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IV5 KARST RESEARCH TECHNIQUES
TECHNIQUES FOR ESTIMATING
RECHARGE TO A KARSTIC F.W.J.Leaney and A.L.Herczeg Sinkholes and other karstic
features are a significant component of recharge to many carbonate aquifers in temperate
and humid regions throughout the world. Their importance to the water balance of karstic
aquifers in semi-arid regions with low topography have received much less attention. This
study focuses on an investigation into recharge mechanisms to a lime- stone aquifer in
South Australia which is extensively utilised for irrigation. The study area is in a low
lying, semi- arid region of South Australia where mean annual rainfall is 500 mm yr-1,
potential evapo-transpiration rates are high (up to 2, 000 mm yr-1) and there
is no permanent surface water. We use naturally ocurring isotopic and chemical tracers to
establish the importance of a number of natural ( sinkholes and swamps) and artificial
(boreholes) features in the landscape for point-source recharge to a karst aquifer.
Conventional approaches for estimating recharge using bore hydrographs and purposeful
tracer studies such as dyes or chemicals are not appropriate in these regions because
dispersion in areas of low hydraulic gradients are beyond detection limits on a time scale
of weeks to months.
IDENTIFICATION AND SEPARATION
OF WATER-TRACING DYES USING Ruth G.Lyons, Department of Geography and Oceanography, University College, ADFA, University of New South Wales, Northcott Dr,ACT 2600, Australia Problems encountered in field applications of water tracing dyes include background fluorescence and interference between dyes, where the complexity of hyrological systems, particularly in karst areas, make multiple dye tracing experiments desirable. The fluorescence of water tracing dyes may vary dramatically according to the pH of the water and this property can be used to address these problems. The response of a number of commonly available water tracing dyes to pH is investigated; the distinctive curves provide a means of distinguishing between dyes, and between dyes and background fluorescence due to algae. It is not necessary to reproduce the full pH response curve to utilize these properties. Recommendations are made on the use of pH buffering to improve sensitivity in detecting dyes, and for quantitative laboratory analysis. Buffering to a small number of predetermined pH can be used effectively to distinguish both between dyes which fluoresce at the same wavelength, and between natural and induced fluorescence. It is particularly useful in the case of the green dyes, both for detection when there are high natural backgrounds and because it enables more than one green dye to be used simultaneously. If Rhodamine is used together with, for example, Fluorescein and Pyranine, triple dye tracing experiments can be executed.
SPECIAL PROBLEMS OF GROUNDWATER
MONITORING James F.Quinlan Reliable monitoring of
groundwater quality in any terrane is difficult. There are many ways in which violation of
sound principles of monitoring-network design and good sampling protocol makes it easy to
acquire data that are not representative of the water or pollutants within an aquifer. In
karst terranes it is especially easy for irrelevant data, which inadvertently misrepre-
sent conditions within the aquifer, to be obtained.
1. Where to monitor for pollutants: The only relevant locations are at springs, cave streams, and wells that have been shown by tracing tests to include drainage from the facility to be monitored rather than at wells to which traces have not been run but which were selected because of their convenient downgradient locations. Wells located on fracture traces and fracture-trace intersec-tions and wells located randomly can be successfully used for monitoring, but only if there is a positive trace from the facility to them. Often successful monitoring can only be done several kilometres away from the facility. 2. Where to monitor for background: The only relevant locations are at springs, cave streams, and wells in fractured rock-in which the waters are geochemically similar to those to be monitored for pollutants but which have been shown by tracing tests not to drain from the facility- rather than at wells selected because of their convenient locations upgradient from the facility site. This, too, may have to be done several kilometres away from the facility. 3. When to monitor: Before, during, and after storms or meltwater events-rather than regularly with weekly,quarterly, semiannual,or annual frequency. 4. How to determine reliably and economically the
answers to Problems 1.2.and 3:Reliable monitoring of groundwater on karst
terranes can be done,but it is not cheap or easy.
THE APPLICATION OF THE
BIOLOGICAL DETECTION
Ivanovskiy O.T.1, Samoilova S.B.2 ANNOTATION The report is concerned to the application of the
biological detection and ranging for mapping of the chalk, carbonate and sulphate karst.
The example of Rovno Nuclear Power Station and the cities Dzerzhinsk and Kentauis
considered. The high efficiency of the method in resolving problems of the engineering
geology of the karst regions of the country is based on the actual results.
The biological detection and ranging effect is conditioned by the physical fields complex affection - the magnetic field, the gravitational field and the electrostatic field etc.- on an operator organism. At the present stage of art the problem of the biological
detection and ranging effect origin is not solved. One of the hypothesis of its origin is
worth of paying attention .
THE BIOLOGICAL DETECTION AND RANGING SURVEY The region of Rovno Nuclear Power Station (NPS) placing has
unfavourable engineering and geological conditions, i.e. ,It is a karst region and
neotectonic movements occur there. At the depth of 20-25 metres there is the Middle
Quaternary non-segmented fluvioglacial and frontal morainic formations, represented by
sands, under which stretch sedimentations of glauconitic clays of the Upper Palaeogene
Kharkov stage 0.5 m thickness, that uninformaly are deposited by spots on the chalk
sedimentations of the upper chalk. The thickness of the chalk strata is 13-15 m. In the
mass of the former there are crackings and cavities, filled with sand, sand loam and
clays. Under the chalk not everywhere the basalt conglomerates are deposited on the lime
cement of the Lower Cenomanian (thickness 0.2 through 0.7 m). Described sedimentations,
represented by basalts, stretch on the eruptive rock of the Berestovsky suite of the Upper
Proterozoic at the inspected depth of 50 m.
