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Coastal Geomorphology - Science topic

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Dear All,
I have an issue regarding a sediment transportation simulation. I have computed the sediment transport rate based on a 20 years wave climate, and simulated the sediment drift for the total time span and either by monthly filtering of the data, the monthly sediment transport is also computed. However there is a problem that the summation of monthly sediment transport is much more than what I have calculated for the total time span. Is it possible this happening? Is there any reason behind this?
I appreciate it if you could share your Idea with me.
Best
Saeideh
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There are several potential reasons, which are hard to distinguish based on what you've written. However, the 'obvious' answer is that sediment transport is ALWAYS a timescale-dependent parameter. The cumulative answer will always be larger the shorter the timescale you are applying it to. This was discussed in some seminal papers like de Vriend et al (1991) and Cowell et al (2003), along with some discussion by Pilkey. For a 'light version' try Gallop et al (2015). It is one of the concepts behind 'morphological' parameters.
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  • I am trying to use the DSAS tool (version 5) for both ArcMap 10.4.1. and ArcMap 10.8 in Windows 10. I am able to output the transects, but when it comes to trying to calculate the statistic. I get an error message telling me to reference the DSAS_log (photo attached) (which does not provide a clear solution of what the error is). I wonder how to solve this problem? I have tried to re-create the baseline multiple times and am getting the same error for both two versions of ArcMap (10.4 &10.8). Knwoing that I followed the Guide and I am using (English US and mm/dd/yyyy format).
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I had the same problem and solved it by working on preprocessing. My steps were: Digitize the shorelines (with a fixed zoom scale) and create a baseline on the mainland, you may have to create both on the mainland and on the water (depending on our region). You must use shapefiles in the same coordinate system, and must be based on meters (UTM). In the case of your shorelines had been digitalized in different shapefiles, use the "Merge" tool to join all shorelines in one shapefile. In ArcCatalog, click with the right bottom in the folder you want to put your geodatabase, so go to "New" and in "Personal Geodatabase". After that, with a double click in the archive just created, click with the right bottom in the space of it, and go to "Import" to put there two shapefiles, one with your shorelines and other with the baseline(s).
Some classes and their types are required, so you should check if your shapefiles have:
- Baseline:
--> User created: id (Long Integer)
--> Created by DSAS through Attribute Automator: SHAPE_Length (Double), DSAS_ID (Long Integer)
- Coast:
--> User created: id (Long Integer), Uncy (Double), Date_ (Text).
--> Created by DSAS via Attribute Automator: DSAS_date (text), DSAS_uncy (Double), DSAS_type (text)
I leave the uncertainty field (Uncy) empty and DSAS defaults to 10 meters in this case. After that, I used the DSAS video (https://www.usgs.gov/media/videos/introduction-dsas-v50-sample-data-workflow) as a guide.
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"Coastal Geomorphology" of Eric Bird -second edition- book has a number of quite harsh expressions for me as a hydraulic engineer. It might be prepared for geologists and earth scientists. I wonder if anyone has a summary -as a presentation for example- to ease understanding the book for other backgrounds.
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I can't find a summary Amaal, but you can look inside parts of the Ebook version here
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Mangroves have the ability to absorb up to four times more carbon dioxide by area than upland terrestrial forest ecosystems, carbon dioxide is stored as blue Carbon in the sediment of the mangroves swamps and marshes and green carbon in the soils of the terrestrial forest floors, and that carbon sink forms the carbon pool, but the result obtained from the analysis of the sediment samples of both types of ecosystems doesn't reflect that quantity, the organic carbon of the mangroves swamps ranges from 36 to 69%, whereas, the organic carbon content of the soils of the terrestrial forest ecosystems varies from 16 to 66%, then where and how the extra carbon stored in the mangroves sediments as blue Carbon which is four times more than that of the green carbon of the forest soil?
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Convey my thanks for such a relevant article that nicely elaborated of the carbon draining from the terrestrial forest floors arrested in the mangroves ecosystems and that is seen at a glance, I will go through the paper later on and use as citation in my work
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In no article or work that I have managed to find is there any kind of quantification of the error in applying automatic or semi-automatic methods of positioning the shoreline. If this is done when working with satellite data, when switching to UAV images it is not done. Does anyone know how to show me readings and insights on the subject?
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The accuracy of the UAV-derived digital surface models was assessed against equivalent topographic profiles via root-mean-square error and found to be <0.21 m based on Lowe et al., 2019.
Lowe, M.K.; Adnan, F.A.F.; Hamylton, S.M.; Carvalho, R.C.; Woodroffe, C.D. Assessing Reef-Island Shoreline Change Using UAV-Derived Orthomosaics and Digital Surface Models. Drones 2019, 3, 44.
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I would like to analysis Landsat ETM+ image to demarcate the suspended sediment transportation along the offshore (coastal area).
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You used Modis and Sentinel 3 data for SPM mapping
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We want to model shoreline change and morphological changes there.
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Delft 3D is a good choice
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Has anyone used drogues, quadcopters, blimps and balloons/kitoons for mapping coastal  features and processes e.g. SAV, emergent vegetation, pollutants, oil slicks, bathymetry, currents, etc.?
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I used a quadcopter for scanning areas and develop a new map for the area to use it for civil engineering in new projects
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Coastal geomorphology, by definition, is the study of the morphological development and evolution of the coast as it acts under the influence of winds, waves, currents, and sea-level changes.
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Ensuring that the coast does not retreat due to marine geomorphological operations, in other words, that the land is not lost to water due to demolitions.
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I like to know about models or methods to make coastal inundation map.
Aim of the study: To predict and make a coastal inundation map for future sea level rise.
Study Area: Bangladesh.
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This study is novel, I am also carrying out a similar research over the Gulf of Guinea. You would need to access the topographic data from the USGS data archive, there you can download the actual SRTM/ASTER(DEM) data covering your study area. After the data acquisition, you can then perform datum conversions and re-projections. Then, you can process the Digital Elevation model for the area using Spatial Analyst tools, creating TINs, etc.
You will then calculate the levels of sea surface heights at varying distances from the shoreline.
If you have access to LIDAR images, It would generate a better inundation results.
check out this article for further explanation.
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I want to estimate the mass of organic and inorganic carbon in mostly carbonatic sand samples (90% Calcite /Dolomite). There is little evidences of clays in my samples, which add error to the standard LOI procedure. Also, I am expecting low OM (organic carbon) content from my sand samples as compared to mud flats or other type of more organic soils.
Current procedure:
  1. oven dry subsamples (30-50g) at 60 deg C for 3 days, to get moisture measurement
  2. Furnace ignition at 550 deg C for 4h for organic carbon (organic matter) estimation
  3. Furnace ignition at 950 deg C for 2h for inorganic carbon (carbonates) estimate
However, I recently came across a paper which empirically demostrated that carbonatic sand and muds with low content of organic matter (below 5%) present high variance in LOI-estimated organic carbon (using T=550 degrees Celsius).
Thus, I think I should remove salt from my sand samples BEFORE the LOI procedure.
I was thinking to simply rinse my samples with fresh water, stir it, let all the particules settle, and change water a few times, then oven dry them and procede to LOI at the furnace.
Problem:
I am worried about interfering with the OM in the sample.
Does anyone have any hint on how I could make sure that salt does not have an influence on my LOI estimate of Organic Carbon?
