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High Resolution Aerial Monitoring Network
High Resolution Aerial Monitoring Network

Evaluation guide

Using QGIS for land-cover analyses

Excerpt from the university lecture note Visual Interpretation of Orthophotos by Dr Gábor Bakó and Dr Krisztina Demény

The manual mapping operations of land-cover analysis are described in the Visual Interpretation lecture note and in numerous publications on vegetation mapping and evaluation. This short guide provides quick help only for carrying out the most basic operations and functions as a checklist for the most common problems. It was created to give rapid guidance to specialists who have not previously worked with GIS software and do not have time to learn its operation in detail.

The only supported purpose of this description is to establish manual patch mapping with complete area coverage, without gaps or overlaps.

1. Downloading QGIS:

In the Download menu, click the latest long-term release, which is the most stable version. If the operating system is 64-bit, choose that version. In Windows, this can be checked by right-clicking the “This PC” icon in File Explorer and selecting “Properties”. If Windows is 32-bit, download the 32-bit version. During installation, accept the default settings.

2. First launch and settings

On first launch it may indicate that a new version is available, but do not update, because that is a beta version and is not stable.

First steps:

In the lower-right corner, change the projection from EPSG:4326 to the HD72/EOV EPSG:23700 coordinate reference system. This can be done by clicking the lower-right corner and using the pop-up window. If the projection is not offered, search for it in the filter.

If the HD72 EOV option is not offered, it can be found using the filter.

In the top menu, open Settings / Options. On the General tab, select the interface language you want to use; this guide refers to the English menu names. On the CRS tab, set the default coordinate reference system for new projects to EPSG:23700 - HD72/EOV*. Click OK and restart QGIS so the settings are retained. *Note: in EPSG:23700 - HD72/EOV, HD72 is the base datum and EOV is Hungary's Unified National Projection, introduced in 1975. EPSG:23700 is the identifier of this system in the international EPSG database.

3. First workflow

Create a folder for the work. Inside it, create a subfolder whose name consists of the topic name and the date. Save a project file here by clicking the floppy-disk icon in the top toolbar; its name should follow the pattern proj_topicname, for example Proj_Merzse.qgz.

3.1 Adding the raster layer

Add an orthophoto or another two-dimensional raster map layer by opening the Data Source Manager and selecting Raster. Choose the required file and make sure the correct coordinate reference system is selected. A raster layer can also be added from the top menu. In the coordinate-system selector, choose HD72/EOV, or set and verify it later on the Source tab of the layer properties.

3.2 Creating a new vector layer:

Top Layer menu / Create Layer / New Shapefile Layer

Use the following settings in the window: File encoding: UTF-8. Geometry type: Polygon. If a point map is required, for example to mark standing deadwood trunks or torsos, select point geometry; for linear features, select line geometry. For complete land-cover mapping without overlaps or gaps, however, the polygon type is the appropriate choice. The projection should be EPSG:23700 - HD72 / EOV, which should already appear because of the earlier settings. For the file name, browse to the working folder and save the Shape file containing the map layer next to the project file. This file type consists of several component files, which must remain in the same folder: Shp, Shx, Dbf, Cpg, Prj, and Qpj. When sending the completed map to someone, all of these files must be sent together.

3.3 Loading a vector map

To load an existing layer, open the Data Source Manager. Select Raster for an orthophoto or another raster map, or Vector for a vector layer, and browse to the required file. Click Add, then Close. If QGIS asks for the projection, choose HD72/EOV (EPSG:23700). When opening a vector file, make sure the encoding is UTF-8. If System was left selected and strange characters appear in the attribute table, correct the encoding on the Source tab of the layer properties; the projection can be changed there as well. If the map does not appear, verify the projection, then right-click the layer and select Zoom to Layer. In the Layers panel, place raster layers such as the orthophoto below the vector layer to be edited.

3.4 Drawing

The vector layer should be above the raster layer in the layer list. To draw on the orthophoto, select the vector layer in the Layers panel, then click Toggle Editing. The first time, configure overlap avoidance. Right-click an empty part of the upper toolbar and make sure the Advanced Digitizing and Snapping toolbars are enabled. Enable snapping with the red horseshoe icon, open Advanced Settings, and choose the option for editing the advanced settings. Click the eye icon and tick the checkboxes before and after the name of the layer to be edited:

In the checkbox on the left, select which layer the setting applies to. The checkbox on the right must also be enabled so that polygons cannot be drawn on top of one another.

Click the overlap icon and select Avoid Overlap on Active Layer. This command is available from QGIS 3.16 onward and helps prevent accidental overlaps. After clicking Add Polygon Feature, zoom in far enough to trace object boundaries accurately. Place vertices with the left mouse button and close the shape with the right mouse button. Set the layer transparency on the Symbology tab, using a colour that remains visible against the imagery. Start a neighbouring polygon inside the existing one, trace its boundary, and finish inside the existing polygon so QGIS removes the overlap automatically. Take care not to create multipart patches, narrow slivers, or omitted triangles. Use Ctrl+Z to undo. Selected patches can be deleted with Del, and an immediate deletion can also be undone with Ctrl+Z.

