Fishing district

Žitava č. 4

CarpNo. 2-5630-1-1ŽitavaVáh basin
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Fishing district boundaries: Čiastkové povodie Žitavy od vzdúvadla v obci Žitavce po cestný most v obci Obyce a potoky Čerešňový, Drevenica, Stráňka, Pelúsok, Kopanický, Širočina, Podegarský, Rohožnica, Bočovka, Telinský, Kováčovský a Melecký od ústia po pra

fishing district length
172km
district
Nitra
region
Nitra Region
Aerial image of fishing district Žitava č. 4 with the line highlighted
Blue line: course of the fishing district (approximate). Orthophoto mosaic of Slovakia © GKÚ Bratislava, CC BY 4.0Google Maps

By the water now

Fishing conditionsFish activity indexOur calculation (0–100): the base is set by water temperature, adjusted by light, turbidity, oxygen, weather and other factors according to how well they are supported by studies. For each factor you can see the confidence and the source. A planning aid, not a bite forecast.

The score, the best window of the day and what pushes it up or down

Fishing conditions

Fish activity indexOur calculation (0–100): the base is set by water temperature, adjusted by light, turbidity, oxygen, weather and other factors according to how well they are supported by studies. For each factor you can see the confidence and the source. A planning aid, not a bite forecast.

Loading data…

Water

Water level, temperature, modelled flow and gradient

Water level

Water levelThe water level at the nearest SHMÚ gauge in centimetres above the gauge zero. It is the water level at the station, not the depth of the water at the fishing district.
020406080100

Obyce – Žitava · level stable

The level is measured at an SHMÚ gauge; it is not the depth of the water in the fishing district.

Source: SHMÚUpdated 10 Nov 2026 16:45

Modelled flow

Modeled flowAn estimate of the amount of water in the river (m³/s) from the GloFAS model, not a measurement. The resolution is about 5 km, so on small streams it may show a larger river nearby.

Loading data…

Elevation profile of the watercourse

Elevation profileHow the altitude of the watercourse changes downstream. It is calculated from a digital relief model (tens of metres), not from a water-level measurement, so it is approximate, especially for narrow streams.

Gentle gradient The current is noticeable, with shallows and slacks alternating. A transition between a lowland and a foothill watercourse.

1001502002500 km10 km20 km30 km
Elevation profile of the fishing district downstream: from 241 to 136 m a.s.l. over 32.3 km.
Downstream, from the upper end of the fishing district (left) to the lower end
Highest point
241 m a.s.l.
Lowest point
131 m a.s.l.
FallFallThe difference in altitude between the upper and lower end of the fishing district in metres. The greater the fall over a shorter length, the faster the water.
110 m
SlopeWatercourse gradientFall per kilometre in per mille (‰, metres per kilometre). Up to 2 ‰ is a slow lowland river, 5 to 10 ‰ a foothill river (grayling, trout), above 10 ‰ a fast stream.
3.4 ‰
SinuositySinuosityThe length of the watercourse divided by the straight-line distance between its ends. 1.0 is a straight watercourse; above 1.3 it meanders strongly. Meanders create pools under the banks and shallows in the reaches between.
1.15
Source: Open Topo Data (eudem25m)Updated 4 Nov 2026 11:04

Weather and forecast

Hour by hour, pressure and the next few days

Weather and forecast

Loading data…

Sky: sun, moon and solunar windowsSolunar periodsCalculated from the position of the Moon: major periods (about 2 h) around the Moon's passage above and below the horizon, minor periods (about 1 h) around moonrise and moonset. A scientifically unconfirmed theory: in a study of 361 fishing trips (Quigley et al. 2023) it did not predict bites. We treat it as a hypothesis with a weight of at most ±2 points.

Where the sun and moon are right now and when the best windows of the day will come

Sky: sun and moon

Solunar periodsCalculated from the position of the Moon: major periods (about 2 h) around the Moon's passage above and below the horizon, minor periods (about 1 h) around moonrise and moonset. A scientifically unconfirmed theory: in a study of 361 fishing trips (Quigley et al. 2023) it did not predict bites. We treat it as a hypothesis with a weight of at most ±2 points.

Drag along the axis to see where the sun and moon will be.

  • Sun
  • Moon
  • Golden hour
  • Main period
  • Minor period

Sun

  • Dawn06:13
  • Sunrise06:46
  • Sunset16:14
  • Dusk16:48

The day lasts 9 h 28 min.

MoonMoon phaseAt full and new moon the gravitational effect is strongest. On a clear full-moon night predators and carp often feed at night, and the day after may be weaker.

Nov1% illuminated
  • Moonrise08:19
  • Moonset16:16

Full moon around 24 Nov, new moon around 9 Dec.

Windows of the daySolunar periodsCalculated from the position of the Moon: major periods (about 2 h) around the Moon's passage above and below the horizon, minor periods (about 1 h) around moonrise and moonset. A scientifically unconfirmed theory: in a study of 361 fishing trips (Quigley et al. 2023) it did not predict bites. We treat it as a hypothesis with a weight of at most ±2 points.

  • Main solunar period22:55–00:55
  • Golden hour (morning)06:16–07:46
  • Minor solunar period07:49–08:49
  • Main solunar period11:20–13:20
  • Golden hour (evening)15:14–16:44
  • Minor solunar period15:46–16:46
  • Main solunar period23:46–01:46

Solunar theory is not scientifically confirmed; we treat it as a supplement. The golden hour is the time around sunrise and sunset, when fish often bite.

Map and fishing district data

Course of the water, spots along the water, character and basic data

48.47291, 18.27227 OpenStreetMap

The line shows the course of the fishing district according to the "Rybárske revíry" data 2026. Verify access points and exact boundaries on site.

Fishing district details

Manager
SVP, š.p. OZ Piešťany
Fishing district user
SRZ
Organization
MO SRZ Zlaté Moravce (Local SRZ organization)
Area
Western Slovakia
Purpose
Fishing district
Minimal stocking
K2 100kg, Zu1 500 pcs, Pds1 500 pcs

Characteristics

  • DepthDepthThe greatest depth from the fishing district description. Shallows warm up quickly and are rich in food; deep pools give shelter and a more stable temperature. 0.2–1.5 m
  • BottomBottomThe bottom material determines which fish live here and where they find food. Fish zones can be recognized by the bottom: rocky, gravelly, sandy to muddy. stony – gravelly
  • Watercourse lineWatercourse lineThe shape of the watercourse seen from above. In bends there is a deep scour under the outer bank and a shallow bar under the inner one; a winding stream has more shelter and changes in depth. undulating
  • ShadingShadingThe share of the water surface in shade. Shade lowers summer water temperatures and supplies insects and shelter; a sunny section warms up faster and becomes more overgrown. 20%
  • VegetationVegetationTree and herbaceous vegetation on the banks. Roots and branches create shelter, and leaves and twigs falling in provide food. It also determines where you can cast and where your rig gets snagged. alder, willow, poplar
  • Cross-channel structuresCross-channel structuresWeirs, steps and dams hold back water and stop fish from migrating. Below them a deep plunge pool with oxygenated water forms. none
What this means for anglersexplanation of the bottom, vegetation, watercourse line and other data of this fishing district
  • Depth: Medium, 1–3 m

    The most common type: shallows alternate with deeper spots and fish move according to the time of day and temperature.

  • Bottom: Gravel bottom

    Well-oxygenated water and plentiful food (aquatic insect larvae). Typical of the grayling and barbel zones; gravel bars also serve many fish as spawning grounds.

  • Bottom: Stony bottom

    Typical of fast mountain and foothill streams. There are shelters for trout and other fish among the stones, but your rig often gets snagged.

  • Watercourse line: Undulating line

    Pronounced bends. Under the outer bank there is usually a deep hole, on the inner side a shallow gravel or sand bar.

  • Shade: Partly shady, 11–40%

    A balanced stretch: there is a source of insects and also enough light for aquatic plants.

  • Vegetation: Willow

    Grows by the water; the roots stabilize the bank and create shelters beneath the surface. The branches hang over the water and provide shade and insects.

  • Vegetation: Alder

    A typical tree of stream and river banks. A dense root system creates undercut banks and shelters, and the leaves decompose quickly.

  • Vegetation: Poplar

    Tall, fast-growing trees. They provide shade and insects, and branches and leaves fall into the water.

  • Cross-channel structures: none

    Fish can move freely along the watercourse; the section is more continuous.

The explanation is general and based on the fishing district description in the data and on common fishing practice. Actual conditions on site may differ; check them before you fish.

Confluences and risk spots

  • COV VrableWastewater discharge point
    0.0 km
  • COV Zlate MoravceWastewater discharge point
    0.0 km
  • COV Zlate MoravceWastewater treatment plant · capacity 21,473 PE
    Details
    Load
    17,739 of 21,473 PE (83%)
    Treatment
    mechanical, biological, nitrogen and phosphorus removal
    Polishing and disinfection
    microfiltration
    Meets the requirements
    BOD₅, COD, nitrogen, phosphorus
    0.1 km
  • COV VrableWastewater treatment plant · capacity 9,000 PE
    Details
    Load
    6,329 of 9,000 PE (70%)
    Treatment
    mechanical, biological, phosphorus removal
    Meets the requirements
    BOD₅, COD
    0.1 km

Spots within 3 km of the watercourse are shown.

Source: VÚVH (CC BY 4.0)Updated 9 Nov 2026 18:38

Law and fishing rules

Closed season, fishing hours, minimum sizes and daily limit. For guidance only: check them in the fishing regulations of the fishing district

Closed season for all fish

§ 13, paragraphs 3 and 5 of the Act

15 Mar – 31 May

fishing for all fish prohibitedoutside this period

The ban does not apply 1 May – 31 May during fishing competitions (§ 13, para. 3). It also does not apply to carp waters that are watercourses (but not reservoirs, dead-end, dead and cut-off arms), or to other water bodies (§ 13, para. 5). Check in the fishing regulations of the district which case your district is.

