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Anyone has field experience on eficiency of using this type of casting traps (image attached) versus more "traditional" pots ? If applied to the blue crab, would be optimal.
The idea would be to use these casting traps to cover a wider geographical area (also more replicates) on a much shorter time period. And avoid the trouble of going once to deploy the pots and having to go back one or two days later to retrieve them.
Any thoughts or knowledge on any study carryed-out with such casting traps would be well appreciated.
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Hi João ,
The crab rings are widely used in brackish waters of India, especially from south-west coast for mud crab. Since this fishery is sustenance level, reports is very limited. Currently, we working on traps and pots of India, a review article on this underway. I'll share you once its published.
Best wishes,
Chinna
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Several studies have been described the Pollution Load Index (PLI ; Tomlinson et al. 1980) to assess the extent of pollution status of the trace metal in a site of interest. The pollution load index is calculated as the nth root of the number of multiplied contamination factor (CF) values. However, practically say for example concentration of lead (Pb) was very high, but 9 other metals very low, your answer is going to be low (say for example (baseline level; 1)>PLI; indicating not deterioration by metal pollution)!! How PLI of a site really can be reliable information? Please help me in this regard. Advance thanks
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Effectively, the PLI softens the differences that exist between the evaluated metals, being able to deliver a misinterpretation of the real state of the sediments under study, but we must not forget that this index is only a tool that allows to unite results under a single value for a better compression of the system under study. Therefore, the first is an expert evaluation of each of the individual parameters and the PLI later to improve the understanding of the metals analyzed as a whole. An evaluation of metals in sediments can not be based only on the PLI is a complement to facilitate the overall interpretation.
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Can anybody explain possible effects of estuarine mixing on  benthic distribution, especially salinity and feeding behavior?
Which zone would be the benefit of high diversity?
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Dear Jayachandran,
you mean all living beings? reaction is too different. But working at the lab of the Danube and Limans (Estuaries) we found several interesting facts. Even desalinated the Estuary never lose completely its marutime or brackish water fauna. Look, please, my last presented publication about the Sassyk ciliates fauna! As well  what happened with this ineresting freshened basin after desalination are gathered in our book (as well my site). If estuary is of some large river and practically fresh, so marine fauna can penitrate over the deep relict river bad and it can be the very upper part of this type Estuary. Moreover  in this relic river bad is concentrated hydrogen sulphide that is suitable for anaerobic organismes od marine origin. I wrote about the Dnieper-Bug Estuary. As about tides it can stimulate exchange of the organismes but is not comfortable for a stable fauna. Therefore in the locality of the Estuary with abruptly changing regime it will be enough poor fauna, eg especially if salinity will be changing from 1-2 over 5-7 promille diapazone and back.
Extra interesting can be redistribution of the primary production of phytoplancton that can be consumpted in the deeper layers and in benthos...
I have enough much books on the question, so if necessary, call me by RG mailing, Will send.
Andrey
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Can someone please help me to get some good references on the following:
1.     Stable Isotope analysis in estuarine or marine water
2.     Suspended particulate matter determination,
3.     Dissolved Inorganic nutrients analysis in marine water.
I will be really thankful.
Kind regards
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 Dr Faizul Nisha  Thanks a lot. I am sure these will be a great helo to me.
Kind regards
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I am going to use WEAP to simulate model of river basin system in estuaries area regarding water supply and demand. 
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Again. Thanky you very much, Mr William and Mr. Mahdi
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I'm currently researching on the photosynthetic activity of phytoplankton present in estuarine waters and how it is affected by pollution. I would like to know if there is a best way to measure the water quality? And if that is sufficient to measure the photosynthetic activity in the water.
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Dear Victoria, I would have a first question before. How is the turbidity in your estuary? A very large amont of estuaries are turbid or even hyper turbid and this prevent this kind of estuary from blooming with phytoplankton. So the photosynthetic activity can be very much reduced or close to null because of the poor water transparency. So in turbid estuary it may be not so simple to disentangle the effect of pollutant from the effect of suspended mater unless you work in experimental conditions.
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Is the Moynapara tidal creek (as Das, Gautam K, has mentioned in the article called "Holocene tidal flat sedimentation in the Sunderban Biosphere Reserve, NE India" published in Coastal Zone Management journal, spl. publication, vol.2 in 2000) same as the Kalnagini Khal (as mentioned in the topographical sheet published in 1972 by SOI)?
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Try MNDWI water index with Landsat 5-8 / SPOT 5 imagery. 
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As far as my observation, Nypa inhabit on the stream edges where it can constantly receive salt and fresh water. So I am just wondering to know, could this species make a wide homogenous patches like other mangroves (e.g., Rhizophora spp.), away from stream edges. Any published literature to substatiate its habitat preferences would be more helpful. Thanks! 
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I think Nypa can survive in mangrove in inlands also where tidal waves are frequent. Global Invasive species database says
"Nypa fruticans (nypa palm) inhabits estuarine habitats from Sri Lanka to the Ganges delta to the west Pacific. It grows up to 10 m tall and produces large buoyant propagules that are dispersed with ocean currents. It was intentionally introduced to Nigeria, and has since spread to Cameroon. In the Niger Delta it invades deforested and exposed mudflats and forms dense monospecific stands which outcompete native mangrove species. The lack of stilt roots, absence of leaf litter and dense structure reduce estuarine habitat and may negatively affect native biodiversity."