Do not snap the points to the points of the existing patch, because a point may be missed and a gap or sliver may be created. Also avoid creating multipart polygons by letting the boundary of an older polygon split the new patch into two parts.

3.5 Splitting a polygon and adding a ring

Splitting a polygon: when cutting features, make sure to select the scissors icon with the grey-green polygon symbol. Feature cutting will not be performed if another polygon is selected, even outside the zoomed image area, or if there is a geometry error in the polygons affected by the cut. A cutting line drawn across several polygons will split several polygons, and it may sometimes temporarily split a patch that should not be divided. Make sure to merge such parts again immediately so they do not remain segmented. Adding a ring: use the Add Ring icon when a smaller polygon of another type or code must be created inside a larger area. This icon cuts out the area; after that, add the inner polygon again with Add Polygon Feature and save it with the new name.

3.6 Merging features

When merging two polygons, make sure the data of the resulting larger polygon come from the polygon whose attributes are valid for the entire combined area:

Select the row whose data should appear in the new merged patch, then click the “Attributes from selected feature” icon to copy its data into the “Merge” row, which contains the attributes of the new patch. The cells in the Merge row can also be edited manually.

3.7 Saving

It is very important that saving consists of two parts. The drawn map is saved by deactivating the pencil icon. If this is not done, all geometric changes and attribute-table edits will be lost, because the work is only stored in memory. After that, save the project file, which preserves the zoom level, the current view, colouring, transparency, projection, and special editing settings. This means the projection and overlap-free editing settings described above do not have to be configured repeatedly.

3.8 Creating an attribute table

Open the attribute table with the Open Attribute Table button. If polygons are selected on the map, set the filter in the lower-left corner to Show Selected Features; only the corresponding rows will be displayed. Restore the full list with All Features or by reopening the table. Enable editing with the pencil icon. To create a column, click New Field, enter its name, choose Text (String) and a length of 200. A mistaken column can be removed with Delete Field. Selecting a row highlights the corresponding patch in yellow; use Zoom Map to Selected Rows if it is outside the current view. Clearing a selection and deleting selected features are separate commands, so do not confuse them. It is useful to place the map and table side by side. To copy the attribute table to Excel, select all rows and columns, choose Copy, and paste the data into a new workbook.

4. Numbering the patches

Open the Field Calculator in the attribute table. If such a field does not yet exist, create a new field named “ID” or “Azonosito”. The field type should be Integer, and the output field length should be 10. In the middle, choose Variables / row_number. Double-clicking it fills the left-hand expression window. After confirming, the rows are numbered in a new ID column. If an ID column already exists, select Update Existing Field at the start of the operation. After selecting the correct column name, choose the same command. The purpose of numbering is to make it possible to enter field-collected information into the correct row at any time using a unique identifier. Because numbers are formed during editing and patches may be deleted, split, or merged, it is best to assign the identifier at the end of the lab work, after geometric editing. If the file has been split, or the table is edited separately in Excel, do not renumber the identifier column, otherwise the data cannot be joined again.

5. Area calculation

Area can only be calculated in a metric projection, generally a projected coordinate system. Coordinate systems that operate with angles are not suitable for direct area calculation. In the EOV projection system, therefore, patch areas can be calculated. Open the attribute table for editing, then click the Field Calculator icon. Name the field, for example, Terület. Set Field type to Decimal number (real), with an output field length of 20 and a precision of 2. In the middle, double-click Geometry / $area so the command is inserted into the expression window on the left. After confirming, a new column is created with the area of each patch calculated in m². If polygons are split or merged, the area values become incorrect, so this column must be recalculated with the Field Calculator using Update Existing Field and selecting the column name.

6. Copying the contents of a column under a new column name

If a column name was entered incorrectly earlier, it can be corrected in the layer properties on the Fields tab, but its content can also be copied into a new column. In the Field Calculator, enter the correct column name, field type, and field length, then click Fields and Values in the middle. Expand it with a double click, then double-click the name of the column whose contents should be copied. The new column is created on the right, and the old one can be removed with the Delete Field icon.

7. Correcting column names

Open layer properties from the layer list by double-clicking. Click Source Fields, or in earlier versions the Fields tab. Here, too, the field properties can only be edited after activating the small yellow pencil icon. Double-click a column name to rename it.

8. Drawing regular geometry

By clicking the upper grey toolbar, the Shape Digitizing toolbar can be enabled. It allows regular circles, squares, rectangles, and ellipses to be created. A circle is defined by one point on the circumference and the opposite point.

