Work should start on this in September 2003 and should be 98% completed within 1 day. Subsequent visits over the next few years should take in repeated sessions of plant and root removal work, until the masonry repair programme in Phase 3. permanently prevents such growth from re-appearing. . .....7.3.4. Phased Action Plan, Part 1. (PHASE 2.) ....."The Permanent Removal of all Dumped Waste Materials from the Site" : Prevailing Situation as of 07 August 2002 : The site represents a miniature waste landfill operation, is an utter disgrace and is a sad reflection of the irresponsible attitudes towards the natural environment by the surrounding inhabitants!! Unfortunately, it is far from being a unique example, which is why we shall be thoroughly recording the clean-up event for general consumption by those at all levels in the Trebinje Municipality, via the main Project's Public Education Programme. The fact that the site is an active karst spring of great capacity and a former Proteus Habitat will add weight to the message we wish to convey. The types of non-biodegradeable rubbish that have accumulated in the Vrelo "Oko" access shaft are :- .....a).lorry tyres;..b) chemical containers and oil drums; c).car batteries;..d) building waste such as concrete building blocks; .....e) galvanized sheet metal; f) miscellaneous scrap metal;..g) plastic pipes; h) plastic sheet; i) miscellaneous plastic items .........such as containers and broken items;..j).miscellaneous glass items;..k) miscellaneous wood items; .....l) textiles; m) biological waste. An additional problem is that the mass of rubbish is of the order of two metric tons in weight and because of the prevailing obnoxious conditions, may take several seasons to remove. However, at the time of this survey, the smaller of the two large lorry tyres was removed, together with the car battery and other sundry items that were easily accessible. Action Plan : It is proposed to hire a trailer for transporting the rubbish from Vrelo "Oko" to an authorized refuse site, located elsewhere in the Trebinje Municipality. Although it is estimated that all the accumulated material in the bottom of Vrelo "Oko" presents a mass of about 2 tonnes, at least 25% of this mass represents large masonry limetone blocks, displaced from the structure by the root systems of the trees. Work started on this in September 2003 and will continue in successive years until 100% complete. The following order of activity is proposed, all stages of which should be filmed and photographed for publicity and educational purposes : . ..a) The requisitioned trailer (or other receptacle) would be placed on-site within a few metres of Vrelo "Oko" in readiness to receive the waste material as it is removed from the circular containment shaft. ..b) A rope and pulley-based haulage system would be erected at the top of the shaft to facilitate the safe removal of the heavier components of the waste, such as lorry tyres. ..c) All rubbish would then be hauled to the surface and transferred into the trailer. ..d) All displaced masonry blocks should be set aside on-site for Phase 3. (Reconstruction of the Masonry Infrastructure). ..e) The trailer containing the rubbish would then be towed away to the nearest Municipal Refuse Site for disposal. . Physical inspection, exploration and hydrological monitoring of the fully accessible periodic karst spring-cave can then proceed again after a lapse of at least 40 years. Financial Considerations : The Main Project's funding can more than adequately finance any trailer-hire, fuel and landfill tax costs incurred during PHASE 2. of the Site Restoration Programme. . .....7.3.5. Phased Action Plan, Part 1. (PHASE 3.) "Reconstruction of the Masonry Infrastructure" : Prevailing Situation as of 07 August 2002 : It is already clear from a detailed perusal of the internal visible parts of the circular shaft that the visible bulk of the original Austro-Hungarian Masonry Infrastructure is in a reasonable condition. Thankfully, the masonry blocks were set within the karstic limestone bedrock mouth of the spring-cave and as a result, have an excellent structural foundation. It is also clear that many of the displaced masonry blocks are laying in with the thick pile of accumulated rubbish. Prevailing Situation as of 05 July 2004 : With the removal of the lorry tyres and some of the other large metallic objects from the rubbish pile, more masonry blocks came into view. Action Plan : It was proposed to replace all the displaced masonry blocks into their original positions and to universally fill all the joints between the component blocks of the circular shaft structure and the lower rectangular section. Specialist advice is to be sought on the most suitable formula for a mortar mix which must not have any effect on the water quality of the habitat. This may take several seasons to complete. Financial Considerations : The Main Project's funding was more than adequately able to finance any materials costs incurred during PHASE 3. of the Site Restoration Programme. . .....7.3.6. Phased Action Plan, Part 1. (PHASE 4.) ....."Restoration of the Chemical and Biological Purity of the Local Aquatic Environment" : - Original Action Plan : This part of the Site and Habitat Restoration Programme can only begin after PHASE 2. is 100% completed. The Main Project's Physico-chemical and Bacteriological Monitoring Programme should be providing analyses of water issuing from the Location from 2002 onwards and this will provide useful comparative data for trend-analysis as the Vrelo "Oko" clean-up and Restoration Programme progresses. Analyses have been arranged to be undertaken annually at initial appearance of water (pre-overflow conditions) and periodically after initial overflow from the shaft. The results from this Location can be compared with other nearby confirmed and active Proteus Habitats. .....