Claim Missing Document
Check
Articles

Found 2 Documents
Search

THE POTENTIAL USED OF EPIPELIC DIATOM AS BIOINDICATOR OF WATER QUALITY: part I Tri Retnaningsih Soeprobowati; Hendarko Soegondo; Boedi Hendarto; Indro Sumantri; Budiyanto Toha
JOURNAL OF COASTAL DEVELOPMENT Vol 2, No 2 (1999): Volume 2, Number 2, Year 1999
Publisher : JOURNAL OF COASTAL DEVELOPMENT

Show Abstract | Download Original | Original Source | Check in Google Scholar | Full PDF (7636.763 KB)

Abstract

Biomonitoring methods for water quality, such as coli form content, diversity and evenness indices of macrobenthic invertebrates and plankton which are recently used, actually have some weaknesses. Escherichia coli only indicated pollution caused by faecal coli; macrobenthic invertebrates have not ability to live in all substratum, whereas the population of phytoplankton are affected by current as they are floating in the surface water. Therefore, the method which are more effective have to be developed. Epipelic diatoms have potential characteristics as bioindicator of water quality because the have ability to accumulate physic-chemical component of aquatic ecosystem and respond it immediately. This research is conducted in order to find out a new alternative of biomonitoring method ( species indices of diatoms ) which are more significant, effective and efficient by determine water quality map absed on diatoms and determines the species which responsible to the grouping. Sediments samples were taken from 7 rivers in the Northern Coast of Central Java (called Pantura): Karanggeneng-Rembang, Juana-Pati, Banjir Kanal Timur-Semarang, Banjir Kanal Barat-Semarang, Banger-Pekalongan, Pekalonghan-Pekalongan, and Gung-Tegal. Temperature, dissolved oxygen, salinity, pH and turbidity were measure in-situ.  Analysis of water and sediment samples include total nitrogen, total phosphorus,silica, heavy metals of Cu, Cr, and Cd. Extraction, preparation and identification of diatoms followed Wetzel & Likens (1991) and Round (1993). The`data were then analysed using Primer package progamme version 4.0 which is produced by Plymouth Marine Laboratory, United Kingdom (Carr, 1997). The Multi Dimentional Scaling (MDS) ordination was done to make grouping and was followed by SIMPER analysis to determine responsible species (Clarke & Warwick, 1994). Based on diatom community, 7 river Pantura could be divided into 3 groups: Group I, consisted of Gung and Pekalongan Rivers, Group II of Banjir Kanal Timur, Barat and Banger Rivers and Group III Karenggeneng and Juana Rivers. Synedra ulna was responsibled for those grouping and are therefore could be promoted as bioindicator of water quality in the Indonesian river. Research still should be developed, especially for diatoms in the bottom layer of sediment samples to reconstruct ecological condition in the past and to predict the condition in the future.
PERUBAHAN LUAS HUTAN MANGROVE DI PULAU KEMUJAN TAMAN NASIONAL KARIMUNJAWA Suryanti Ign; Boedi Hendarto; Dhaud Anggoro
Pena Jurnal Ilmu Pengetahuan Dan Teknologi Vol 20, No 1 (2011): Pena Maret 2011
Publisher : LPPM Universitas Pekalongan

Show Abstract | Download Original | Original Source | Check in Google Scholar | DOI: 10.31941/jurnalpena.v20i1.24

Abstract

Karimun Island is one of the islands with the potential of natural resources is one of the verylarge which is a mangrove forest on the island Kemujan. Human activities and tourismactivities tend to threaten the existence of mangrove forest on the island Kemujan.Information changes in land and development of human activities necessary for sustainablemanagement of mangrove forests. This study aims to determine the level of mangrove forestcover in the island Kemujan, knowing that human activity significantly affects the conditionof mangrove forests Kemujan Island National Park Karimunjawa. The study was conducted in 2 phases: a preliminary study in August and the last study in December 2009. The methodused in this study is the imaging method of observation and mapping, the research conductedto observe the phenomenon in the field to get actual data related to materials research. Dataobtained from satellite image analysis and determination of the cause of the significant factorsprocessed by SEM. As a result of image interpretation, in 1991, 2001 and 2009 found thatisland Kemujan gradually changing area. In 1991, the area is 11.734 ha kemujan whichgradually changed to 12.617 hectares in 2001 to 2009 by 11.177 HA. The main reason thesechanges based on public perception derives from public activities such as cleaning ponds,seaweed cultivation and so on.Keyword : mangrove forest, satellite imagery, kemujan island, SEM analysis