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Research Detail

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Mohd Abdul Awal
Environmental Scientist, Ministry of Environment and Forest, Health & Pollution Research Farm, Long Island City, New York, USA

Natural forest resources (Sundarbans) in Bangladesh has been facing tremendous problems, including that of dieback (top-dying), shrimp farming, human destruction, deforestation, illicit felling, miss-management of the main tree species (Heritiera fomes) which is affecting millions of trees. The present work has investigated one of the possible factors that might be causing this top-dying, namely the concentrations of various chemical elements present in the sediments, particularly heavy metals, though other chemical parameters such as the pH, salinity, moisture content of the sediment and nutrient status were also assessed. A questionnaire survey was conducted among different groups of people inside and outside of Sundarbans to explore local perceptions as to the possible causes of top dying. The present work has explored some of the possible factors involved, focusing particularly on the relationship between the amount of top-dying in different places and the concentrations of a number of chemical elements present in the soil and water, in order to test the hypothesis that chemical pollution might be responsible. The vegetation structure was assessed in terms of tree height, bole diameter, species present, and regeneration status; and the intensity of top-dying within the plots was recorded on a rank scale. Most of the elements studied had no significant correlation with the top dying of Heritiera fomes. However, Sn, Exchangeable K, and soil pH were significantly related, and three elements, namely Pb, Zn, Ni, were also close to significance. Sn concentration is negatively associated with top dying. Soil pH varied significantly in the different plots. Exchangeable K was positively associated with the tree diameter whether the top dying was severe or mild.

  Shrimp Farming, Chemical Contamination, Abnormal Elemental Concentration, Chemical Contamination, Health Problems,
  The wider Sundarbans
  
  
  Conservation and Biodiversity
  Analysis and interpretations
  1. To investigated the possible factors that might be causing this top-dying, namely the concentrations of various chemical elements present in the sediments, particularly heavy metals, though other chemical parameters such as the pH, salinity, moisture content of the sediment an d nutrient status were also assessed.
  2. To explore local perceptions as to the possible causes of top dying.

The field and laboratory methods used in this study and discussed as below:

Field Sampling Methods: The Sundarbans Reserved Forest is located at the south west corner of the Ganges River Delta close to the Bay of Bengal, mainly on the sea-shore line, river banks, channels, and small creeks.

Site Selection and Location of the Study Area: The location of these compartments within the Chandpai area, and the location of this area in the wider Sundarbans. Fieldwork was performed in October, 2003 to March, 2004. Locations of sampling points were determined using a Global Positioning System with a precision of 5-10 m. For one typical plot, in compartment 31, the altitude was recorded as 4.4 m above sea level. Among the three compartments, compartment number 26 was selected as an area highly affected by top-dying, where most of the trees were affected severely. The sampling was conducted in a randomized block design, in that a plot was sited within a particular top-dying intensity block, but the precise location of that plot was randomized so as not to collection. Thus in total nine plots were sampled, representing a range of top-dying intensities. Intensive field data collection was made among these nine selected plots. Observations were performed from observation towers during low and high tides, also traversing the forest floor and vegetation on foot, as well as using a speed boat, trawlers, country required to gain access.

Vegetation Recording Methods in the Field: Within each of the nine 20m x 20m plots, each adult tree was assessed for three parameters. The diameter at 1 m height was recorded (in cm) by using a tree diameter- measuring tape or slide calipers depending on girth.

Soil and Water Sampling Methods: As stated above, from the three selected compartments, a total of nine plots of 20m x 20m were selected. Fro m each of these plots, seven soil samples were collected; one from the centre of the plot, four (one each) from all the corners, and two from the middle sides of the plot. This field sampling method followed the W.H.O, U.K, and E.P.A systems of standard laboratory and field sampling principles, rules and regulations.

Questionnaire Survey of Local People: In order to establish the views of local people about the incidence and causes of top-dying, a questionnaire was prepared for asking peoples either individually or in groups. This survey was done among people living or working in the 17 Sub-Districts of Sundarbans, making a distinction between those living within and outside of Sundarbans. They were asked whether they had seen the top-dying disease of Heritiera fomes (Sundri) in Sudarbans for a long time, either through living within the Sundarbans or through visiting Sundarbans for their daily work, for their professional work such as forestry officials, for fishing or for collecting wood as wood cutters, for seasonal honey collection, or other purposes. In this way, 50 questionnaires were filled up through interview, mostly of groups and sometimes of individual people.

