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easynem (version 1.0.3)

calc_nemindex: Calculate multiple nematode ecological indices and generate nemindex class

Description

The calc_nemindex() is used to Calculate multiple nematode ecological indices and generate nemindex-class. The ecological indexes that can be calculated by this function include MI, sigMI, sigMI25, MI25, PPI, WI, NCR, CI, BI, SI, EI, etc.

Usage

calc_nemindex(data)

Value

A nemindex-class for storing nematode ecological indices analysis results.

  • MI, Maturity Index. Indicates environmental disturbance resulting from perturbations (range, 1-5). Low values (<2) indicate an early (primary or secondary) successional stage or a temporary level of increased nutrient availability. Values close to 2 indicate a high level of disturbance with low soil food web structure, while intermediate values (2.5–3) indicate some soil food web maturity. High values (>3) indicate a well-structured and complex soil food web likely with connectivity and energy flow between trophic levels.

  • sigMI, Sigma Maturity Index (SigmaMI). Indicates environmental disturbance resulting from perturbations in non-agricultural soils (range, 1-5). Low values (<2) indicate a high level of nutrient availability and minimal plant-parasitic pressure, while values close to 2 indicate a high level of disturbance with low soil food web structure. Intermediate values (2.5–3) indicate some soil food web maturity. High values (>3), in turn, indicate a well-structured and complex soil food web likely with connectivity and energy flow between trophic levels, which might include larger plant-parasitic nematodes. This index is less sensitive to enrichment in agricultural soils.

  • sigMI25, Sigma Maturity Index 2-5 (SigmaMI25). computes the MI for all nematodes in the c-p2-5 range (Neher & Campbell, 1996). The index recognizes that the higher c-p value plant-feeding species also provide information of environmental stress but bears some of the burden of the SigmaMI in situations of nutrient enrichment.

  • MI25, Maturity Index 2–5. Indicates Environmental disturbance resulting from perturbations unrelated to nutrient enrichment in agricultural fields (range, 2-5). Low values (close to 2) indicate substantial disturbance resulting from perturbations unrelated to nutrient enrichment. High values (>3) indicate greater maturity with minimal or no effect resulting from perturbations.

  • PPI, Plant-Parasitic Index. Indicates Assemblage composition of plant-parasitic nematodes (range, 2-5). Low values (close to 2) indicate plant-parasitic nematode assemblages dominated by small and medium-sized ectoparasites that feed on single plant cells. Higher values indicate assemblages dominated by medium and large (semi-) endoparasitic (e.g., Meloidogyne and Heterodera spp.) or ectoparasitic virus transmitting nematodes (e.g., Xiphinema and Longidorus spp.).

  • PPI_MI, PPI/MI. The PPI/MI ratio is lower under nutrient poor conditions than under nutrient rich conditions. It is a sensitive indicator of enrichment in agroecosystems (Bongers & Korthals, 1995; Bongers et al., 1997).

  • WI, Wasilewska Index. Wasilewska Index is calculated by dividing the sum of bacteria-feeding nematodes and fungi-feeding nematodes by the number of herbivorous nematodes. This index is used to indicate the impact of nematode communities on crop production. The smaller the index, the greater the negative impact of nematode communities on crop production.

  • NCR, Nematode Channel Ratio. The Nematode Channel Ratio (NCR) is a parameter used in soil ecology to assess the balance between bacterial and fungal energy channels in the soil food web. This ratio is calculated by comparing the abundance of bacterial-feeding nematodes to fungal-feeding nematodes. High NCR: Indicates a bacterial-dominated energy channel. This is often found in soils with frequent disturbance or high inputs of easily decomposable organic matter. Low NCR: Indicates a fungal-dominated energy channel. This is commonly found in more stable, less disturbed soils, such as forests or natural grasslands, where organic matter decomposition is slower and more complex.

  • CI, Channel Index. Indicates predominant decomposition pathway of organic matter (range, 0-100). Lower values (<50) indicate increasing decomposition dominance by bacteria, while higher values (>50) indicate increasing decomposition dominance by fungi. Bacterial dominance indicates the presence of rapidly decomposed organic matter, while fungal dominated decomposition indicates the slow breakdown of more complex organic matter. The focus on opportunistic bacterial and fungal feeders makes this a highly responsive index, which can be used to detect alternating decomposition pathways over time.