- The first procedure is to clean down all the exposed surfaces of the masonry infrastructure. This must be done only when water start to appear at the base of the stone-lined shaft of Vrelo "Oko" and, more specifically, begins to rise up the shaft from the cave portal at the bottom. This procedure must not use any types of detergents or other chemical cleaning agents. It is advised that coarse bristle-brushes are used to scrub all stone surfaces. The idea is to ensure that none of the washings enter the cave system below but are flushed up and out of the Site with the rising water. .....- Investigation of the cave passages of the Vrelo "Oko" System may be necessary to identify and remove any residual foreign objects that may have ingressed into the cave passages and which may be the possible cause of contamination. - Subsequently Modified Action Plan : This .....- The results of the Chemical and Bacteriological Analyses of the karst water issuing from the Site over several "hydrological years" will have indicated the presence of any localised problems associated with leaking sewers and other household or domestic contaminants in the Zasad urban area. These can then be traced back to the relevants cause(s) and the matter taken to the relevant Competent Authorities for remediation. . 7.4. Acknowledgements of Practical Help, Advice and Assistance from non-Project Workers. All practical help offered to the Habitat Restoration Programme by local residents and others who are not formal Project Workers at Vrelo "Oko" will be acknowledged here. You have our most sincere thanks and your efforts are deeply appreciated. .....1. Mr Zoran Petrović..-..We would like to formally thank this local resident for his great practical help in 2002, 2003, 2004, 2005, 2006 and 2007 with the clearance of the tree and bush growth and for helping with some of the clearance of the rubbish from Vrelo "Oko" at the same time. We are also aware of his efforts in trying to educate the local community about the Project and especially about the importance of not fouling the canal area or the shaft of Vrelo "Oko" with waste materials. Mr Petrović has also become involved in the activity of para-gliding during which he has undertaken detailed aerial photography of the location. One such image can be seen in PART 2. of the Vrelo "Oko" (Zasad) Webpages. .....2. - 8...A PROTEUS HABITAT CONSERVATION PLAN FOR THE VRELO "OKO" (ZASAD) LOCATION. The fact that we MUST visit the site as a dedicated and routine procedure is to ensure that the surrounding population (and others) do not use the site as a dumping ground for their waste materials!! However, there is a long-term, permanent answer even for this problem. 8.1...Proposal : To ensure that the optimal conditions for maintaining a viable Proteus Habitat are maintained as an on-going process. Unfortunately, this simple proposal is not as simple to fulfil as it is to state. It will need a determined effort simultaneously in many directions. The Plan below detailed a course of action to follow. . 8.2. Phased Action Plan, Part 2. (PHASE 1.) : .....8.2.1...To educate the local Community at Zasad into the benefits of adopting the civic responsibility of maintaining a clean environment in and around the Vrelo "Oko" location, mainly in the canal but also in the land above the karst aquifer; ie. clean = safe; no rats; aesthetically pleasing; fresh smelling; healthy. .....8.2.2...To positively discourage the use of Vrelo "Oko" as a dumping ground by our prompt clearance of any waste that may appear from time to time. .....8.2.3...To prevent the use of Vrelo "Oko" as a dumping ground by designing, constructing and installing a metal cover to be permanently fixed to the top. This may take the form of a very thick guage steel grill with a mesh or a complete sheet metal cover. Incorporated into this must be a very strong access door, with an integral lock. All metal components are to be of stainless steel. .....8.2.4...To undertake an annual inspection of the structural condition of the masonry infrastructure, taking the necessary action to undertake immediate repairs to any defects. .....8.2.5...To undertake an annual internal and external inspection of the Site for the location of any new growth of flora and to remove it if any is found. .....8.2.6...To make an attempt to actively involve the relevant Competent Authorities in the Conservation Plan by seeking to encourage them to take some responsibility for it. .....8.2.7...To continue with the long-term chemical and bacteriological monitoring of the karst water environment and to take the necessary action if this is found to deteriorate at any time. .....8.2.8...To encourage the use of controlled water-extraction from the cleansed Site for various purposes by the immediate community at Zasad, in keeping with the fact that we are trying to re-establish the Location as a viable Hypogean Habitat. A suitable submerged sump-structure should be used in conjunction with an agreed maximum permissable extraction rate, in order to guard against inadvertant extraction of Hypogean Species with the water. .....8.2.9...To protect local residents from the dangers of having a deep, open vertical shaft in the middle of their neighbourhood. . 8.3...(8.2.6. Specific) - Attempts to Contact and Involve : Republika Srpska Republički Zavod za Zaštitu Kulturno Istorijskog i Prirodnog Nasleđa, Odelenje Trebinje. .
