Table 1
Soil type, location, ecosystem type, and vegetation characteristics of the study plots.
| Soil type | Location/characteristics | Ecosystem | Vegetation |
|---|---|---|---|
| Hanušovce nad Topľou Altitude 258 – 308 m a.s.l., slope 3 – 7° | Forest 49°00.339′N, 21°31.248′E | Carpinus betulus (90 %), Pinus sylvestris (5 %), sporadically Prunus avium, Fagus sylvatica, and Betula pendula. Understory vegetation dominated by grasses Carex pilosa, Festuca drymeja, and Poa memoralis and | |
| Soil with strong mottling of the soil profile due to redox processes | herbs Dentaria bulbifera and Fragaria vesca | ||
| Stagnosol | caused by stagnating surface water, The topsoil can also be completely bleached (albic horizon). A common name in many national classification systems for most Stagnosols is | Meadow 49°00.658′N, 21°30.058′E | Carex sp., Lolium perenne, Fragaria vesca, Trifolium pratense, Plantago sp. Leucanthemum sp. |
| pseudogley. | Agricultural field 49°00.727′N, 21°30.344′E | Zea mays monoculture | |
| Tŕnie Altitude 550 – 554 m a.s.l., slope 3 – 7° | Forest 48°36.712′N, 19°01.462′E | Carpinus betulus (75 %), Quercus robur (10 %), Tilia cordata (10 %), and sporadically Prunus avium Understory herbaceous vegetation dominated by Viola reichenbachiana, Geranium robertianum, | |
| Soil with a beginning of soil formation. The horizon differentiation is weak. This | Asarum europaeum, Luzula sylvatica, Galium odoratum, and Hedera helix. | ||
| Cambisol | is evident from weak, mostly brownish discolouration and/or structure formation in the soil profile. Cambisols are | Meadow 48°36.683′N, 19°01.494′E | Trifolium pratense, Agrimonia eupatoria, and grasses such as Carex sp., Poa sp., Dactylis glomerata, Trifolium pratense, Rumex acetosa |
| developed in medium and fine-textured materials derived from | |||
| a wide range of rocks, mostly in alluvial, colluvial and aeolian deposits. | Agricultural field N 48°36.660′N, E 19°01.503′E | Zea mays monoculture | |
| Močenok Altitude 135 – 180 m a.s.l., | Forest 48°12.960′N, | Fraxinus excelsior (80 %), Quercus petraea (20 %), and sporadically Robinia pseudoacacia. | |
| slope 0 – 3° Black-colored soil containing a high percentage of humus (4 % to 16 %) | 17°57.854′E | Understory vegetation dominated by grasses Poa nemoralis, Brachypodium sylvaticum, Melica uniflora, and Dactylis polygama | |
| Chernozem | and high percentages of phosphoric cids, phosphorus, and ammonia. Chernozem is very fertile and can produce high agricultural yields with its high moisture storage capacity. Chernozems are also a reference soil group of the World reference | Meadow 49°00.339′N, 21°30.344′E | Carex sp., Phleum pratense, Arrhenatherum elatius, Trifolium pratense, Vicia sp., Rumex acetosa, Achillea millefolium |
| base for soil resources | Agricultural field 49°00.339′N, 21°30.344′E | Zea mays monoculture | |

Fig. 1
RDA triplots of the relationships of abundance of nematode functional guilds, microbial parameters, and soil properties in the forest (A), agricultural field (B), and meadow (C) ecosystems and the Stagnosol (SS), Cambisol (CC), and Chernozem (CM) soil types.
Table 2
Effects of ecosystem type (E), type of soil (S), sampling date (D), and their interactions on basic soil physical and chemical characteristics.
