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Hydrogeology - Science topic

Hydrogeology are includes people interested in groundwater resources, groundwater quality, groundwater modelling
Questions related to Hydrogeology
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Hello, I am currently working on my undergraduate thesis, which focuses on modeling seepage through a dam. I am exploring the use of MODFLOW for this purpose, as it is widely recognized for simulating flow through porous media (based on information from the USGS website and my advisor's suggestion). However, I have been struggling to find relevant papers, case studies, or comprehensive tutorials to guide me in this specific application, which has left me feeling a bit overwhelmed. Additionally, the numerous add-ons and plugins available for MODFLOW make it challenging to understand their differences and how they might apply to my work. I would greatly appreciate any explanations, references, or resources that could help me better understand this topic. Thank you very much!
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Добрый день!
Могу проконсультировать по вопросам аналитического решения задач фильтрации через грунтовые плотины различной конструкции - нужно конкретизировать вопрос.
Многое можете найти в работах Анахаева К.Н.
anaha13@mail.ru 20.01.2025 .
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Importantly the features and the parameters to be considered
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yes I have enough information for assessment along with real conditions, I try to project management by changing data
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Software such as SOLVEQ-XPT, RTest and GeoT.
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Hi I think WATCH program is sutable.
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modern applications
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Stereo aerial photos at appropriate scales are useful for studying the land forms and drainage systems. They are also useful for identifying lineaments, vegetation characteristics, which could be useful in locating potential groundwater sources.
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LAND SUBSIDENCE
Whether capturing the minute variations in earth’s surface using continuous Global Positioning System; or, Extensometers; or, Interferometric Synthetic Aperture Radar would justify the spatio-temporal extent of land subsidence resulting from "petroleum" ‘reservoir compaction’?
In case, if we have a rise in groundwater table; or a groundwater recharge that directly leads to ‘soil swelling’ or an ‘uplift’ respectively (right above the petroleum wellsite), won’t the resulting soil behavior in the unsaturated zone lead to a significant subsidence at the surface level?
If so, then, how could we correlate such a land subsidence to be associated with (petroleum) reservoir compaction in the absence of a proper hydrogeological investigation?
Since, there is no actual reduction in piezometric level within the confined reservoir (pay-zone) thickness, whether, is it becoming too difficult to effectively analyze the mechanism of land subsidence associated with a petroleum reservoir (even, if we manage to deduce the data on the changes in reservoir thickness as well as compressibility)?
In case of a petroleum reservoir, whether the distribution of stress at the interface of a seal and the reservoir would follow the simple correlation, where the ‘total vertical stress’ remains equal to the summation of ‘reservoir pore pressure’ and the ‘effective stress’?
How do we ensure whether Terzhagi’s one dimensional consolidation theory (in the vertical direction) would remain highly sufficient; or, should we also consider the Biot’s coefficient taking into account the load transfer (or maximum and minimum horizontal stresses) on the lateral horizontal directions in deducing the changes in reservoir thickness?
Do we have a direct mechanism by which the data on (petroleum) reservoir compaction that would directly get translated into its equivalent land subsidence in the absence of directly measuring the changes in earth’s surface and reporting the land subsidence using InSAR?
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I don't know if this is helpful because it pertains to groundwater but it might lead you somewhere useful. There is a long is history of major subsidence in the Houston area that might have led to published academic research. https://uh.edu/news-events/stories/2022-news-articles/october-2022/10112022-houston-subsidence.php
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In the literature, there are graphical (approximate) ways to estimate AEV from the soil water retention curve. I wonder, how can one more accurately estimate AEV according to its definition: the suction value at the transition from a saturated to an unsaturated state.
Assuming one has volumetric water content (VWC) vs. suction measurements from laboratory tests (HYPROP test), how can we leverage these values to estimate AEV?
Is it sensible to choose the suction value corresponding to the second largest VWC as the AEV?
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Kindly take a look at my recently published article where we've introduced a new formulation incorporating the air entry value. To apply it, simply fit the experimental data points to the corresponding mathematical expression - equation 23 for volumetric water content, and equation 24 for saturation. You may conveniently access the article on ResearchGate
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Can some elaborate on the geochemistry/hydrogeology ?