OF THE KARST WATER IN VRELO "OKO" (Zasad) : . 9.1. Base-line Dates for Long-term Water Quality Profiling : .....- Sampling of the karst water at Vrelo "Oko" (Zasad) for Physico-Chemical Analysis and the long-term profiling of such values began on 01 March 2002. This type of analysis is undertaken internally by Project Members, using the extensive modern technical resources of the Project. The main consultant analyst is Mr. B. Lewarne, of the Devon Karst Research Society - the UK arm of the Project's partnership. The Project's local Chief Analyst is Mr. Dejan Janković, of the Speleološko društvo "Zelena Brda", the local arm of the Project's partnership in RS-BiH. .....- Sampling of the karst water at Vrelo "Oko" (Zasad) for Microbiological Examination and the long-term profiling of such values began on 07 December 2004. For most of each year, again we rely on local Project Members to undertake the actual sampling procedure. However in this case, the actual analysis is undertaken externally to the Project, which commissions such work on a commercial basis through a competent local health laboratory. .....- Sampling of ponor-input water at the known head of the karst conduit aquifer is now in the planning stage. . 9.2. Physico-chemical Analysis : The physico-chemical profile of the karst water quality of this site is to be compared with that derived from other locations also proven to be connected with same ponor system. It is planned to co-ordinate future water sampling and analysis events such that several sites within the same conduit aquifer "system" are undertaken as closely together on the same day as is possible. This will enable us to evaluate the Vrelo "Oko" water quality through time and in context with the water quality of the other outlets in the same hydrological system, some of which are not situated below or in the vicinity of villages or urban areas. . 9.3. Microbiological Analysis : The bacteriological profile of the karst water quality of this site is to be compared with that derived from other locations also proven to be connected with same ponor system. It is planned to co-ordinate future water sampling and analysis events such that several sites within the same conduit aquifer "system" are undertaken as closely together on the same day as is possible. This will enable us to evaluate the Vrelo "Oko" water quality through time and in context with the water quality of the other outlets in the same hydrological system, some of which are not situated below or in the vicinity of villages or urban areas. Water sampling for microbiological examination is always accompanied by a simultaneous physico-chemical analysis at the site to provide dynamic values of the karst water quality. The Vrelo "Oko" site represents a "karst window" into a karst conduit-aquifer, through which we are observing the rapid transit of karst underground water from Ljubomirsko Polje to another location downstream. , At this and other surrounding locations, Trebinjsko Polje forms a local overflow base-level of erosion for Ljubomirsko Polje. . It was estimated that the clearance of rubbish from the surface shaft should be completed by 2006, thereby giving the possibility of access into the cave system during the following year. Although now completely cleared of rubbish, access to the interior remains partly blocked by cave boulders.
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.......i)..that.Proteus anguinus is a special endemic species, both recognized as such and protected by Legal Statute; .....ii)..that Proteus Habitats are recognized in Legal Statute as special Protected Sites; .. ...iii)..that Vrelo "Oko" in particular is recognized as a Cultural, Historic and Natural Heritage Feature, by having been placed on the Official National List of such Objects and thus, is recognized in Legal Statute as such; ......iv)..that there is a national (legal) system in place for the routine strict inspection of all such sites by the Competent Authorities and to ensure that such locations as are recognized by any of the above-given legal status, are in a good state of repair and preservation and are not being violated by illegal activities. This also assumes the co-existence of strict legal penalties for offenders. In
reality, such assumptions as are illustrated above cannot be made in the
case of RS-BiH Territory. In the post-Bosnian War era, where the Legal
Systems are in a contant state of flux and development and the Constitution
of each of the two Political Entities is under regular change. It must
also be stated that
RELEVANT EXTRACTS FROM BiH-RS CONSTITUTION : .....Section
2. HUMAN RIGHTS AND FREEDOMS.
.....Section
3. ECONOMIC AND SOCIAL ORDER.
RELEVANT BiH-RS ENVIRONMENTAL LEGISLATION AND STATUTES IN LAW : Of
relevance is the following www entry by the BiH Federal Ministry of Physical
Planning and Environment, dated 28 October 1998 :-
INVOLVEMENT OF STATE AUTHORITIES AND INSTITUTIONS. As a first preparatory move, each of these levels will be approached at the current HABITAT RESTORATION PROGRAMME stage of work, so that we may guage interest (or disinterest) and identify useful and effective contacts for the future.