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Nicolas Pucino Yes, some organic material will likely dissolve depending on soak time and temperature, and quality of OM. However, if you are not concerned with sub-ppt resolution, I cannot imagine that the loss would be significant. A simple trial with a few test specimens may reveal how much mass change is associated with the water extraction.
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I want to predict shoreline change in the future by the results or data of DSAS software. Could you please give me any advice? 
Thanks so much!
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there are many mathematical and model based methods are available for shoreline prediction.
the one of the simple method is given below
Future Shoreline Change = Slope * Time interval + Intercept
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Hi ,
I am evaluating the potentials of using S2 imagery with spectral unmixing techniques to retrieve physical properties of beach sand, such as granulometry, humidity and possibly spectrafacies (intendend as discrete classes of mineral mixtures occurring along the Victorian coastline, Australia).
The endmembers I will use are processed based on my VNIR (350-1075 nm) field spectroscopy campaign (ongoing) and planned Vis-SWIR (350-2500 nm) lab-based spectroscopy of sand samples from cross-shore profiles.
I think I will use Linear Spectral Unmixing, depending of the level of intimate mix I will discover in my sand samples.
However, I find it hard to find good literature.
Any idea??
Regards,
Nicolas Pucino
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Nitesh Patidar Thx for your suggestions!
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I am gathering papers about intertidal sediment (sandy beaches) characterisation (facies mapping) based on spectroradiometry.
I am planning to go out in the field, collect sand samples from the swash zone to the backdune depositional environments, evaluate sediment charachteristics and relate them to their spectras.
The spectral profile of bare sand is almost featureless within the VIS range, however, by using a 300-1000 nm spectroradiometer, I hope I will get enough heterogeneity in spectral response to map different "sands" within a sandy beach.
The literature is full of papers about using spectra to get sediment granulometry, mineralogy, organic matter, humidity, and other variables.
However, I am looking into papers about sand classification with broader classes that intrinsically inherit the complex spectral response from their biophysical heterogeneity .
Any idea?
Nick
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Thank for sharing your views Harald G. Dill .
I will keep on investigating until I find an optimal solution.
Best Regards,
Nick
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Hi. Maybe someone know any publications containing information about the morphological division (sub-unit description) of the coastal foredunes and attached sea beach. I found only coarse units in coastal geomorphology terms like "lee\windward slope", "dune crest", "dune foot", but nothing about more fractional zoning. Blowouts are described as "blowouts" without any sub-uniting. Also with the beach - its possible to find some phrases about "berms", but nothing concrete, with descriptions or definitions of their borders ets.
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Dear Aleksandr Danchenkov,
I recently read a paper on coastal geoindicators and I think there are some references in it which could be helpful. See : Coastal geoindicators: Towards the establishment of a common framework for sandy coastal environments. @ Carapuço et al., 2016. Textbook and Encyclopedia on coastal geomorphology or coastal science will aslo help you.
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Hello everyone,
I work with the digital shoreline analysis system (DSAS of USGS) to my thesis, in the process i have a error with the calculate change statistics. The program say: "Unable to find output file 'C:\Users\...DSASCore.out.xml'
Does anyone know what the solution is?
Thanks!
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Thank you Jan Kinne and Federico Solano the error was very simple to solve. In the guide to program appears the solution.
"The computer must be configured to English (USA) and the date format must be mm/dd/yyyy. From the Control Panel menu, choose 'Regional Configuration and Language'> select 'English (USA)' and modify the date configuration to 'mm/dd/yyyy.'"...
Thanks for answering my question.
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I am a bit confused about the terminology used for Sunderban (in West Bengal, India). Is it a delta or estuarine settings.
Or I would say, Sunderban is a complex system of the delta which consists of tidal rivers, estuaries, mangrove forests and creeks.
Thank you
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Yes, as you have rightly understood, it a complex delta system criss-crossed by mighty estuarine rivers; innumerable creeks; tributaries and mangrove forests. Thanks Dr. Bayan for the map, which serves as a ready reference to the RG readers.
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Curiously, the closure of inlets is reported as a series of coastal changes associated with the 1755 and 1848 earthquakes in a Mediterranean lagoon (Nador lagoon, Morocco), my question is : what would be the process behind these closures, and are there any similar reported cases in the world?
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Inlets to coastal lagoons through sandy barrier beaches exist in a delicate equilibrium between wave-driven littoral drift of beach sand (which tends to close inlets), versus tidal curents and riverine currents (which tend to scour sand from the bed of an inlet and keeps it open). Some inlets open and close seasonally if there is a pronounced rainy season-dry season climate.
If an earthquake suddenly decreases the surface area of a lagoon, or diverts a tributary river away from the lagoon, the balance could be sufficiently upset to allow the littoral drift to close the inlet.
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Late Paleocene to early Eocene (56 to 51 Ma) interval is characterized by five distinct transient warming (hyperthermals) events (Paleocene–Eocene thermal maximum (PETM), H1/ETM2/ELMO, H2, I1 and I2) in a super greenhouse globe associated with negative carbon isotope excursions (CIEs)
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check for the very-high resolution oxygen isotope reference curves, especially in papers based on DSDP sites.
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I am looking for a magnetometer in which a survey doesn't require a base station and the diurnal corrections should not be necessary to calculate.
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Procure 3 axis digital magnetometer
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Does anyone have experience in modeling shoreline change (erosion & sedimentation) in peat soil beach ? What kind of software can be used?
Thank you
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To model and mapping longterm shoreline changes, you can use DSAS (Arcgis). If you prefer open software you can also use Station Lines plugin (QGIS). 
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Does anyone have or know of any long-term temporal records for sediment grain size (and sorting) on sandy beaches. 
We have produced a model that was found to be applicable on a number of the high-energy, cross-shore dominated, sandy UK beaches: http://www.sciencedirect.com/science/article/pii/S0025322716300494
and would be interested in evaluating its applicability to other sandy sites.
Kind Regards,
Sam
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As far as I know Prof. K. S. Jayappa in Marine science Department of Mangalore University has such data on western coastal area of the Arabian Sea. I do not have his email address.
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Even if this not the case for natural beaches, I am thinking that mega-nourishments and artificial islands in particular might be exposed to additional currents to the longshore drift generated by breaking waves.  
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Dear Sergiu,
Sorry for my late reply, but I have just had the opportunity to read your answer. Thank you very much for this extensive description of sediment movement. I found very interesting your point about the geostrophic currents as they are not wave generated; and yes I will have a look at Leo van Rijn web page.
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How can we classify oyster reefs on the basis of spatial geometry as we do for coral reefs (fringing, barrier etc)??? 
Any hint or literature share will make my ways easy.
Thank you!
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Please check the below given link and PDF attachments.
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I'm researching coastal in Nha Trang Bay, in Viet Nam by CVI. But I don't understand use it. I found a lot of document about CVI of other scientist. I just don't understand how they can static CVI for region and they divice region in the map. One more things, who can help me explain, in that link, about "Metadata file" i don't understand how they can draw some chart in sheet 1 in file name is "EAST.exl" 
Please, help me!
Thanks all!!!