9. Searching for geometry errors

Clicking the Processing Toolbox icon opens the panel on the right, where the Check Validity command can be searched for. Double-clicking it opens a window in which the layer to be examined must be selected. After running the tool, three new overlays are created: one point layer shows the locations of error points (Error output), one polygon layer shows the valid polygons (Valid output), and the third shows the damaged patches (Invalid output). It is worth switching off the other layers to find these errors, then correcting them in the original layer. Be careful not to delete the edited file instead of the three temporary layers. After opening the Processing Toolbox (Ctrl+Alt+T), type Check Validity into the search field at the top. Double-click the function, select the vector layer to be examined in the window that opens, then click Run at the bottom. Three new overlays are then created in the layer list on the left: the Invalid output patch map represents the faulty polygons, the Valid output represents the problem-free polygons, and the Error output layer marks the error points. Correct the errors in the original overlay. After correcting the errors, it is advisable to delete the three error-analysis layers by right-clicking them and choosing Remove Layer, then run the error check again.

10. Geometry error / several isolated geometries belong to one attribute row

If several isolated geometries belong to a single attribute row, install the Multipart Split plugin from the top Plugins / Manage and Install Plugins menu. Select the multipart patch, then click the new Split featuretypes icon. A light-blue bar at the top shows how many parts the patch has been split into. This way, the distant sub-patches also receive separate rows in the attribute table. They can be edited independently, although their cell contents may also remain identical.

11. Moving an incorrect vertex

Activating the hammer icon, the vertex tool, allows points to be moved and polygons to be corrected. To insert a new point into a boundary line, place the cursor over the middle of the segment. The newly appearing potential vertex can then be moved. For touching patches, make sure the given point is created for both patches; otherwise a narrow triangular gap will appear in the fabric of the complete area-coverage map. If the boundary line is not grabbed in the middle, the entire segment is moved, which leads to errors. This can be fixed with Undo (Ctrl+Z). When correcting one polygon, take great care to correct the neighbouring polygon as well. In the image, a point of the left polygon has been moved to the right, causing it to overlap the polygon on the right; therefore the matching point of the other polygon must also be snapped to the modified point:

12. Colouring the map

Double-click the layer and, on the Symbology tab, set the “No symbols” row to Categorized. In the Symbol field, specify which attribute column should be used for colouring. To discard a previous colouring rule set, click Delete All at the bottom, then use Classify to reload the colouring categories; this also assigns random colours to the categories. By clicking the coloured squares, the colours can be changed freely, either by mixing colours or by entering a hex code for standard colours. Creating a legend: in the same Layer Properties / Symbology panel, not only colours can be set, but legend labels can also be added. Double-click the rows to enter the name belonging to each ID. Saving and loading happen together with the colour scale.

12.1 Saving and loading colouring

The colour scheme can be saved by opening the Style button at the bottom and clicking Save Style. A predefined, previously saved colour scheme can be loaded in the same place with Load Style.

13. Important keyboard shortcuts

Undo: while drawing a polygon, use Backspace. Otherwise use Ctrl+Z. Changes are saved only when the Toggle Editing icon is deactivated. The floppy-disk icon saves the project file, including zoom level, view, colouring, and settings; it does not save the edited map layer itself.

14. Intersecting layers

14.1. Intersecting layers: this may be needed, for example, when imagery along a boundary line is important for an area. This is where the basic command for intersecting two shp files can be found. Clicking it opens the following panel. It is important to set the input and overlay shp layers correctly: input is the layer to be intersected, while the overlay is the layer used for the intersection. After clicking Run, a new shp layer is created, automatically named Metszés. The Metszés.shp layer is a temporary working layer, so if it will be needed later, it must be saved by right-clicking the layer name, then Export / Save Features As, using a clearly identifiable file name.

15. Errors to avoid

Small spikes remain in the overlay if patches are closed incorrectly or if editing changes are not handled carefully. These can later be found after running the multipart tool by clicking the header of the area column in the attribute table and filtering for patches with the smallest areas. The Zoom Map to Selected Rows button can help with this. Self-intersecting polygons must not occur, and similar patch meetings should also be avoided. In the example, the shadows marked in red also influenced the drawing, although they are not relevant from a land-cover perspective. If neighbouring patches differ in any data content, it is worth separating them. For example, if the upper patch is fragmented by grassland patches while its lower half is bare, the difference appearing in the plant species list justifies separation. If, however, there is no difference in their attribute tables, the patches should be merged. Overlapping patches are not permitted. If a distinct patch is defined by a certain characteristic, the area under that patch must be separated from the underlying land-cover patches, and the different property must be entered in the attribute tables of the newly created patches. Some task parts do not need to be performed one by one for each patch. A good example is assigning naturalness level: when filling in the naturalness column of the database, this is typically not done patch by patch. Because the database is unified across all monitoring areas, so that all HRAMN areas can be compared statistically, classification decisions are made according to unified principles. It is useful to open the naturalness guide on the monitoring network website, which follows the recommendations of the staff of the Centre for Ecological Research. Then select the patches where the species composition, structure, pollution level, and the guide on the website allow the given naturalness level. After carefully and precisely selecting the patches corresponding to the given value, open the attribute table. If there are many patches, the selection can be partial, because the next step can be performed several times in succession while continuing to assign the given value in different parts of the map.