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Collected from an estuary
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It looks much more like a seed
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I work on a numerical model for investigating the structure of density and salinity in tidal estuarine system..How much is the Richardson number range in a estuarine system?
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Dear Heron
It is very difficult to provide a range. It all depends on many factors such as salinity, depth, height of tides etc... as you know about them. A very broad figure may vary from 0.01 to 10. The attached paper may help you in many ways. 
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Why sediment methanogenesis is happening over denitrification in the estuarine environment..?
What is the sequence of processes in an ecosystem?
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I suppose by "over" you mean "before" or "above in the sediment". A normal sequence of processes is that denitrification occurs higher in the sediment column than methanogenesis. Denitrification zone is followed (in the downward direction) by zones of Mn and Fe reduction, then sulfate reduction, and then methanogenesis. Some overlap is normal, but I would be very surprised if you indeed have methanogens outcompeting nitrate reducers. What is the system you are studying and what is the evidence for methanogenesis and denitrification? 
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Does anyone know a conservative tracer that can be used to differentiate the relative contribution of water from different tributaries in the upper reaches of an estuary (Salinity≈0), such as the Pearl River Estuary which is consisted of 3 tributaries?
What parameters I have so far are listed below:
Temperature,Salinity,DIC,TA,DO,pH,d13C-DIC,DIN,DIP,Ca2+,TSM,POC
In my case, the Ca2+ and TA could not be effective tracers. 
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We have often used conductivity as a conservative. For example, suppose we have only one streamflow measurement below the confluence with a tributary, and also have measurement of conductivity above and below the confluence and in the tributary. Then, using a simple mixing equation and assuming conductivity acts as a conservative, you can calculate the flows in the upper stream and in the tributary. We also use conductivity balances to assure that our flow measurements are correct. 
This works because total dissolved solids (TDS) which is a good conservative tracer is usually proportional to conductivity. In our day-to-day work we seldom actually estimate TDS, and simply use conductivity as if it was a concentration of a conservative material. 
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In digesting the filtrate of particulate, particle and suspended particulate matter which one is the best methods by using total digestion, leach or combustion for identifying REE concentrations .
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Dear All,
Thank's so much for the answers and ideas. Very useful for my research.
Regard's
Zolhizir bin Daud
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Would any scientist provide me some detailed regarding the query? Why the natural productivity and food production potential of estuaries are so high? 
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If the nutrient potential of the estuary is too (unnaturally) high, several people mentioned eutrophication, secondary production may drop (even precipitously) due to events like hypoxia and anoxia, harmful algal blooms, jellyfish predation on larval nekton, etc.  We already have too many "dead zones" due to sewage input, agricultural runoff, etc.  Don't think we want any more.
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How to compare or correlate estuarine primary production, secondary production & tertiary production with benthic faunal production? How to quantify and model these components in estuarine system?
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Can i know more about GLMmodel
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Thank you for the answers. Based on your suggestions I searched some articles. The link below seems to be useful for better understanding.
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In my study, I want to know of some related research about past sea level change in the area of Chesapeake Bay.Even though there are some articles about sea level change in last 100 years and models to simulation for the future.But ,our focus is the situation in the timescale of holocene,so I would appreciate if you can provide me some articles containing information or data about sea level change in Chesapeake Bay,especially in the holocene.
Thanks a lot. 
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Please look at this: Bratton, J.F., Colman, S.M., Thieler, E.R. and Seal, R.R.I. 2003. Birth of the modern Chesapeake Bay estuary 7.4 to 8.2 ka and implications for global sea-level rise. Geo-Marine Letters, v. 22, 188-197
My comment: The ca. 20 m rise is less likely.
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I was searching for some papers related to different sources of nutrients to the Cochin estuary. I could not find the common ground about the source of water discharges. It would be great if anybody suggest some papers.
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Not related to this estuary, but papers from Spiteri et al. in 2008. are good source of knowledge on the topic in general.
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Australian estuaries are mainly acidified by acid sulfate run-off. But how many of them?
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Have a look at http://link.springer.com/book/10.1007/978-94-007-7019-5 it is a synthesis of the actual state of many Australian Estuaries and the perspectives for the future. I know they talk about acidification in few chapters.
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Does anyone study Annamox bacteria in the marine and estuarine system?
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Hello Jabir.
I think you are referring to Anammox bacteria (not Annamox).
I think these authors studied the Anammox in marine systems:
Rysgaard, S., Glud, R. N., Risgaard-Petersen, N. and Dalsgaard, T. (2004). Denitrification and anammox activity in Arctic marine sediments. Limnology and Oceanography 49(5): 1493-1502
Tage Dalsgaard, Bo Thamdrup, Laura Farías, Niels Peter Revsbech
Anammox and denitrification in the oxygen minimum zone of the eastern South Pacific
Limnology and Oceanography 01/2012; 57:1331-1346
Good luck with Anammox