| Ecosystem | Soil | Date | E × S | E × D | S × D | Ecosystem | Soil | Date | E × S × D | ||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| F | P | F | P | F | P | F | P | F | P | F | P | Meadow | Agricultural field | Forest | Stagnosol | Cambisol | Chernozem | May | July | Sept | F | P | |
| pH/H2O | 28.91 | < 0.01 | 598.43 | < 0.01 | 2.95 | ns | 80.12 | <0.01 | 2.63 | <0.05 | 2.05 | ns | 5.88±0.78 | 5.79±0.75 | 5.54±1.08 | 4.82±0.61 | 5.71±0.41 | 6.68±0.32 | 5.68±0.88 | 5.71±0.87 | 5.81 ±0.92 | 1.08 | ns |
| SM | 60.14 | < 0.01 | 0.99 | ns | 131.43 | < 0.01 | 2.72 | < 0.05 | 5.39 | < 0.01 | 33.88 | ns | 26.33±7.28 | 22.14±5.14 | 30.78±8.64 | 26.15±8.96 | 26.93±8.85 | 26.15±5.75 | 26.68±8.04 | 20.52±5.47 | 32.10±5.3 | 2.53 | <0.05 |
| N | 156.52 | < 0.01 | 122.56 | < 0.01 | 0.15 | ns | 11.22 | < 0.01 | 0.29 | ns | 2.60 | ns | 0.377±0.10 | 0.205±0.07 | 0.395±0.13 | 0.244±0.06 | 0.300±0.09 | 0.434±0.15 | 0.326±0.12 | 0.321±0.12 | 0.331±0.16 | 1.36 | ns |
| C | 275.46 | < 0.01 | 140.58 | < 0.01 | 0.08 | ns | 6.33 | < 0.01 | 0.41 | ns | 1.89 | ns | 3.588±1.05 | 1.955±0.85 | 4.395±1.28 | 2.429±0.84 | 3.127±1.321 | 4.382±1.48 | 3.298±1.38 | 3.271±1.40 | 3.369±1.64 | 1.87 | ns |
| S | 32.62 | < 0.01 | 51.84 | < 0.01 | 2.11 | ns | 10.39 | < 0.01 | 4.79 | < 0.01 | 3.75 | ns | 0.071±0.02 | 0.048±0.01 | 0.070±0.02 | 0.049±0.02 | 0.060±0.01 | 0.082±0.02 | 0.067±0.03 | 0.060±0.18 | 0.063±0.02 | 2.71 | <0.01 |
| C/N | 171.64 | < 0.01 | 7.51 | < 0.01 | 1.81 | ns | 49.09 | < 0.01 | 1.86 | ns | 1.21 | ns | 9.49±0.54 | 9.35±0.98 | 11.28±1.06 | 9.86±1.70 | 10.08±1.21 | 10.18±0.56 | 9.95±1.32 | 10.04±1.24 | 10.14±1.16 | 1.80 | ns |
[i] E: meadow, agriculture and forest; S: Stagnosol, Cambisol and Chernozem; D: May, July, and September
pH/H2O, acidity; SM, soil moisture content N, total nitrogen content C, organic carbon content S, total sulphur content; C/N, carbon to nitrogen ratio. The means ±SEs of nematode abundance for the three ecosystems, soil types, and sampling dates are shown.
Table 3
Effects of ecosystem type (E), type of soil (S), sampling date (D), and their interactions on nematode abundance, functional guilds and microbial communities.
| Ecosystem | Soil | Date | E × S | E x D | S :D x | Ecosystem | Soil | Date | E × S × D | ||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| F | P | F | P | F | P | F | P | F | P | F | P | Meadow | Agricultural field | Forest | Stagnosol | Cambisol | Chernozem | May | July | Sept | F | P | |
| Nabund | 2.36 | ns | 92.49 | < 0.01 | 15.04 | < 0.01 | 37.97 | < 0.01 | 5.57 | < 0.01 | 1.63 | ns | 479.8±119.8 | 540.1±322.5 | 451.8±169.5 | 351.6±150.1 | 435.8±104.9 | 671.3±260.3 | 549.2±276.3 | 418.1±165.9 | 504.1±201.8 | 1.59 | ns |
| Nspec | 5.69 | < 0.01 | 4.87 | <0.01 | 0.88 | ns | 12.45 | < 0.01 | 1.98 | ns | 2.98 | ns | 33.2±5.7 | 25.2±6.2 | 37.1±4.1 | 24.1±5.8 | 32.5±6.3 | 38.5±7.5 | 33.0±7.7 | 29.0±11 | 31.7±8.4 | 1.12 | ns |
| Ba1 | 6.19 | < 0.01 | 85.42 | <0.01 | 1.24 | ns | 21.63 | < 0.01 | 1.78 | ns | 1.76 | ns | 10.9±11.1 | 38.6±43.9 | 22.18±21.8 | 4.2±5.8 | 41.9±41.6 | 25.6±20.7 | 22.6±30.4 | 21.1±25.6 | 28.1±36.3 | 0.97 | ns |