Thank You
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Climate change, environmental degradation, and deforestation can all have significant impacts on groundwater quality. Some of the ways in which these factors can affect groundwater quality include:
Changes in temperature and precipitation patterns: Climate change can alter temperature and precipitation patterns, which can affect the recharge and discharge rates of groundwater aquifers. This can lead to changes in the quantity and quality of groundwater resources.
Land use changes: Deforestation, urbanization, and other land use changes can affect the quality of groundwater resources. For example, deforestation can lead to soil erosion, which can contaminate groundwater with sediment. Urbanization can lead to the contamination of groundwater with pollutants from human activities, such as industrial waste and sewage.
Environmental degradation: Environmental degradation, such as the release of pollutants into the environment, can contaminate groundwater resources. For example, the release of chemical fertilizers and pesticides into the environment can contaminate groundwater with toxic chemicals.
Overall, climate change, environmental degradation, and deforestation can all have negative impacts on groundwater quality, which can have serious consequences for the health of both human and ecological communities that rely on these resources. It is important to address these issues and take steps to protect and preserve groundwater resources for the future.
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Due to the quite deep water level in boreholes (the depth of the borehole is around 700 m, depth to the water table is around 150-200 m) and a significant rate required for the test, airlift testing is chosen.
No observation boreholes located near the pumping one so drawdown may be measured only in the pumping borehole.
The idea is to set a level logger hung on a wire at the bottom of the borehole (without piezometer), then install an airlift system above it and carry out a pumping test.
My concern is that fluctuation of water level due to airlift work will be too high to be suitable for further hydrogeological calculations (estimation of hydraulic conductivity). In other words, there will be too much "noise" and no strait line interval could be defined to calculate the parameter.
Any comments are really appreciated.
Thanks in advance.
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Hello Nikolay,
I join William in his comment and thank him for the link provided, also agree with your concerns. The use of a classic dipmeter to check some recordings is indeed mandatory. Some questions: is there any specific reason not to lower a pump ? (costy ? casing diameter ? water level too deep ?...any well efficiency value ?). Measuring the residual drawdown is a good alternative if you had a constant discharge during pumping. I enclose a link that will not probably solve your problem but may be add some hints.
Regards, Alessio
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I wish to know if a PhD in hydrogeology is relevant in getting a job outside Academia, and if it is, what are the possible job opportunities?
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Yes, a Ph.D holder in hydrogeology can work in the following areas:
*Designing of dewatering schemes
* Urban water planning
* Water treatment industries
*Mining operations
* Groundwater Exploration Industries
*Oil Companies ...in the areas involving working with prediction of pore pressures
* Research institutes
* Companies involved with geothermal exploration
* Cleaning of polluted aquifers in coastal areas by various companies
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How effective do you think satellite images are for groundwater exploration works? What is the most effective method of groundwater exploration by the way? Any idea?
So many articles are published online today regarding groundwater exploration works in different parts of the globe. Experts in the area (Hydrogeology) are using different methods to investigate groundwater availability and potentials in different areas. However, I didn’t see the levels of uncertainties of using one method or the other. I read one article today, where they used satellite images as major inputs to explore groundwater. But, there’s no information about the levels of uncertainty of their work. Should it be presented that way? How effective do you think satellite images are for groundwater exploration purposes? What’s the most effective method of groundwater exploration by the way?
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Satellite images assist with planning geophysical profiles which give more information about the depth, orientation as well as degree of weathering of structures and contact zones.
It also provides insight into regional lineaments orientation.
Best groundwater exploration is exploration drilling following a desktop assessment (which will include a water balance) and geophysical survey etc. Basically calibrating the geological maps and geophysics again to the drill log.
Also an aquifer can potentially be ideal, but without rainfall or other replenishing resource, no water can be sustainable abstracted at economical volumes. Hence artificial recharge and transboundary recharge methods are increasing in some areas - to take advantage of having a 'dam' underground but make up for the lack of rainfall in that area. Hence satellite imagery mostly only speak to the geology, and the lineaments with which groundwater is more probable and associated - but not to whether groundwater actually is available. That only a drill bit can do.