  • EI, Enrichment Index. Indicates food availability and nutrient enrichment (range, 0-100). Low (0–30), intermediate (30–60), and high (60–100) values indicate equivalent levels of food availability (e.g., labile organic carbon) and nutrient enrichment.

  • SI, Structure Index. Indicates Soil food web structure and complexity, as well as disturbance due to environmental (e.g., salinity and drought) or anthropogenic (e.g. tillage, mining, and chemical pollution) causalities (range, 0-100). Low (0–30), intermediate (30–60), and high (60–100) values indicate equivalent levels of soil food web complexity. Lower values are indicative of perturbed soil food webs, while higher values indicate a structured soil food web.

  • BI, Basal Index. Indicates food web structure and complexity (range, 0-100). Low (0–30), intermediate (30–60), and high (60–100) values indicate equivalent levels of soil perturbation. Therefore, higher values (>50) are indicative of a depleted and damaged soil food web.

  • TotalBiomass, Total biomass of nematode community.

  • MetabolicFootprint, Metabolic Footprints. Indicates magnitude of ecosystem functions and services fulfilled by nematode community (range, 0-infinite). Higher metabolic footprint values are indicative of greater carbon channelling and therefore an increased contribution to the fulfilment of soil ecosystem functions and services. This can be considered per trophic group (e.g. bacterivore footprint), or per component of the nematode community that indicate enrichment (enrichment footprint) and structure (structure footprint).

  • EnrichmentFootprint, Enrichment Footprint.

  • StructureFootprint, Structure Footprint.

  • HerbivoreFootprint, Herbivore Footprint.

  • FungivoreFootprint, Fungivore Footprint

  • BacterivoreFootprint, Bacterivore Footprint.

  • PrOmFootprint, Metabolic footprint of an omnivorous predatory nematode.

  • Numbers, Number of nematodes.

  • CAssimilated, Carbon assimilated by nematodes.

  • CRespired, Carbon consumed by nematode respiration.

Arguments

data

An easynem-class data.

Details

To facilitate code interpretation, it is recommended to use the pipe symbol |> to connect functions:

nem_index <- nem |> calc_nemindex()

References

  • https://shiny.wur.nl/ninja/

  • http://nemaplex.ucdavis.edu/Ecology/Indices_of_ecosystem_condition.html

  • Du Preez G, Daneel M, De Goede R, et al. Nematode-based indices in soil ecology: Application, utility, and future directions. Soil Biology and Biochemistry, 2022, 169: 108640.

  • Bongers T. The maturity index: an ecological measure of environmental disturbance based on nematode species composition. Oecologia, 1990, 83: 14-19.

  • Bongers T, Goede R G N, Korthals G W, et al. Proposed changes of cp classification for nematodes. 1995.

  • Ferris, H. O. W. A. R. D., and Tom Bongers. "Indices developed specifically for analysis of nematode assemblages." Nematodes as environmental indicators. Wallingford UK: CABI, 2009. 124-145.

  • Goede, RGM de, T. Bongers, and C. H. Ettema. "Graphical presentation and interpretation of nematode community structure: cp triangles." (1993): 743-750.

  • Ferris, Howard, Tom Bongers, and Ron GM de Goede. "A framework for soil food web diagnostics: extension of the nematode faunal analysis concept." Applied soil ecology 18.1 (2001): 13-29.

  • Ferris, Howard. "Form and function: metabolic footprints of nematodes in the soil food web." European Journal of Soil Biology 46.2 (2010): 97-104.

See Also

Other functions in this R package for data calculations: calc_beta2, calc_compare, calc_compare2, calc_beta, calc_alpha, calc_funguild, calc_funguild2, calc_mf, calc_mf2, calc_ter, calc_ter2, calc_ef, calc_ef2.

Examples

Run this code
nem <- read_nem2(tab = nemtab, tax = nemtax, meta = nemmeta)
nem_index <- nem |> calc_nemindex()
show(nem_index)

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