Ecological Status of Hot Springs in Eastern Amhara Region: Macroinvertebrates Diversity

Authors

  • Sisay Derso Ethiopian Public Health Institute
  • Abebe Beyene Jimma University
  • Melaku Getachew Wollo University
  • Argaw Ambelu Jimma University

Keywords:

Hot spring, Macroinvertebrate, Ecological status, Diversity,

Abstract

 Springs are the places where ground water is discharged at specific locations. They vary dramatically as to the type of water they discharge. Hot springs is having the temperature of the water lies significantly above the mean of annual air temperature of that region. Temperature is one of the most important factors that govern species abundance and distribution. The objective of this study is to examine the relationship between biological parameters (macroinvertebrate diversity) with physicochemical water and habitat quality of hot springs in Easter Amhara Region. A cross-sectional study of physical, chemical and biological components of the hot springs was carriedout to assess their ecological status. Samples were collected from March to May 2013. Biological samples were collected to provide a qualitative description of the community composition at each sampling site. Water samples were collected for analysis of selected physicochemical parameters following water quality assessment protocols. A total of 1095 macroinvertebrates classified into 10 orders and 31 families of macroinvertebrates were collected from the 12 sampling sites. The most abundant orders were Diptera 49.90%, Odonata 15.53%, Coleopteran 12.97%, and Ephmeropetra 9.5% represented by 14 families. Macroinvertebrate taxa were absent at B1 and H1 sites with the temperature of 72 0C and 70 0C respectively. However, in this study, the macroinvertebrate taxa (Chironomidae and Hydrobiidae) were found within a temperature of 52 oC at S1 and H1 sites. The results are also revealed that as the temperature gradient declines, the macroinvertebrate diversity flourished.

Due to this fact, both macroinvertebrate diversity and family biotic index were negatively correlated with temperature and the correlations were significant. Human disturbance and habitant conditions varied considerably among sites in the study area. Although human disturbance and water pollution are among the factors influencing ecological quality, the strong correlations between water temperature and species diversity suggest that temperature is the major environmental gradient affecting aquatic biodiversity in hot springs.