My 2c.
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Hello dear comunity,
I need help to check Multi-collinearity for groundwater conditioning factors, im using MCDM to target groundwater prospective areas
Im hoping that someone can answer my question
Thnks you,
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Machine Learning algorithms are the answers here.
It depends on what you are looking for and the relationship between the parameters. Decision tree and Regression algorithms are often recommended
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The packed bed column (H = 2m) is filled with alternate soil (coarse) and sand samples. I want to study the residence time of my target compound but before that I require a tracer to monitor the flow for calculating the HRT. What are the suitable tracers available that are cost effective as well as inert (should not interact and adsorb on soil and sand)?
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What can we use as a non-reactive tracer for soil ground water for monitoring different reactions like denitrification?
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I would like to work on the estimation of the hydrogeological potential of an area from satellite images. However, I would like to do this without carrying out verification in the field
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No for a local exploration. But, I think for a regional exploration of acuifers and groundwater, the lito-permability characterization is the firs step (you use the geologic map and do an hydrogeological preliminary characterization, and obtein differents hidrogeologycal units, some of these with more potencial will be acuifers). Then, you can use 1) satelital imagen for identify some springs or origin of rivers; 2) model and values of rainfall, temperature, evapotranspiration, and others; 3) field trip for inventory of evidence of groundwater (well, spring, others) and the local geologycal-hydrogeologycal setting (if is possible, take water samples for hidrochemics analysis); and 4) analyze the above information and the background of hydrogeological, geophysics and hydrologic information. Finally, you will recognize the best acuifers for more detail hydrogeological research in the future.
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Many open source programs exist in the field of geology with all its specializa (Water resources , hydrology , Hydrogeology, Geostatistics ,Quality water .......etc) that many people are unaware of.
What software do you want to suggest to us ?
Thanks
Reghais Azzeddine
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Here is a list of common software and free alternatives
Software list
Illustrator => Inkscape, Scribus
Photoshop => gimp
Matlab => Python, R, GNU Octave
Anaconda, R studio, Jupyter notebook, Spyder
ArcGIS Pro and ArcGIS Online => QGIS, GRASS, uDig , GEODA, FOSS4G, Leaflet
PowerPoint => Google slides, LibreOffice, FreeOffice
Microsoft Word => LaTex, Google docs, LibreOffice, FreeOffice
Excel => Google sheets, LibreOffice, FreeOffice
Microsoft OS, Mac OS (and older computers) => Linux (Ubuntu, many others)
Others
GitHub, Arduino, Raspberry pi, Audacity, BRL-CAD, freecad, Dia, PDFCreator, Blender, Cinelerra, Bluefish, KeePass, 7-Zip, Psiphon, Clonezilla, VLC, Quanta Plus, NixNote, Overleaf, TeXstudio
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Hello Everyone,
I am a hydrologist and want to model baseflow (i.e. surface-water groundwater interactions) via the development of a numerical groundwater model (GW model). One of the critical input parameters for the development of the GW model is the hydrogeology of the catchment in question.
Bore-well lithology datasets required for preparation of hydrogeology map or Fence Diagram is very limited (2 borewell logs only), Since, my study area lies in the headwater mountainous region. I am planning to do an electrical resistivity survey for mapping the hydro-geology of the basin in the catchment area of 102 Km2. I have a few questions, in planning Electrical survey in the basin-
1. What could be the optimum number of resistivity profiles required for appropriate representation of hydrogeology of the basin?
2. How to identify the most appropriate locations for Electrical resistivity profiling representative of the basin under consideration?
I request you all to give suggestions in this respect.
Thanking You.
Regards
Rajat
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In general, for this area of land, you must first try to drill at least 10 boreholes. This is so that you can have parametric soundings to calibrate and validate electrical soundings.
Now, and given that the number of drilling is very limited, it seems judicious to me to carry out a grid of 500 m and to carry out a sounding (SEV) with AB/2 of 1000 m in each point of the grid.
The solicited depth of the SEV depends on the increase in the depth of the aquifers (according to geological data). It is therefore necessary to increase the length of electrical soundings in the areas of increase in P and to add SEVs with AB/2 between 3000 and 5000 m (for example).
