2. ENVIRONMENTAL ChEMISTRy & TEChNOLOGy 2.1. Lectures
2. ENVIRONMENTAL ChEMISTRy & TEChNOLOGy 2.1. Lectures
2. ENVIRONMENTAL ChEMISTRy & TEChNOLOGy 2.1. Lectures
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Chem. Listy, 102, s265–s1311 (2008) Environmental Chemistry & Technology<br />
P16 ThE NATuRAL AND ANThROPOLOGICAL<br />
CONTAMINATION SOuRCES OF ThE<br />
HALČIANSKY WATER RESERVOIR<br />
SLAVOMíRA KAŠIAROVá a and MELánIA<br />
FESZTEROVá b<br />
a Trenčín University of A. Dubček, Department of public<br />
management, Študentská 2, 911 50 Trenčín, Slovakia<br />
b Constantine the Philosopher University, Faculty of Natural<br />
Sciences, Department of Chemistry, Tr. A. Hlinku 1, 949 74<br />
Nitra, Slovakia<br />
kasiarovas@azet.sk<br />
Introduction<br />
Many technical sights, as an integral part of a landscape<br />
structure, are at the same time its dominant features as they<br />
are directly related to its history. In the Banská Štiavnica<br />
region they are mostly related to mining traditions. Importance<br />
of water reservoirs, also called “tajchy”, in the region<br />
stems their recreational utilisation. The cleanliness of water<br />
is therefore a key issue 1 .<br />
This study has focused on the identification of possible<br />
natural and anthropogenic sources 2 of pollution in the model<br />
territory of the Halčiansky water reservoir and consequently<br />
on its contamination. Water reservoirs built to provide the<br />
water energy for driving mining machinery are a part of a<br />
mining history. As such they are a typical landscape-ecological<br />
component of the Banská Štiavnica landscape. Because of<br />
their significance they are listed on The State List of Cultural<br />
Monuments as sights of technical development and on The<br />
World Catalogue of Water Reservoirs.<br />
Experiment and Methods<br />
In the model territory of the Halčiansky Water Reservoir,<br />
conditions of potential movement of water and related contaminants<br />
were analysed in relation to natural and anthropogenic<br />
sources of contaminants with the use of GIS (Geomedia<br />
Professional) tools. The aim of the analysis was to determine<br />
the vector of the transport and representative sampling points.<br />
Based on the system analysis of the above conditions, the<br />
selection of sampling points was proposed with the sampling<br />
points for the transport system set as transparent. Samples of<br />
water taken at the representative points (period 2006–2007)<br />
were analysed in situ by spectrophotometer (Hach DR 2000,<br />
Horiba) and related to an assumed model of contamination.<br />
The results of physical-chemical analysis were further compared<br />
with the expected transit and interpretation of the contamination<br />
in the territory.<br />
Results and Discussion<br />
The following characteristics have been derived from<br />
the results and water quality monitoring:<br />
(i) Water reaction, conductivity, turbidity, temperature,<br />
salinity, nitrates (1.3–<strong>2.</strong>2 mg dm –3 ) and amount of chlorides<br />
(1.6–9.3 mg dm –3 ) and sulphates (18–33 mg dm –3 ) complied<br />
s365<br />
with the norm no. 490/2002 Z. z. during all seasons, and no<br />
measured value exceeded the norm.<br />
(ii) An increase of ammonia, nitrites, phosphates concentrations<br />
and of chemical consumption of oxygen exceeding<br />
the limit value set by the norm no. 491/2002 Z. z. was<br />
recorded during all four seasons.<br />
Free ammonia – concentration values of nH3 were in a<br />
range of 0.07–1.07 mg dm –3 them exceeding the limits<br />
of the norm ( < 0.3 mg dm –3 ). In the vicinity of the sampling<br />
points 2 and 3 there were grazing grounds foraged<br />
by cattle and sheep and an agricultural land fertilized by<br />
ammoniac, sulphate ammonia or liquid manure, increasing<br />
concentration of ammonium salts in water. Cattle<br />
excrements and fertilizers are entering water reservoir<br />
by the run-off flowing down the surrounding slopes.<br />
The directions of run-off conditions also confirm this.<br />
Another source of pollution at the sampling points 5 and<br />
6 was stabled cattle and cesspools from the residential or<br />
recreational areas.<br />
The most distinctive representation of pollution in the<br />
form of nitrites 0.004–0.226 mg dm –3 was detected in<br />
spring when the concentration of those contaminants<br />
exceeded the value set up by the norm almost eleven<br />
times. Mutual comparison of sampling points indicated<br />
the highest concentration of nitrites at the sampling<br />
sites 3, 4, 5 and 6. nitrites are products of biochemical<br />
oxidation of ammonia and to lesser extent products of<br />
the reduction of nitrates. Their sources are household<br />
sewage and wastewater.<br />
There were also excessive concentrations of phosphates<br />
0.6–<strong>2.</strong>1 mg dm –3 , which exceeded limits set up by the<br />
norm five times, with maximum concentrations registered<br />
in autumn at the sampling site <strong>2.</strong> Main sources of<br />
phosphates are household sewage and wastewater together<br />
with dead bodies of plants and animals.<br />
Chemical consumption of oxygen 10–2,800 mg dm –3<br />
•<br />
•<br />
•<br />
•<br />
had the highest value in winter, at the sampling site 1<br />
(the dam), exceeding the limit value set up by the norm<br />
eighty times. Organic water pollution can be both of<br />
natural (leaches from the organically rich soil, forest,<br />
peat bog, etc.) and artificial origin (pesticides, fertilisers).<br />
The above results have shown that the selection of sampling<br />
points based on the system analyses and GIS outcomes<br />
confirmed assumptions of physical-chemical analysis of<br />
water in natural and residential zones. The exceptions were<br />
nitrates and chlorides concentrations, in case of which the higher<br />
values were expected especially in the agricultural areas<br />
or residential zones.<br />
Conclusions<br />
Results of potential conditions of contaminants in the<br />
territory of the vector movement of water and gravitation<br />
confronted with results of physical-chemical analyses show<br />
the relevance of the model. This will enable an effective