Statistical Analysis: Initial statistical analysis of quantitative data, particularly of the elemental concentrations, consisted of calculation of arithmetic means, standard deviations and standard error values for each variable separately. Data on the severity of top-dying for each tree in a plot, which had been recorded as ‘not affected’, ‘mildly affected’, ‘moderately affected’, and ‘highly affected’, were converted into a four-point scale (0-3), so that they could be summed and an average (median) could be determined for each plot, thus producing an index based on ranked data. Comparisons of the strength of relationship between two variables were assessed by correlation: the Pearson’s product-moment correlation coefficient wh ere both variables were fully quantitative or the Spearman’s rank correlation coefficient where the top-dying index was one of the variables. In the case of the Spearman’s coefficient, the probability of the outcome was determined by using the approximation to a t-statistic appropriate to these tests (Sokal and Rohlf, 1981). Occasionally, a Pearson’s correlation coefficient was calculated where top-dying was one of the variables, in order to check on the extent of the difference between the rank and quantitative versions for these data. Data on frequencies of seedlings or saplings in each of the plots and compartments were tested by χ2; contingency table analysis to determine whether there was an association between the selected plot type (severely, moderately or little affected by top-dying) and the three chosen compartments. A similar consideration of the different compartments as comprising one factor, and the plot type as a second, was used to test the pattern of elemental concentration s and other variables by a 2-factor analysis of variance test w ith replication. This allows an assessment of the significance, not only of the two factors separately but also of the interaction term linking the two factors. It should be noted th at the plot type was not a strictly controlled factor, since th e three categories of top-dying intensity were relative to each other within any one compartment and might not have been exactly equivalent between the three categories; interpretation of the results from these tests therefore needs to bear th is in mind. MINITAB Release 14 Statistical Software has been us ed for windows on CD-ROM, 2004 edition for all data analysis, both statistical and graphical, except for those produced automatically by the Excel package attached to the ICPMS.

  Agriculture, Forestry and Fisheries, 2014; 3(5): 329-340, doi: 10.11648/j.aff.20140305.11, ISSN: 2328-563X (Print); ISSN:2328-5648 (Online)
  http://article.sciencepublishinggroup.com/pdf/10.11648.j.aff.20140305.11.pdf
Funding Source:
1.   Budget:  
  

The selection of sites has not produced clear statistical differences in the amount of top-dying evident; probably because of the way the data were collected. However, it is believed that there is notable variation between plots and compartments, and certainly this seems to be reflected in the ability of the trees to regenerate. However, the link between top-dying and the size of the trees is not clear, with tree height and diameter not being directly related consistently to amount of top-dying, although moisture content of soil was inversely related. Since the great majority of trees present in all plots is the species Heritiera fomes, this means that the comments above are essentially referring to the response of this species rather than that of any others. So that, the Sundri, by contrast, prefers largely fresh water in which it resembles the mesophytes, but the species is adapted to the wet swampy condition of the Sundarbans by virtue of its leaves having partly xerophytic adaptations and plentiful pneumatophores which help cope with the saline swamps of the Sundarbans. The vegetation need sound ecological balanced to survive but due to deforestation, illicit felling, human destruction are responsible for the heavy metal contamination in soil, water and vegetation. The elements Pb, Sn, and Zn were highlighted earlier in this discussion, and although not all of them quite reached statistical significance. About two thirds of the elements have concentrations which are elevated compare to other reference sources in the Sundarbans. The positive trend linking two of them to top-dying suggests a likely mechanism of influence, namely that greater concentration of the heavy-metal weaken the resistance of the tree to attack by the pathogenic fungi. This might well be a process that other elements contribute to as well, but has not been picked out by the analysis as showing a link because of the variability between samples inherent in the data. In this respect, the anomaly of the negative relationship indicated for Sn is harder to explain, but a possible process might be an antagonistic response of Sn and another element, so that when Sn is less abundant the other element can have a stronger (deleterious) effect on the trees, thus allowing more top-dying to occur. Considering the limitations of the current planning process in Bangladesh, it is possible that within a few short decades, as water tables fall, rivers run dry and lakes shrivel, water–riots will become the order of the day. Coastal lands include some of the most productive of ecosystems with a wide range of natural functions, but are also one of the most threatened habitats because of their vulnerability and attractiveness for ‘development’. The first global conservation convention, the Ramsar Convention, focused solely on coastal lands and wetlands, and it has recently been strengthened and elaborated with regard to the wise use of all coastal areas such as Sundarbans.

  Journal
  


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