The protection periods by species (below) apply independently of this closed season.

Daily fishing hours

§ 11 of the Decree

Applies only outside the closed season. Outside these hours fishing is prohibited (§ 14(b) of the Act).

January to April, November, December6.00 – 21.00 h

May4.00 – 24.00 h

June to October0.00 – 24.00 h

Months missing from the table fall within the closed season. The hours in November and December on trout and grayling waters relate to the exception for fishing huchen (§ 13, para. 4 of the Act); check in the fishing regulations what may be caught at that time. On border waters the hours in the permit or the fishing regulations apply (§ 11, para. 2 of the Decree). The Act regulates night fishing in two wordings that seem to contradict each other at first sight, so always ask about it in the fishing regulations of the district or the fishing guard.

Rods, baits and fishing days

§ 18 of the Act
Number of rods
at most 2
Permitted methods
bottom fishing, float fishing, spinning, fly fishing
Hooks and baits
on a rod at most 2 hooks (bottom fishing, float fishing), artificial lure at most 3 hooks, a hook at most 3 points, fly fishing at most 3 flies
Live or dead baitfish
prohibited 15 Mar – 31 May; otherwise at least 10 cm and above the minimum size
Fishing days of the week
the law specifies no restriction
Ice fishing
prohibited (watercourses, reservoirs, arms)
Other
spinning and fly fishing with a fish imitation prohibited 15 Mar – 31 May; fishing from a boat prohibited on reservoirs 1 Jan – 31 May

This is a summary. For baits, hooks and groundbait also read the fishing regulations of the district, because the user may tighten the conditions.

How many fish you may keep per day

§ 14 of the Decree
  • 1pcsBlue groupsterlet, Siberian sturgeon, wels catfish
  • 2pcsGreen groupeel, carp, burbot, zander, pike, tench, barbel, lake brown trout, brown trout, grayling (combined)
  • 4pcsYellow grouprainbow trout, brook trout, common nase, vimba bream; added to the green or blue group (at most 4 fish in total)
  • 5kgOther speciesfor example crucian carp, breams, dace and chub (combined); invasive species are not counted

The blue and green groups cannot be combined. The limit applies per day, also when fishing in several districts, and once it is reached, fishing for that day ends. The species groups follow the SRZ interpretation of January 2026, not the text of the section directly. The district user may set a lower limit in the permit, in which case the stricter one applies.

Protection periods by species§ 10 of the Decree

During this period the species must not be caught, even if the water type otherwise allows fishing at that time. It applies independently of the closed season for all fish.

1 Jan – 15 Mar
burbot
1 Jan – 31 May
grayling, spirlin, northern pike
1 Jan – 15 Jun
wels catfish, zander (pikeperch), Volga pikeperch
1 Jan – 31 Oct
huchen (in border waters 1 Jan – 31 Aug)
15 Mar – 31 May
common carp in carp waters (does not apply 1 – 31 May during competitions, nor on other water bodies); asp, chub, dace, ide, sterlet, Siberian sturgeon, tench, barbel, vimba bream, zope, white-eye bream, common bream, common nase
1 Sep – 15 Apr
brown trout, brown trout (lake form)
1 Sep – 28 Feb
peled

Some species are protected all year round (for example zingel and streber, lampreys, gudgeons, spined loaches, maraena whitefish, Carpathian barbel, sabre carp) and fishing for them is always prohibited. The full list of species is in the guide The fishing law, rule by rule.

Minimum sizes§ 12 of the Decree

The shortest length from which you may keep a fish. The district user may raise the size, so look for the valid value in the permit and the fishing regulations.

Show as a list

Total length is measured from the front of the head to the end of the longest ray of the tail fin (§ 12, para. 4). No minimum size applies, for example, to sunbleak, Prussian carp, European perch, roach, stone loach and invasive species.

Before and after fishing

  • Carry your fishing license and permit while fishing and show them when checked (§ 12 of the Act). Check that they are valid.
  • Before you start fishing, write down the date and the district number (no. 2-5630-1-1); after fishing, write down the number and weight of your catch (§ 14(d) of the Act). Fishing without a record is an offense.
  • Prohibited fishing methods, night fishing, competitions and other rules are covered in the guide The fishing law, rule by rule.

As of 6 Nov 2026: Act no. 216/2018 Coll. on fisheries (wording effective 1 Jan 2022) and Decree no. 381/2018 Coll. (wording effective 1 Jan 2019); we found no newer wording. The law may change; you can find the current wording on Slov-Lex (Act) and Slov-Lex (Decree).

News from the organization and catches from the fishing district

Catches from the fishing district

Nobody has recorded a catch in this fishing district yetBe the first: after approval it will also appear here in the ranking.

Terrain in 3D

Loading the 3D terrain model…

Water according to public sources

Water quality, river basin, bottom, fish, aquatic insects, wildlife and hazards from open databases. Except for wildlife and hazards, they are also included in the activity score.

Water suitability for the fishing district type

Water suitability for the district typeIndex 0 to 100: how well the properties of the water match the needs of trout, grayling or carp, depending on the district type. It is not a bite forecast or a statement about which fish live there.
81from 100
Water of above-average suitability for carp and cyprinids

The water is in the top 26% of 896 carp fishing districts with data.

  • Best fit: water acidity (pH)

Reliability medium: we used 5 water data points; the rest are missing and are not part of the assessment.

  • Stream zoneLevel of evidence: Partly supported

    gradient 3.4 ‰, 186 m a.s.l. → barbel zone

    Based on gradient and elevation, the stream lies in an area that corresponds to the barbel zone. For carp and cyprinids this is a marginal zone: suitable, but not ideal.

    What we know about it

    European streams are divided from source to mouth into zones with typical fish: trout, grayling, barbel and lowland; they are determined mainly by gradient and stream size (Huet 1959), and the zones can also be used to assess the condition of streams (Aarts and Nienhuis 2003). We estimate the zone from the gradient of the fishing district's line and its elevation; it is a simplification without stream width. A match between the zone and the fishing district type adds +1 to quality, a clear mismatch −1.

    Sources: Huet 1959; Aarts and Nienhuis 2003

    69
  • Water hardnessLevel of evidence: Hypothesis

    ≈ 16.1 °dH (2.9 mmol/l of calcium and magnesium), ŠGÚDŠ atlas

    Harder water with enough calcium and magnesium is more productive, has a larger food supply and buffers acidity swings better.

    What we know about it

    Water with calcium and magnesium is more productive and buffers acidity swings better: trout production was higher in calcareous hard waters (Almodóvar et al. 2006), and an index based on dissolved solids and depth predicts fish yield from lakes (Ryder et al. 1974). In Irish streams, however, geology did not change trout density (Lehane et al. 2004), and Downing et al. (1990) showed that production is related rather to primary production. Hence only ±1 point. Hardness comes from the ŠGÚDŠ atlas, not from a measurement in the fishing district; it replaces the separately assessed bedrock of the basin.

    Sources: Almodóvar et al. 2006; Lehane et al. 2004; Ryder et al. 1974

    96
  • Water acidity (pH)Level of evidence: Partly supported

    pH 7.9, ŠGÚDŠ atlas

    The pH is within the range in which fish commonly thrive.

    What we know about it

    Below about pH 6 fish suffer, and trout and grayling are more sensitive than cyprinids (Alabaster and Lloyd 1982); in acidic soft water, aluminium is released from the soil and damages gills (Gensemer and Playle 1999). The pH from the atlas is a model estimate, so the reduction is only −1 or −2, and only where we have no pH measurement (which is assessed by a separate factor).

    Sources: Alabaster and Lloyd 1982; Gensemer and Playle 1999

    100
  • MineralizationLevel of evidence: Hypothesis

    ≈ 503 mg/l, ŠGÚDŠ atlas

    High mineralisation: rich water, but already stressful for sensitive species.

    What we know about it

    Dissolved solids (mineralisation) are related to the fertility of the water, which is why Ryder used them to estimate fish production in lakes (Ryder 1965, Ryder et al. 1974). Downing et al. (1990) showed, however, that primary production is a better predictor of production. It does not enter the score, only the suitability index.

    Sources: Ryder 1965; Ryder et al. 1974; Downing et al. 1990

    100
  • Metals in sedimentLevel of evidence: Partly supported

    0 elements among the highest 10 % in Slovakia (ŠGÚDŠ atlas 1999)

    None of the toxic elements in river sediment is among the highest values. In hard water metals are less toxic, because calcium competes for sites on the gills.

    What we know about it

    The toxicity of metals to fish decreases with water hardness, because calcium competes with the metal for sites on the gills (Pagenkopf 1983). The ŠGÚDŠ atlas gives only the rank among streams, not a concentration comparable with a limit (MacDonald et al. 2000). In hard water we therefore rate metals more leniently, in soft water more strictly.

    Sources: Pagenkopf 1983; Gensemer and Playle 1999; MacDonald et al. 2000

    100

How this water would suit each type

  • Trout66
  • Grayling80
  • Carp81

The same water data evaluated against the requirements of trout, grayling and carp. The fishing district is registered as a carp district; its type is highlighted.

The index 0 to 100 compares the properties of the water with the requirements of the species (60 is the neutral value, 100 the ideal). The verbal rating comes from comparison with other fishing districts of the same type, because most Slovak waters have good values for their species. The index does not affect whether fish really occur in the fishing district (that is decided by stocking and the manager). Hardness, pH and mineralisation from the atlases are historical and model estimates. Only a small part of this feeds into the conditions score and fishing district quality (hardness ±1, atlas acidity −2 to 0, stream zone match ±1 to quality).