| Ba2 | 5.49 | < 0.01 | 12.36 | <0.01 | 11.48 | < 0.01 | 35.72 | < 0.01 | 6.11 | < 0.01 | 2.44 | ns | 159.4±80.3 | 181.8±118.6 | 190.8±84.5 | 145.8±87.3 | 150.3±52.0 | 214.6±122.0 | 207.8±117.8 | 147.2±75.4 | 165.8±81.2 | 1.70 | ns |
| Ba3 | 39.96 | < 0.01 | 117.06 | <0.01 | 2.9 | ns | 29.93 | < 0.01 | 1.24 | ns | 3.98 | ns | 2.3±5.0 | 0.0±0.0 | 3.1±5.5 | 0.0±0.0 | 0.2±0.7 | 5.11±6.5 | 1.0±2.6 | 2.9±6.4 | 1.4±3.3 | 2.12 | ns |
| Ba4 | 5.82 | < 0.01 | 28.8 | <0.01 | 0.07 | ns | 1.9 | ns | 0.69 | ns | 0.77 | ns | 3.7±7.2 | 1.5±3.6 | 2.9±4.0 | 0.9±1.6 | 0.6±1.3 | 6.6±7.5 | 2.9±6.3 | 2.5±4.8 | 2.7±4.7 | 0.83 | ns |
| Ca3 | 15.89 | < 0.01 | 24.98 | <0.01 | 0.67 | ns | 7.47 | < 0.01 | 0.47 | ns | 0.27 | ns | 1.0±1.7 | 0.0±0.0 | 0.6±1.2 | 0.0 ±0.0 | 0.3±0.9 | 1.3±1.8 | 0.4±1.2 | 0.6±1.4 | 0.5±1.3 | 0.22 | ns |
| Ca4 | 45.67 | < 0.01 | 63.63 | <0.01 | 0.08 | ns | 31.3 | < 0.01 | 0.23 | ns | 0.14 | ns | 3.9±3.9 | 1.8±3.5 | 10.4±9.7 | 1.0±2.2 | 7.0±7.6 | 8.1±8.4 | 5.1±6.8 | 5.8±8.3 | 5.2±6.9 | 0.80 | ns |
| Ca5 | 11.63 | < 0.01 | 11.63 | <0.01 | 1.22 | ns | 11.63 | < 0.01 | 1.22 | ns | 1.22 | ns | 0.0±0.0 | 0.6±1.6 | 0.0±0.0 | 0.6±1.6 | 0.0±0.0 | 0.0±0.0 | 0.2±0.9 | 0.3±1.3 | 0.1 ±0.4 | 1.22 | ns |
| Fu2 | 7.03 | < 0.01 | 50.64 | <0.01 | 3.42 | < 0.05 | 30.43 | < 0.01 | 6.69 | < 0.01 | 1.42 | ns | 97.8±34.7 | 155.6±156.7 | 87.5±52.6 | 68.1±38.5 | 90.1±40.4 | 182.7±143.5 | 122.4±127.5 | 92.2±126.2 | 126.2±104.5 | 1.42 | ns |
| Fu3 | 4.06 | < 0.05 | 4.06 | <0.05 | 0.79 | ns | 7.88 | < 0.01 | 0.57 | ns | 0.57 | ns | 1.4±4.5 | 0.0±0.0 | 0.3±1.2 | 0.3±1.2 | 0.0±0.0 | 1.4±4.5 | 0.5±0.3 | 0.5±1.2 | 0.8±2.7 | 0.68 | ns |
| Fu4 | 29.26 | < 0.01 | 18.65 | < 0.01 | 0.18 | ns | 14.74 | < 0.01 | 1.20 | ns | 0.90 | ns | 3.7±4.9 | 0.0±0.0 | 5.3±9.3 | 1.9±4.4 | 0.9±2.2 | 6.2±9.2 | 3.6±8.3 | 2.8±5.4 | 2.5±5.3 | 0.89 | ns |
| Om4 | 4.24 | < 0.05 | 43.16 | < 0.01 | 2.41 | ns | 10.80 | < 0.01 | 0.62 | ns | 1.13 | ns | 31.2±29.8 | 21.7±19.0 | 41.0±37.0 | 16.0±16.8 | 35.8±22.2 | 52.1 ±35.1 | 41.5±37.2 | 33.2±25.2 | 29.3±24.0 | 0.55 | ns |
| Om5 | 5.32 | < 0.05 | 22.74 | < 0.01 | 0.94 | ns | 4.84 | < 0.01 | 0.65 | ns | 2.36 | ns | 19.8±7.4 | 8.7±12.1 | 15.4±13.2 | 8.2±9.1 | 8.6±5.3 | 20.1±13.7 | 12.8±10.3 | 12.5±14.2 | 11.7±9.1 | 1.87 | ns |
| Pp2 | 19.66 | < 0.01 | 1.02 | ns | 6.47 | < 0.01 | 9.28 | < 0.01 | 1.03 | ns | 2.55 | ns | 62.4±42.9 | 54.8±47.0 | 25.3±20.1 | 46.7±46.9 | 43.3±29.1 | 52.4±46.3 | 49.4±33.9 | 33.0±27.5 | 59.9±54.4 | 2.55 | ns |
| Pp3 | 27.71 | < 0.01 | 24.21 | < 0.01 | 0.11 | ns | 14.19 | < 0.01 | 0.75 | ns | 5.04 | < 0.01 | 74.9±43.3 | 57.8±39.2 | 28.1±24.5 | 36.6±36.2 | 49.2±30.5 | 74.7±46.3 | 58.4±46.8 | 49.1±34.6 | 52.9±41.5 | 2.38 | ns |
| Pp5 | 3.46 | < 0.05 | 3.78 | <0.05 | 0.59 | ns | 7.78 | < 0.01 | 0.37 | ns | 0.37 | ns | 0.27±0.95 | 0.0±0.0 | 0.5±1.3 | 0.3±0.9 | 0.0±0.0 | 0.5±1.3 | 0.4±1.2 | 0.2±0.8 | 0.2±0.8 | 0.48 | ns |