The establishment of the geo-electrical profiles can be distributed, according to the configuration of the ground, in the following way:
Total number of SEV Number of profile Number of SEV/profile
Zone 1 24 04 06
Zone 2 18 03 06
Zone 3 20 05 04
Best regards
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Need research topics in the fields mentioned above, especially topics that might be related to oil and gas.
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Also, see the following topics:
  • Catchment hydrobiogeochemistry.
  • Catchment hydrology.
  • Cold region hydrology.
  • Computational hydraulics.
  • Computational river mechanics and sediment transport.
  • Evapotranspiration of riparian systems.
  • Extreme value statistics.
  • Drought monitoring and prediction.
  • See the link: https://has.arizona.edu/research-focus-areas
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I need help on getting a research topic for my PhD dissertation, in the fields of seismics and earthquake geophysics. I will also appreciate suggestions in the field of hydrogeology.
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Thanks a lot.
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hydro-geochemistry, hydrogeology, hydrochemistry, chemistry
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Dear Dr Nafaa Brinis . See the following useful RG link:
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Since histograms can be applied in many different field in Hydrogeology is it possible to use it for predicting aquifer type.
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yes very nice question. lets see how hydrogeologist think over it.
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If you are aims to do a model based on aquifer parameters to discuss the Environmental impact problems such as land subsidence due to increasing groundwater withdrawal what are the requirements data?
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To build a model with MODFLOW you need :
- Topographic
- top and bottum of aquifer
- Boundarys conditions
- Surface water elevations
- Geologic
- Hydrogeologic (conductivities, Groundwater total heads)
- Climate (Rainfall, Evapotranspiration, Recharge)
- Pumping Information
- Irrigation Information
- Stady state or transient
- Contaminates
- Water chemistry
- Density Flow (Salinity, NAPL).
- ...
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It is exciting to see that this year’s Nobel Prize for physics goes to complex system studies. Fingering flow (wetting front instability) in unsaturated soils is a typical complex-system problem. The complex system is partially characterized by emergence and adaptation. For highly non-linear unsaturated flow, the emergent pattern is the fingering, and the corresponding adaptation principle is the optimality, such as the minimization of global flow resistance. Based on these ideas, I have mathematically demonstrated that the relatively permeability is a function of both saturation and water flux, while the traditional theory considers the relative permeability as a function of saturation only. The work was supported by experimental results and documented in a recent book
One key issue in applying the complex-system framework to unsaturated flow is to find a physical principle to describe the adaptation. To do that, does anyone have a more general principle than the minimization of the global flow resistance?
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Please find the attached files. Regards.
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Can any body help me know the diffusion coefficient of Europium(III) in pure water and the relative literature. Thank you!
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What is the diffusivity coefficient of Europium (Eu3+) in water?
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I working on aquifer parameters from pumping well data
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Usually, only the transmissivity or hydraulic conductivity of the aquifer can be determined for simple Theis model for a quasi-stationary regime using the Jacob method. Storativity cannot be determined due to the skin effect of the borehole wall.
If the curve S-lgt has stabilized, then try the Dupuis equation for steady-state regime. Use the last points. The radius of influence of the well R can be found in multi-strength textbooks.
Usually, in any case, the error in the conductivity value does not exceed 30-40%.
It is best to use the model (aquifer, filter location, distance to river ...) that is closest to your design
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Hello everyone,
I am new to hydro-chemistry and planning to analyze freshwater (pristine environment) water samples for trace element analysis using ICP-MS. I have gone through literature for identification of suitable filter type for in-situ sample filtration and found that people have used a variety of filter types Cellulose Nitrate/PES Filter/Millipore filters/Polytetrafluoroethylene/Ester cellulose millipore/Polycarbonate, etc.
I was wondering which could be the most suitable filter choice for freshwater sample filtration?
I request you to give your valuable suggestions in this respect.
Thanking you all.
Regards
Rajat
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Make sure before you purchase too many sample containers etc, that the supplies are appropriately metal-free. This applies to filters as well, and the acids you will need to stabilize the trace elements in the sampled water. Check the lids too: liners may be treated with something that might look like field contamination, but was in the flexible disc inside the screw-on lid.