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You may want to look into CJ Jackson's work using AMBUR software he developed.  Here is a document that may assist in your search:  http://southatlanticalliance.org/wp-content/uploads/2014/09/05-CJ-AMBUR-HVA-GSAA-4th-Annual-Meeting.compressed.pdf
Here also is a project that may provide useful information for you:  https://coast.noaa.gov/digitalcoast/stories/delawarebay.html
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I have parsed all of the data from a geojson file which represents the shoreline of a lake by connecting to the API of a website that has a bathymetric map of my lake of interest. 
EXAMPLE
for feature in data['features']:
if feature['properties']['OBJECTID'] != 488 and feature['properties']['OBJECTID'] != 320:
if feature['properties']['DEPTH_M'] == 0:
print(feature['properties']['DEPTH_M'])
SHORELINE_iter = (feature['geometry']['coordinates'])
SHORELINE += [SHORELINE_iter]
Shore = []
for q in range(0, len(SHORELINE)):
for i in range(0, len(SHORELINE[q])):
SHORE = (SHORELINE[q][i])
Shore += [SHORE]
x = []
y = []
for b in range(0, len(Shore)):
X = Shore[b][0]
x += [X]
Y = Shore[b][1]
y += [Y]
plt.scatter(x, y)
How may I use these coordinates as a path to interpolate various profiles representing data that extends perpendicular from the shoreline at various stations along the shoreline? I have coordinates which represent each point of data acquisition. We are sampling vertical water columns as we move away from the shoreline (towards the center of the lake) for intervals of 5,10,20 and 40 meters in order to get an idea of the variability of geochemical properties in the vertical water column as you move away from the shoreline. Should I use kriging? GIS? Python?
I can elaborate and explain more upon any questions you may have.
Thanks.
Jack
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Dear Jack, to resolve the question I suggest you a digital terrain model software as Surfer (Golden Software), simply to use. This sw can interpolate/extrapolate georeferenced points, considering the lake shore as a blanket file (impassable), and elaborate curves from your data (through the kriging, minimum curvature or other algorithm) imported/digited in a worksheet. Is possible to obtain in few minutes 2D and 3D maps (DTM, DEM, vector maps, etc.) of both emerged and submerged landscape/parameters. You could test it as free trial: http://www.goldensoftware.com/products/free-trial
Get a look at the overview...
Best, Carlo
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For the coastal area analysis I want to calculate Biomass change detection and water change detection of Landsat Data. I already run the model in ERDAS 14 for NDVI and NDWI. How can we extract biomass and water index from this processed images?
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I am looking for in-situ measurements of wave heights for the Caspian Sea. I see that people published a comparison of wave modeling results with the in-situ data, so there are data from at least a few stations available, like Anzali, Neka, Amirabad, Fort-Shevchenko, Neftyanye Kamni, Kochubey, Astrakhan, Makhachkala, but simple googling does not show any downloadable data. Do you know where can I get the data, whom to ask and how open they are?
Many thanks!
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Hi Nadia there is a website that contains tidal gauges hourly datasets of 5 local stations in northern part of IRAN (ANZALI / CHALUS / AMOL / BABOLSAR and BEHSHAHR stations ) considering the website is IRNIAN and due to linguistic difficulties I can help you with downloading the data if it is needed.the address link is as follows :
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I want estimate production rates of the biogenic fraction of coastal sediments where this fraction is the dominant one
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Dear Francesco,
You may obtain some crude chronological estimate by trying the following:
A) Select the robust taxa and observe their taphonomic state (abrasion, disarticulation, fragmentation, secondary rounding, etc.).
B) Note the annual input rate (seasonally variable) of the chosen taxa and the rate of taphonomic changes with time.
C) Use data from steps A and B to infer the antiquity (very rough estimate only) of the rehash assemblage.
Best wishes
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Can you possibly help me to identify the following images?
These were collected from the Chilika lake ecosystem dated 12.12.2008. But proper identification was not made till now.
can anybody help me on this aspect and also can you provide the available literature on this species?
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Dear Debasish 
The samples that you have posted , was living or fossil stage ? 
Best 
Aravinda 
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Is anyone working on modeling how changes to coral reefs may change coastal erosion models.  This is something I am very interested in getting into and is wondering if anyone would be interested in collaborating or has suggestions on who to speak to.  Thanks!
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Hello David,
Please get in touch with Joseph M Maina of the University of Queensland. That is his expertise, you can visit his researchgate profile at  https://www.researchgate.net/profile/Joseph_Maina8 and also his google page for his publications at https://scholar.google.com/citations?user=Go7V_2AAAAAJ&hl=en
I am also appending one of his recent publications on a study on coral reefs in Madagascar.
Goodluck,
Beckline.
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I intend to evaluate the effects of sea level rise on the sandy beaches of the insular Caribbean. Studies done by me, as part of this study, show that 75% of beaches are affected by erosion. Brunn's rule and the subsequent adjustments made, start from the principle that applies to beaches in dynamic equilibrium and these, as I said before, are not. What other predictive numerical model can I use? Would it be scientifically adequate to show that the erosion observed on the beaches is its equilibrium condition and on this basis to use Brunn's rule? I will be very grateful for your contributions, best regards.
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Hi Ridel!
With your question you are addressing a highly complex issue for which there is no simple solution. For all we know, mean global sea level is currently rising at  an average rate of about 1 mm/year or 10 cm/century. Contrary to the claim by NOAA, there is no evidence for an acceleration in the rate of sea level rise, their satellite altimetry data having been unjustifiably manipulated, as recently revealed by Mörner (and conceded by NOAA).
Thus, accepting an average global rate in sea level rise of 10 cm/century since the end of the Little Ice Age, one can offhand say that it is quite impossible to extract this signal from beach morphodynamic and sea level data in the short term because the scale of both by far exceeds the scale of sea level rise (by several orders of magnitude in both the vertical and horizontal). A possible approach would be to trace the landward displacement of the storm high-water line (transition from sand to vegetation) over as long a period as possible, but several decades at the very least. Aerial photographs would be a great asset if they are available (consult Offices of the Surveyor General).
Numerical models are of little value because the output entirely depends on the completeness and accuracy of the input data. Irrespective of how incomplete these data are, a model always gives you an answer, the reliability of which, however, is entirely unknown. Such exercises can therefore serve as useful background information but not as a solution.
As far as individual beaches are concerned, one needs to assess the overall sediment budget, i.e. whether, and if yes, what the magnitude and rate of sand supply from external sources is (streams, coastal erosion, longshore transport). As already pointed out by  Norman and Alexander above, you also need to pay attention to (perhaps) cyclical changes in wave climate induced by, e.g. the change from El Nino to La Ninja conditions, as well as regional tectonic (and neotectonic) crustal movements.
I hope my comments are of some use. You are certainly tackling a formidable but nevertheless challenging issue. Good luck with it.
Regards, Burg
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When I access the site global wave stadistics I not find specifying information about the starting year of compiling on winds and waves information of the global wave stadistics. I understand that this is information compiled for many years, but I need to know from when.
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My suggested answer is the work of U.S. Navy Lieutenant Matthew Fontaine Maury, who (1) compiled weather and sea condition information from old sailing logs, (2) asked outbound sea captains to keep regular logs of weather and sea conditions and send them back to him, (3) offer each participating sea captain a set of new nautical charts with compiled information included, and (4) published the compiled information in several books, starting about 1850.  See http://www.oldsaltblog.com/2011/11/the-wave-glider-of-2011-and-matthew-fontaine-maury-of-1850/.  (One of my ancestors was such a participating captain.)