Excerpt

Bakó Gábor, Demény Krisztina 2020: Visual Interpretation of Orthophotos, Óbuda University, lecture note


Download sample overlay and guide

Download vector overlay

Shape-format overlay file (shp, shx, prj, dbf, cpg) and documentation in a ZIP archive. Size: 340 KB.

Download (.zip)

Overlay creation guide

PDF guide prepared for QGIS 2.4.6 for creating and using overlays.

Open (PDF)

Database structure

Attribute type Description
LC (Land cover) The land-cover element represented by the patch
Dominant species The dominant plant species of the upper canopy layer or grassland
Associated species

Other woody and herbaceous plant species and fungal species observed in the patch. The aim is to record the 10 species with characteristic cover, as well as protected and invasive species.

The methodology for identifying associated species is based on a dual weighting system:

  1. Species with higher cover usually have greater ecological contribution, and this is reflected in most ecosystem services. This is therefore the primary data-storage criterion.
  2. Which special species are found in the given patch:
  • protected species
  • species indicating environmental contamination or pressure (invasive species with environment-transforming functions)
  • species not typical of the given climate area (noteworthy observations).
Habitat Habitat classification of the given patch (ÁNÉR 2011)
Potential vegetation Vegetation that can be expected in the given area without anthropogenic influence
Naturalness Evaluation of the patch naturalness, from 0 to 5
Soil type Genetic soil type
Estimated soil depth Average depth of the productive soil layer in the patch, with dm precision
Soil texture class Debris; coarse sand; sand; sandy loam; loam; clay loam; clay; clayey sand; sandy clay; heavy clay; muck and peat classifications
Land use Functionality of the surface
Disturbance Effects observed in the patch, and factors causing or threatening degradation
Area Actual size of the patch (m2) (calculated automatically)
Anomalies Unusual phenomena observed in the patch that should be mentioned, such as disturbance or factors causing or threatening degradation
Comment Any relevant property of the patch can be described here; for example, the meaning of deadwood is also indicated here
Originator List of contributors involved in entering the patch data
Identifier Patch identifier number (automatic)

Land-cover categories of the database

LC (Land Cover) code and short name Short description of the category Unified symbol-system code
1 Canopy cover of woody vegetation Canopies of open-grown trees and the upper canopy outline of continuous tree groups #B6F9EA
2 Gaps in forest canopy cover Areas without canopy cover appearing between forest trees #F0EDC1
21 Gaps interpreted down to the understorey #F0EDC1
22 Opening of the upper canopy layer Gaps with a closed intermediate canopy layer #F0EDC1
23 Gaps covered with deadwood Gaps densely covered with branches, deadwood, or brushwood piles. #F0EDC1
3 Artificial objects Built objects, buildings, fences, structures, signs, and other artificial facilities #D6A4A9
4 Open water surfaces without cover Water surface not covered by vegetation or an artificial object #B3D6F9
41 Mires Wet areas where the soil consists of peat, formed from peat moss and other humified or peat-forming plant material. Areas that are permanently wet and theoretically never dry out. #EAF1DD
42 Inland marshes Freshwater marshes #8DB3E2
422 Marsh surface with submerged vegetation Marsh in which submerged vegetation can be observed #8DB3E2
43 Standing waters Lakes and reservoirs #B8CCE4
432 Standing-water surface with submerged vegetation Open water surface in which submerged vegetation can be observed #B8CCE4
433 Floating vegetation patch Floating fen, floating vegetation patch, floating Typha island #B8CCE4
44 Running waters Water surfaces of brooks, streams, rivers, and large rivers #DBE5F1
442 Running-water surface with submerged vegetation Open water surface in which submerged vegetation can be observed #DBE5F1
45 Reedbeds Areas covered with reed #EBBE34
450 Water surface within reedbed Open water surface found within reed #EBBE34
451 Surface cleared during reed cutting Open water surface under which traces of reed cutting can be observed #EBBE34
453 Homogeneous reedbed Reed surface of approximately the same age #EBBE34
455 Thinning of reedbed Segmented, collapsing reedbed degraded for unknown reasons #EBBE34
5 Bare soil Dirt roads, soils with compacted top layer, tamped earth, without vegetation #CBBAB6
6 Grasslands Natural grasslands and semi-natural meadows #D6E3BC
61 Wet and mesic grasslands Fen meadows, marsh meadows, mesic grasslands #D6E3BC
62 Tall-herb stands Tall-herb stands occurring in dry, saline, fen, marsh, and ruderal areas #D6E3BC
631 Closed dry grasslands Closed rocky grasslands, forest-steppe meadows, semi-dry clearings #D6E3BC
632 Open dry grasslands Open sand steppe grasslands, calcareous open rocky grasslands, open siliceous rocky grasslands, and scree slopes #D6E3BC
7 Karren and bare rocks Debris, rock walls, rocks, rock outcrops, block fields #F1F5F6
8 Artificial surfaces Concrete, asphalt-covered, and paved surfaces #374134
81 Waste cover Waste appearing on the surface from legal or illegal disposal #454339
9 Anthropogenic areas Densely built-up continuous areas covered by non-natural vegetation between buildings and solid surfaces, where more detailed analysis is not relevant for the given sample area #EBBEBD
91 Urban green areas Vegetation-covered areas belonging to the urban fabric, including urban parks and vegetation-covered cemeteries. #FDE9D9
92 Intensively used urban green areas Campsites, sports fields, leisure parks, golf courses, racecourses, etc. #FBD4B4
11 Raw material extraction Surface extraction of raw materials, such as sand pits and quarries, or extraction of other materials in open-pit mines #E36C0A
12 Depots, landfills, spoil heaps Landfills and spoil heaps of mining, industrial, and residential origin, primarily inert or municipal waste. #984806
13 Construction sites Areas under construction, areas affected by soil or bedrock extraction, earthworks, or surface transformation #CA6008
14 Agricultural areas Cereal production, field vegetable production, fodder production, row crops, and abandoned fallow areas not older than two years #FFC000
15 Vineyards Areas planted with grapevine #FFD525
16 Orchards Land parcels planted with fruit trees and shrubs: homogeneous crops or mixed fruit species, with stable grassy interspaces between fruit trees. Sweet chestnut and walnut plantations also belong here. #DDDB89
162 Abandoned, overgrown orchards Unmanaged, weedy, overgrown plantations #DDDB89
17 Pasture Highly productive areas densely covered with grass, dominated by species of the grass family (Gramineae). These areas are mainly used for grazing or mowing. Crop rotation is not used here, but overseeding, fertilisation, water regulation, and irrigation may be applied. #E7E4B9
18 Shrublands Shrub cover accounts for more than 20% of the combined surface covered by vegetation and soil. #8DE1C1
19 Other #7030A0