As you say you are new to hydrochemistry , I would recommend you speak to a local expert (university researchers or government environment office etc), see what equipment they use etc and get an idea of what you need for your purposes.
Also speak to the analytical laboratory that will be doing your analysis and find out what they need in a sample: they may have done this work before and will have some suggestions that could save you a lot of time, travel, and plastic containers if you haven't thought of some important details.
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In one of the prior study I am referring to, they have collected the depth of each subsurface layer but do not have any other parameters like SPT N value. The study is about an aquifer system. They have not mentioned about the type of boring they carried out. What kind of other studies require only subsurface layer depths, but not other parameters? What are the field tests that can be used to estimate subsurface layer depths?
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Mines tailing to check the effect of heavy metals released during mining on the environment and the population in particular
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Is there any relationship between geologic or hydro-geologic domains (eg. sedimentary) and a range of rock strength or hardness?
Is it possible to rank geological domains on ranges of rock strengths?
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Hi Amaury,
There is not a classification for your case but there is definitely a relationship between rocks' hardness and strength with hydrological interactions. The main process in this regard is water-rock interactions which is strong in soft rock types and the host rocks with high amount of cracks and interaction surface.
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Two major flow mechanisms for preferential flow in unsaturated zone are the existence of macro pores or structures and wetting front stability (fingering flow). Do you have any field evidence or theoretical arguments to tell which of the two mechanisms is more important?
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The occurrence and development of figuring flow (wetting front instability) in unsaturated zone are very much like those of turbulence flow in pipes. The environment disturbance may determine transition from laminar flow to turbulent flow. However, once fully developed, the turbulent flow is not significantly impacted by the disturbance any longer. Along the same line, the heterogeneity may impact the initial stage of fingering flow, but not the fully developed fingering flow that is mainly determined by the nonlinear nature of the unsaturated flow.
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What classical examples in the literature of contamination by agrochemical, herbicide, fungicide, insecticide and pesticide residues in groundwater in agriculture?
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In the literature of contamination by endosulfan pesticide residues found in groundwater in agriculture, hence it was banned.
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Please, can you suggest a high graphical resolution software for creating hydrogeochemical graphs, especially for Gibb's diagrams?
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Much chemical process modelling and/or simulation work can be done with the widely-used Microsoft’s Excel.
Application example ― Simulations carried in Excel 5.0 with Visual Basic for Applications (VBA) macros ― The recursive least squares algorithm (RLS) allows for (real-time) dynamical application of least squares regression to time series. Years ago, while investigating adaptive control and energetic optimization of aerobic fermenters, I have applied the RLS algorithm with forgetting factor (RLS-FF) to estimate the parameters from the KLa correlation, used to predict the O2 gas-liquid mass-transfer, while giving increased weight to most recent data. Estimates were improved by imposing sinusoidal disturbance to air flow and agitation speed (manipulated variables). The power dissipated by agitation was accessed by a torque meter (pilot plant). The proposed (adaptive) control algorithm compared favourably with PID. Simulations assessed the effect of numerically generated white Gaussian noise (2-sigma truncated) and of first order delay. This investigation was reported at (MSc Thesis):
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Hello all,
i am new to water chemistry, i have been looking at trends in the water chemistry parameters, and found there is significant decreasing trend in Stream-water temperature, Ca, Mg, Na, and chloride along with discharge both in the monsoon and non-monsoon seasons.
Like From Jan 1994, Jan 1995, Jan 1996...... Jan 2018 (for Non-Monsoon period) Sept 1994, sept 1995, sept 1996...................Sept 2018 (Monsoon period)
Note- watershed (1000 km2 drainage area, Western Ghats, India) is free from dams and other water structures.
What could be possible drivers of trends in the above parameters?
Please provide your valuable suggestions.
Thanks in advance.
