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Diversity and Structure of Trichoptera Communities and Water Quality Variables in Streams, Northern Thailand T

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Diversity and Structure of Trichoptera Communities and Water Quality Variables in Streams, Northern Thailand T World Academy of Science, Engineering and Technology International Journal of Environmental and Ecological Engineering Vol:9, No:9, 2015 Diversity and Structure of Trichoptera Communities and Water Quality Variables in Streams, Northern Thailand T. Prommi, P. Thamsenanupap changes, benthic macroinvertebrates are often used as Abstract—The influence of physicochemical water quality indicators of the effects of human activity on water system and parameters on the abundance and diversity of caddisfly larvae was they provide information on habitat and water quality [7]. The studied in seven sampling stations in Mae Tao and Mae Ku organic enrichment of water caused by both domestic and watersheds, Mae Sot District, Tak Province, northern Thailand. The industrial effluents is a common anthropogenic impact on streams: MK2 and MK8 as reference site, and impacted streams (MT1-MT5) were sampled bi-monthly during July 2011 to May urban watercourses. This kind of pollution changes physical 2012. A total of 4,584 individual of caddisfly larvae belonging to 10 and chemical characteristics of lotic systems, thus affecting family and 17 genera were found. The larvae of family the assemblage of benthic macroinvertebrates [4], [8]. Hydropsychidae were the most abundance, followed by Amongst the benthic macroinvertebrates, order Trichoptera Philopotamidae, Odontoceridae, and Leptoceridae, respectively. The (or caddisflies) are probably the most widely distributed and genus Cheumatopsyche, Hydropsyche, and Chimarra were the most larvae are common in running water (8-13% of total abundance genera in this study. Results of CCA ordination showed the total dissolved solids, sulfate, water temperature, dissolved abundance) [9] and they represent one of the relatively well oxygen and pH were the most important physicochemical factors to studied orders of aquatic insects in South East Asia [10], [11]. affect distribution of caddisflies communities. Changes in the The larvae of many species coexist in running waters and they caddisfly fauna may indicate changes in physicochemical factors are known to have specific habitat and environmental owing to agricultural pollution, urbanization, or other human requirements [12]. Caddisflies have been described as the activities. Results revealed that the order Trichoptera, identified to most ecologically diverse group of aquatic insects, with species or genus, can be potentially used to assess environmental water quality status in freshwater ecosystems. 13,574 described species [11]. As a numerically dominant group in rivers and streams, caddisflies are important to the Keywords—Caddisfly larvae, environmental variables, diversity, functioning of freshwater ecosystems because of their ability streams. to partition habitats and trophic resources [13]. Their response to perturbation and reliance on plant matter for food are I. INTRODUCTION reasons why caddisflies are widely used in several aspects of RESHWATER benthic macroinvertebrates inhabit river water quality monitoring [14]. Furthermore, their well- F and stream beds, lakes and reservoirs and are associated described biology and taxonomy facilitate interpretation of with various types of substrates such as mineral sediments, water quality assessments. The use of species level detritus, macrophytes and filamentous algae [1]. They are identification to monitors water quality pollution is much essential elements in lentic and lotic trophic webs, more precise than using family or generic level [15]. The aim participating in the energy flow and nutrient cycling [2]. They of this study was to investigate the diversity and structure of are also important food resources for fish [3] and some caddisflies communities in relation to water quality variables insectivorous birds [4]. The distribution of aquatic organisms in order to explore the bioindication potential of caddisflies is the result of interactions among their ecological role, the larvae for assessing water quality deterioration in northern physical conditions that characterize the habitat, and food Thailand. availability [5]. Thus, the community structure of benthic macroinvertebrates depends on a number of factors, such as II. MATERIAL AND METHODS water quality, type of substrate, particle size of sediment, A. Description of the Study Area International Science Index, Environmental and Ecological Engineering Vol:9, No:9, 2015 waset.org/Publication/10002209 water flow, sediment organic matter availability, oxygen Mae Tao and Mae Ku watersheds are located in the lower concentration as well as environmental conditions surrounding part of Mae Sot district, Tak