What follows from this

Public sources in the conditions scoreData on oxygen, nutrients, reservoir depth, watercourse size, bottom, fish species and insect swarming slightly adjust the "Fishing conditions" score. Each adjustment is shown separately in the score breakdown.
−14−40+4+120
Public data about this water hardly change the activity score.
  • Biggest boost: Water hardness +1
  • Biggest deduction: Nitrogen in groundwater (SHMÚ) −1

We assessed 17 factors; 4 of them change the score. The adjustments range from −14 to +12 points so that they do not outweigh the weather and water temperature. They are counted in the score, in the ranking and in the filters.

Water and oxygen+1

  • Water hardnessLevel of evidence: Hypothesis

    ≈ 16.1 °dH, ŠGÚDŠ atlas

    Harder water is more productive, has more food and buffers acidity swings better.

    What we know about it

    Water with calcium and magnesium is more productive and buffers acidity swings better: trout production was higher in calcareous hard waters (Almodóvar et al. 2006), and an index based on dissolved solids and depth predicts fish yield from lakes (Ryder et al. 1974). In Irish streams, however, geology did not change trout density (Lehane et al. 2004), and Downing et al. (1990) showed that production is related rather to primary production. Hence only ±1 point. Hardness comes from the ŠGÚDŠ atlas, not from a measurement in the fishing district; it replaces the separately assessed bedrock of the basin.

    Sources: Almodóvar et al. 2006; Lehane et al. 2004; Ryder et al. 1974

    +1

Pollution−1

  • Surface water quality (SHMÚ)Level of evidence: Anglers' practice

    site Obyce, above on Žitava, on the fishing district line, standard not met in 1 of 4 years (2022 to 2025); in 2023: COD (chemical oxygen demand), benzo(a)pyrene

    The nearest SHMÚ monitoring site on this watercourse fails the standards only for indicators that are not counted in the score: most streams exceed the extremely low PAH standard (benzo(a)pyrene and similar), and salts, iron or manganese are often natural. You can find the indicators in the breakdown for the fishing district.

    What we know about it

    The nearest SHMÚ monitoring site on the same watercourse: unmet water quality standards for the years 2022 to 2025 (newer years carry more weight). Lack of oxygen and organic pollution directly weaken fish (Davis 1975), ammonium and nitrites are toxic, and nutrients feed algae. The exact amount by which an unmet standard lowers the bite is not verified, so this is angling practice and caution. The deterioration is at most 5 points and only lowers: what SHMÚ does not report is not proof of cleanliness. Benzo(a)pyrene and other PAHs are not counted in the score because most watercourses exceed their extremely low standard.

    Sources: SHMÚ, surface waters; Government Regulation of the SR no. 269/2010; Davis 1975

    0
  • Nitrogen in groundwater (SHMÚ)Level of evidence: Partly supported

    nitrates typically 13.7 mg/l (standard 50), ammonium above the standard at 1 of 8 stations

    Groundwater reaches streams as base flow and carries nitrogen from fields and waste. Nitrates feed algae and contribute to nighttime oxygen crashes; nitrites are toxic to fish. Nitrites and ammonium can also be natural in deep groundwater, so at most one point is deducted for them. The data reliability is 100% (8 stations within 10 km, nearest 0.2 km, data from 2025), and the adjustment was applied in full.

    What we know about it

    Groundwater reaches streams as base flow. The typical nitrate value from stations within 10 km (moderate from 25 mg/l, significant from 50 mg/l, which is the drinking-water standard) indicates how much nitrogen the water brings: it feeds algae and contributes to night-time oxygen crashes (Camargo et al. 2005). Nitrites and ammonium above the standard at any station add one point, because nitrites are poisonous to fish (Lewis and Morris 1986); in deep groundwater they can also be natural, so only one point. The adjustment is multiplied by the reliability of the data.

    Sources: SHMÚ, groundwater; Camargo et al. 2005; Lewis and Morris 1986

    −1

Life by the water0

  • Aquatic insect hatchesLevel of evidence: Anglers' practice

    0.4× the average month, 5 of 155 observations in the year, iNaturalist

    Aquatic insects are scarce this month; food near the bottom matters more.

    What we know about it

    Anglers fish "by the insects" (dry and wet fly). A measured relationship between catches and insect hatches is not documented in our sources.

    0

Do not change the score

Data for these factors is missing or within the normal range:

  • Dissolved oxygen
  • Nutrients in the water
  • Water acidity (pH)
  • Water acidity from the atlas
  • Ammonium ions in water
  • Water temperature for local species
  • Harmful substances in groundwater
  • Iron in groundwater
  • Chlorides in groundwater
  • Wastewater treatment plants
  • Watercourse size
  • Bottom by geology
  • Invasive species nearby

The rules are indicative and based on fishing practice and scientific studies; for each factor you can see how well it is supported. Weather, air pressure and water temperature affect the score more than this data does.

Water pollution

Water pollution (SHMÚ)Water quality indicators that fail the standards at the nearest monitoring site on the same watercourse in the SHMÚ yearbooks for 2022 to 2025.
Surface water, 2023
2indicators fail the standard, slightly
Treatment plants within 2 km
2no unmet requirements

Surface water: nearest monitoring site

Obyce, aboveŽitava, river km 49.5 · right at the fishing district
2 indicators in 2023
2022202320242025
Indicator2022202320242025
Oxygen and organic matter
COD (chemical oxygen demand)–site not in the yearbook●standard not met–site not in the yearbook–site not in the yearbook
PAHs: 1 substance (not counted in the score)
Indicator2022202320242025
PAHs (combustion and deposition)
benzo(a)pyrene–site not in the yearbook●standard not met–site not in the yearbook–site not in the yearbook

Polycyclic aromatic hydrocarbons. The standard for benzo(a)pyrene is extremely low (0.17 ng/l), so most streams exceed it; the main sources are combustion and atmospheric deposition.

  • standard not met
  • no unmet standard
  • site not in the yearbook

Other sites on the same watercourse

  • Tesárske MlyňanyŽitava, river km 39.3 · right at the fishing district3 indicators
  • HulŽitava, river km 3.5 · 12 km from the fishing district7 indicators
Polluted water in Slovakia: the worst places and polluters

The data comes from the SHMÚ yearbooks (surface waters 2022 to 2025). The yearbook lists the sites that failed the standard; a site missing from the yearbook is not considered clean. We determine the distance and the match of the watercourse name ourselves, so the assignment is indicative.

Groundwater nearby

Groundwater nearby (SHMÚ)Measured groundwater values from stations within 10 km of the fishing district (nitrates, harmful substances, ammonium, iron, chlorides) and the SHMÚ yearbooks.

Groundwater within 10 km (8 stations)

  • Vieska nad ZitavouZlaté Moravce district · borehole or well · 0.2 km from the fishing district
    natural substances only
    2017 to 2025

    Exceeded in 2025:

    • Manganese
    Measured values, year 2025, sampling 1 Oct 2025 (2 samplings, the highest value of the year for each substance)
    • Nitrates8.8 mg/l
    • Ammonium0.02 mg/l
    • Nitrites0.05 mg/l
    • Iron0.01 mg/l
    • Chlorides83.2 mg/l
    • Antimony24% of the standard
  • Nova Ves nad ZitavouNitra district · borehole or well · 0.2 km from the fishing district
    natural substances only
    2017 to 2025

    Exceeded in 2025:

    • Manganese
    • Total iron
    • Ammonium
    • TOC
    • COD-Mn
    Measured values, year 2025, sampling 2 Oct 2025 (2 samplings, the highest value of the year for each substance)
    • Nitrates13.7 mg/l
    • Ammonium0.75 mg/l
    • Nitrites0.01 mg/l
    • Iron0.22 mg/l
    • Chlorides32.9 mg/l
    • Nickel25% of the standard
  • Zlate MoravceZlaté Moravce district · borehole or well · 0.3 km from the fishing district
    natural substances only
    2017 to 2025

    Exceeded in 2025:

    • Manganese
    • Total iron
    Measured values, year 2025, sampling 1 Oct 2025 (2 samplings, the highest value of the year for each substance)
    • Nitrates22.2 mg/l
    • Ammonium0.02 mg/l
    • Nitrites0.01 mg/l
    • Iron0.32 mg/l
    • Chlorides89.2 mg/l
    • Aluminium15% of the standard
    • terbutryn30% of the standard
    • benzo(a)pyrene80% of the standard
Show 5 more
  • MachulinceZlaté Moravce district · borehole or well · 0.3 km from the fishing district
    no exceedance in 2025
    2017 to 2025

    Last exceeded in 2024:

    • Manganese
    Measured values, year 2025, sampling 1 Oct 2025 (2 samplings, the highest value of the year for each substance)
    • Nitrates9.8 mg/l
    • Ammonium0.01 mg/l
    • Nitrites0.05 mg/l
    • Iron0.003 mg/l
    • Chlorides94 mg/l
    • Aluminium15% of the standard
  • MelekNitra district · borehole or well · 0.6 km from the fishing district
    natural substances only
    2017 to 2025

    Exceeded in 2025:

    • Manganese
    • Total iron
    Measured values, year 2025, sampling 2 Oct 2025 (2 samplings, the highest value of the year for each substance)
    • Nitrates18.5 mg/l
    • Ammonium0.09 mg/l
    • Nitrites0.03 mg/l
    • Iron1.17 mg/l
    • Chlorides58.9 mg/l
    • Arsenic27% of the standard
  • DyckaNitra district · borehole or well · 1.5 km from the fishing district
    substances from human activity
    2017 to 2025