Regards
Rajat
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A couple of my earliest Researchgate entries and citations may be informative, even though different conditions. Many water quality parameters have influence from flow rate (discharge), and in part often due to rainfall dilution effect, runoff and movement of sediment and other non-point pollutants and nutrients during storms. You may find a hysteresis effect with markedly higher values during rising limb of hydrograph, and lower rates as hydrograph recedes. Geology and groundwater and its chemistry influences contribute to varying degrees as some streams loose water to groundwater, while others gain water inputs from groundwater for substantial periods of time. There are many books and papers on the subject, as well as professional or informational courses. It is not unusual to find these trends. Stream temperature in many locations increases in the summer growing season as more solar radiation, higher temperatures with lower streamflow often combine to elevate temperatures. Streams heavily augmented by groundwater or springflow as well as dense forest cover have substantially less effect than conditions without these benefits. In one of my studies, mountain streams without dense forest cover actually had lower winter temperatures, so forested stream buffers may have a moderating effect on temperature extremes in both summer and winter. It is highly useful to have recording water levels to estimate flow rates with time. A relative moderate expense tool for this is transducer (vented or barometric adjusted unvented). Streams with excessive sediment may contribute to transducer fouling, but properly installed, they can collect high quality data for weeks or months without service. The USGS collects flow data every 15 minutes, and appropriate for your study area. For small catchments, more frequent readings may be needed. A variety of tools or techniques are available to collect samples during storms or more routinely, if ample research funding exists.
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I wish to use gamma ray logs from a named field to estimate shear wave logs for the area.
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Please Refer :
Engineering Geology Field Manual volume ii, 2nd Ed, Chapter 14.
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Physically measuring depth of water in a borewell is very difficult. First we need to dissemble the cap of the borewell. Then we need to allow measuring tape inside borewell which is very tedious.
There are SONAR based technologies for this purpose. Based on the time required for sound waves to reflect from the water level, they determine the depth of water level.
How accurate are these methods?
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Audible sound or even infrasound rather than ultrasonic sound is usually used in order to measure a longer distance (no need to be straight) and avoid interfering reflections by the obstacles or well wall along the way. Sound transmission and reception can be done using a laptop PC, table or handphone with a speaker and microphone. MLS (Maximum Length Sequence) signal can be used as the stimulus and the lag time of the echo can be found by the second highest peak of the auto correlation function. Time delay measurement accuracy is in the order of 0.05 ms. The water depth measurement inaccuracy could be mainly attributed to the estimation error in the average air temperature in the well, which is used to determine the average sound speed. For manual measurement, the water depth could simply be measured by tapping the well cover or burst a balloon, see example at https://www.virtins.com/forum/viewtopic.php?f=24&t=1842.
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Hello, I am starting my master's thesis work on a Peruvian project. They have limited budget, and do not have yet any piezometer on the site. They do have 3 small open pits (3-4 meters long, 1 meter wide, 7 meters deep) for soil characterization. All of 3 have water on the bottom, and they use this "level" as a measure for water levels. I am not sure if those levels are representative for the actual water level, as I think the water level can be much higher, and when cutting with these open pits, it just "falls" by gravity action. Do you have any experience with using open pits data for water levels?
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The groundwater level can differ from the level in pits from what is called "seepage phase", which can be significant in finer soils but negligible in coarser ones. (Bear J., Verruijt A. (1987) Introduction to Numerical Methods. In: Modeling Groundwater Flow and Pollution. Theory and Applications of Transport in Porous Media, vol 2. Springer, Dordrecht. https://doi.org/10.1007/978-94-009-3379-8_8)
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Could you let me now any publication oriented to that question or discussing it ?
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I recommend that you look at the topography as this influences in some way the hydraulic gradient line.
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I am new to hydrogeology but I want to understand what is required to be measured at the field or site which will form basis for MODFLOW FLEX 3D modeling.. I want to to know the specifics to be gotten at the site. The rivers, lake, recharge... where do I require resistivity, every form of measurements needed to be calculated, please I’d like to know and where I can get the information I need as well... thanks
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Dear Lawrence,
Since you are new to hydrogeology I would suggest you start with Applied Groundwater Modelling by Andreson and Woessner and Groundwater Modeling - An introduction to groundwater flow and solute transport modelling by Rausch. Also Fundamentals of groundwater modelling by Huasam Baalousha. The latter two are available on Research Gate, but the applied Groundwater Modelling good is not only a good read but a good reference.