The colour codes shown in the table can be loaded from a QML file optimised for QGIS:

Download style QML

Naturalness categories of the database

0Surfaces covered with pavement or artificial cover

1Completely degraded / at the beginning of regeneration

Only weeds and uncharacteristic species dominate; no more natural vegetation type can be recognised, so this category is not used for semi-natural or near-natural vegetation.

 2Strongly degraded / weakly regenerated condition

The species set is uncharacteristic; disturbance-tolerant species, weeds, and invasive weeds dominate. The vegetation structure is disintegrated or poorly developed, with monodominant, even-aged patches and few coexisting species. The vegetation is often fragmented and the site is generally degraded; a more natural habitat can hardly be named. Even if the original habitat can be recognised, its condition is still very poor, and the cover of adventive species is usually high.

3Moderately degraded / moderately regenerated condition

Natural species dominate, but there are few character species; in other cases, several character species occur together with many disturbance-tolerant species, and weeds may also be common. The site is often moderately degraded and the vegetation structure is not good, being homogeneous, even-aged, or unnaturally patchy. In other cases the structure is better, but the species set is uncharacteristic. A more natural habitat can almost always be named, but its condition is not good.

4- “so-called good”, “near-natural” / “well” regenerated condition

The vegetation structure is good and/or natural species dominate, with many character species and usually few disturbance-tolerant species. Characteristics of naturalness levels 3 and 5 often combine: I. a patch that is poorer in species and may be weedier, but has a very good structure; II. a species-rich patch with poor structure; III. an old forest stand with missing species or poor structure; IV. one vegetation layer is in a substantially better condition than another. This is the broadest naturalness category.

5Natural condition

A sanctuary-value area that is rich in specialist, associated, and site-indicator species compared with the vegetation type, has a good structure, and is among the best 10-50-100 stands of the given habitat nationally or regionally. Weeds and invasive species are absent or almost absent, and the site is in a natural condition (after Takács and Molnár 2007).


References:


Bölöni J., Molnár Zs., Horváth F. & Illyés E. (2008) Naturalness-based habitat quality of the Hungarian (semi-)natural habitats. Acta Botanica Hungarica 50(Suppl.), pp. 149-159.


Bölöni J., Molnár Zs., Kun A. (eds.) (2011): Magyarország élőhelyei. A hazai vegetációtípusok leírása és határozója. ÁNÉR 2011. MTA ÖBKI, Vácrátót, pp. 441.


Takács Gábor és Molnár Zsolt (Szerk.) 2007: Nemzeti biodiverzitas-monitorozó rendszer. XI. Élőhely-térképezés, Második átdolgozott kiadás, Sarród, Vácrátót pp. 23-24.

