PART 1

Surface Water Quantity

The monitoring of surface water discharges and levels was similarly to previous years performed on 15 gauging stations on the Slovak side and 13 gauging stations on the Hungarian side (Tab. 1-1). The location of the stations is shown on Fig. 1-1. The Parties in the intergovernmental Agreement have undertaken to mutually exchange the data of agreed gauging stations in order to prepare the joint evaluation. Joint measurements had also been performed in order to help the evaluation of discharges flowing into the Danube downstream of the Čunovo weir and into the Mosoni branch of the Danube. Based on these measurements jointly agreed time series data were accepted. These data creates the basis for evaluation of the measures realised according to the Articles 1-3 of the Agreement.

Table 1-1: List of gauging stations

 

Country

Station No.

Location and station name

1

Slovakia

1250

Danube, Bratislava-Devín

2

Slovakia

2545

Danube, Hamuliakovo

3

Slovakia

2558

Danube, Dobrohoą»

4

Slovakia

1251

Danube, Gabčíkovo

5

Slovakia

1252

Danube, Medveďov

6

Slovakia

1600

Danube, Komárno

7

Slovakia

2848

réservoir, Čunovo - dam

8

Slovakia

2552

Danube, Čunovo - downstream the Čunovo weir

9

Slovakia

2851

Mosoni Branch of the Danube, Čunovo - intake

10

Slovakia

3126

left-side river arm system, intake at Dobrohoą»

11

Slovakia

2849

power canal, Gabčíkovo Power station

12

Slovakia

2850

tailrace canal, Gabčíkovo Power Station

13

Slovakia

3124

seepage canal - upper water level, Čunovo

14

Slovakia

3125

seepage canal - lower water level, Čunovo

15

Slovakia

1653

Malý Danube, Malé Pálenisko

1

Hungary

0001

Danube, Rajka

2

Hungary

0236

Danube, Doborgaz

3

Hungary

0002

Danube, Dunaremete

4

Hungary

0005

Danube, Komárom

5

Hungary

0011

Mosoni Danube, Mecsér

6

Hungary

0018

Mosoni Danube, Bácsa

7

Hungary

0043

Danube, submerged weir

8

Hungary

0237

right-side river arm system, Helena

9

Hungary

0082

seepage canal, lock No. I.

10

Hungary

0084

seepage canal, lock No. II.

11

Hungary

0090

seepage canal, lock No. V.

12

Hungary

0103

seepage canal, lock No. VI.

13

Hungary

0106

Zátonyi Danube, Dunakiliti, Gyümölcsös út

 

In the intergovernmental Agreement, signed on April 19, 1995 the Parties agreed on the temporary water management regime. It was agreed that in case of average annual discharge 2025 m3.s-1 at Bratislava the annual average of 400 m3.s-1 is to be discharged to the Danube downstream of Čunovo. The daily amount of water discharged to the Danube riverbed depends on the discharge reaching the Bratislava-Devín profile, taking into consideration the rules of operation described in the Annex 2 of the Agreement. The discharge in the vegetation period, depending on hydrological conditions, should fluctuate between from 400 to 600 m3.s-1, in the non-vegetation period the discharge should not be less than 250 m3.s-1. In case of floods the amount of water above 600 m3.s-1 discharged through the inundation weir is not taken into consideration when the annual average is calculated. There was agreed an additional 43 m3.s-1 of water discharged to the Mosoni branch of the Danube through the intake structure at Čunovo and the right side seepage canal.

On the basis of average annual discharges for different years at station No. 1250 it can be stated that the average annual discharge in hydrological year 1999 was much more higher than the average considered in the Agreement (Tab. 1-2) and the highest since signing the Agreement.

Table 1-2: Average annual discharges

Station No.

Hydrological year

Average discharge (m3.s-1)

1250

1990

1710.93

1250

1991

1752.37

1250

1992

1774.62

1250

1993

2030.20

1250

1994

1908.32

 

Agreement

2025.00

1250

1995

2277.82

1250

1996

1992.91

1250

1997

2093.63

1250

1998

1722.90

1250

1999

2560.96

In hydrological year 1999 the minimal average daily discharges occurred in the period from September 1999 to October 1999. Low discharges occurred also at the end of January and beginning of February 1999. The lowest average daily discharge occurred at October 26, 1999 when reached the value 1040 m3.s-1. The maximal average daily discharges occurred during high discharge periods in November 1998 (5385 m3.s-1), at the end of February 1999 (5613 m3.s-1) and in during May 1999 (5715 m3.s-1). The yearly maximum discharge occurred in May 27, 1999 when reached the value 5788 m3.s-1. Based on these values it can be stated that the high or low discharges does not reached extraordinary values. In spite of this, the average yearly discharge in 1999 was the highest one in the last ten years.