    Exceeded in 2025:

    • Manganese
    • Total iron
    • Conductivity at 20 °C
    • TOC
    • Benzo(a)pyrene
    Measured values, year 2025, sampling 2 Oct 2025 (2 samplings, the highest value of the year for each substance)
    • Nitrates3.2 mg/l
    • Ammonium0.37 mg/l
    • Nitrites0.21 mg/l
    • Iron10.9 mg/l
    • Chlorides20.9 mg/l
    • Aluminium45% of the standard
    • benzo(a)pyrene100% of the standard
  • Novy TekovLevice district · borehole or well · 4.1 km from the fishing district
    substances from human activity
    2017 to 2025

    Exceeded in 2025:

    • Ratio of NO3 to NO2
    • Nitrates
    Measured values, year 2025, sampling 21 Oct 2025 (2 samplings, the highest value of the year for each substance)
    • Nitrates59.9 mg/l
    • Ammonium< 0.01 mg/l
    • Nitrites0.01 mg/l
    • Iron0.004 mg/l
    • Chlorides32.9 mg/l
    • Arsenic13% of the standard
  • Kozarovce – za MlynomLevice district · borehole or well · 4.1 km from the fishing district
    substances from human activity
    2017 to 2025

    Exceeded in 2025:

    • Ratio of NO3 to NO2
    • Nitrates
    Measured values, year 2025, sampling 20 Oct 2025 (2 samplings, the highest value of the year for each substance)
    • Nitrates50 mg/l
    • Ammonium0.08 mg/l
    • Nitrites0.05 mg/l
    • Iron0.002 mg/l
    • Chlorides49.1 mg/l
    • Arsenic54% of the standard
  • substances from human activity
  • natural substances only
  • no exceedance recorded

Groundwater reaches streams as base flow, so the connection to the stream at the fishing district is only indirect. Natural substances (iron, manganese, sulfates, conductivity) are not counted in the yearbook-based assessment.

The data comes from the SHMÚ yearbooks (groundwater 2017 to 2025).

Wastewater treatment plants

Wastewater treatment plants near the fishing districtPlants within 2 km of the district: overload, compliance with EU requirements and discharged load (BOD₅, COD, nitrogen, phosphorus in tonnes per year).
  • COV Zlate Moravceon the fishing district line · capacity 21,473 PE · mechanical, biological, nitrogen and phosphorus removal
    within the standard
    83% of capacity
  • COV Vrableon the fishing district line · capacity 9,000 PE · mechanical, biological, phosphorus removal
    within the standard
    70% of capacity

Treatment plants within 2 km of the fishing district. The treatment plant need not lie upstream of the fishing district; we do not assess the watercourse at the plant. Load is the ratio of the pollution produced to the capacity of the treatment plant (PE = population equivalent).

River basin and reservoir

Reservoir depth (HydroLAKES)Average depth, volume and water retention time in the reservoir from the HydroLAKES database (WWF). The depth is estimated by a model from the surrounding terrain, so it is approximate.

Watercourse from the HydroRIVERS database matched with the fishing district, line deviation about 317 m

Catchment above the spotWatercourse size (HydroRIVERS)The catchment area above the spot, the stream order and the average flow from the HydroRIVERS database (WWF). It determines whether it is a stream, a river or a large river.
295 km²medium river
Average flow
1.43 m³/smodel value
Stream order (Strahler)
3middle course
Channel gradient
3.4 ‰Gentle gradient

The data come from a global database with a coarser resolution (tens of metres), so they are only approximate for small waters. Depth and volume are model averages.

Bed and bedrock

Bottom and bedrock (ŠGÚDŠ)The bedrock under the water according to the hydrogeological map of Slovakia at 1 : 50,000 (ŠGÚDŠ). It tells whether the surroundings are gravelly, sandy, clayey, muddy or rocky.

After rain the water quickly turns turbid and fish hunt more by smell.

  • Gravels 33%
  • Clays and loams 67%
Springs and outflows
0none within 1 km

According to the geological map: fluviálne sedimenty: litofaciálne nečlenené nivné hliny, alebo piesčité až štrkovité hliny dolinných nív a nív horských potokov, holocén

The fishing district description states the bottom: gravel, bedrock, stony; the geological map shows something different, and the district description is more precise.

The map shows the bedrock geology, not the exact bottom at the spot. The actual bottom material may differ, especially where sediment has been deposited.

Aquatic insects

Aquatic insect swarming (iNaturalist)How many observations of mayflies, caddisflies and stoneflies people nearby recorded this month compared with the annual average. For fly anglers it hints at insect hatches.

Few insects November: 0.4× the average month

  1. Jan
  2. Feb
  3. Mar
  4. Apr
  5. May
  6. June
  7. July
  8. Aug
  9. Sep
  10. Oct
  11. Nov
  12. Dec
  • MayfliesMayflies0Mayflies: dry fly on the surface, especially at dusk.
  • CaddisfliesCaddisflies0Caddisflies: in the evening and at night by the bank; a nymph and a wet fly also work.
  • StonefliesStoneflies0Stoneflies: clean, cold streams, often already at the end of winter and in early spring.
Photo credits

0.4× the average month, 5 of 155 observations in the year, iNaturalist.

The observations are added by people from the surrounding area; they are not measurements at the water. They show when aquatic insects usually appear and are useful mainly for fly fishing.

Groundwater: measured values

Groundwater nearby (SHMÚ)Measured groundwater values from stations within 10 km of the fishing district (nitrates, harmful substances, ammonium, iron, chlorides) and the SHMÚ yearbooks.

A typical value from 8 groundwater stations within 10 km of the fishing district (nearest 0.2 km), measured in 2025. Closer stations carry more weight. This is groundwater near the district, not a measurement in the watercourse itself. The standard is the limit that SHMÚ gives for the indicator (for drinking water); a value equal to the standard counts as an exceedance, as it does at SHMÚ. The label "somewhere above the standard" means that the typical value is below the standard but at least one station exceeds it; which one is shown on the tile. Fish are more sensitive to some substances than people are.

00.75

Ammonium

0.02mg/l

above the standard somewhere

Standard 0.5 mg/l. Range 0.005 to 0.75 mg/l, 8 stations. Above the standard: 1 of 8 (Nova Ves nad Zitavou, 0.2 km from the fishing district).

00.75

Nitrites

0.03mg/l

far below the standard

Standard 0.5 mg/l. Range 0.01 to 0.21 mg/l, 8 stations.

075

Nitrates

13.7mg/l

above the standard somewhere

Standard 50 mg/l. Range 3.2 to 59.9 mg/l, 8 stations. Above the standard: 2 of 8 (highest: Novy Tekov, 4.1 km from the fishing district).

012

Oxygen

0.17mg/l

low oxygen

Mark on the dial: 9 mg/l, the guideline for salmonid waters. Range 0.075 to 7.61 mg/l, 8 stations.

020

Water temperature

12.5°C

warmer

Range 11.4 to 14.3 °C, 8 stations.

510

pH

7.06

suitable for fish

Range 6.7 to 7.35, 8 stations.

08

Water hardness

5.66mmol/l

hard

Range 2.96 to 7.07 mmol/l, 8 stations.

00.3

Iron

0.22mg/l

above the standard

Standard 0.2 mg/l. Range 0.002 to 10.9 mg/l, 8 stations. Above the standard: 4 of 8 (highest: Dycka, 1.5 km from the fishing district).

00.075

Manganese

0.35mg/l

above the standard

Standard 0.05 mg/l. Range 0.002 to 5.32 mg/l, 8 stations. Above the standard: 5 of 8 (highest: Nova Ves nad Zitavou, 0.2 km from the fishing district).

0375

Chlorides

83.2mg/l

below the standard

Standard 250 mg/l. Range 20.9 to 94 mg/l, 8 stations.

0375

Sulphates

104mg/l

below the standard

Standard 250 mg/l. Range 28.8 to 175 mg/l, 8 stations.

0188

Conductivity

97.8mS/m

close to the standard

Standard 125 mS/m. Range 64.3 to 164 mS/m, 8 stations. Above the standard: 1 of 8 (Dycka, 1.5 km from the fishing district).

0150%

Metals and metalloids

24% of standard

below the standard

Highest: Arsenic 5.4 µg/l (54% of the standard, 4.1 km from the fishing district). 8 stations.

0150%

Pesticides

30% of standard

below the standard

Highest: terbutryn 0.03 µg/l (30% of the standard, 0.3 km from the fishing district). 2 stations.

0150%

Solvents and benzene

0% of standard

not detected

Below the limit of quantification: substances from this group were not detected in the samples. 3 stations.

0150%

PAHs (combustion, petroleum substances)

80% of standard

close to the standard

Highest: benzo(a)pyrene 0.01 µg/l (100% of the standard, 1.5 km from the fishing district). 3 stations. Above the standard: 1 of 3.