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Any expiriences with this logger please? Interesting feature for me is User-replaceable battery. Is it easy replace it in the field? Any leaking possible? Is it apropriate to use it for measuring in-snow temperature? What is the price in your country? Thanks!
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You might also check out Onset Hobo data loggers. The old versions several decades ago were very inexpensive, and needed to be contained in a water proof capsule.  To save funds, extra protection was added with plastic whirl-pak bags as very inexpensive. The new data loggers are likely better and more expensive, and some issues with people finding and damaging, so se started to include a note on who to contact, what the temperature recorders were doing to help identifymand improve fish habitat.  I have had good results with them (Hobos) as long as not damaged,,stolen or taking on water.  The technology has improved in the last 20 years.  I have not used Tinytag, but in an earlier researchgate question, some individuals found them reliable.  I made sure we secured them in sections of plastic pipe that were cabled to strong roots or other relatively immovable oblects, hand burying cable under rocks if available to obscure detection.  It is important to provide map and description of location if the person installing will not be servicing the data loggers, perhaps even capture a picture of site.  If stream is likely to be intermittent, you may want to locate in pool, but I usually preferred sections with more velocity to avoid sediment burial if evident.
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Questionnaire is carried out in order to develop my master thesis: The impact of user-defined parameters on DEM accuracy. By using feedbacks from the users who works with DEMs the conclusion about users perception of the importance of user-defined parameters in digital terrain modelling will be performed. 
Thanks in advance to all !
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What is difference between abrasion and coastal erosion?
Is there any different factor between abrasion and coastal erosion?
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Abrasion is a term mainly related to rocky shores. Coastal erosion is a wide concept. More agents are involved in it.
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Methodologies that I have encountered thus far are 1). Ultrasonic sensors, 2) Hi-Res sonar, 3) Optical backscatter arrays (e.g., Sedimeter) and photovoltaic arrays (PEEP sensor), 4) Green-laser altimeters, 5) Load cells. 
Do you know of other novel techniques that can measure fine-scale sedimentation in the offshore environment? Any favorite commercially-available instruments?
Thanks!
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Before you even start to develop an instrument to measure the bed level you have to ask yourself, "How do I define the bed level?". What is "the bottom"? Sometimes it is very clear, but at other times what visually is the bottom is not what one would define as the bottom if probing with a stick. Fluid mud looks like the bottom but a diver can swim through it. Second, for what purpose do you need to know the bottom level? The SediMeter was developed to detect sediment transport. If the sediment transport takes place through migrating bed forms the resolution does not have to be that high, or if there is net accumulation or net erosion. But if the sediment transport takes place as sheet transport, bedload over a flat bed that does not change level, then the instrument needs to be able to detect very small changes. If it can detect the addition or removal of a single grain of sediment, then it for sure has sufficient resolution. As far as I know, only the SediMeter is capable of doing that, and that was the original purpose of me developing it 31 years ago.
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I am analysing wind speeds and directions from the Newcastle Nobby’s Signal Station AWS. This station is situated at 33 m above mean sea level and 10m above ground, at the Hunter River mouth (NSW; AUstralia). It is a coastal weather station, being located on a headland facing the ocean, south of Stockton Bight, a 34km long embayment.
As you can see from my image "WindSpeedLongTerm", I calculated the annual means for every year I had. From 2000 on the annual mean wind speeds (WS) dropped significantly to very low values.
This in turn, greatly affects the sand Drift Potential (see DP_Year image) that I calculated using Freyberger's method, essentially taking into account the wind speed threshold to mobilise sand of the granulometry, type and roughness occurring in this area, and frequency of wind above the threshold occurring from each direction.
I need your help to figur out why wind speed and sand drift potentials dropped so dramatically during 2000-2015 period.
I checked the equipment history report and except some equipment replacements and maintainence, nothin relevant seems to be happened.
The accuracy is still the same (.00) and always 3h readings (thus 8 wind speeds per day).
From 2000 on more Null Values were found (red Nas in the first image), but in my opinion not so many to justify such a drop.
I checked the Southern Oscillation Index (SOI) to see if something strange happened but nothing unusual to my knowledge (I didn't check correlations, only visual plots comparison).
According to the SOI and the Australian Bureau of Meteorology data, a prolonged moderate La Niña period occur prior 2001, then near to neutral conditions established, except some weak El Niño conditions in 02-03 and 06-07. After 06-07,  La Niña and neutral conditions dominated, with the exception of 09-10 weak to moderate El Niño event. La Niña then  dominates especially from 2010-12, where SOI indicated a strong El Niña period.
2012, 2013, 2014 were ENSO neautral all the time, except end of 2014 when very near El Nino thresholds were reached, Then early May 2015, El Nino conditions were up again.
Was the period 2010-15 a particular La Niña/neautral period in some way I don't understand?
Thx for any suggestion.
Nic
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There is usually a significant diurnal cycle in wind speeds. At coastal stations, the diurnal cycle is often even much larger than on land due to the sea-breeze system. So if you have less observations, you may end up using the time of the day where wind speeds are on average always higher or lower than using another time of the day etc. Changing the number of observations will always change the mean value systematically.
As an example, see the figure for the daily cycle of different wind farms and imagine you change the time or sampling rate... It will significantly impact the daily/annual mean. I just took one of the first examples I found on that - it may be very different for your location.
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The Swiss Federal Institute for Forest, Snow and Landscape Research (WSL) developed an intuitive photogrammetric tool for extracting georeferenced vector data directly from a single oblique unrectified image, outputting GIS-compatible files. This user-friendly and open-source platform opens new perspective for digital photogrammetry-GIS integration.
Very few inputs are necessary for performing the tool:
- The photograph
- The DEM
- The GCPs real-world coordinates
- Auxiliary files to facilitate the procedure (orthophoto, topographic maps, vector data.
Basically, the first step is the self-calibration of the camera lens, which can be performed by the tool, or by any independent software. In addition, if data about internal and external orientation of the camera are accurately known (calibration reports, metric camera), they can be added manually in the calibration process, improving the precision of the following image georeferencing and orthorectification. Once the calibration parameters are calculated, it is possible to place the photograph in the real world, so that a ray originating from the camera centre and passing through a selected point in the picture plane, will intersect the DEM in the projected real point.
Then you draw polygons or lines on the oblique photo and extract them in popular GIS format for further analysis.
Besides the input accuracies (photographs pixel resolution, DEM and camera calibration data), the accuracy of the WSL Monoplotting tool is related to the precision of the georeferencing process and the angle of the optical ray relying the DEM to the photograph. In fact, the low angle of incidence caused by terrestrial highly oblique photographs means that a small error in placing GCPs in the terrestrial photo results in larger inaccuracies in the DEM/orthophoto correspondent.
The question is:
How would you design an experimental test for its potential use in coastal settings?
I am thinking about:
shoreline shift
coastline evolution
rocky cliffs dynamics
sand-spits accretions
coastal responses to climate change
coastal engineering works
landuse changes
Thanks in advance for any suggestion.
Nic
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Hi Nicolas, it is good to hear about people doing monoplotting with oblique photography!  Thanks to you and to the other specialists giving feedback.