Author Biographies

Sisay Derso, Ethiopian Public Health Institute

Environmental Health Research Team

Abebe Beyene, Jimma University

Department of Environmental Health science and technology,

Melaku Getachew, Wollo University

Environmental Health

Argaw Ambelu, Jimma University

Department of Environmental Health Science and technology

References

[1] Oliver, J., venter, S. J. & Jonker, Z. C. (2011). Thermal and chemical characteristics of hot water springs in the northern part of the Limpopo Province, South Africa.
[2] Bhusare, D. U. & Wakte, S. P. (2011). Microbiological and physiochemical attributes of hot water sulphur spring of Unkeshwar. Life Science, 2(4), pp. 4-6.
[3] Kruse, A. F. (1997). CHARACTERIZATION OF ACTIVE HOT-SPRINGS ENVIRONMENTS USING MULTISPECTRAL AND HYPERSPECTRAL REMOTE SENSING. Analytical Imaging and Geophysics LLC, pp. 1-8.
[4] Sen, S. K., Mohapata, S. K., Satpathy, S. & Rao, G. (2010). Characterization of hot water spring source isolated clones of bacteria and their industrial applicability. International Journal of Chemical Research, 2(1), pp. 01-07.
[5] Haki, G. D. & Gezmu, T. B. (2012). Physico-chemical properties of waters from some Ethiopian hot springs and the risk to the health of the community. Greener Journal of Physical Sciences, pp. 138-140.
[6] Beyene, A., Legesse, W., Triest, L. & Kloos, H. (2009). Urban impact on ecological integrity of nearby rivers in developing countries: the Borkena River in highland Ethiopia. Environ Monit Assess, Volume 153, pp. 461-476.
[7] Torrisi, M., Scuri, S., Dell'Uomo, A. & Cocchioni, M. (2010). Comparative monitoring by means of diatoms, macroinvertebrates and chemical parameters of an Apennine watercourse of central Italy: The river Tenna. Ecological Indicators, p. 910–913.
[8] Camargo, J. A., Gonzalo, C. & Alonso, Á. (2011). Assessing trout farm pollution by biological metrics and indices based on aquatic macrophytes and benthic macroinvertebrates: A case study. Ecological Indicators, p. 911–917.
[9] Rosenberg, D. & Resh, V. (1993). Freshwater Biomonitoring and Benthic Macroinvertebrates., New York: Chapman & Hall.
[10] De Pauw, N., Gabriels, W. & Goethals, P. (2006). River monitoring and assessment methods based on macroinvertebrates. In: Ziglio, G., Siligardi, M., Flaim, G. (Eds.), Biological Monitoring of Rivers: Applications and Perspectives.. John Wiley & Sons, p. 113 – 134.
[11] Hering, D. et al. (2003). The development of a sy st em to as s e ss t he e colog ical q uality o f s tream s based o n macroinv ertebrates — design of the s amp ling programme with in the A QEM p roject.. Int . R ev. H ydrobiol, p. 45–361.
[12] Dominguez-Granda, L., Lock, K. & Goethals, P. L. (2011). Using multi-target clustering trees as a tool to predict biological water quality indices based on benthic macroinvertebrates and environmental parameters in the Chaguana watershed (Ecuador). Ecological Informatics , p. 303– 308.
[13] Brazner, J. et al. (2007). Evaluation of geographic, geomorphic and human influences on Great Lakes wetland indicators: A multi-assemblage approach. Ecological Indicators , p. 610–635.
[14] Ambelu, A., Lock, K. & Goethals, P. (2010). Comparison of modelling techniques to predict macroinvertebrate community composition in rivers of Ethiopia. Ecological Informatics , p. 147– 152.
[15] Pace, G. et al. (2011). Macroinvertebrate assemblages at mesohabitat scale in small sized volcanic siliceous streams of Central Italy (Mediterranean Ecoregion). Ecological Indicators , p. 688–696.
[16] Tamene, B., Bekele, T. & Kelbessa, E. (2000). An Ethnobotanical study of the Semi-wetland Vegetation of Cheffa.
[17] Getachew, M. et al. (2012). Ecological assessment of Cheffa Wetland in the Borkena Valley, northeast Ethiopia: Macroinvertebrate and bird communities. Ecological Indicators, p. 63–71.
[18] MCKEE, J. (2007). ETHIOPIA: COUNTRY ENVIRONMENTAL PROFILE, Addis Abeba: EC Delegation.
[19] Piguet, F. (2002). Cheffa Valley: refuge for 50,000 pastoralists and 200,000 animals, Addis Ababa: UN-Emergencies Unit for Ethiopia.
[20] UN-HABITAT (2005). A Guidebook for Local Catchment Management in Cities, NAIROBI: Communication Consultants.
[21] Baldwin, D., Nielsen, D., Bowen, P. & Williams, J. (2005). Recommended Methods for Monitoring Floodplains and Wetlands. Canberra City: Murray-Darling Basin Commission.
[22] Deliz Quinones, K. (2005). Water quality assessment of a tropical freshwater marsh using aquatic insects. s.l., s.n., p. 1–148.
[23] Cummins, K. (1973). Trophic relations of aquatic insects. Ann. Rev. Entomol.. p. 183–206.
[24] APHA (1995). standard methods for examination of water and wastewater. washington DC: American Public Health association.
[25] Rosgen, D. (1996). Applied Morphology. In: Applied River Morphology. Lakewood, Colorado: Wildland Hydrology.
[26] Barbour, M. T., Gerritsen, J., Snyder, B. D. & Stribling, J. B. (1999). Rapid Bioassessment Protocols For Use in Streams and Wadeable Rivers: Periphyton, Benthic Macroinvertebrates, and Fish. Washington, DC 20460: EPA 841-B-99-002.
[27] MDEP, (. D. o. E. P. (2009). Quality assurance project plan for biological monitoring of Maine’s rivers, streams, and freshwater wetlands., Augusta Maine: Bio-Monitoring Program, QAPP Bureau of Land and Water Quality.
[28] Turkmen, G. & Kazanci, N. (2010). Applications of various diversity indices to benthic macroinvertebrate assemblages in streams of a n atural park in Turkey. BALWOIS.
[29] Smith, B. & Wilson, J. B. (1996). A consumer's guide to evenness indice. OIKOS , pp. 70-82.
[30] Gamito, S. (2010). Caution is needed when applying Margalef diversity index. Ecological Indicators , p. 550–551.
[31] Minaya, V. et al. (2013). Scale-dependent effects of rural activities on benthic macroinvertebrates and physico-chemical characteristics in headwater streams of the Mara River, Kenya. Ecological Indicators , p. 116– 122.
[32] Burgmer, T., Hillebrand, H. & Pfenninger, M. (2009). Effects of climate-driven temperature changes on the diversity of freshwater macroinvertebrates. Global change and conservation ecology.
[33] Wallace, J. B. & Anderson, N. (2002). HABITAT, LIFE HISTORY, AND BEHAVIORALADAPTATIONS OF AQUATIC INSECTS. In: An INTRODUCTION TO THE AQUATIC INSECTS OFF NORTH AMERICA. s.l.:KENDALL/HUNT PUBLISHING COMPANY.
[34] Stark, J., Fordayce, R. & Witerbourn, M. (1976). AN ECOLOGICAL SURVEY OF THE HOT SPRINGS AREA, HURUNUI RIVER, CANTERBURY, NEW ZEALAND. MÄURI ORÄ, pp. 35-52.
[35] Kotze, D., Ellery, W., Macfarlane, D. & Jewitt, G. (2012). A rapid assessment method for coupling anthropogenic stressors and wetland ecological condition. Ecological Indicators , p. 284–293.
[36] Hilsenhoff, W. L. (1988). Rapid field assessment of organic pollution with a familly level Biotic Index. J. N.Am.Benthol.Sco., pp. 65-68.
[37] Mandaville, S. M. (2002). Benthic Macroinvertebrates in Freshwaters Taxa Tolerance Values, Metrics, and Protocols, New York: Soil & Water Conservation Society of Metro Halifax.
[38] Buendia, C. et al. (2013). Detecting the structural and functional impacts of fine sediment on stream invertebrates. Ecological Indicators, p. 184–196.
[39] . Chiputwa, B., Morardet, S. & Mano, R. (2005). DIVERSITY OF WETLAND-BASED LIVELIHOODS IN LIMPOPO RIVER BASIN. pp. 1-28.

Downloads

Published

2015-10-02

How to Cite

Derso, S., Beyene, A., Getachew, M., & Ambelu, A. (2015). Ecological Status of Hot Springs in Eastern Amhara Region: Macroinvertebrates Diversity. American Scientific Research Journal for Engineering, Technology, and Sciences, 14(2), 1–22. Retrieved from https://asrjetsjournal.org/index.php/American_Scientific_Journal/article/view/665