How it affects fish and the water
Ammonium
Ammonium ions are not very toxic in themselves, but depending on pH and temperature part of them turns into ammonia (NH₃), which damages the gills and stresses fish. The higher the pH and temperature, the more ammonia there is (Emerson et al. 1975). The repealed Directive 2006/44/EC gave a guideline of at most 0.04 mg/l of ammonium for salmonid waters and 0.2 mg/l for cyprinid waters.
Nitrites
Nitrites are toxic to fish: they pass through the gills into the blood and turn hemoglobin into methemoglobin, which does not carry oxygen, so fish "suffocate" even in oxygenated water. Salmonids are the most sensitive; chlorides in the water reduce the toxicity (Lewis and Morris 1986). Directive 2006/44/EC gave a guideline of 0.01 mg/l for salmonid waters.
Nitrates
Nitrates do not harm adult fish immediately, but they feed algae and plants and so contribute to over-fertilization and nighttime oxygen crashes. For sensitive aquatic animals (salmonids, amphibians, some invertebrates) Camargo et al. (2005) recommend keeping nitrates below 2 mg of nitrogen per liter, which is about 9 mg/l of nitrates.
Oxygen
Fish, especially salmonids, need a lot of oxygen. Directive 2006/44/EC gave a guideline of 9 mg/l for salmonid waters (in at least half of the measurements) and never less than 7 mg/l. Groundwater from deeper layers often has less of it; in the stream it is re-oxygenated only after it emerges.
Water temperature
Groundwater has an almost constant temperature throughout the year. Inflow from springs can therefore cool a stream in summer and warm it in winter, and such sections often serve as refuges for cold-water fish (Hayashi and Rosenberry 2002).
pH
Fish tolerate a pH of roughly 6 to 9 (Directive 2006/44/EC). Outside this range the gills are damaged and the toxicity of ammonia and metals changes.
Water hardness
Harder water (more calcium and magnesium) is better for fish: calcium protects the gills and reduces the toxicity of metals such as copper and zinc (Pagenkopf 1983), and keeps the pH stable. Soft water is more sensitive to metals and to acidification.
Iron
Iron is dissolved in groundwater at depth. When the water reaches the air, it oxidizes and precipitates as brown flocs that clog gills, cover gravel with eggs and invertebrates, and destroy shelters (Vuori 1995).
Manganese
Manganese is natural in deeper groundwater. For fish it tends to matter less than iron; the standard applies mainly because of the taste and color of drinking water.
Chlorides
Chlorides come from road salt, fertilizers and waste. The US EPA (1988) set 230 mg/l for long-term protection of aquatic life and 860 mg/l for short-term.
Sulphates
Sulfates are common in groundwater; they come from rocks (for example gypsum), fertilizers and mines. Together with chlorides they raise the mineralization of the water; the standard of 250 mg/l is set for drinking water.
Conductivity
Conductivity shows the total amount of dissolved salts. A higher value in groundwater is often natural (limestone, gypsum), but a sharp increase in a stream points to an inflow of salts from roads, mines or waste.
Metals and metalloids
Copper, zinc, nickel, cadmium and mercury are toxic to fish even at low concentrations, more so in soft water than in hard water (Pagenkopf 1983). The groundwater standard is set for drinking water, not for fish.
Pesticides
Pesticides get into groundwater from fields. The standard of 0.1 µg/l per substance (0.5 µg/l in total) is a drinking-water standard and is very strict; fish are usually harmed only by a much higher concentration. The value mainly shows how heavily the surroundings are burdened by agriculture.
Solvents and benzene
Chlorinated solvents (for example tetrachloroethene) and benzene come from industry, treatment plants and petrol stations. They are toxic and break down slowly in groundwater.
PAHs (combustion, petroleum substances)
PAHs are formed by combustion and petroleum spills. The standard for benzo(a)pyrene (0.01 µg/l) is very strict for drinking water because it is a carcinogen.

Sources

  1. Camargo, J. A., Alonso, Á., Salamanca, A. (2005): Nitrate toxicity to aquatic animals: a review with new data for freshwater invertebrates. Chemosphere 58, 1255–1267.
  2. Lewis, W. M., Morris, D. P. (1986): Toxicity of nitrite to fish: a review. Transactions of the American Fisheries Society 115, 183–195.
  3. Emerson, K., Russo, R. C., Lund, R. E., Thurston, R. V. (1975): Aqueous ammonia equilibrium calculations: effect of pH and temperature. Journal of the Fisheries Research Board of Canada 32, 2379–2383.
  4. Directive 2006/44/EC on the quality of fresh waters needing protection or improvement in order to support fish life (repealed in 2013; we give its values here only as an expert guideline).
  5. Vuori, K.-M. (1995): Direct and indirect effects of iron on river ecosystems. Annales Zoologici Fennici 32, 317–329.
  6. Pagenkopf, G. K. (1983): Gill surface interaction model for trace-metal toxicity to fishes: role of complexation, pH, and water hardness. Environmental Science & Technology 17, 342–347.
  7. U.S. EPA (1988): Ambient Water Quality Criteria for Chloride. EPA 440/5-88-001.
  8. Hayashi, M., Rosenberry, D. O. (2002): Effects of ground water exchange on the hydrology and ecology of surface water. Ground Water 40, 309–316.

Fish, wildlife, plants and hazards around the waterWildlife and hazards by the water (GBIF)Game animals, birds, plants and hazards (bear, ticks, mosquitoes, giant hogweed) that people have recorded around the water. It is not part of the fishing conditions score and is for information only.

Species that have been observed or recorded around the water. Wildlife, plants and hazards do not enter the fishing conditions score and are for information only. The name of a species leads to its page.

MallardBird

Mallard

many records
Most records: May.
About the species

The most common duck; it nests by almost every water with bankside vegetation.

Grey heronBird

Grey heron

protected speciesmany records
Most records: May.
About the species

It stands in the shallows and lies in wait for small fish. It is easy to see along the banks of ponds and slow streams.

Great egretBird

Great egret

protected speciesmany records
Most records: September.
About the species

A large white heron that hunts fish and frogs in the shallows. In Slovakia its numbers are rising, and in winter it can also be seen by watercourses.

Mute swanBird

Mute swan

protected speciesmany records
Most records: May.
About the species

A large white waterbird that nests by slow waters, reservoirs and ponds with vegetation.

Common kingfisherBird

Common kingfisher

protected speciesquite a few records
Most records: September.
About the species

A small bird that dives for little fish. It nests in steep banks of clean streams.

DragonfliesWildlife

Dragonflies

quite a few records
Most records: June.
About the species

Predatory insect. The larvae live underwater for several months to years; adult dragonflies hunt in the air above the water.

CaddisfliesWildlife

Caddisflies

a few records
Most records: June.
About the species

Insects whose larvae, in many species, build protective cases from pebbles, sand or plants.

Grass snakeWildlife

Grass snake

protected speciesa few records
Most records: August.
About the species

A harmless snake with two yellow spots on the nape. It swims well and hunts frogs, fish and newts.

Pond sliderWildlife

Pond slider

invasive speciesa few records
Most records: March.
About the species

A non-native turtle from America that got into the wild from home pet keeping. It is invasive in Europe.

Eurasian beaverWildlife

Eurasian beaver

protected speciesa single record
Most records: January.
About the species

A herbivore that changes the stream and its banks with dams and burrows. It is protected. It creates shallows and pools where fish and insects thrive.

Fire salamanderWildlife

Fire salamander

protected speciesa single record
Most records: October.
About the species

Black with yellow spots. Lives in deciduous forests by clean mountain streams; the larvae develop in the stream.

Green frogs (water frogs)Wildlife

Green frogs (water frogs)

protected speciesa single record
Most records: September.
About the species

A group of green frogs that sit by the bank and jump into the water when disturbed.

Common reedPlant

Common reed

quite a few records
Most records: September.
About the species

Tall grass that forms extensive reed beds around ponds and on banks.

Black alderPlant

Black alder

quite a few records
Most records: July.
About the species

A riparian tree whose roots reach below the water surface.

Yellow flag irisPlant

Yellow flag iris

quite a few records
Most records: June.
About the species

A tall wetland plant with yellow flowers that grows on damp banks.

Japanese knotweedInvasive plant

Japanese knotweed

invasive speciesa few records
Most records: July.
About the species

An invasive herb from East Asia that forms dense stands up to three metres tall.

Broadleaf cattailPlant

Broadleaf cattail

a few records
Most records: July.
About the species

A wetland plant with a brown cylindrical fruiting spike.

Common duckweedPlant

Common duckweed

a few records
Most records: September.
About the species

A tiny floating plant that can cover the whole surface of standing water.

Castor bean tickRisk

Castor bean tick

to be reckoned withquite a few records
Most records: April.
How to protect yourself

Transmits tick-borne encephalitis and Lyme disease. It waits in tall grass and in the vegetation along banks.

How to protect yourself: From spring to autumn check yourself after fishing, use repellent and tuck long trousers into your socks. Remove a tick as soon as possible with tweezers. A vaccination against encephalitis exists.

MosquitoesRisk

Mosquitoes

to be reckoned withquite a few records
Most records: April.
How to protect yourself

They breed in standing water, so they are worst around reservoirs, oxbow lakes and floodplain forests, especially at sunset.

How to protect yourself: When fishing in the evening and at night wear long sleeves, repellent and a net. Warmth and humidity after rain speed up mosquito development.

Giant hogweedRisk

Giant hogweed

to be reckoned withinvasive speciesa few records
Most records: March.
How to protect yourself

An invasive plant that grows along stream banks and on wet meadows. In sunlight its sap causes skin burns.

How to protect yourself: Do not touch it and do not walk through the vegetation. If the sap gets on your skin, wash it off with water and soap and protect the area from the sun. See a doctor for larger burns.

Wild boarRisk

Wild boar

to be reckoned witha single record
Most records: August.
How to protect yourself

It comes to the water to wallow and drink, mainly at dusk and at night.

How to protect yourself: A wild boar sow with piglets can be aggressive. Keep your distance, do not spend the night on a game trail and do not leave food scraps near the water.

HorsefliesRisk

Horseflies

to be reckoned witha single record
Most records: May.
How to protect yourself

Large biting flies. They are most active on hot, windless days near water and on meadows.

How to protect yourself: They sting painfully, especially in summer around midday. Light-colored clothing with long sleeves and repellent help.

Wildlife, plants and hazards: records come from observations and also reflect where observers move around; they are not density measurements or a guarantee of an encounter. They apply to the surroundings of about 35 × 55 km.