Applied habitat categories (Á-NÉR)

Hínárnövényzet - Euhydrophyte vegetation

A24 – Lápi hínár - Euhydrophyte vegetation of oligotrophic lakes and ponds

A5 – Szikes tavak hínárnövényzete - Athalassal saline euhydrophyte communities

Aa – Források, gyors folyású patakok hínárnövényzete - Euhydrophyte vegetation of springs and streams

Ab – Folyók, áramló vizű csatornák hínárnövényzete - Euhydrophyte vegetation of rivers

Ac – Álló- és lassan áramló vizek hínárnövényzete - Euhydrophyte vegetation of naturally eutrophic and mesotrophic still waters


Nádasok és mocsarak - Marshes

B1a – Nem tőzegképző nádasok, gyékényesek és tavikákások - Eu- and mesotrophic reed and Typha beds

B1b – Úszólápok, tőzeges nádasok és télisásosok - Floating fens, oligotrophic reed and Typha beds of fens

B2 – Harmatkásás, békabuzogányos, pántlikafüves mocsári-vízparti növényzet - Glyceria, Sparganium and Schoenoplectus beds

B3 – Vízparti virágkákás, csetkákás, vízi hídőrös, mételykórós mocsarak - Water-fringing helophyte beds with Butomus, Eleocharis or Alisma

B4 – Lápi zsombékosok, zsombék-semlyék komplexek - Tussock sedge communities

B5 – Nem zsombékoló magassásrétek - Non-tussock tall-sedge beds

B6 – Zsiókás, kötő kákás és nádas szikes vizű mocsarak - Salt marshes

BA – Fragmentális mocsári- és/vagy hínárnövényzet mozaikok álló és folyóvizek partjánál - Fine scale mosaic or zonation of marsh communities


Forrásgyepek és tőzegmohás lápok - Springs, transition mires and raised bogs

C1 – Forrásgyepek - Springs

C23 – Tőzegmohás átmeneti lápok és tőzegmohalápok - Transition mires and raised bogs


Nedves gyepek és magaskórósok - Rich fens, wet grasslands and tall-herb vegetation

D1 – Meszes láprétek, rétlápok (Caricion davallianae) - Rich fens

D2 – Kékperjés rétek - Molinia meadows

D34 – Mocsárrétek - Mesotrophic wet meadows

D5 – Patakparti és lápi magaskórósok - Tall-herb vegetation of stream banks and fens

D6 – Ártéri és mocsári magaskórósok, árnyas-nyirkos szegélynövényzet - Tall-herb vegetation of floodplains, marshes and mesic shadowed forest fringes


Domb- és hegyvidéki üde gyepek - Mesic hay meadows, pastures and dry heaths

E1 – Franciaperjés rétek - Arrhenatherum hay meadows

E2 – Veres csenkeszes rétek - Festuca rubra hay meadows and pastures

E34 – Hegy-dombvidéki sovány gyepek és szőrfűgyepek - Nardus swards and other acidofrequent grasslands on shallow soils

E5 – Csarabosok - Dry Calluna heaths


Szikesek - Halophytic habitats

F1a – Ürmöspuszták - Artemisia salt steppes

F1b – Cickórós puszták - Achillea steppes on meadow solonetz

F2 – Szikes rétek - Salt meadows

F3 – Kocsordos-őszirózsás sziki magaskórósok, rétsztyepek - Tall-herb salt meadows and meadow-steppes

F4 – Üde mézpázsitos szikfokok - Dense and tall Puccinellia swards

F5 – Padkás szikesek, szikes tavak iszap- és vakszik növényzete - Annual salt pioneer swards of steppes and lakes


Nyílt szárazgyepek - Open dry grasslands

G1 – Nyílt homokpusztagyepek - Open sand steppes

G2 – Mészkedvelő nyílt sziklagyepek - Calcareous open rocky grasslands

G3 – Nyílt szilikátsziklagyepek és törmeléklejtők - Siliceous open rocky grasslands


Zárt szárazgyepek - Dry and semi-dry closed grasslands

H1 – Zárt sziklagyepek - Closed rocky grasslands

H2 – Felnyíló, mészkedvelő lejtő- és törmelékgyepek - Calcareous rocky steppes

H3a – Köves talajú lejtősztyepek - Slope steppes on stony soils

H4 – Erdőssztyeprétek, félszáraz irtásrétek, száraz magaskórósok - Semi-dry grasslands, forest-steppe meadows

H5a – Löszgyepek, kötött talajú sztyeprétek - Closed steppes on loess

H5b – Homoki sztyeprétek - Closed sand steppes


Nem ruderális pionír növényzet - Non-ruderal pioneer habitats

I1 – Nedves felszínek természetes pionír növényzete - Natural pioneer vegetation of wet substrates