| Cmic | 175.55 | < 0.01 | 295.91 | <0.01 | 2.84 | ns | 5.02 | < 0.01 | 0.69 | ns | 2.64 | <0.05 | 335.2±118.3 | 207.9±91.5 | 400.1±145.5 | 183.0±65.9 | 325.9±119.4 | 434.4±109.2 | 316.0±129.1 | 300.4±143.4 | 326.8±157.8 | 19.0 | ns |
| Richn | 3.60 | < 0.05 | 50.90 | <0.01 | 11.28 | < 0.01 | 1.88 | ns | 0.68 | ns | 14.01 | < 0.01 | 26.2±2.39 | 25.5±1.86 | 26.5±2.93 | 24.2±2.3 | 26.8±1.96 | 27.2±1.9 | 25.8±1.8 | 26.9±1.9 | 25.5±3.2 | 3.19 | < 0.01 |
| Diver | 3.15 | <0.05 | 53.52 | <0.01 | 0.69 | ns | 1.96 | ns | 2.24 | ns | 4.69 | < 0.01 | 14.51±2.6 | 13.85±2.4 | 14.9±3.0 | 12.1 ±2.9 | 15.6±2.3 | 15.6±2.4 | 14.2±2.1 | 14.7±2.7 | 14.5±3.2 | 34.2 | < 0.01 |
| E: meadow, agriculture and forest; S: Stagnosol, Cambisol and Chernozem; D: May, July, and September | |||||||||||||||||||||||
[i] Ba1,2,3,4, bacterivores; Fu2,3,4, fungivores; Ca3,4,5, carnivores; Om4,5, omnivores; Pp2,3,5, plant parasites; Nabund, meannematode abundance/100 g dry soil, Nspec, mean nematode species number/100 g dry soil; Cmic, microbial biomass carbon content; Richn, richness of microbial functional groups; Diver, diversity of microbial functional groups. The means ±SEs of nematode abundance for the three ecosystems, soil types, and sampling dates are shown.
Table 4
Effects of ecosystem type (E), type of soil (S), sampling date (D), and their interactions on nematode trophic-web descriptors.
| Ecosystem | Soil | Date | E × S | E × D | S × D | Ecosystem | Soil | Date | E × S × D | ||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| F | P | F | P | F | P | F | P | F | P | F | P | Meadow | Agricultural field | Forest | Stagnosol | Cambisol | Chernozem | May | July | Sept | F | P | |
| MI | 18.86 | < 0.01 | 21.28 | <0.01 | 5.56 | < 0.01 | 44.11 | < 0.01 | 4.22 | < 0.01 | 2.04 | <0.05 | 2.32±0.19 | 2.21±0.23 | 2.37±0.23 | 2.25±0.20 | 2.24±0.23 | 2.41±0.23 | 2.33±0.25 | 2.32±0.24 | 2.24±0.19 | 1.83 | <0.05 |
| ΣMI | 11.34 | < 0.01 | 25.74 | < 0.01 | 3.89 | < 0.05 | 28.66 | < 0.01 | 2.27 | ns | 0.95 | ns | 2.38±0.17 | 2.28±0.16 | 2.39±0.21 | 2.28±0.15 | 2.30±0.15 | 2.45±0.20 | 2.35±0.22 | 2.38±0.18 | 2.31 ±0.16 | 1.46 | ns |
| PPI | 0.70 | ns | 16.05 | < 0.01 | 7.03 | < 0.01 | 8.30 | < 0.01 | 2.24 | ns | 6.25 | < 0.01 | 2.5±0.20 | 2.53±0.22 | 2.51±0.26 | 2.43±0.24 | 2.53±0.20 | 2.62±0.20 | 2.59±0.23 | 2.60±0.21 | 2.38±0.22 | 6.41 | < 0.01 |
| H' | 125.08 | < 0.01 | 87.76 | < 0.01 | 0.73 | ns | 22.99 | < 0.01 | 0.99 | ns | 2.50 | <0.05 | 2.91 ±0.22 | 2.60±0.15 | 3.02±0.29 | 2.64±0.18 | 2.88±0.25 | 3.01±0.30 | 2.82±0.26 | 2.85±0.28 | 2.86±0.33 | 2.67 | <0.05 |
| EI | 4.52 | < 0.05 | 9.05 | < 0.01 | 1.46 | ns | 14.80 | < 0.01 | 0.76 | ns | 2.32 | ns | 41.3±9.9 | 46.7±12.4 | 46.2±11.3 | 38.9±5.6 | 47.8±14.8 | 47.1±10.5 | 42.3±9.4 | 46.3±13.2 | 45.3±11.8 | 4.70 | < 0.01 |
| SI | 4.53 | < 0.05 | 61.88 | < 0.01 | 1.78 | ns | 25.55 | < 0.01 | 6.20 | < 0.01 | 3.60 | <0.01 | 44.3±18.4 | 41.0±13.3 | 49.2±18.4 | 30.7±12.1 | 50.5±10.8 | 53.2±18.2 | 44.5±19.4 | 47.1±16.5 | 42.9±15.7 | 2.06 | <0.05 |