U-SERIES DATING OF LAST
INTERGLACIAL HIGH SEA Teh-Lung Ku1, M.Ivanovich2, and
Shangde Luo1 U-series chronologies of the emerged coral limestone terraces on Barbados, West Indies, together with those of the terraces from New Guinea, have formed the basis for most late Pleistocene eustatic models. The so- called "Barbados sea level model" has been challenged in recent years, however. A major issue is whether during oxygen isotope stage 5e, when Rendezvous Hill reef complex on Barbados Island formed , the sea rose above the present position for one relatively brief period of <10,000 yr., or for two or more periods spanning approximately from 140,000 to 115,000 yr. B.P.. Evidence for the latter scenario has not come from initial studies of Barbados but from elsewhere; it is also inconclusive because of the dating uncertainties involved. We have carried out careful redeterminations of U-series ages on a suite of 29 Acropora palmata samples systematically collected from four of the lowest terraces on the island. Diagenetic disturbance may have caused the age spreads at some sampling outcrops. A model for the diagenetic exchange of uranium isotopes in coral samples with those in groundwater explains the anomalous 234U/238U ratios in samples with apparently unaltered mineralogy (aragonite) and trace element (Mg and Sr) chemistry. It shows that age dispersions of 5-10% can be engendered by a U exchange coefficient of the order of 10-6 yr-1. The lower-limit terrace ages, estimated from averaging the multiple measurements, are 81,000± V V VV 2000 yr. (Worthing), 105,000± V V VV 1000 yr. (Ventnor), 120,000± V V VV 2000 yr. (Maxwell), and 117,000± V V VV 3000 yr. ( RendezvousHill). No evidence was found of previously inferred bipartite sea levels centering around 118,000 and 135,000 yr. ago. This study documents the need of dating coral with the high precision/sensitivity mass-spectrometric techniques for future resolution of the temporal relationships among sea level changes, climate oscillation, and astronomical forcing-relationships originally addressed by the Barbados sea level model.
THE GEOMORPHOLOGICAL ANALYSIS
OF THE CURVED AXIS OF HORI,Nobuyuki1, ARAKAWA,Tatsuhiko1
and MIURA,Hajime2 Recently, some dating methods have been suggested as a
possibility of estimating age through the analysis of secondary deposits. Speleothems have
presented many interesting results on the topic of environmental changes during the
Quaternary period. On the other hand, the study of tectonic movements in coral reef areas
has been developed by dating fossil corals. However, in the humid tropical or sub-tropical
regions, many fossil corals have been recrystallized, and consequently it has been
difficult to clarify the age.
THE PROLONGED MINIMA AND MAXIMA OF SOLAR ACTIVITY V.N.Dermendijev1, G.T.Buyukliev1,
Y.Y.Shopov2 Abstract: We study a new indirect index of solar activity - the Intensity of Luminescence of Cave Flowstone Microzones. This index correlates directly with the solar activity. Using a time series of the index with resolution 4-5 pixels/year we study some of the statistical properties of the solar activity cycle during 28 prolonged minima and 21 prolonged maxima. 1.THE NEW INDEX OF SOLAR ACTIVITY Proxy data on past solar activity nowadays provide a useful
means of approaching the problem of solar magnetic field generation ( Dermendjiev et al.,
1990). For this purpose, however, we need time series of data capable of distinguishing
individual solar cycles. In this work we study from this point of view 28 prolonged minima
of solar activity in the past (until 22000B.C.) using time series of a new indirect index.
2.THE PROLONGED MINIMA AND MAXIMA OF THE LLMZA DATA We had the possibility of obtaining time series of LLMZA
data with time resolution about 5 pixels/year spanning 22000 years. It contains 110000
measurement. We use this long time series of proxy data of solar activity to seek answers
to the following questions: 1) Does the 11 year cycle continue during the Maunder, Sporer,
and other prolonged minima of the past solar activity? 2) Is the 11 year cycle typical of
the epochs of normal activity and prolonged maxima of solar activity? and 3) Is there any
correlation between duration of the minima, considered as phase shifts of a very long
cycle reflecting possible global stochastic nature of solar activity, and the amplitude
change of the subsequent activity?
The empirical distribution of the periods obtained for the
prolonged minima and maxima determined from LLMZA data are shown on Fig.1. As one can
deduct from this figure, the solar cycle is shorter during the prolonged minima (mean
value T=7.85 years). The distribution of the periods during the prolonged maxima shows a
specialfeature. When the solar cycle is longer, the preferred period is 14-15 years. It is
interesting to note also that there are no periods of 11-14 years. The very good time
resolution of LLMZA data also gives us the possibility of studying the correlation between
the duration of the prolonged minima, considered as phase shifts of a very long cycle, and
the amplitude change of the subsequent activity maxima. The results obtained from a 12000
years long time series are shown on Fig.2. The correlation coefficient r = 0.422 is
positive and statistically significant.
Fig.1 Empirical
distrbution of the solar cycle periods
This work was supported by the Ministry of Culture, Science and Education under Grant No. 1162/88.
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