I have no experience extracting features from this kind of material, but I have a bit of experience in doing monoplotting (with ILWIS-ITC, there is a free downloadable academic version) and working with traditional photogrammetric photos (close to vertical).  Also, if you have the opportunity, test the PHOTOMOD software (a russian product), that is very powerful (it includes UAVs processing); you can get freely  the full version but limited to some amount of photos (no more than 15 I think, or no more that some amount of megabytes of data, DEMs, etc). I can´t remember now if it has a monoplotting option,but it is very precise and efficient for traditional photogrammetric processing, also includes satellite imagery processing capabilities. It computes authomatically the tie points using correlation and performs the relative orientation of the photos fastly.
Regarding your question, if you need to test the methodology for oblique photos, I think that the coastal locations are probably the worst scenario (what  is precisely your need). You can test the methodology over cities or places in which you can  accurately measure the coordinates.
I have had good experience processing isolated photos (again, close to vertical) extracted from videos over coastal zones and getting precise planimetric coordinates from high resolution imagery (some GIS commercial software give you access to hi-res satellite imagery when you purchase their software). For the altimetric info I have had good luck with the DEM that I got.
I am speaking of  digital photos with resolution between 50 cm. and 1 meter. Perhaps your coastal oblique photo has 20 cm. or better, for which this kind of satellite sources will be not useful. In any case you need good GCPs...
Hope this helps a bit...
Best regards
Gabriel
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Kite Aerial Photography (KAP) has so many advantages that they are at least as suitable as UAVs for monitoring coastal dynamics.
Think about it, kites are:
  1. less regulated, which means higher altitudes thus wider footprints
  2. extremely inexpensive and portable
  3. non-intrusive, licensing-free
  4. wind-friendly, the more wind the more payload, thus, more sensors (RGB camera, micro-Lidar, Multispectral sensors, IMUs, GPS)
  5. less stable than UAVs, which is good for Structure from Motion algorithms because the same point is seen in diferent angles and scales and more off-nadir images means less doming effect
Obviously zero wind means no kites.But coastal areas are windy by nature.
Moreover, if you set target points, record accurate location (dGPS), then use the targets network to orthorectify the KAP imagery, Structure from Motion algorithms produce DSMs and Orthoimages as good as UAVs.
One of the most important coastal issue that has been tackled with a KAP  approach received international attention in the 2014, when it was used for the worldwide famous Dutch project “Zandmotor”.
The point is:
Help me find at least 5 robust arguments that can refrain kites from being the next coastal monitoring tool.
Especially in Least Developed Countries or in Pacific Coutries where low-lying atolls are drowning and UAVs or fine resolution satellite imagery are just too expensive to use.
Cheers,
Nic
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Kite are already used for coastal monitoring. You are right, it is an inexpensive method. However, I agree with the previous comment: they are difficult to control and sometimes crash. And if developping, this activity might be regulated.
Coastal monitoring is not only beach monitoring... What about cliffs ?  You can pilot a drone from the top of the cliff, the drone flying at lower altitude than you. This is not possible with a kite.
Moreover, some beaches are surrounding by cliffs and therefore the flight plan of the kite may be restricted...
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Hello.
I want to calculate the CVI along a coast. I have all the data needed. What troubles me is how to calculate the slope near the coast. The easy way is just to create a DEM and then use this to assign a value to a polyline representing the coast with multiple segments.
However if i do this, i take into account only the nearest cell of the slope Raster to the coast..
If i have pixel size of 5 m since i am working with maps of 1:5000 scale i think this is too narrow and not that representive of the whole beach slope..
Maybe it is a better way if i just measure the distance to the contour of 1 or  meters and then calculate the slope that will be assigned to the polyline representing the coast?
What do you think?
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In my remember the coastal slope concern the inland behind the dune. Because CVI is sea level rise impact oriented, the slope is supposed to take into account the ability of the sea level to submerge the coastal zone. This is the reaseon why cliffs are considered as "safe" to sea level rise and barrriers, salt marshes, deltas... are potentially "very sensitive risk".
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This will be a thorny question but are there any reliable references that test these methods against other dating techniques such as OSL?
Where does it work best, what environments, preferred age range, etc. Are there instances where it can be very wrong?
I am currently reviewing AAR and ESR papers dating coastal deposits in moderate latitudes in Tasmania and there are some apparently conflicting evidence that I am trying to understand.
Any help would be appreciated.
Thanks
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Thanks Kenneth. Very helpful paper.
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As far as I am concerned, three sets of seismic facies can be discerned at the incised-valley filling system during the transgression period, namely the fluvial lag deposits, estuarine muds or sands, and a estuarine/transgression progradation. However, what is really weird when I track the infilling system at a buried fluvial channel system offshore of the Long Island, New York is that I can not find the second seismic facies - I can only find the fluvial lag deposits and onlap landward progradation. And the progradation exhibits landward is also very difficult to explain. Is there anyone can provide me some guidance to explain this infilling structure? or kindly recommend some references for me? Thanks a lot. 
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Perhaps it is the interpretation of estuarine that is wrong. The transgression of the Pleistocene glacial termination was very rapid. I published about a lake site in Maine (Borns et al., 2004), Ross Pond, with glaciomarine clays in the bottom 2 m of core, then a narrow (ca 3 cm) pyrite-rich deposit that points to anoxia such as occur in a salinity stratified lake or fjord, then organic rich lake gyttja. The transition from marine to lake occurred within 50 yrs. Other researchers examining late glacial sediments in Maine and New Hampshire (i.e. Belknap and Kelley) have published many papers about offshore transgressive sequences. Perhaps you can find an analogous situation there.
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Any specialist on this platform. In sand grade beach sediments, how do you explain the preponderance of rutile over zircon and tuormaline and vice versa while suggesting provenance?
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The predominance of rutile over zircon and tourmaline in beach sand sediments occurs when the area of origin consists of high temperature, high pressure igneous rocks, granites, pegmatites and anorthosites. Furthermore, the rutile came from schists, high pressure gneisses and metamorphosed limestones.
Conversely, tourmaline predominates when tourmaline-rich granites and pegmatites or as well as high-temperature hydrothermal veins are present in the area of origin.
The predominant occurrence of zircons points to areas of origin with mafic pegmatites and carbonatites, as well as zirconium-rich igneous and metamorphic rocks.
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I have several imagery of costal webcam deployed along the coast and I would like use them for study the regression and recovery of shoreline and beachface about different kind of beaches (pebbles and sandy).
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Dear Colleagues and Friends,
Distance can be measured from image service by using ArcGIS.
Best regard,
V.V. Than
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These structures are about a meter in diameter, displaying striking laminated structure.
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Hi Syed!
I agree with the rest of the respondents that you are in all likelihood dealing with a stromatolitic structure. For the sake of precision, these are produced by microbes (!) not algae, although in earlier days one generally spoke of algal mats. The main culprits, however, are cyanobacteria which, for a long time, used to be erroneously called "blue-green algae", hence the reference to "algal mats". Today one would preferentially speak of "microbial mats". I suggest you get in touch with Nora Noffke (Old Dominion University, USA) who is a world expert on thus structures (e-mail: nnoffke@odu.edu).
Regards, Burg Flemming
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I mainly want to calculate the portion of sand which can pass through a rock groyne due to the littoral drift. 
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Obviously, Malcolm has given a very good and detailed answer and kindly mentioned my paper.