Photo credits

Animal and plant catalog

Source: GBIFUpdated 6 Nov 2026 15:59

Ground under the water: geology, faults and radon

Bedrock, watercourse and springs on the map, values at the location of the water, geomagnetic activity and earthquakes. This is information about the environment; only small hypotheses marked with a confidence level (faults and rocks, geomagnetic storm) enter the score.

The bedrock map needs JavaScript to be turned on.

The map can be panned and zoomed; the ŠGÚDŠ layers are stored on this server. © State Geological Institute of Dionýz Štúr. Base map scale 1 : 50,000 (faults and geology); radioactivity and magnetics are coarser.

Values at the water spot

Values at the water spotBedrock radon risk, uranium, thorium, potassium, gamma radiation and magnetic anomaly at a single spot by the water (marked with a dot on the map).

Radon risk of the bedrock

medium

Common for most of Slovakia.

08

Uranium (eU)

2.8ppm

common

Typical background of the rocks.

020

Thorium (eTh)

8.4ppm

around the crustal average

Natural background of the rocks.

04

Potassium (K)

1.53%

below the crustal average

Natural background of the rocks.

0150

Gamma radiation

57nGy/h

around the world average

Natural background of the bedrock.

SVJZ

Magnetic anomaly (ΔT)

5nT

above the average of the surroundings

Deviation of the magnetic field from the average of the surroundings.

The values apply to a single spot (marked with a dot on the map), not as an average of the whole watercourse or river basin. Radon is a natural tracer in groundwater; the map does not include radon in water, only the bedrock risk.

Mark on the dial: the average of the upper continental crust (uranium 2.7 ppm, thorium 10.5 ppm, potassium 2.3%; Rudnick and Gao 2003) and the world average of the natural outdoor dose 59 nGy/h (UNSCEAR 2000). The needle does not swing towards “good” or “bad”; it only shows where the value lies.

Elevated uranium or radon is only information about the rock. It has no proven significance for bites; it helps to read what bedrock the water comes from.

Faults and springs

Faults and springsThe distance to the nearest tectonic fault on the geological map and the number of springs nearby. Fissure groundwater flows out along faults.
250 m1 km3 km8 km

Nearest fault

up to 250 m

fault nearby

Tectonic fault on the geological map.

Springs and outflows

0

none marked

None within 1 km.

covered by younger sediments detected at the surface

Fissure groundwater flows out of the bedrock along faults and at springs. It tends to be cooler in summer and warmer in winter than the water in the stream, so according to anglers' experience fish stay near such places in extreme weather (summer and winter islands of a more suitable temperature).

However, fresh fissure water can have little oxygen. This is anglers' experience, not a phenomenon measured at this fishing district.

Faults are from the geological map at 1 : 50,000. Springs come from a hydrogeological map that covers only some regions, so zero does not mean there are no springs there.