The course of discharges during the hydrological year can be characterised as follows (Fig. 1-2): there were two peaks during the November 1998, the second with maximum discharge of 5700 m3.s-1, then the discharges quickly decreased to the 1795 m3.s-1 at the end of November 1999. Decreasing tendency of winter discharges were several times broken by sudden increase of discharge caused by great amount of precipitation in the catchment area - in the middle of December 1998 the discharges reached 4466 m3.s-1, in the first decades of January and February the discharges raised up to 2800 m3.s-1. In the third decade of February 1999 a flood wave occurred with maximum discharge of 5775 m3.s-1, followed with another one at the beginning of March, which reached 4860 m3.s-1. The decreasing discharges in the second half of March and during April 1999 fluctuated around 2700-2800 m3 .s-1. At the end of April the discharges began to rise and in the first half of May 1999 reached 5018 m3.s-1 and at beginning of the second decade culminated at 5788 m3.s-1, which was the yearly maximum. After the culmination in May the slowly decreasing discharges in June and July 1999 several times rose up, up to 4000 m3.s-1. The discharges during the August 1999 fluctuated around 1800 m3.s-1. At the end of month the discharges slightly increased and culminated at the beginning of September 1999 at 3325 m3.s-1. After the decrease of discharges in the middle of September down to 1200 m3.s-1, the discharges at the end of September reached 2008 m3.s-1. After this small culmination the discharges decreased and at the end of October 1999 reached the yearly minimum 1040 m3.s-1.

1.1. Discharge into the Danube downstream of Čunovo

The determination of the average daily amount of water discharged to the Danube downstream of Čunovo was based on average daily discharges measured at stations Doborgaz and Helena (Fig. 1-3).

The monthly characteristics of the discharges into the Danube in the hydrological year 1999 were as follows:

Year                1998                                                                            1999

Month

Nov

Dec

Jan

Feb

Mar

Apr

May

June

July

Aug

Sept

Oct

Minimum

239

236

240

232

374

520

584

572

549

371

252

239

Average

558

288

247

348

548

579

657

598

592

443

346

267

Maximum

1696

567

281

716

629

614

974

661

626

564

567

334

The average annual discharge in the Danube at Bratislava-Devín profile was 2560.36 m3.s-1.

The average annual discharge flowing to the Danube downstream of Čunovo was 456.07 m3.s-1 in hydrological year 1999. If we do not take into account discharges over 600 m3.s-1 during higher discharges in 1999* the annual average was 443.64 m3.s-1. This means that in the year 1999 Slovakia fulfilled the average annual discharge jointly agreed in the Agreement, even some more water was discharged to the Danube. The difference comes from the difference between the discharge daily adjusted according to the tabulated discharge and the formula used for calculation of the average annual discharge in Annex No. 2 of the Agreement. In the non-vegetation period in several occasions the minimum discharges differed from the agreed values. On the other side in the vegetation period the maximal values were sometimes higher.

1.2. Discharge into the Mosoni Branch of the Danube

The discharge into the Mosoni branch of the Danube according to the Agreement should be 43 m3.s-1, which is composed by the discharge released to the Mosoni branch of the Danube through the intake structure at Čunovo and the discharge through the seepage canal. The common profiles for discharge measurements on the Mosoni branch of the Danube are situated on the Slovak territory at 0.160 rkm and upstream of lock No. I on the Hungarian territory. The average daily discharges were agreed according to the joint discharge measurements performed at both profiles. In the evaluation the data measured just downstream of the intake structure were considered (Fig. 1-4).

The monthly characteristics of the discharges in the Mosoni Danube in the hydrological year 1999 were as follows:

Year                   1998                                                                             1999

Month

Nov

Dec

Jan

Feb

Mar

Apr

May

June

July

Aug

Sept

Oct

Minimum

22.4

31.2

36.7

20.8

39.9

37.5

40.0

42.8

37.2

20.5

20.5

19.3

Average

37.2

41.1

41.7

30.9

41.5

42.8

43.0

45.4

44.1

38.7

43.0

32.5

Maximum

42.5

43.8

42.8

46.6

43.1

44.5

47.6

48.4

47.8

47.4

47.8

47.4

The average annual discharge was 40.20 m3.s-1.