| CI | 53.82 | < 0.01 | 61.48 | < 0.01 | 0.11 | ns | 182.05 | < 0.01 | 13.74 | <0.01 | 3.14 | <0.05 | 68.5±16.8 | 57.9±30.1 | 52.7±16.3 | 64.4±18.9 | 52.7±28.8 | 61.9±18.4 | 60.1±23.8 | 61.6±24.9 | 57.5±20.3 | 15.57 | <0.01 |
| NCR | 7.77 | < 0.01 | 34.25 | < 0.01 | 5.17 | < 0.01 | 42.19 | <0.01 | 6.01 | <0.01 | 1.88 | ns | 0.65±0.12 | 0.63±0.16 | 0.69±0.13 | 0.69±0.14 | 0.70±0.12 | 0.57±0.12 | 0.69±0.12 | 0.65±0.13 | 0.64±0.16 | 4.02 | < 0.01 |
| TD | 19.17 | < 0.01 | 15.09 | < 0.01 | 0.009 | ns | 16.81 | <0.01 | 1.75 | ns | 1.15 | ns | 12.2±2.4 | 10.5±4.2 | 14.7±2.1 | 10.5±3.2 | 13.2±1.9 | 13.7±2.4 | 12.3±0.8 | 12.5±0.7 | 12.9±0.7 | 1.34 | ns |
[i] E: meadow, agriculture and forest; S: Stagnosol, Cambisol and Chernozem; D: May, July, and September
MI, maturity index; ΣMI, sigma maturity index; PPI, plant parasitic index; H´, Shannon diversity index; EI, enrichment index; SI, structure index; CI, channel index; NCR, nematode channel ratio; TD, trophic diversity. The means ±SEs of the nematode-community descriptors for the three ecosystems, soil types, and sampling dates are shown
Table 5
Spearman´s rank correlation coefficients between nematode abundance, species number, functional guild, microbial parameters and soil properties.
| pH/H2O | SM | N | C | S | C/N | |
|---|---|---|---|---|---|---|
| Nabund | 0.35** | 0.68*** | 0.42*** | 0.29** | ns | ns |
| Nspec | 0.22* | ns | 0.31* | 0.37*** | ns | ns |
| Ba1 | 0.44** | ns | 0.25*** | 0.22* | 0.31*** | ns |
| Ba2 | ns | -0.23*** | ns | ns | ns | ns |
| Ba3 | 0.54*** | 0.26* | 0.44*** | 0.41*** | 0.42*** | 0.21* |
| Ba4 | 0.43*** | ns | 0.30*** | 0.29*** | 0.30*** | ns |
| Ca3 | 0.44*** | 0.46*** | 0.39*** | 0.40*** | 0.39*** | 0.33*** |
| Ca4 | 0.41*** | ns | 0.21* | 0.22* | 0.22** | 0.21** |
| Ca5 | ns | 0.41*** | 0.35* | ns | 0.36* | 0.26* |
| Fu2 | 0.55*** | ns | 0.35*** | 0.29** | 0.37*** | ns |
| Fu3 | ns | ns | ns | ns | ns | ns |
| Fu4 | 0.39*** | 0.37*** | 0.29*** | 0.26** | 0.27** | ns |
| Om4 | 0.42*** | ns | ns | ns | 0.33** | ns |
| Om5 | 0.38*** | ns | 0.21* | ns | 0.23** | ns |
| Pp2 | ns | ns | ns | ns | ns | -0.27*** |
| Pp3 | 0.47*** | 0.24*** | ns | ns | ns | ns |
| Pp5 | 0.39*** | 0.37*** | 0.28*** | 0.28*** | 0.29** | 0.38*** |
| Cmic | 0.70*** | 0.39*** | 0.90*** | 0.91*** | 0.83*** | 0.51*** |
| Richn | 0.46*** | ns | 0.47*** | 0.45*** | 0.53*** | ns |
| Diver | 0.47*** | ns | 0.40*** | 0.38*** | 0.50*** | ns |
Ba1,2,3,4, bacteriovores; Fu2,3,4, fungivores; Ca3,4,5, carnivores; Om4,5, omnivores; Pp2,3,5, plant parasites; Cmic, microbial biomass carbon content; Richn, richness of microbial functional groups; Diver, diversity of microbial functional groups; pH/H2O, acidity; SM, soil moisture content; N, total nitrogen content; C, organic carbon content; S, total sulphur content; C/N, carbon to nitrogen ratio
Table S1
Mean abundance of nematode species (100 g of dry soil) in the three ecosystems (forest (FOR), meadow (MEA), and agricultural field (AGR)) and types of soil (Stagnosol (SS), Cambisol (CS), and Chernozem (CM)) (n=45). Bold figures indicate dominance >2 but <5%, and bold and underlined figures indicate dominance >5%.