Geology nearby: rock, water, sediments, boreholes

Geology and geochemistry around the waterRock under the water, composition of water and sediments according to the atlases, radioactivity, geothermal potential, boreholes, old mine workings, deposits, burdens, landslides and gold in sediments, from ŠGÚDŠ maps and registers.
Halda z ťažby a spracovania andezitu – 5 – spoil heap (160 m from the water)Halda Obyce – 5 – spoil heap (310 m from the water)Halda zo spracovania andezitu – 5 – spoil heap (330 m from the water)Halda z ťažby andezitu – 5 – spoil heap (360 m from the water)Halda z kameňolomu – 5 – spoil heap (1.2 km from the water)Halda zo spracovania andezitu – 5 – spoil heap (2.0 km from the water)Vráble – skládka KO (časť Židová) – SK2001000P (90 m from the water)Vráble – areál Tesly (TESGAL) – SK1000400P (470 m from the water)Zlaté Moravce – bývalý areál Calexu – SK1000400P (600 m from the water)Zlaté Moravce – rušňové depo – SK1000400P (650 m from the water)Čierne Kľačany – skládka TKO (pod jabloňovým sad – SK2001000P (860 m from the water)Volkovce – Závada – occasional (20 m from the water)Tesáre nad Žitavou – permanent (30 m from the water)Zlaté Moravce – Kňažice – none (30 m from the water)Machulince – permanent (30 m from the water)Mankovce – Zlatno – none (40 m from the water)Hosťovce – permanent (50 m from the water)Malé Vozokany – occasional (50 m from the water)Dolné Sľažany – occasional (60 m from the water)Martin nad Žitavou – occasional (60 m from the water)Čierne Kľačany – occasional (60 m from the water)Obyce – permanent (60 m from the water)Neverice – occasional (60 m from the water)Kostoľany pod Tribečom – none (60 m from the water)Volkovce – permanent (60 m from the water)Kostoľany pod Tribečom – none (60 m from the water)Mochovce – pri trati – Mochovce – none (60 m from the water)Beladice – Veľké Chrašťany – occasional (70 m from the water)Dolné Sľažany – occasional (70 m from the water)Vieska nad Žitavou – permanent (70 m from the water)Beladice – Veľké Chrašťany – occasional (90 m from the water)Telince – none (90 m from the water)Zlaté Moravce – occasional (100 m from the water)Mankovce – Hušťavky – Mankovce – none (110 m from the water)Kostoľany pod Tribečom – none (110 m from the water)Zlaté Moravce – none (110 m from the water)Martin nad Žitavou – none (110 m from the water)Slepčany – cannot be estimated (120 m from the water)Červený Hrádok – occasional (120 m from the water)Slepčany – none (130 m from the water)Ladice – occasional (130 m from the water)Obyce – none (130 m from the water)Červený Hrádok – occasional (140 m from the water)Zlaté Moravce – none (150 m from the water)Veľké Vozokany – permanent (160 m from the water)Volkovce – occasional (160 m from the water)Skládka Židová Vráble – Vráble – none (160 m from the water)Dolné Sľažany – none (160 m from the water)Vráble – Podmáj – Vráble – permanent (170 m from the water)Zlaté Moravce – occasional (180 m from the water)Volkovce – none (200 m from the water)Vieska nad Žitavou – cannot be estimated (200 m from the water)Machulince – occasional (210 m from the water)Ladice – none (220 m from the water)Zlaté Moravce – none (220 m from the water)Veľké Vozokany – cannot be estimated (220 m from the water)Velčice – none (220 m from the water)Tesárske Mlyňany – Tesáre nad Žitavou – occasional (230 m from the water)Zlaté Moravce – Opatovce nad Žitavou – none (240 m from the water)Nemčiňany – occasional (240 m from the water)Volkovce – occasional (240 m from the water)Beladice – Malé Chrašťany – none (240 m from the water)Velčice – none (260 m from the water)Dolné Sľažany – none (270 m from the water)Ladice – none (270 m from the water)Neverice – none (310 m from the water)Mochovce – cintorín – Mochovce – none (320 m from the water)Ladice – cannot be estimated (330 m from the water)Obyce – none (340 m from the water)Nemčiňany – none (340 m from the water)Nevidzany – occasional (340 m from the water)Mlyňany – cannot be estimated (340 m from the water)Malé Vozokany – none (350 m from the water)Veľké Vozokany – Červený Hrádok – occasional (360 m from the water)Obyce – none (390 m from the water)Velčice – none (400 m from the water)Kostoľany pod Tribečom – none (400 m from the water)Velčice – occasional (420 m from the water)Volkovce – occasional (440 m from the water)Tajná – Nevidzany – occasional (440 m from the water)Ladice – occasional (450 m from the water)Zlaté Moravce – occasional (450 m from the water)Mochovce – HYDROSTAV – Mochovce – none (460 m from the water)Machulince – none (470 m from the water)Vieska nad Žitavou – cannot be estimated (490 m from the water)Obyce – permanent (510 m from the water)Machulince – none (530 m from the water)Malé Vozokany – none (530 m from the water)Vieska nad Žitavou – cannot be estimated (540 m from the water)Velčice – none (570 m from the water)Čierne Kľačany (Za kostolom) – Čierne Kľačany – none (580 m from the water)Čifáre – permanent (580 m from the water)Zlaté Moravce – none (590 m from the water)Obyce – none (590 m from the water)Velčice – none (600 m from the water)Obyce – none (600 m from the water)Lovce – permanent (600 m from the water)Lovce – permanent (610 m from the water)Nevidzany – Červený Hrádok – occasional (640 m from the water)Mochovce (Waste transport, a.s.) – Mochovce – none (650 m from the water)Obyce – none (670 m from the water)Hosťovce – none (720 m from the water)Kostoľany pod Tribečom – none (750 m from the water)Hosťovce – none (770 m from the water)Obyce – occasional (800 m from the water)Beladice – Pustý Chotár – none (830 m from the water)Zlaté Moravce – occasional (850 m from the water)Lovce – cannot be estimated (860 m from the water)Beladice – Pustý Chotár – none (880 m from the water)Obyce – occasional (900 m from the water)Čifáre – Fertále – Čifáre – occasional (910 m from the water)Obyce – permanent (910 m from the water)Horné Sľažany – none (910 m from the water)Tajná – Nová Ves nad Žitavou – none (930 m from the water)Horné Sľažany – occasional (940 m from the water)Zlaté Moravce – permanent (960 m from the water)Machulince – occasional (1.0 km from the water)Beladice – Veľké Chrašťany – none (1.1 km from the water)Beladice – Beladice II – none (1.1 km from the water)Nevidzany – permanent (1.2 km from the water)Veľké Vozokany – none (1.3 km from the water)Machulince – none (1.5 km from the water)Zlaté Moravce – Pod Kalváriou – Zlaté Moravce – none (1.5 km from the water)Veľké Chyndice – cannot be estimated (1.6 km from the water)Tehla – none (1.7 km from the water)Malé Chyndice – none (1.8 km from the water)Źikava – Žikava – occasional (1.9 km from the water)Topoľčianky – none (1.9 km from the water)Topoľčianky – none (2.0 km from the water)Topoľčianky – none (2.1 km from the water)Michal nad Žitavou – none (2.1 km from the water)Obyce – KD-1 – non-spa (870 m from the water)Klasov – Vráble-1 – non-spa (3.5 km from the water)KD-1 – j1 (1.3 km from the water)G-1 – l2 (9.9 km from the water)b1 (700 m from the water)b1 (1.7 km from the water)Volkovce – gravelly sands and sands (170 m from the water)Čierne Kľačany – building stone (200 m from the water)Obyce – building stone (330 m from the water)Obyce – building stone (700 m from the water)Machulince – brick raw materials (820 m from the water)Zlaté Moravce II – brick raw materials (1.3 km from the water)Hostie – building stone (2.4 km from the water)Súlovce – building stone (3.8 km from the water)Jelenec – quartzite (3.8 km from the water)Jelenec – building stone (3.8 km from the water)Čierne Kľačany – building stone (180 m from the water)Volkovce – gravelly sands and sands (220 m from the water)Obyce – building stone (340 m from the water)Obyce – building stone (710 m from the water)Zlatno – quartzite (730 m from the water)Machulince – brick raw materials (820 m from the water)Zlaté Moravce II – brick raw materials (1.3 km from the water)Ladice – ceramic clays (1.4 km from the water)Beladice – lignite (2.2 km from the water)Hostie – building stone (2.4 km from the water)Žikava – ceramic clays (2.4 km from the water)Súlovce – building stone (3.8 km from the water)Jelenec – building stone (3.8 km from the water)Jelenec – quartzite (3.8 km from the water)Horné Lefantovce – ceramic clays (5.0 km from the water)Ladice – ceramic clays (1.4 km from the water)Žikava – ceramic clays (2.5 km from the water)Horné Lefantovce – ceramic clays (5.0 km from the water)Obyce – building stone (50 m from the water)Nemčiňany I – gravelly sands and sands (270 m from the water)Opatovce – Kamenné vráta I – building stone (380 m from the water)Opatovce – Kamenné vráta – building stone (470 m from the water)Machulince – building stone (740 m from the water)Dolné Sľažany – ceramic clays (280 m from the water)Martin nad Žitavou – ceramic clays (290 m from the water)Telince – ceramic clays (400 m from the water)Čifáre – ceramic clays (560 m from the water)Lovce – Fe ores – magnetite (760 m from the water)Zlatno – ceramic raw materials – quartz (1.3 km from the water)Obyce – ceramic clays (1.3 km from the water)Vajka nad Žitavou – ceramic raw materials (1.3 km from the water)Beladice – limestone (2.1 km from the water)Veľký Ďur – ceramic clays (2.5 km from the water)Kmeťovo – brick raw materials (3.9 km from the water)Topoľčianky – ceramic raw materials – granitoids (4.1 km from the water)Topoľčianky – ceramic raw materials – granitoids (4.3 km from the water)Tehla – brick raw materials (4.5 km from the water)Machulince – volcanic rocks (490 m from the water)CIFARE – Landslides (110 m from the water)– Landslides (370 m from the water)LADICE – Landslides (820 m from the water)ZLATE MORAVCE – Landslides (1.4 km from the water)– Landslides (1.4 km from the water)Zlaté Moravce – širokoprofilový vrt (Ø vŕtania nad 600 m (10 m from the water)Zlaté Moravce – úzkoprofilový vrt s obyčajnou pitnou a ú (20 m from the water)Hosťovce – úzkoprofilový vrt s obyčajnou pitnou a ú (20 m from the water)Zlaté Moravce – Čierna Dolina – úzkoprofilový vrt s obyčajnou pitnou a ú (20 m from the water)Mochovce – monitoring borehole (30 m from the water)Čierne Kľačany – úzkoprofilový vrt s obyčajnou pitnou a ú (30 m from the water)Zlaté Moravce – monitoring borehole (30 m from the water)Zlaté Moravce – úzkoprofilový vrt s obyčajnou pitnou a ú (30 m from the water)Žitavany – úzkoprofilový vrt s obyčajnou pitnou a ú (30 m from the water)Vráble – úzkoprofilový vrt s obyčajnou pitnou a ú (30 m from the water)Čitáre – monitoring borehole (30 m from the water)Vráble – úzkoprofilový vrt s obyčajnou pitnou a ú (40 m from the water)Vráble – úzkoprofilový vrt s obyčajnou pitnou a ú (40 m from the water)Beladice – úzkoprofilový vrt s obyčajnou pitnou a ú (40 m from the water)Čierne Kľačany – úzkoprofilový vrt s obyčajnou pitnou a ú (50 m from the water)Volkovce – úzkoprofilový vrt s obyčajnou pitnou a ú (50 m from the water)Vráble – úzkoprofilový vrt s obyčajnou pitnou a ú (50 m from the water)Beladice – úzkoprofilový vrt s obyčajnou pitnou a ú (50 m from the water)Kostoľany pod Tribečom – úzkoprofilový vrt s obyčajnou pitnou a ú (60 m from the water)Vráble – úzkoprofilový vrt s obyčajnou pitnou a ú (60 m from the water)Čifáre – monitoring borehole (60 m from the water)Nemčiňany – úzkoprofilový vrt s obyčajnou pitnou a ú (60 m from the water)Čierne Kľačany – úzkoprofilový vrt s obyčajnou pitnou a ú (60 m from the water)Zlaté Moravce – širokoprofilový vrt (Ø vŕtania nad 600 m (60 m from the water)Hosťovce – úzkoprofilový vrt s obyčajnou pitnou a ú (60 m from the water)Choča – úzkoprofilový vrt s obyčajnou pitnou a ú (60 m from the water)Nemčiňany – úzkoprofilový vrt s obyčajnou pitnou a ú (60 m from the water)Martin nad Žitavou – monitoring borehole (60 m from the water)Obyce – monitoring borehole (60 m from the water)Nemčiňany – úzkoprofilový vrt s obyčajnou pitnou a ú (60 m from the water)Vráble – úzkoprofilový vrt s obyčajnou pitnou a ú (60 m from the water)Volkovce – úzkoprofilový vrt s obyčajnou pitnou a ú (70 m from the water)Beladice – Chrašťany – monitoring borehole (70 m from the water)Červený Hrádok – monitoring borehole (70 m from the water)Vráble – úzkoprofilový vrt s obyčajnou pitnou a ú (70 m from the water)Nová Ves n/Žitavou – úzkoprofilový vrt s obyčajnou pitnou a ú (70 m from the water)Nemčiňany – úzkoprofilový vrt s obyčajnou pitnou a ú (70 m from the water)Nemčiňany – úzkoprofilový vrt s obyčajnou pitnou a ú (70 m from the water)Zlaté Moravce – úzkoprofilový vrt s obyčajnou pitnou a ú (70 m from the water)Zlaté Moravce – úzkoprofilový vrt s obyčajnou pitnou a ú (70 m from the water)vodárensky využívaný vrt – Hydrogeological boreholes (10 m from the water)vodárensky využívaný vrt – Hydrogeological boreholes (20 m from the water)vodárensky využívaný vrt – Hydrogeological boreholes (20 m from the water)existujúci hydrogeologický vrt – Hydrogeological boreholes (30 m from the water)existujúci hydrogeologický vrt – Hydrogeological boreholes (30 m from the water)vodárensky využívaný prameň – Groundwater springs (30 m from the water)existujúci hydrogeologický vrt – Hydrogeological boreholes (30 m from the water)existujúci hydrogeologický vrt – Hydrogeological boreholes (30 m from the water)existujúci hydrogeologický vrt – Hydrogeological boreholes (40 m from the water)existujúci hydrogeologický vrt – Hydrogeological boreholes (40 m from the water)existujúci hydrogeologický vrt – Hydrogeological boreholes (40 m from the water)výtok z podzemnej drenáže (trubky, horizontálne – Artificial hydrogeologically significant objects (50 m from the water)existujúci hydrogeologický vrt – Hydrogeological boreholes (50 m from the water)existujúci hydrogeologický vrt – Hydrogeological boreholes (50 m from the water)existujúci hydrogeologický vrt – Hydrogeological boreholes (50 m from the water)existujúci hydrogeologický vrt – Hydrogeological boreholes (60 m from the water)existujúci hydrogeologický vrt – Hydrogeological boreholes (60 m from the water)vrt s prelivom – Hydrogeological boreholes (60 m from the water)existujúci hydrogeologický vrt – Hydrogeological boreholes (60 m from the water)vodárensky využívaný vrt – Hydrogeological boreholes (60 m from the water)existujúci hydrogeologický vrt – Hydrogeological boreholes (60 m from the water)existujúci hydrogeologický vrt – Hydrogeological boreholes (60 m from the water)výtok z podzemnej drenáže (trubky, horizontálne – Artificial hydrogeologically significant objects (60 m from the water)prameň – Groundwater springs (70 m from the water)existujúci hydrogeologický vrt – Hydrogeological boreholes (70 m from the water)existujúci hydrogeologický vrt – Hydrogeological boreholes (70 m from the water)existujúci hydrogeologický vrt – Hydrogeological boreholes (70 m from the water)vrt s prelivom – Hydrogeological boreholes (70 m from the water)existujúci hydrogeologický vrt – Hydrogeological boreholes (70 m from the water)existujúci hydrogeologický vrt – Hydrogeological boreholes (70 m from the water)existujúci hydrogeologický vrt – Hydrogeological boreholes (70 m from the water)existujúci hydrogeologický vrt – Hydrogeological boreholes (80 m from the water)prameň – Groundwater springs (80 m from the water)existujúci hydrogeologický vrt – Hydrogeological boreholes (80 m from the water)existujúci hydrogeologický vrt – Hydrogeological boreholes (90 m from the water)existujúci hydrogeologický vrt – Hydrogeological boreholes (90 m from the water)existujúci hydrogeologický vrt – Hydrogeological boreholes (90 m from the water)existujúci hydrogeologický vrt – Hydrogeological boreholes (90 m from the water)pramenná línia – Groundwater springs (90 m from the water)existujúci hydrogeologický vrt – Hydrogeological boreholes (100 m from the water)Nová Ves nad Žitavou, 1800m V od K190 – well (20 m from the water)Ladice, v obci pri potoku, 600m S od K204 – well (20 m from the water)Nová Ves nad Žitavou, 1200m J od K154 – source (30 m from the water)Slepčany – RD, 1800m SSZod K188 – borehole (30 m from the water)Velčice, 800m J od rybníka, 700m JV odK314 – well (50 m from the water)Martin nad Žitavou, č.d.180 – well (60 m from the water)Maňkovce, 600m od mlyna, 1600m SSV od K220 – source (70 m from the water)Čierna dolina, 800m JJZ od K224 – borehole (80 m from the water)Velčice, 600m ZJZ od K232 – well (90 m from the water)Olichov, 600m ZJZ od K 454 – well (90 m from the water)Čierne Kľačany, 500m VJV od K 224 – borehole (90 m from the water)Velčice, 1300m JJV od K314 – well (90 m from the water)Maňkovce – pri MŠ, 1000m SV od K220 – well (90 m from the water)Maňkovce – starý mlyn, 1500m JJV od K419 – well (90 m from the water)Kostoľany pod Tribčom – v obci pod zastávkou, vý – source (90 m from the water)Vráble, 130m SZ od K149 – borehole (90 m from the water)Chyzmerovce, 600m Z od K174 Čižmárova 8 – well (100 m from the water)Lovce, pre RD, 600m VSV od K 330 – well (100 m from the water)Veľké Chyndice – pútnické miesto, zachytený zdro – well (120 m from the water)Martin nad Žitavo, 950m JV od K 229 – well (130 m from the water)Choča-oproti RD, 1000m SV od K206 – well (140 m from the water)Prílepy, 500m SV od K210 – borehole (140 m from the water)Slažany – prameň v obci upravený do podoby kamen – source (140 m from the water)Horný Oháj, 2100m VJV od K166 – borehole (160 m from the water)Hosťovce, č.d. 168, 500m ZJZ od K 228 – well (190 m from the water)Machulince, pred domom č.153 – well (190 m from the water)Slažany, pri cintoríne, 1500m JJV od K208 – well (200 m from the water)Slažany, pri železnici, 300m S od K194 – well (220 m from the water)Hosťovce, 300 m SV od K213 vrt JRD Tríbeč – borehole (220 m from the water)Vráble, 700m S od K143 – well (240 m from the water)Machulince – JV od obce, v koryte potoka, vyššie – source (260 m from the water)Lúčnica nad Žitavou, 1550m JZ od K143 – borehole (280 m from the water)Nová Ves nad Žitavou, 1250m JV od K168 – well (280 m from the water)Zlaté Moravce, 800m ZJZ od K212 – borehole (280 m from the water)Neverice, pri kostole,700m S od K177 – well (290 m from the water)Malé Chrasťany, 1200m SSZ od K166 – well (290 m from the water)Neverice, na konci, 1300m Z od K226 – borehole (300 m from the water)Choča, 900m JV od K206 – well (300 m from the water)Veľké Chrasťany, 1900m SSV od K193 – borehole (310 m from the water)Zlaté Moravce, Holého ul. 31 – well (310 m from the water)zlato 1 ks – gold (930 m from the water)20 km