Because rock groynes have voids, they are apriory permeable to water and sediment. Groyne efficiency can often be observed by the elevation differential. This differential was found in the paper to be the main predictor for rate of throughput and this was independent on wave environment, probably just due gravity helped reduced being submerged. There must also be a relationship between void size, void connectivity and sediment size.
One could obviously have a finer core, or have a sheet pile spine within the rock groyne to make it less permeable.
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Sedimentological data are numerous in the field of paleoenvironmental, they are often put in relation with hydrological changes on or with different milieu. However, data that can quantitatively measure flows (m3/s) are much rarer. Sedimentological data associated with calculating Froude could possibly fill that gap?
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Example of calculation of quatitative parameters of paleoflows using sedimentological data you can see in "Reconstruction of paleohydrodynamic conditions during the formation of Upper Jurassic conglomerates of the Crimean Peninsula"
A. V. Lalomov
Lithology and Mineral Resources 04/2007; 42(3):268-280. DOI:10.1134/S0024490207030066
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Meaning, we occasionally see isolated sand waves which are anomalously tall and steep, albeit with a relatively short crest length. The surrounding scour is identical to the scour around a bluff body such as a cylinder. I feel sandwaves may build to a tipping point, beyond which some sort of change in flow regime takes place(?) Is this described in any literature? These sand waves are from the North West Shelf of Australia. Thanks.
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 A simple model used for different purposes (pdf attached) by the way we have the sandwave as an complete outcrop
The shells are acting as sedimentary particles
The evidence from sedimentary structures and the stratigraphic and biostratinomic context of shell layers are used here to describe how shell beds are formed within a sedimentary sand wave. Shell beds in the Pliocene San Nicola´s Formation,
within the Baja California Central Domain, were accumulated through the physical processes of gravity induced flow currents. The hydraulic regime and sedimentary differences between the up-current slope and the leeward slope part of
the sand wave can be explained by flow stratification. The taphonomic differences between the fossil concentrations of the bottom and the upper layers in the leeward slope are a result of a change in the current dynamics for the basin. The
leeward slope side of the sand wave represents episodic, short-term, dynamic bypassing in gravity-induced, low-flow current beds creating shell beds.
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I know how to about cross validation in RMSE for past shoreline calculation.
Here I have attached an image showing exactly what I am asking?
Please can anybody help me.
Thank you
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thank you Mr. Van
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Which image(sensor) and method(technique) can result in more accurate results?
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The real answer depends upon the estimated amount of shoreline change for the are in question.  One to two feet of shoreline change is not detectable within satellite imagery, whereas 30 to 200 feet of change would be.  High resolution aerial imagery is best for electing and measuring small mounts of shoreline change. Also, the precision of the spatial geometry is potentially the most important parameter to be aware of.  If the imagery spectral resolution is 1 meter or less, but the spatial resolution is 3 meters or more (as most satellite imagery is) then you can not be sure that your amount of shoreline change measured is than the spatial resolution. In fact, the estimated error would be double the spatial resolution, meaning the placement of your shoreline will be somewhere within six meters of its location in the image.
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RMSE = sqrt (calculated - actual shoreline divided by tth transects).
I am using by DSAS, please any body help me.
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Hello Vasudevan -
I am not certain that I understand the question.  Are you saying that you have RMSE estimates and want to know what values went into estimating them?  That would appear to be a problem that has many possible solutions. I mean, the solutions are not unique. Many values could have given the same result.  
Perhaps I do not understand. Could you supply more details for everyone? 
Cheers - Jim 
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As distinct from State/local council policy & guidelines & theoretical modelling  for climate change and coastal recession,I am interested in looking at adaptive or barrier based models specific to identified "at risk" locations on the Western Victorian Coastline. Sandy beach front communities in particular with minimal land area for urban expansion.  
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Hi David, - Risk models and vulnerability assessments and work on the Western Victorian coastline is quite limited, perhaps considering looking at the latest Victorian Coastal Strategy 2014, and the Victorian Coastal Hazard Assessment 2012 for relative citations on coastal process modelling. Hydrology and geomorphology models could assist. 
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I am trying to find information or examples of beach nourishment in macro tidal areas. Mainly, I want to have an idea of the challenges faced when dealing with these kind of designs.
In the areas I'm looking at (6 m tidal range, 5 - 50 km fetch, no swell, low gradient profile), medium to fine sand is found only in the subtidal and supratidal region, with the intertidal region composed mainly by gravel. This might point to the use of hard engineering methods as well.
Any help is appreciated.
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Juan Carlos,
There is excellent experience in the UK with beach replenishment in macro-tidal ranges - especially gravel beach replenishment. The CIRIA Beach Management Manual (2010) is perhaps the "go to" information source for our practitioners when considering a potential scheme. It was free to download for those registering onto CIRIA's website back in 2010/11 when it was published. From what I can see the free download has been discontinued. Do try to see if you can find a free download from CIRIA, but if not a wider web search for a download of the manual might be productive. This manual is absolutely excellent and I really cannot recommend it strongly enough - its vital for all applied coastal scientists working in macro- and meso- tidal environments!
I estimate the challenges involved with beach replenishment in macro-tidal environments as follows:
1. Potentially large quantities of recharge sediments would be required to cover the long cross-shore profiles. This is a key issue with sand recharge as beach gradients are lower and profiles are longer. A second related problem is that its very difficult to control longshore transport losses using groynes as the long profiles mean that groynes would need to be uneconomically long and high. A successful scheme I know in this category is the "Lincshore" replenishment on the Lincolnshore coast (tidal range 5 to 7m). Its a very large and expensive scheme that has involved several cycles of replenishment, but it is seen as sustainable as the beach performs very important coastal defence and amenity functions and there are appropriate sources of marine dredged sand available. a paper can be downloaded from the following link: 
At Blackpool  (8m tidal range) the UKs largest coastal resort town has been protected by a major new sea wall rather than a replenishment scheme due to concerns about the quantity of replenishment sand required and its potential stability on the beach if constructed. 
2. There are concerns of offshore loss of replenished sediments in areas with high tidal range. Risks are lessened in the case of your beaches since the short fetches mean lesser exposure to high storm waves. However, there are also risks of sediment loss due to tidal currents if there are any tidal channels or fast flowing currents near to the toes of your beaches.
A solution would be to consider gravel rather than sand replenishment as gravel is preferentially retained on the upper portion of the beach profile and is less easily transported seaward during storms - also it generates steeper and shorter profiles. It does however remain susceptible to losses if there are tidal channels adjacent to the toes of your beaches. Best practice is to try to source replenishment sediment that is on average a little coarser than the indigenous gravel at your beach. Its OK if there are some finer sediments incorporated, but large quantities of intermixed sand are not recommended as it can significantly reduce beach porosity and hence increase risks of offshore losses in the early stages before the replenished beach can become naturally sorted. If there is significant drift on your beaches then you may wish to consider using short rock groynes to control the upper beach. Another possibility could be to use a longer terminal groyne at the downdrift end of a beach to collect drifting gravel and then excavate and truck it back updrift and reintroduce it to the beach (recycling). Good beach monitoring is required to optimise such management operations.
If appropriate sources of gravel for replenishment are not available reasonably close to your intended scheme sites then you may wish to consider a sea wall and/or rock revetment scheme. If your beaches are heavily depleted be aware of the potential problem of wave reflection and toe scour that can be caused by constructing sea walls on such beaches.