The discharges in the right side seepage canal were measured at two profiles. The first is at Čunovo on the Slovak territory; the second is placed at lock No. II on the Hungarian territory. In the evaluation the data observed at lock No. II on the seepage canal on Hungarian territory were considered.

The monthly characteristics of the discharges recorded at lock No. II were as follows:

Year                   1998                                                                            1999

Month

Nov

Dec

Jan

Feb

Mar

Apr

May

June

July

Aug

Sept

Oct

Minimum

1.88

1.68

1.78

1.99

1.31

1.49

1.07

1.40

1.31

1.40

1.15

0.85

Average

2.42

1.97

1.91

2.22

1.70

1.93

2.00

1.80

1.45

1.54

1.29

1.13

Maximum

3.36

2.21

2.10

2.95

1.99

2.82

2.57

2.21

1.58

1.68

1.49

1.40

The average annual discharge was 1.78 m3.s-1.

The total average annual discharge discharged into the Mosoni branch of the Danube was 41.98 m3.s-1. Taking into consideration the accuracy of the discharge measurements it can be stated that the agreed average annual discharge was fulfilled.

1.3. Water distribution on the Hungarian territory

The goal of the water distribution on the Hungarian side is to provide continuous water supply into the main and side river arms in the inundation area, into the river branches on the flood-protected area and into the Mosoni Danube.

1.3.1. Water supply into the inundation area

The inundation area on the Hungarian side can be supplied by water from two sources: 

a.) From the Danube, through two openings in the riverbank, by manipulating the increased water level by the submerged weir and the Dunakiliti dam. The total inflowing discharge is measured at Helena profile.

b.) The second source is from the seepage canal through the lock No. V.

Joint discharge measurements by both Parties were performed at the Helena profile too. The measurements were jointly evaluated and based on joint evaluation the common time series of average daily discharges were prepared.

The monthly discharge characteristics at Helena profile in hydrological year 1999 were as follows:

Year                   1998                                                                            1999

Month

Nov

Dec

Jan

Feb

Mar

Apr

May

June

July

Aug

Sept

Oct

Minimum

29.0

15.0

10.0

11.0

33.0

71.0

78.0

47.0

74.0

76.0

29.0

17.0

Average

55.5

38.3

16.9

32.7

79.3

105

121

109

93.4

96.5

69.0

30.5

Maximum

136

59.0

39.0

85.0

106

134

169

136

115

123

113

59.0

The average annual discharge was 70.81 m3.s-1.

The monthly discharge characteristics at the lock No. V:

Year                   1998                                                                            1999

Month

Nov

Dec

Jan

Feb

Mar

Apr

May

June

July

Aug

Sept

Oct

Minimum

0.0

17.4

21.3

6.6

9.6

4.4

5.0

4.8

7.1

0.0

0.0

6.5

Average

7.8

20.8

24.7

14.2

11.7

7.9

11.7

7.8

10.1

7.0

15.3

16.6

Maximum

18.6

25.3

28.3

26.9

16.1

10.4

28.0

20.0

14.6

10.6

29.5

28.0

The average annual discharge was 12.99 m3.s-1.

The monthly discharge characteristics of the total amount of water discharged into the inundation area in hydrological year 1999 (Fig. 1-5):

 Year                   1998                                                                            1999

Month

Nov

Dec

Jan

Feb

Mar

Apr

May

June

July

Aug

Sept

Oct

Minimum

34.5

40.3

35.9

29.0

49.1

79.4

97.0

52.8

83.3

86.2

57.7

25.5

Average

63.2

59.0

41.7

46.8

91.0

113

133

117

104

104

84.3

47.1

Maximum

136

77.4

60.3

92.6

120

141

177

142

122

131

116

83

The total average annual discharge supplied to the inundation area was 83.80 m3.s-1.

1.3.2. Water supply into the Mosoni Danube

The water supply into the Mosoni Danube is provided from the seepage canal through the lock No. VI (Fig. 1-6). The discharge is measured at the profile downstream of the lock.

The monthly characteristics of the discharges through the lock No. VI in hydrological year 1999 were as follows:

Year                   1998                                                                            1999

Month

Nov

Dec

Jan

Feb

Mar

Apr

May

June

July

Aug

Sept

Oct

Minimum

11.5

15.2

12.7

10.3

24.5

28.6

15.7

22.2

19.7

20.0

13.1

8.7

Average

30.9

18.8

17.1

17.9

29.0

33.2

30.4

34.4

31.3

30.7

24.9

16.0

Maximum

40.2

21.1

19.3

29.6

30.2

35.1

39.7

38.9

35.5

34.7

35.1

20.0

The average annual discharge in the Mosoni Danube at lock No. VI. was 26.24 m3.s-1.

