Journals / Turkish Journal of Zoology / 2017 / Cilt: 41 - Sayı: 3

A nonparametric approach in quantifying species richness of Lumbricidae in East Serbia, Balkan Peninsula

Pages
487–494
Publication Date
2022-11-05
DOI
—
🏛️Bibliographic metadata and full text access for this article are provided via DergiPark.
DergiPark Record ↗
✨

AI Summary & Key Takeaways

AI Insight
⚡ TL;DR(Too Long; Didn't Read)

Chao 2 generally outperforms other estimatorssince it attains near-asymptotic stability and, therefore, more accurate prediction of earthworm species richness.

📌 3 Key Takeaways

🎯
Objective & Hypothesis:The concept of species richness is currently the most basic and most often used parameter in quantitative assessments ofbiodiversity.
📊
Key Findings & Data:Our database included 2615 individuals from a total of 54 species.
💡
Conclusion & Impact:Chao 2 generally outperforms other estimatorssince it attains near-asymptotic stability and, therefore, more accurate prediction of earthworm species richness.
🔬Design:Research Article
📍Scope:Comprehensive Sample
⚙️Variables:Domain Parameters

Abstract

The concept of species richness is currently the most basic and most often used parameter in quantitative assessments ofbiodiversity. The species richness of Lumbricidae was investigated in East Serbia, one of the highly complex areas in the eastern andcentral part of the Balkan Peninsula. Our database included 2615 individuals from a total of 54 species. Quantification of speciesrichness was done by using the observed number of species and richness estimators. A nonparametric approach was used to evaluatethe performance of various estimation techniques: Chao 2, Jackknife 2, and Bootstrap. However, only Chao 2 reached the asymptote,maintaining values of 77 until the end of the curve. A total of 70.12% of the estimated number of Lumbricidae living in East Serbia weredetected in our field study and we should expect that 23 lumbricid taxa will be added to the inventory in the future. The sampling effortneeded to find additional species undetected during the sampling is 214 individuals. Chao 2 generally outperforms other estimatorssince it attains near-asymptotic stability and, therefore, more accurate prediction of earthworm species richness.

🔖

Cite This Article

SEKULIC, J., TRAKIC, T., STOJANOVIC, M. (2022). A nonparametric approach in quantifying species richness of Lumbricidae in East Serbia, Balkan Peninsula. Turkish Journal of Zoology, Cilt: 41 - Sayı: 3, 487–494. https://ajindex.com/articles/616159

📄 Full Text PDF Viewer

📄

PDF görüntüleyici hazırlanıyor...

References (10)

  1. Blakemore R (2008). Cosmopolitan Earthworms: An Eco-taxonomic Guide to the Species. Yokohama, Turkey: Verm Ecology. Brose U (2002). Estimating species richness of pitfall catches by non- parametric estimators. Pedobiologia 46: 101-107.
  2. Cardoso P, Gaspar C, Pereira LC, Silva I, Henriques SS, Silva RR, Sousa P (2008). Assessing spider species richness and composition in Mediterranean cork oak forests. Acta Oecol 33: 114-127.
  3. Chao A (1987). Estimating the population size for capture–recapture data with unequal catchability. Biometrics 43: 783-791.
  4. Chao A, Colwell R, Chih-Wei L, Gotelli N (2009). Sufficient sampling for asymptotic minimum species richness estimators. Ecology 90: 1125-1133.
  5. Chazdon RL, Colwell RK, Denslow JS, Guariguata MR (1998). Statistical methods for estimating species richness of woody regeneration in primary and secondary rain forests of NE Costa Rica. In: Dallmeier F, Comiskey JA, editors. Forest Biodiversity Research, Monitoring and Modeling: Conceptual Background and Old World Case Studies. Paris, France: Parthenon Publishing, pp. 285-309.
  6. Coddington JA, Young LH, Coyle FA (1996). Estimating spider species richness in a southern Appalachian cove hardwood forest. J Arachnol 24: 111-128.
  7. Cognetti L (1906). Nuovi dati sui Lumbricidi dell’Europa orientale. Boll Mus Zool Comp Anat 21: 1-18 (in Italian). Colwell RK (2006). EstimateS: statistical estimation of species richness and shared species from samples. Storrs, CT, USA: Department of Ecology & Evolutionary Biology, University of Connecticut. Colwell RK, Coddington JA (1994). Estimating terrestrial biodiversity through extrapolation. Phil Trans B 345: 101-118.
  8. Csuzdi CS, Zicsi A (2003). Earthworms of Hungary. Pedozoologica Hungarica No. 1. Budapest, Hungary: Natural History Museum and Hungarian Academy of Sciences. Dey A, Chaudhuri PS (2013). Quantifying earthworm species richness in the pineapple and mixed fruit plantations of West Tripura, India-A non-parametric approach. Eur J Soil Biol 59: 31-35. Džukić G, Kalezić ML (2004). The biodiversity of amphibians and reptiles in the Balkan Peninsula. In: Griffiths HI, Kryštufek B, Reed JM, editors. Balkan Biodiversity: Pattern and Process in the European Hotspot. Dordrecht, the Netherlands: Kluwer Academic Publishers, pp. 167-192.
  9. Gaston KJ (1996). Species richness: measure and measurement. In: Gaston KJ, editor. Biodiversity: A Biology of Numbers and Difference. Oxford, UK: Blackwell Science, pp. 77-113.
  10. Gaston KJ (2000). Global patterns in