I hope the information is useful and I wish you success in your feasibility studies.
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I want shorelines data (lat&long) and i can't find it for all of world , for Mesh construction in sms (http://www.aquaveo.com/software/sms-surface-water-modeling-system-introduction) , i have it for persiangulf ,, for us i can download it from noaa website (http://www.ngs.noaa.gov/NSDE/) but for elsewhere i don't know !!
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Have you tried the Global Self-consistent, Hierarchical, High-resolution Geography Database?
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Is it suitable to conduct a mangrove propagule dispersal simulation using MIKE 21 advection/simulation module?
Can anyone suggest what other module in this software is also suitable for this simulation with tidal and salinity as its input field data?
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Hello Atteleth, 
I personally don´t think you should use the advection/dispersion module from MIKE 21, which takes into account decay of the modeled substance. What you can do is do a MIKE 21 HD simulation and then in plot composer add particules. This particules will move according to the hydrodynamics in your modelling and they can give you an idea of how the propagule will distribute in your study area. An alternative is to use the ABM from MIKE 21, which allows you to determine how the propagule will propagate, but since they are only floating, then I guess there is no point on complicating your study!
I hope this helps. Cheers.
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I'm trying to find information for estimating the beach response to an underwater landslide in a sandy beach (medium sand).
The crown of the landslide is located near the lowest astronomical tide level, thus it is influenced by wave action in low tide (tidal range ~7 m). The beach is located in an inland sea, therefore it is influenced only by local wind waves of Tp < 7 s and Hsig < 0.4 m 65% of the time.
In the original profile, which was generally stable during a very long time (there is no historic evidence of change), the beach slope was 0.1 in the intertidal zone with a change to 0.4 in the underwater region. In the new profile, the intertidal slope is maintained, but the position of the slope change moved onshore and it is now 0.3 (see attached figure).
The beach was formed by successive pre historical alluvial landslides in a very sloped area. Water depths up to 500 m are found 1 km offshore.
Thanks in advance.
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Hola Juan, if you look at Figure 3a in the below from Pisco Peru 2007 tsunami you will see a tsunami runup induced slump and wrackline on Playa Tunga along Bahia de la Independencia’s desert coastline (sandy desert beach and continuous desert sand inland). This location is south of the Paracas Peninsula in Peru.
Fritz, H.M., Kalligeris, N., Borrero, J.C., Broncano, P., Ortega, E. (2008). The 15 August 2007 Peru tsunami runup observations and modeling, Geophys. Res. Lett., 35, L10604, doi:10.1029/2008GL033494.
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I am currently pursuing my PhD studies in streambank erosion monitoring studies. However, this kind of study is still lacking in Malaysia. There's no devices installed by our authority to monitor streambank erosion especially with heavy storms in Malaysia. I am currently using conventional erosion pins to monitor streambank erosion. I would like to compare the manual method with PEEP sensors as it is more accurate and provide automated instruments for continuous bank erosion measurement. 
Thank you
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The PEEP can use to monitor the real-time change of beachface ?
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I am confused, this i started beginner in this field, how to calculate shoreline erosion and accretion in arcgis, Now i have digitized different years of shorelines. now what will do next, so experts pls give me your suggestions.
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Well, what you could do is: 1. establish a series of control points along your digitised shorelines, with profile lines perpendicular to the shore at these control points. 2. Use the measure tool in ArcMap to measure the distance between each different epoch (age) shoreline along these profile lines. 3. Divide the measured distance by the time difference for each digitised shoreline. This will give you rates of shoreline change (positive for accretion, and negative for erosion) at each profile/control point location. This is, obviously, the manual way of doing things, and something that I had to do to calculate rates of change for my PhD and is, therefore, something I am very familiar with.
Another method is to use the Digital Shoreline Analysis System - available from: http://woodshole.er.usgs.gov/project-pages/dsas/ . This is a freely available shoreline analysis add-on for ArcMap, which can calculate rates of change statistics for historic shoreline data. I haven't actually used it myself, although I did get as far as downloading one of the older versions, but I would go for this first. You can always try the manual way, if you really want to, at a later date.
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I'm trying to detect maximum run up occured during nigth from a coastal video monitoring system. Attached is typical image where soil moisture difference is quite obvious, some times is not that much. 
Any suggestions are welcome
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Take in mind that water strongly decreases its reflectance when move to the Infrared. If it is not possible for you take NIR or SWIR images, tray at last to “play” with the Red region of the spectrum.  
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Although I have been able to get most of the information related to Landsat 8 and its bands from landsat.usgs.gov website, still, I haven’t been able to explore the complete potential of its bands, especially the new Band 1 (Coastal/Aerosol Band : 433-453 nm) and its application in coastal and near shore processes research. I tried searching for previous research articles in using coastal band but I was not quite satisfied with the search results.
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Dear Dr. Hubert, this is an excellent research paper link which you have provided by Vanhellemont & Ruddick. Precisely what I have been looking for. I have started following your updates. I see that you have also done some work in 'ocean color remote sensing'. Are you still associated with the coastal water study in Hanoi? Thank you so much for your pertinent answer. 
Dear Dr. Mauricio, you have a very keen sense of observation. This is a brilliant idea. Thank you for this first-rate research paper. Those guys in Scripps have been doing some great quality research. I am deeply thankful for your efforts in putting together these significant research papers related to S.California bight and Chile's river plumes. Have you also been doing your research in Chile area?
These are some of the finest answers I've received so far for my question. Since I am just a budding researcher my motivation has always come from being able to observe things by 'standing on the shoulders of giants' like you. Therefore I will be indebted if you have any advice, suggestions or recommendations in order for me to do some quality research which would be beneficial for humans and mother nature alike. Right now I'm at the stage of collecting and examining closely relevant research papers related to remote sensing of coastal regions, all the possible threats which might range from small-scale sand erosion to mighty coastal hazards and the prospect of planning mitigation measures along with analyzing pre and post disaster scenarios for coastal resilience. Conservation of biodiversity in these regions is another area of concern for me.
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The archaeological record is useful to look at in terms of palaeo hazards but has not been utilized that much yet.
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We sent two interesting cites on the subject:
Lario, Javier; Luque, Luis; Zazo, Cari; Goy, José Luis; Spencer, Chris; Cabero, Ana; Bardají, Teresa; Borja, Francisco; Dabrio, Cristino J.; Civis, Jorge; González-Delgado, J. Ángel; Borja, Tsunami vs. storm surge deposits: a review of the sedimentological and geomorphological records of extreme wave events (EWE) during the Holocene in the Gulf of Cadiz, Spain César; Alonso-Azcárate, Jacinto. Zeitschrift für Geomorphologie, Supplementary Issues, Volume 54, Number 3, July 2010, pp. 301-316(16)
M.A. Rodríguez-Pascua, R. Pérez-López, J.L. Giner-Robles, P.G. Silva, V.H. Garduño-Monroy, K. Reicherter. A comprehensive classification of Earthquake Archaeological Effects (EAE) in archaeoseismology: Application to ancient remains of Roman and Mesoamerican cultures. Quaternary International 242 (2011) 20-30.