During the non-vegetation period in the hydrological year 1999 low water period was simulated in Mosoni Danube water supply as well. This was reached by redirecting a great part of the water in the seepage canal to the inundation area through the lock No. V, while the water amount taken from the Danube was reduced, even stopped.

Besides the water supply function the lock No. I has also a flood protection function. It prevents floods to enter the flood-protected area. During the hydrological year 1999 there was no need to keep the lock closed.

1.4. Characteristics of the Danube on the Čunovo-Vámosszabadi stretch

The Danube stretch between Čunovo and Vámosszabadi can be divided into four different sections according to the prevailing influence. The characteristics of these sections are based on data obtained from the following gauging stations: Rajka, Hamuliakovo and Dunakiliti, Doborgaz and Dobrohoą», Dunaremete and Gabčíkovo, Vámosszabadi and Medveďov.

The four sections on the Čunovo-Vámosszabadi stretch are the following:

  1. Čunovo - Dunakiliti section is dammed and the water level is kept higher by the submerged weir and the Dunakiliti dam. Since the bottom weir was built, the water level at Dunakiliti corresponds to the average water level before damming, while upstream is the water level, comparing to the average water level before damming, lower. This dammed section allows the water supply to the right side river branch system. The amount of water discharged to the river branch system is determined by manipulation at the Dunakiliti weir. The water is kept in the mid water riverbed. The average flow velocity fluctuate in the range between 0.3-0.6 m.s-1.
    The water level at the Hamuliakovo gauging station (rkm 1850) fluctuated in the range from 122.49 to 124.24 m a. s. l. and the average water level was 123.11 m a. s. l. The water level in the Rajka profile (rkm 1848) fluctuated from 122.43 to 123.84 m a. s. l. and the average water level was 123.04 m a. s. l (Fig. 1-7).
  2. The section between Dunakiliti and Dunaremete is not impounded and the water level is low. The difference between the present water level and the water level in the river branches is about 3 m. The water level in the Dobrohoą» profile (rkm 1838.6) fluctuated in the range from 117.10 to 120.67 m a. s. l. and the average water level was 117.80 m a. s. l. The water level in the Dunaremete profile (1825.5) fluctuated from 113.36 to 116.76 m a. s. l. and the average water level was 114.05 m a. s. l (Fig. 1-8). The average flow velocity fluctuates in the range between 0.94-1.53 m.s-1.
  3. The section between Dunaremete and Sap is influenced by the backwater effect and the water level changes depend on the discharges in the tail-water canal. The length of the upstream section influenced by the backwater effect from the confluence of the tail water canal and the Danube (rkm 1811) depends on the actual discharge distribution between the power station and the Danube old riverbed. At regular operation of the Gabčíkovo hydropower station it can be stated that the backwater effect reaches the Dunaremete profile (rkm1825.5) at discharges over 2500 m3.s-1. The water level in the Gabčíkovo profile (rkm 1819) fluctuated in the range from 111.70 to 115.55 m a. s. l. and the average water level was 112.80 m a. s. l (Fig. 1-9).
  4. The discharge in the Sap – Vámosszabadi section equals approximately to the discharge at Bratislava and is additionally influenced by the operation of Gabčíkovo hydropower station. The daily water level fluctuation at this stretch depends on the hydropower station operation. Higher changes occur at low discharges in the Danube due to the ratio of the total discharge and the capacity of one turbine, which is put into operation or stopped. The average annual discharge at the Vámosszabadi – Medveďov profile in 1999 was 2522.55 m3.s-1. The water level in the Medveďov profile (rkm 1806.3) fluctuated in the range from 109.13 to 114.22 m a. s. l. and the average water level was 111.28 m a. s. l (Fig. 1-10).

 

   
Fig. 1-1 Monitoring network of gauging stations agreed in the frame of the Joint monitoring   Fig. 1-2 Surface Water - Discharge Bratislava-Devín   Fig. 1-3 Surface Water - Discharge Rajka
       
   
Fig. 1-4 Surface Water - Discharge Čunovo-Mosoni Danube   Fig. 1-5 Surface Water - Discharge Helena   Fig. 1-6 Surface Water - Discharge Lock No. VI
       
   
Fig. 1-7 Surface water level Hamuliakovo - Rajka Fig. 1-8 Surface water level Dobrohoą» - Dunaremete   Fig. 1-9 Surface water level Gabčíkovo
         
Fig. 1-10 Surface water level
Medveďov