| Ecosystem | Soil | ||||||
|---|---|---|---|---|---|---|---|
| Taxon | TG/FG | FOR | MEA | AGR | SS | CS | CM |
| Mesorhabditis spp. juvs | Ba1 | 13.5 | 0.6 | 13.4 | 17.4 | 10.1 | |
| Panagrolaimus rigidus | Ba1 | 2.0 | 6.1 | 7.2 | 1.3 | 5.8 | 8.2 |
| Rhabditis spp. juvs | Ba1 | 6.7 | 4.3 | 18.1 | 2.9 | 18.7 | 7.4 |
| Acrobeles ciliatus | Ba2 | 20.3 | 2.8 | 0.4 | 23.4 | ||
| Acrobeloides buetschlii | Ba2 | 0.4 | 0.4 | ||||
| Acrobeloides nanus | Ba2 | 43.0 | 40.9 | 30.1 | 30.2 | 45.1 | 38.2 |
| Acrobelophis minimus | Ba2 | 0.6 | 0.6 | ||||
| Acrolobus emarginatus | Ba2 | 0.1 | 0.1 | ||||
| Anaplectus granulosus | Ba2 | 2.5 | 5.1 | 2.7 | 2.4 | 1.9 | 7.2 |
| Cervidellus cervus | Ba2 | 0.1 | 0.1 | ||||
| Cervidellus vexiliger | Ba2 | 5.8 | 2.7 | 0.6 | 8.4 | ||
| Cephalobus persegnis | Ba2 | 17.7 | 14.3 | 22.7 | 24.4 | 27.6 | 11.5 |
| Ereptonema arcticum | Ba2 | 1.9 | 1.9 | ||||
| Eucephalobus mucronatus | Ba2 | 2.9 | 1.3 | 1.6 | |||
| Eucephalobus oxyuroides | Ba2 | 12.6 | 13.5 | 17.5 | 22.1 | 7.7 | 13.9 |
| Eucephalobus striatus | Ba2 | 7.2 | 3.3 | 44.8 | 13.5 | 5.1 | 39.4 |
| Eumonhystera dispar | Ba2 | 1.0 | 1.0 | ||||
| Eumonystera filiformis | Ba2 | 1.7 | 2.4 | ||||
| Geomonhystera villosa | Ba2 | 1.0 | 1.0 | ||||
| Heterocephalobus elongatus | Ba2 | 8.6 | 4.0 | 9.7 | 10.2 | 9.9 | 2.2 |
| Heterocephalobus eurystoma (N) | Ba2 | 0.7 | 0.7 | ||||
| Chiloplacus demani | Ba2 | 7.4 | 5.8 | 1.6 | |||
| Chiloplacus propinquus | Ba2 | 18.2 | 22.6 | 23.8 | 21.6 | 12.2 | 30.8 |
| Chiloplacus symmetricus | Ba2 | 1.0 | 1.0 | ||||
| Plectus acuminatus | Ba2 | 1.1 | 8.1 | 0.9 | 5.6 | 2.6 | |
| Plectus cirratus | Ba2 | 7.3 | 3.1 | 3.9 | 4.3 | 2.1 | |
| Plectus communis | Ba2 | 3.1 | 3.1 | ||||
| Plectus longicaudatus | Ba2 | 3.8 | 2.0 | 1.8 | |||
| Plectus parietinus | Ba2 | 6.3 | 9.9 | 7.6 | 7.0 | 4.4 | 12.4 |
| Plectus parvus | Ba2 | 10.9 | 15.0 | 15.5 | 4.6 | 5.8 | |
| Plectus rhizophilus | Ba2 | 0.9 | 0.9 | ||||
| Plectus silvaticus | Ba2 | 1.3 | 1.3 | ||||
| Seleborca complexa | Ba2 | 0.7 | 0.7 | ||||
| Stegelletina leopolitensis (N) | Ba2 | 0.1 | 3.2 | 0.9 | 2.4 | ||
| Wilsonema schuurmansstekhoveni | Ba2 | 6.5 | 1.7 | 1.8 | 3.6 | 2.9 | |
| Aulolaimus oxycephalus | Ba3 | 1.1 | 1.1 | ||||
| Bastiania gracilis | Ba3 | 0.2 | |||||
| Prismatolaimus intermedius | Ba3 | 2.3 | 1.2 | 3.5 | |||
| Teratocephalus lirellus | Ba3 | 0.1 | 0.1 | ||||
| Teratocephalus terrestris | Ba3 | 0.7 | 0.2 | 0.5 | |||
| Alaimus parvus | Ba4 | 0.6 | 0.6 | ||||
| Alaimus primitivus | Ba4 | 2.2 | 3.7 | 1.3 | 0.4 | 0.5 | 6.3 |
| Amphidelus coronatus | Ba4 | 0.2 | 0.2 | ||||
| Amphidelus elegans | Ba4 | 0.2 | 0.1 | 0.2 | 0.1 | ||
| Tripyla affinis | Ca3 | 0.6 | 0.8 | 1.4 | |||
| Trischistoma monohystera | Ca3 | 0.3 | 0.3 | ||||
| Clarkus papillatus | Ca4 | 2.6 | 1.8 | 0.8 | 2.3 | 3.0 | |