The first question of groundwater modelling is do you need a model? Several basic calculations and analytical solutions can be better than using a groundwater model. There are good flow charts to follow in regards to the modelling process.
As you start to read you will start to realise that although modelling is data intensive, models if conceptualised correctly can be very useful even with limited data. Some of the parameters can be estimated via a literature review if not available and can be refined during the calibration process.
As Ajoy Saha said at the very least some basic geological information is a must that is followed by hydrological data and hydrogeological data (T, k, water levels etc.).
My final comment will be to kindly remember that the software is a programme that can be used once you understand how to work the programme. However successful groundwater modelling or any other modelling is dependent on you understanding the limitations of your data and the limitations of the final product.
Best Wishes,
Raoul
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I am doing a small research to review the water related open source tools / software (e.g FREEWAT).
if you have used/developed/ heard of similar tools,please share it with me ?
Thanks in advance
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Yes USGS based softwares eg MODFLOW, Modelmuse, mt3dms, modpath. check their website for more info. All softwares are free and open source
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Hi
Would you please let me know if the following is accurate as an answer to the question:
Suppose we have sensors which measure the volumetric soil water content of a soil layer for a long period (more than 6 months) and also high temporal resolution (half-hourly). Could I assign the maximum in this dataset to the saturation point?
I understand that we do need to have a lengthy rainfall event, how long the event should be so that the above proposal works?
And if there is any other way that I can get to the saturation point of a soil layer from the volumetric soil water content data/sensors, please let me know.
Mostly focused on the topsoil and preferably only using the dataset.
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There are standard methods for testing soils to consider. Usually soil samples are taken and put into a container of water so the soil is saturated from the bottom, about 24 hours. Unless there is a water table to saturate soils in the field, ability in reaching saturation may vary with the conditions. I remember we had a dry period and wildfire, then a substantial rain, about 3-5 inches. Water was pounded on the surface the next day, but the soil scientist found the soil totally dry about 12-18 inches below the surface. I also learned that an upper clay layer needs to be saturated before the lower sandy layer can effectively gain water and this is related to the tension with which clay holds water as compared to sands. Some soil layers have difficulty becoming saturated, such as well developed forest soils seldom exhibit runoff due to high infiltration and macropores from roots, etc. other soils as hydric soils are saturated frequent enough to exhibit hydric soil indicators due to frequency of high water table. Sampling the soil depth or horizon is probably the most reliable using standard methods to saturate and measure.
I would not use just the high reading in 6 month period, unless at least I reviewed nearby stream gauging stations and the rainfall during the 6 month produced at least a bankfull streamflow event, which occurs generally about every year, and the stream channel is at a level where flooding begins for stable channels that have not aggraded or degraded. I would want to be pretty sure there was a reasonable likelihood of saturation based on evidence like the streams were near or at flooding. The other option might be to set up so the area with the data sensors can be irrigated for long enough so the detectors stabilize after reaching their approximate maximum. Saturating from the surface can apparently leave some air spaces unfilled, but unless the area periodically has a high water table, the air spaces may not be filled easily to saturation by rainfall anyway.
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I have Total iron content in water express in mg/L. I want to convert it into mEq/L in order to calculate it percentage. But I do not know how to do it because it not Fe(II) nor Fe(III) but total iron which is the sum of both. I do not know which charge I have to use or the method to overcome this issue.
Thank you in advance
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I've been searching online for how to do this but my head is starting to hurt. 📷 I've never been good at math and forget chemistry! I found a conversion formula but it was for Ca and you have to know the valence or something like that so I thought I'd try looking up "valence of CaCO3" but that didn't work. I probably wasn't even on the right track. This is what I was looking at;
milliequivalents per liter (meq/L) - meq/L is another method of expressing concentration, when the analytes are dissolved and disassociated in solution. meq/L is also equal to millimoles of charge per liter (mM+/L or mM-/L depending on valence). To calculate meq Ca/L from the reported value in mg/L, we must know something about calcium.