The line is the water of the fishing district, the light band is the 3 km zone in which boreholes, mine workings and burdens were searched for. The map shows the nearest objects (at most a few dozen from each register), not all of them. The points correspond to the position in the register; area objects are marked by their centre.

Rock under the water

River alluvium86% of the water line

10% granitoids, 5% young sediments

Gravelly and sandy bottom and floodplains; the water is replenished from groundwater in the alluvium. Geological Map of Slovakia 1:50,000.

510

Water according to the atlas

pH 7.9modelled estimate

water type Ca–Mg–HCO₃

Mineralisation 503 mg/l, hard water (16.1 °dH). Interpolation of measurements from the Geochemical Atlas of Slovakia, not a measurement in the stream.

Elements in river sediment

0 from 15elements in the top 10 %

highest: Nickel 33.0 mg/kg

Position of the highest-ranked element among the sample points on streams in Slovakia: percentile 78. Interpolation of the Geochemical Atlas of river sediments.

1 km2 km49 °C84 °C

Heat underfoot

49°C at 1,000 m depth

heat flow 76 mW/m²

At a depth of 2,000 m about 84 °C (increase of 36 °C per kilometre). Atlas of Geothermal Energy of Slovakia.

Old mine workings

6objects within 3 km

Nearest: Halda z ťažby a spracovania andezitu (spoil heap), 160 m from the water.

Gold in river sediment

1sample with gold

13 ore minerals in the sediment

Up to 1 grain in one sample (930 m from the water). Panning prospecting counted gold grains in a concentrate from river sediment.

Trace elements in the stream water

4 from 9indicators in the top 5 %

highest: Lithium 88.0 μg/l

Position of the highest measured value in the distribution of all surface water samples in Slovakia: percentile 99 (Stará Žitava).

Boreholes and groundwater analyses

1,306boreholes within 3 km

2635 water analyses nearby

Of these, 1305 have an archive report from Geofond. The boreholes are hydrogeological, geological, engineering-geological and other.

0 °C120

Geothermal energy

51°C at the wellhead

2 geothermal boreholes within 10 km

Warmest: Klasov – Vráble-1, yield 8.0 l/s, 3.5 km from the water.

Environmental burdens and landfills

134sites within 3 km

5 environmental burdens, 129 landfills

Nearest burden: Vráble – skládka KO (časť Židová), 90 m from the water. Proximity does not mean that substances leak from the site into the water.

Deposits and ore occurrences

47records within 5 km

33 deposits, 14 ore occurrences

Geofond registers, the metallogenetic map and the mineral resources map.

Landslides and slope deformations

5areas within 3 km

Documented landslides in the Geofond register. A landslide into a stream can cloud the water and change the bed.

The data come from registers, maps and atlases of the State Geological Institute of Dionýz Štúr and describe the environment around the water. Proximity of a mine working or burden does not mean the water is polluted. The chemistry of water and sediments is a modelled estimate from interpolated maps of the Geochemical Atlas of Slovakia, not current monitoring or a measurement in the stream.

Detailed geology and geochemistry of the whole stream: rock under the water, water composition, elements in sediments, radiation, geothermal potential, metals, gold in sediment, mine workings, boreholes with analyses.

Geomagnetic activity

Geomagnetic activity (Kp)The planetary Kp index (0 to 9) measures the fluctuation of the Earth's magnetic field. From 5 it counts as a geomagnetic storm. The last 48 hours and a forecast for 24 hours are shown.
09

Kp index

1.3from 9

quiet field

Latest measurement (10 Nov 2026 13:00). The dot on the dial is the highest forecast for the next 24 hours.

Highest forecast Kp in the next 24 hours: 3.0 (quiet field).

Kp (0 to 9) measures the fluctuation of the Earth's magnetic field caused by the solar wind. From 5 it counts as a geomagnetic storm. Fish, especially salmonids and eels, sense the magnetic field. That their bites depend on Kp has not been shown, though: these are anglers' observations and hypotheses.

The value is the same for the whole of Slovakia. It enters the activity score only during a strong geomagnetic storm (a hypothesis, −1 to −2 points).

Earthquakes nearby

Earthquakes nearbyTremors recorded within 150 km of the water in the last 30 days (GFZ GEOFON catalog).
S

Earthquakes nearby

0tremors

no tremors

Within 150 km over the last 30 days (from magnitude 0.0).

According to angling lore, fish (especially catfish and eels) react restlessly to tremors beforehand or stop biting. This is not reliably proven, and with weak tremors it is coincidence. People mostly do not notice deeper tremors from the Carpathians (for example near Komárno and Dobrá Voda) at all.

The GEOFON catalog is global; weak tremors near Slovakia may not all be in it. It is not counted in the activity score.

Data: © ŠGÚDŠ (geological, geophysical and hydrogeological maps), NOAA SWPC (Kp index), GFZ GEOFON (earthquakes). A link between the geomagnetic field, tremors or radon and fish bites has not been reliably proven, so they are not counted in the activity score. The method is described in Methodology.

From space: what the Copernicus satellites show

Sentinel-2 (optical) and Sentinel-1 (radar), updated roughly every 6 days

Satellite data for this fishing district is being prepared. It is usually ready within a few minutes; refresh the page later.

Historical images

Changes in the surroundings and nature from 2017 to 2023: how the banks, vegetation and landscape around the water change. The images switch automatically; you can also browse them by hand.

Aerial image of fishing district Žitava č. 4 from 2017
2017imaged 24 Aug 2017
Aerial image of fishing district Žitava č. 4 from 2020
2020imaged 2 Aug 2020
Aerial image of fishing district Žitava č. 4 from 2023
2023imaged 1 Jun 2023

Orthophoto mosaic of Slovakia © GKÚ Bratislava, NLC Zvolen. The year and day of imaging depend on the location, so individual years may differ in season and weather.