| Coomansus parvus | Ca4 | 1.3 | 0.1 | 1.3 | 0.1 | ||
| Coomanus zschokkei | Ca4 | 0.7 | 0.7 | ||||
| Ironus macramphis | Ca4 | 0.4 | 0.4 | ||||
| Mylonchulus brachyuris | Ca4 | 3.2 | 1.7 | 0.9 | 1.0 | 2.4 | 2.5 |
| Prionchulus muscorum | Ca4 | 2.5 | 2.5 | ||||
| Paravulus hartingii | Ca5 | 0.6 | 0.6 | ||||
| Aphelenchoides bicaudatus | Fu2 | 0.3 | 0.1 | 0.1 | 0.3 | ||
| Aphelenchoides composticola | Fu2 | 9.7 | 11.0 | 0.9 | 7.4 | 5.3 | 8.9 |
| Aphelenchoides limberi | Fu2 | 1.4 | 0.2 | 1.2 | |||
| Aphelenchoides parietinus | Fu2 | 5.5 | 7.4 | 14.8 | 3.2 | 3.0 | 21.6 |
| Aphelenchoides saprophilus | Fu2 | 1.1 | 1.3 | 1.0 | 0.1 | 1.3 | |
| Aphelenchus avenae | Fu2 | 22.8 | 39.5 | 82.4 | 21.2 | 35.6 | 88.0 |
| Ditylenchus dipsaci | Fu2 | 0.6 | 0.5 | 1.1 | |||
| Ditylenchus intermedius | Fu2 | 3.6 | 15.7* | 8.3 | 4.7 | 6.3 | |
| Ditylenchus longicauda | Fu2 | 1.1 | 0.7 | 0.4 | |||
| Ditylenchus longimetricalis | Fu2 | 2.7 | 1.0 | 1.7 | |||
| Ditylenchus myceliophagus | Fu2 | 1.7 | 0.7 | 0.6 | 1.7 | ||
| Ditylenchus parvus (N) | Fu2 | 1.2 | 1.2 | ||||
| Ditylenchus tenuidens (N) | Fu2 | 0.8 | 0.8 | ||||
| Ditylenchus sp. | Fu2 | 1.7 | 1.7 | ||||
| Filenchus discrepans | Fu2 | 2.6 | 2.6 | ||||
| Filenchus misellus | Fu2 | 1.0 | 1.0 | ||||
| Filenchus polyhypnus | Fu2 | 7.2 | 7.2 | ||||
| Filenchus thornei | Fu2 | 3.3 | 2.1 | 2.1 | 3.3 | ||
| Filenchus vulgaris | Fu2 | 8.1 | 19.1 | 32.2 | 17.6 | 13.7 | 35.2 |
| Hexatylus viviparus | Fu2 | 0.5 | 0.5 | ||||
| Nothotylenchus acris | Fu2 | 0.7 | 0.7 | ||||
| Paraphelenchus obscurus (N) | Fu2 | 4.6 | 4.6 | ||||
| Paraphelenchus pseudoparietinus | Fu2 | 1.5 | 1.8 | 0.8 | 2.1 | 2.1 | |
| Diphtherophora communis | Fu3 | 0.3 | 1.4 | 0.3 | 1.4 | ||
| Tylencholaimus mirablis | Fu4 | 0.7 | 0.9 | 1.6 | |||
| Tylencholaimus stecki | Fu4 | 4.3 | 2.8 | 1.9 | 0.9 | ||
| Tylencholaimus teres | Fu4 | 0.3 | 0.3 | ||||
| Aporcelaimus superbus | Om4 | 0.4 | 0.4 | ||||
| Campydora demonstrans | Om4 | 0.2 | 0.2 | ||||
| Crassolabium ettersbergense | Om4 | 2.4 | 1.0 | 1.4 | 2.0 | ||
| Dorydorella bryophila | Om4 | 3.7 | 6.7 | 10.4 | |||
| Dorylaimoides micoletzkyi | Om4 | 1.4 | 2.4 | 1.7 | 1.3 | 0.8 | |
| Ecumenicus monohystera | Om4 | 0.2 | 0.4 | 2.4 | 0.2 | 2.8 | |
| Eudorylaimus carteri | Om4 | 3.9 | 19.5 | 9.2 | 10.8 | 10.5 | 11.3 |
| Eudorylaimus leuckarti | Om4 | 9.9 | 2.3 | 2.5 | 1.5 | 2.7 | 10.5 |
| Eudorylaimus iners | Om4 | 3.4 | 3.4 | ||||
| Eudorylaimus opistohystera | Om4 | 2.9 | 2.1 | 1.4 | 2.3 | 4.1 | |
| Eudorylaimus spp. juvs | Om4 | 7.5 | 3.1 | 3.3 | 2.1 | 6.5 | 5.3 |
| Mesodorylaimus meyli | Om4 | 2.0 | 2.0 | ||||
| Microdorylaimus parvus | Om4 | 2.8 | 0.2 | 2.4 | 5.6 | 0.2 | |
| Pungentus silvestris | Om4 | 0.7 | 3.5 | 4.2 | |||
| Aporcelaimellus obtusicaudatus | Om5 | 7.8 | 2.2 | 6.8 | 2.3 | 4.7 | 11.6 |
| Axonchium propinquum | Om5 | 0.1 | 0.1 | ||||