I2 – Löszfalak és szakadópartok növényzete - Semi-desert vegetation on loess cliffs

I3a – Kőfalak pionír növényzete (csak definíció) - Pioneer vegetation of rock walls

I4 – Árnyéktűrő nyílt sziklanövényzet - Open vegetation of shaded cliffs and screes


Cserjések és szegélyek - Scrub

J1a – Fűzlápok - Willow carrs

J3 – Folyómenti bokorfüzesek - Riverine willow scrub

M6 – Sztyepcserjések - Continental deciduous steppe thickets

M7 – Sziklai cserjések - Deciduous rock thickets

M8 – Száraz-félszáraz erdő- és cserjés szegélyek - Thermophilous forest fringe vegetation

P2a – Üde és nedves cserjések - Wet and mesic pioneer scrub

P2b – Galagonyás-kökényes-borókás száraz cserjések - Dry and semi-dry pioneer scrub

P2c – Idegenhonos cserje vagy japánkeserűfű fajok uralta állományok (csak definíció) - Stands of non-native shrubs or Reynoutria species


Láp- és ligeterdők - Riverine and swamp woodlands

J1b – Nyírlápok, nyíres tőzegmohalápok - Birch mire forests

J2 – Láp- és mocsárerdők - Swamp woodlands

J4 – Fűz-nyár ártéri erdők - Riverine willow-poplar woodlands

J5 – Égerligetek - Riverine ash-alder woodlands

J6 – Keményfás ártéri erdők - Riverine oak-elm-ash woodlands


Üde lomboserdők - Mesic deciduous woodlands

K1a – Gyertyános-kocsányos tölgyesek - Lowland oak-hornbeam woodlands

K2 – Gyertyános-kocsánytalan tölgyesek - Sessile oak-hornbeam woodlands

K5 – Bükkösök - Beech woodlands

K7a – Mészkerülő bükkösök - Acidofrequent beech woodlands

K7b – Mészkerülő gyertyános-tölgyesek - Acidofrequent oak-hornbeam woodlands


Fényben gazdag tölgyesek és erdő-gyep mozaikok - Dry deciduous woodlands

L1 – Mész- és melegkedvelő tölgyesek - Closed thermophilous Quercus pubescens woodlands

L2a – Cseres-kocsánytalan tölgyesek - Pannonian-Balcanic Quercus cerris-Quercus petraea woodlands

L2b – Cseres-kocsányos tölgyesek - Quercus cerris-Quercus robur woodlands

L2x – Hegylábi zárt erdőssztyep tölgyesek - Closed mixed steppic oak woodlands on loess

L4a – Zárt mészkerülő tölgyesek - Closed acidofrequent oak forests

L4b – Nyílt mészkerülő tölgyesek - Open acidofrequent oak forests

L5 – Alföldi zárt kocsányos tölgyesek - Closed lowland steppic oak woodlands

M1 – Molyhos tölgyes bokorerdők - Quercus pubescens scrub

M2 – Nyílt lösztölgyesek - Open loess steppe oak woodlands with openings

M3 – Nyílt sziki tölgyesek - Open salt steppic oak forests

M4 – Nyílt homoki tölgyesek - Open steppic oak forests on sand

M5 – Homoki borókás-nyárasok - Poplar-juniper sand dune forests and thickets


Sziklás erdők - Rocky forests

LY1 – Szurdokerdők - Forests of ravines

LY2 – Törmeléklejtő-erdők - Mixed forests of slopes and screes

LY3 – Bükkös sziklaerdők - Limestone beech forests

LY4 – Tölgyes jellegű sziklaerdők és tetőerdők - Mixed relic oak forests on rocky soils


Fenyvesek - Coniferous forests

N13 – Mészkerülő lombelegyes fenyvesek - Acidofrequent mixed coniferous forests

N2 – Mészkedvelő erdeifenyvesek - Calcareous pine forests


Egyéb fátlan élőhelyek - Other treeless vegetation

OA – Jellegtelen fátlan vizes élőhelyek - Uncharacteristic wetlands

OB – Jellegtelen üde gyepek - Uncharacteristic mesic grasslands

OC – Jellegtelen száraz-félszáraz gyepek - Uncharacteristic dry and semi-dry grasslands

OD – Lágyszárú évelő özönfajok állományai (csak definíció) - Stands of invasive forbs

OF – Magaskórós ruderális gyomnövényzet (csak definíció) - Ruderal tall-herb vegetation

OG – Taposott gyomnövényzet és ruderális iszapnövényzet (csak definíció) - Trampled and ruderal vegetation


Egyéb erdők és fás élőhelyek - Other tree-dominated habitats

P1 – Őshonos fafajú fiatalosok (csak definíció) - Saplings of native tree species

P3 – Újonnan létrehozott, őshonos vagy idegenhonos fafajú fiatal erdősítés (csak definíció) - New afforestations