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I have kept attention on the quantification of the contribution of each organic matter source to the coastal salt marshes. In general, carbon and nitrogen radioactive isotopes are used in the mixing model to calculate these contributions. However, these two indexes are not enough to solve the model when the number of the organic matter sources is larger than three, which might include autochthonous source like plant debris, and allochthonous sources as fluvial sediment, off-shore planktons, benthic algae, etc. In that way, C/N ratio can be an index used in mixing model for source partition and contribution calculation ?
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C/N ratios of bulk organic matter are cheap and easy to determine with high accuracy. However, the problem is that the C/N ratio of each and every organic matter source varies greatly, and not just with the tissue type of the source material (there is great differences in the C/N ratio between woody tissues and leaf tissue of the very same tree, for example) but also with the level of organic matter degradation. In a forest, the leaf litter on the ground may have C/N ratios between 20 and 30. In the underlying topsoil the ratios will have dropped to values between 10 and 20. Degraded organic matter in some clay-rich tropical soils (e.g. oxisols) can have C/N ratios down to 8. Litter and soil are already two potential end-members on the terrestrial side with great ranges in their individual C/N ratio. Plants from the littoral zone have variable C/N ratios, bacterial biomass has very low C/N ratios (~4) etc. ...
As you already recognised yourself there is a great range of sources, definitely more than three, and organic matter degradation will just add further variability. It depends on your study site. In some settings, where long-distance transport processes have averaged out the details, C/N ratios may well work to identify, for example, phases of generally higher or lower terrestrial input. However, using C/N ratios to disentangle contributions from anything more specific than the usual aquatic vs. terrestrial organic matter sources, I'm afraid, this won't work. This requires a multi-proxy study and organic-geochemical fingerprinting of the potential organic matter sources in your study area. Isotopes are a good start and biomarkers are very useful, too.
Hope this helps.
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I'm looking for methods to make measurements of sediments transport close to sea bottom along shore from different direction. I'm looking for simple sediment traps which are used to measure such horizontal transport.
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You can find a brief description of varius methodologies in :
Balouin.Y., Howa.H., Pedreros.R., Michel.D. (2005) Longshore sediment movements from tracers and models, Praia de Faro, South Portugal., Journal of Coastal Research, Vol. 21, n°1, pp. 146-156.
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Concerned about the degree of sediment compaction at depth in the Wax Lake Delta in the Atchafalaya Basin, Louisiana.
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Deltaic systems are so dynamic (on a spatio-temporal scale) to a level that it is near impossible to estimate their variations. Further, 5km is too great a distance that may show numerous variations.
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Does anyone have any links to any references on this?
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Dear Tran Thanh
Yes, there is, provided the beach slope and mean grain size are both measured at mid-tide level. This was already shown by Bascom (1951) Relationship between sand size and beach face slope. Transactions American Geophyssical Union 32:866–874. This simple empirical approach does not require any high-tech equipment other than an angle meter (e.g. a Bevel-Box) but still gives a very good first-order impression of beach morphodynamic state and its temporal evolution if slope angles (and mean grain size) are measured frequently at the same location(s). An improved plot can be found in Flemming (2011: Geology, Morphology, and Sedimentology of Estuaries and Coasts, page 17-19, Fig. 13) and Flemming and Göttisheim (2013: Geo-Marine Letters 33, Fig. 8). Both papers can be downloaded from my publication profile in ResearchGate.
Best regards
Burg Flemming
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SPH is used equation of state P=B[(rho/rho0)^gamma-1]. Gamma-score is different for each material, e.g. water=7, gas=1.4. I want to know what is this score for gravel, sand and/maybe soil.
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I am quite late but here are some explanations about the Tait equation. It was established in the 19th century according to experimental results on sea water. The gamma coefficient has nothing to do with some volume weight. It is only a coefficient used to get close to experimental results. Trying to use this equation of state with sand and/or soil seems to be out of its domain of use.
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When monitoring coastal erosion or accretion by remote sensing data, a common difficulty is the determination of the coastline. Where is it located on the coastal profile in the dominated – tide and dominated - wave coasts? Can you share your experiences?
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In general set the coastline using remote sensing techs is quite tricky. According to my experience the accuracy of any methods depends on the amount of field data you have (number of images, local tide prediction, wave climate, etc). That's why we had been using Video cameras in conjunction with tide measurements and topographic surveys to set the coastline position. Using such a system you will be able to build a huge database of coastlines for each wave-tide condition. There are many algorithm to estimate the coastline position from video images (i.e: Plant et al., 2007 "The Performance of Shoreline Detection Models Applied to Video Imagery" and Almar et al., 2012 "Video-Based Detection of Shorelines at Complex Meso–Macro Tidal Beaches"), but none of them work for all conditions. Changes in light, bright, solar radiation, clouds, sand reflectance, etc may affect the detection process and also the accuracy of the method. However, those methods may work with satellite images as well.
For a more general view on RS techniques applied for Shoreline detection see Moore (2010) "Shoreline Mapping Techniques".
Hope it will be helpful
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Equations which allow to measure shapes quantitatively for each piece.
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Amr Saleem,
I was wondering if you were looking for an image processing system, in such case the answer depends very much on the dataset you are going to use. Automated recognition from single images isn't working perfectly as yet in gavel environments.
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For my thesis I need soil samples from meander loops, the depth of sampling must be about 2 meters. Actually I don’t have any developed tools for sampling. The important data that I need from samples is grain size and cohesion of soil in different depth.
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I drilled lots of meander cutoffs for my PhD with a 100mm diameter commercially available hand auger set. Different auger heads are available for both sandy sediments and for more clayey sediments. In my meander cutoffs which had filled with a silt-clay plug, I used the 'soil' auger head until I reached the sandier former bedload sediments at depth where I switched to the 'sand suger' head. It is easy to extract sediment samples at 5-10 cm intervals from the auger heads with a dinner knife and collect the sediments in plastic bags for laboratory processing. Attached is a book chapter that outlines some of this work - hope this helps!
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The first is open-source, the others are expensive suites. Is there any drawback in using Xbeach for long-term modeling (10 years simulation) on a shoreline of about 25 km?
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Dear Filippo, you are talking about very different tools and as all numerical models there is not the "medicine for all illnesses". First of all, you must realize that none of the tools available at the moment can cope with a 10 year simulation over 25 km of coastline! For sure it is not very feasbile with 2-d or 3-d computational domains, where even building a grid over 25 km would make you miss all coastal features, unless you have a 25 km straight coastline, which I doubt. Over such a space you are forced to work in 1-d mode and for this I think Xbeach is far better that other models at least for dune-beach erosion. The fact is that to run 10 years of waves will not be easy, unless you play around a lot with time-scaling, which may make the mode unstable. If the 10 years of waves means instead a wave climate representative of those 10 years, that is a different thing. I hope it helps
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I've played with proxies from bathymetry at large scales or lidar data where available, but this is not very satisfactory. My goal is to compute wave reflection from shorelines (see Ardhuin & Roland JGR 2012).
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I don't have an answer. Just to say that I'm interested too in knowing data base of shoreface slopes.
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You may know that coastal regions of Bangladesh are irregular. As far my knowledge, there are very scanty of records on it. I am interested to study the coastal morphological phenomenon of this coast. If anyone of you have any experience regarding this matter, please share your experience.
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You can build a polygon of the shape of your study area and measure the area of this polygon. If you measure the area over time, you can obtain the quantitative change over time.