Province, northern Thailand. The the watercourse [4], [6]. Because they reflect environmental main agricultural products in this area are rice, soybean, sugar cane and garlic. The main industries are zinc mines and T. Prommi is with the Faculty of Liberal Arts and Science, Kasetsart textiles. The seven sampling sites were selected in this study University, Kamphaeng Saen Campus, Nakhon Pathom Province, 73140 (Fig. 1). Study sites in Mae Tao watershed included MT1, Thailand (phone: +66 34 281105-6; fax: +66 34 281057; e-mail: MT2, MT3, MT4 and MT5, which runs through the mine. [email protected]). P. Thamsenanupap was with Department of Environmental Education, Agricultural activities were found along the length of this Faculty of Environmental and Resources Studies, Mahasarakham University, stream. MK2 and MK8, which both are parallel flow with Maha Sarahkam, Thailand (e-mail: [email protected]). International Scholarly and Scientific Research & Innovation 9(9) 2015 1065 scholar.waset.org/1307-6892/10002209 World Academy of Science, Engineering and Technology International Journal of Environmental and Ecological Engineering Vol:9, No:9, 2015 that stream, were located in Mae Ku watershed. The stream river in general. Also, the stream from watershed in Phop Phra from Mae Tao and Mae Ku watersheds flows to the Moei district, Tak Province flows to Mae Hong Son via Mae Sot, River. This river is the borderline between Myanmar and Mae Ramat, and Tha Song Yang, to merge into the Salween Thailand. It is 327 km long, flowing towards the north unlike a River in Myanmar before flowing into the Gulf of Martaban. International Science Index, Environmental and Ecological Engineering Vol:9, No:9, 2015 waset.org/Publication/10002209 Fig. 1 The sampling sites in Mae Tao (MT1-MT5) and Mae Ku (MK2, MK8) watersheds, Mae Sot District, Tak Province, Northern Thailand International Scholarly and Scientific Research & Innovation 9(9) 2015 1066 scholar.waset.org/1307-6892/10002209 World Academy of Science, Engineering and Technology International Journal of Environmental and Ecological Engineering Vol:9, No:9, 2015 B. Sample Collection physicochemical variables on the abundance of the caddisfly At each site, the sample was collected bi-monthly during larvae using the SPSS (Statistical Package for Social Science), July 2011 to May 2012. The physicochemical water quality Version 13.0. Canonical correspondence analysis (CCA) of parameters were measured at all sampling stations between 09 PC-ORD Version 4.0 [20] investigate the contribution of the a.m and 5 p.m prior to aquatic insect sampling. Three environmental stressors on the distribution and abundance of replicates of the physicochemical water quality parameters transformed caddisflies species data (log(x+1)). The Monte- were recorded directly at each sampling site and included pH, Carlo test was applied to test the significance of the produced measured by a pH-meter Waterproof Model Testr30, water canonical axes with 998 permutations at P < 0.05. The biplot temperature (WT) was measured by a hand-held thermometer, ordination diagram was produced using CanoDraw for and dissolved oxygen (DO), which was measured by a Windows 10. In the CCA, taxa constituting more than 0.1% of HACH® Model sensION 6 DO meter cyberScan Model the total abundance were selected, and in totals, 14 taxa were DO110, total dissolved solid (TDS) was measured by a used in the analyses. EURECH CyberScan CON110 conductivity/TDS meter. Water samples from each collecting period were stored in III. RESULTS 2- polyethylene bottles (500 mL). The sulfate (SO4 ) and nitrate- A. Physicochemical Water Quality Parameters nitrogen (NO -N) were determined in accordance with the 3 Table I summarized the means, standard deviations of standard method procedures [16]. measured physicochemical water quality parameters at the At each sampling period, semi-quantitative samples of sampling sites taken during the six sampling periods. caddisflies larvae from the different microhabitats (riffles, Dissolved oxygen was not varied significantly during the time depositional zones, different types of vegetation), were of measured (P>0.05), whereas water temperature, pH, total collected. A D-frame [5] aquatic hand net (mesh sieve 250 dissolved solids, sulfate and nitrate-nitrogen were varied μm) was used. Lotic habitats with stony substrates were significantly during the time of measured (P<0.05). sampled during about 15 minutes along an approximately 100 Temperature varied from 24.11 (MK2) to 27.22Cº (MK8). The m reach by hand-picking. Other habitats (fine sediments, lowest mean value of dissolved oxygen (4.32 mg l-1) was roots, submerged and aquatic vegetation) were sampled at found in the downstream station (MT4 and MT5), and the least in three different zones along the same reach. The highest values were observed in upper stream station (≥4.35 contents of the aquatic hand net
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