P45 – Fáslegelők, fáskaszálók, legelőerdők, gesztenyeligetek - Wood-pastures and Castanea sativa woods

P6 – Parkok, kastélyparkok, arborétumok és temetők az egykori vegetáció maradványaival vagy regenerálódásával (csak definíció) - Parks, botanical gardens, old churchyards

P7 – Hagyományos fajtájú, extenzíven művelt gyümölcsösök - Extensive orchards with ancient cultivars

P8 – Vágásterületek (csak definíció) - Cutting areas

RA – Őshonos fajú facsoportok, fasorok, erdősávok - Scattered native trees or narrow tree lines

RB – Őshonos fafajú puhafás jellegtelen vagy pionír erdők - Uncharacteristic or pioneer softwood forests

RC – Őshonos fafajú keményfás jellegtelen erdők - Uncharacteristic hardwood forests and plantations

RDa – Őshonos lombos fafajokkal elegyes fenyves származékerdők - Coniferous forests and plantations mixed with native deciduous tree species

RDb – Őshonos lombos fafajokkal elegyes idegenhonos lombos és vegyes erdők - Non-native deciduous forests and plantations mixed with native tree species


Idegenhonos fafajok uralta erdők és faültetvények - Forests and plantations dominated by non-native tree species

S1 – Ültetett akácosok (csak definíció) - Robinia pseudoacacia plantations

S2 – Nemesnyárasok (csak definíció) - Populus × euramericana plantations

S3 – Egyéb tájidegen lombos erdők (csak definíció) - Plantations of other non-native deciduous tree species

S4 – Ültetett erdei- és feketefenyvesek (csak definíció) - Scots and black pine plantations

S5 – Egyéb ültetett tájidegen fenyvesek (csak definíció) - Plantations of other conifers

S6 – Nem őshonos fafajok spontán állományai (csak definíció) - Spontaneous stands of non-native tree species

S7 – Nem őshonos fajú facsoportok, erdősávok és fasorok (csak definíció) - Scattered trees or narrow tree lines of non-native tree species


Agrár élőhelyek - Agricultural habitats

T1 – Egyéves, intenzív szántóföldi kultúrák (csak definíció) - Annual intensive arable fields

T10 – Fiatal parlag és ugar (csak definíció) - New abandonments of arable lands

T11 – Csemetekertek, faiskolák, kosárkötő fűz ültetvények (csak definíció) - Nurseries, Salix viminalis plantations

T12 – Évelő energianövények ültetvényei (csak definíció) - Plantations of energy plants

T2 – Évelő, intenzív szántóföldi kultúrák (csak definíció) - Perennial intensive arable fields

T3 – Zöldség- és dísznövénykultúrák, melegházak (csak definíció) - Vegetable and flower plantations, greenhouses

T4 – Rizskultúrák (csak definíció) - Rice fields

T5 – Vetett gyepek, füves sportpályák (csak definíció) - Sown or fertilised grasslands and sports grounds

T6 – Extenzív szántók (csak definíció) - Extensive arable fields

T7 – Intenzív szőlők, gyümölcsösök és bogyós ültetvények (csak definíció) - Intensive vineyards and orchards

T8 – Extenzív szőlők és gyümölcsösök (csak definíció) - Extensive vineyards and orchards

T9 – Kiskertek (csak definíció) - Gardens


Egyéb élőhelyek - Other habitats

U1 – Belvárosok, beépített faluközpontok, lakótelepek (csak definíció) - Cities, areas with blocks of flats

U10 – Tanyák, családi gazdaságok (csak definíció) - Farms

U11 – Út- és vasúthálózat (csak definíció) - Roads and railroads

U2 – Kertvárosok, szabadidős létesítmények (csak definíció) - Suburbs and recreation areas

U3 – Falvak, falu jellegű külvárosok (csak definíció) - Villages

U4 – Telephelyek, roncsterületek és hulladéklerakók (csak definíció) - Yards, wastelands, dumping grounds

U5 – Meddőhányók, földdel már befedett hulladéklerakók (csak definíció) - Mine dumps, dumping grounds covered by soil

U6 – Nyitott bányafelületek (csak definíció) - Open mines

U7 – Homok-, agyag-, tőzeg- és kavicsbányák, digó- és kubikgödrök, mesterséges löszfalak (csak definíció) - Sand, gravel, clay and peat mines, loess walls


Vizek - Water bodies

A1 – Nagy folyók és tavak nyílt vízi növényzete (csak definíció) - Open-water vegetation of large rivers and lakes

A213 – Gyepes vizes élőhelyek, csatornák, kis tavak vegetációja (csak definíció) - Vegetation of grassland-related water bodies, canals and small ponds

R1 – Mesterséges felszíni vizek (csak definíció) - Artificial water bodies



Data source:

novenyzetiterkep.hu https://novenyzetiterkep.hu/eiu2011