| Discolaimus major | Om5 | 0.9 | 0.9 | ||||
| Discolaimus texanus | Om5 | 0.5 | 0.5 | ||||
| Epidorylaimus agilis | Om5 | 0.4 | 0.4 | ||||
| Mesodorylaimus bastiani | Om5 | 2.6 | 2.9 | 2.1 | 4.8 | 0.6 | 2.1 |
| Metaxonchium coronatum | Om5 | 0.6 | 0.6 | ||||
| Nygolaimus brachyuris | Om5 | 1.1 | 0.3 | 0.8 | |||
| Oxydirus oxycephalus | Om5 | 2.5 | 2.1 | 1.7 | 0.6 | 2.0 | 2.6 |
| Paraxonchium laetificans | Om5 | 0.6 | 0.1 | 0.5 | 1.2 | ||
| Prodorylaimus acris | Om5 | 0.6 | 0.4 | 0.4 | 0.6 | ||
| Aglenchus agricola | Pp2 | 1.9 | 6.4 | 32.9 | 10.3 | 4.8 | 28.7 |
| Basiria gracilis | Pp2 | 0.7 | 0.7 | ||||
| Basiria similis | Pp2 | 0.6 | 0.3 | 0.3 | |||
| Basiria tumida | Pp2 | 2.0 | 1.8 | 0.2 | |||
| Boleodorus thylactus | Pp2 | 0.5 | 24.8 | 6.8 | 21.3 | 6.6 | 4.0 |
| Boleodorus volutus (N) | Pp2 | 0.4 | 0.4 | 0.8 | |||
| Cephalenchus intermedius (N) | Pp2 | 0.2 | 0.2 | ||||
| Coslenchus andrássyi (N) | Pp2 | 0.7 | 0.7 | ||||
| Coslenchus costatus | Pp2 | 1.8 | 1.9 | 3.7 | |||
| Ecphyadophora tenuissima (N) | Pp2 | 0.4 | 0.4 | ||||
| Malenchus acarayensis | Pp2 | 9.1 | 7.6 | 4.4 | |||
| Malenchus bryophilus | Pp2 | 12.4 | 2.2 | 14.6 | |||
| Malenchus exiguus | Pp2 | 2.6 | 10.1 | 2.7 | 1.0 | 6.8 | |
| Malenchus gratiosus | Pp2 | 0.9 | 0.9 | ||||
| Neopsilenchus magnidens | Pp2 | 0.5 | 0.5 | ||||
| Tylenchus davainei | Pp2 | 4.6 | 5.4 | 1.6 | 2.7 | 2.9 | 5.9 |
| Paratylenchus bukowinensis | Pp2 | 15.8 | 11.5 | 4.3 | |||
| Paratylenchus microdorus | Pp2 | 10.9 | 3.5 | 6.4 | 1.0 | ||
| Paratylenchus projectus | Pp2 | 3.4 | 3.4 | ||||
| Psilenchus hilarulus | Pp2 | 2.0 | 0.9 | 2.6 | 0.2 | ||
| Amplimerlinius macrurus | Pp3 | 0.7 | 14.8 | 14.3 | 0.7 | ||
| Bitylenchus dubius | Pp3 | 10.8 | 12.8 | 4.1 | 19.5 | ||
| Bitylenchus maximus | Pp3 | 2.2 | 1.7 | 0.5 | |||
| Geocenamus brevidens | Pp3 | 7.1 | 5.2 | 6.5 | 1.7 | ||
| Geocenamus microdorus | Pp3 | 21.0 | 21.0 | ||||
| Geocenamus nanus | Po3 | 8.8 | 8.8 | 5.0 | |||
| Helicotylenchus canadensis | Pp3 | 3.8 | 1.3 | 5.1 | |||
| Helicotylenhus digonicus | Pp3 | 11.0 | 0.6 | 3.3 | 8.4 | ||
| Helicotylencus dihystera | Pp3 | 10.2 | 10.2 | ||||
| Heterodera mani juvs | Pp3 | 1.2 | 1.2 | ||||
| Heterodera avenae juvs | Pp3 | 0.3 | 0.6 | 0.9 | |||
| Meloidogyne hapla | Pp3 | 1.1 | 1.1 | ||||
| Nagelus obscurus | Pp3 | 1.1 | 1.1 | ||||
| Pratylenchoides crenicauda | Pp3 | 0.8 | 0.5 | 1.3 | |||
| Pratylenchus crenatus | Pp3 | 1.3 | 0.7 | 0.6 | |||
| Pratylenchus penetrans | Pp3 | 4.6 | 9.7 | 7.5 | 9.7 | ||
| Pratylenchus pratensis | Pp3 | 9.1 | 7.4 | 6.3 | 0.6 | 6.8 | |
| Tylenchorhynchus bicaudatus | Pp3 | 0.1 | 0.1 | ||||
| Tylenchorhynchus cylindricus | Pp3 | 2.3 | 2.3 | ||||
| Longidorus elongatus | Pp5 | 0.3 | 0.3 | ||||
| Longidorus intermedius | Pp5 | 0.5 | 0.5 | ||||
| Total number of species | 99 | 90 | 53 | 60 | 81 | 102 | |