12...NOTES ON THE AUSTRO-HUNGARIAN HERITAGE AT VRELO "OKO" (ZASAD). . The area covered by the Region and Municipality of Trebinje in Eastern Herzegovina was once a very important strategic, military territory of the Austro-Hungarian Empire. Its contiguous border with the historic Kingdom of Montenegro and the close proximity of the former Imperial Naval port of Kotor (Cattaro) resulted in the construction of many hilltop fortifications and other military infrastructure, most of which still survives to this day. The town of Trebinje was also geographically very important to the expansionist ambitions of Austro-Hungary and was the location of a major Imperial Garrison. Two of the many benefits of the period combining firstly, from 1885 (when the Austro-Hungarian Empire given an internationally-approved Mandate to occupy Bosnia & Hercegovina) and secondly, continuing from 1908 (when Austro-Hungary unilaterally annexed Bosnia & Hercegovina), was the hydro-melioration of the karst in Bosnia & Herzegovina and the introduction and construction of a network of fresh water supplies. In many locations, these two aspects came together in a single project as at Vrelo "Oko", (Zasad). As a matter of interest, the hydro-melioration of Trebinjsko Polje was achieved by dealing with a number of locations in the same way as at Vrelo "Oko" and which, under the original natural conditions, also replicated Vrelo "Oko". Another great benefit of the Austro-Hungarian Period was through the enactment of Laws in Statute for the protection of Caves, Cave Habitats and the Hypogean Fauna. . Searching for the original documentation relating to the design and construction of such projects as that at Vrelo "Oko", (Zasad) has not been an easy task. There are several possible sources of information. 1.
The Austro-Hungarian Imperial Archives :
Unfortunately,
we are not always blessed with such easy means of access to vital and otherwise
very interesting information. In the case of localised small projects such
as the hydro-melioration at Vrelo "Oko", meticulously accurate drawings,
plans and supportive documentaion would have undoubtedly been drawn up
and equally undoubtedly would have been archived in the typically efficient
way that Austro-Hungary organized its administrative affairs. In the case
of Vrelo "Oko", we have hope that such documentation survives because,
as alluded to earlier, it was one single hydro-melioration project in a
whole related series of such local ones dedicated to achieving the greater
aim of the hydro-melioration of Trebinjsko Polje - a fairly large-scale
project of considerable technical achievement.
2.
Bosnia & Herzegovina State Archive :
3.
Trebinje Regional and Municipal Archives :
The nub of the problem of refuse collection and its subsequent disposal was this :- .....i) There was no organized system of regular refuse collection by the Municipal Authority, either on a house to house or street by street basis. The Municipality then began hiring large waste skips to be strategically placed at various locations in the main town and which could be used by households in which to dump their domestic waste. .....ii) The policy for waste disposal was to concentrate all that was collected by private contractors onto one single un-lined, open waste dump, located on the bare karst to the south-east of Trebinje. At this semi-controlled location, a small Landfill Tax was levied on each delivery, which was dumped and burned. .....iii) At first, anyone could deliver any type of waste to the site, where it could be dumped after payment of the Landfill Tax. Latterly, there was some measure of access control. .....iv) The effects on the underlying karst hydrology had many implications for the associated karst springs situated locally in Mokro Polje and further afield in the Croatian Dalmatian Littoral. Below, we provide general images of the old landfill site. This is where all the legally disposed waste from Vrelo "Oko" at Zasad, ended up.
The location of a landfill
site for municipal waste-disposal in this karst area had a high probability
of causing trans-State Boundary water pollution problems.
The provision of rubbish collection skips is now more ubiquitous in Trebinje. However, the issue of where the rubbish is now dumped and how that landfill site is managed, remains to be clarified.
14. BIBLIOGRAPHY : [.* denotes a stock item in the Society's Reference Library.] 1...Petrović
B. & Prelević B. (1965) *
"Hydrologic Characteristics of the Karst Area of Bosnia and Herzegovina
and a Part of Dalmatia with Special Consideration of Underground Water
Connections."
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