Calcium has a molecular weight of 40.08 grams/mole Calcium has a valence of +2 The equivalent weight = (40.08grams/mole)/(2 equivalents/mole) = 20.04 grams/eq To convert to mg/meq you simply multiply g/eq by 1000 mg/g and divide by 1000 meq/eq, thus g/eq = mg/meq If your sample contains 30 mg Ca/L, what is the concentration in meq/L?
Meq Ca/L = (30 mg Ca/L)/(20.04 mg/meq) = 1.50 meq Ca/L
Anyways, I just want to know if you have alkalinity test results of 110 mg/L, what is that in meq/L? (I'd like to know how to solve the problem too for future reference)
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Are there any easy ways or equations to estimate the recharge value from rainfall?
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R = 1.35 (P-14)0.5
The Chaturvedi formula has been widely used for preliminary estimation of ground water recharge due to rainfall. It may be noted that there is a lower limit of the rainfall below which the recharge due to rainfall is zero
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Dear all,
I would like to have feedback on your personal experience with autonomous resistivity meters. I know some systems are well documented, but your personal perspective and your contacts will be of great help to me and my research group.
The system we are looking for must be able to perform daily measurements with up to 100 electrodes. We want to be able to download datasets or change protocols remotely. The system will be powered with solar panels and batteries.
We instrumented a large scale site last summer for my doctoral project. About 400 electrodes were buried to monitor the hydrogeological behavior of the site. We plan to perform autonomous monitoring with some of these electrodes (about 100). Transient monthly measurements will be also carried out with the remaining electrodes. The sketch of the site configuration is attached below.
Thank you in advance for your advice or contacts.
Adrien
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I am using the chloro-alkaline indices, but I don’t know if it is the right way.
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Well,
Anthropogenic compounds can be dedicated from the PhreeqC software results.
Regards
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We have a hydrogeological setting of triassic layers, which are characterised by a ground water flow and mixing system. We tried to separate the sources of the groundwater flow and mixing system via hydrochemistry (ions), isotopes (deuterium, oxygen-18, tritium, carbon-14, strontium-isoptopes and sulphur isotopes), and still is not enough information to understand fully the hydrogeological regime. Which could be other approaches or tracers to separate the different aged components ?
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Well,
Regards
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hydraulic researchers, hydraulic modelling
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In my view, you can use Flow-3d and OpenFoam. But flow-3d is quite a user-friendly software.
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I have SP, Gamma and Resistivity (both lateral and N16-N64) logs along with Electrical Conductivity value of the water sample of the area (collected through tube well). I have calculated the lateral resistivity (Rt) for each depth. I am getting Silt, clay and sand lithologies in the borehole. I would like to determine the Formation Resistivity Factor (F), Porosity, hydraulic conductivity and permeability value correctly. Kindly help me with step wise procedures. 
NOTE: Archie constant a & m varies for different lithologies like silt, clay and sand. 
Looking forward!!
Regards,
Ashok
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The best and easiest book is AAPG ASQUITH and Gibson book full of charts and log interpretation. It is recommended for reading and applications
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Aquifer studies
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Well,
In fractured rocks, water only moves through the fractures, even if the unfractured matrix blocks are porous. This means that the effective porosity of the rock mass is linked to the volume of these fractures. A fractured granite, for example, has a matrix porosity of 1 to 2 %, but its effective porosity is less than 1% because the matrix itself has a very low permeability.
Regards
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What reference studies (Book, Article, Tesis etc) you know used ER Method was applied using the Vertical Electrical Survey (SEV) technique (Wenner-Schlumberger, dipole-dipole arrays) for definition of intrinsic vulnerability index to water contamination underground?
Are there any studies that have used this method to set parameters for analyzing groundwater vulnerability to contamination por geoelectric layers?
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What are the methods, techniques, lines of thought, university labs considered vanguards in hydrogeology?
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Interesting that you should ask this. I have been pondering the subject myself. My conclusion is that our computer abilities exceed our physical hydrogeology skills. We have wonderful models that have ridiculous parameters for real-world materials, yet by manipulating these parameters some semblance of the real picture emerges. What if we actually built models with real parameters and manipulated the model code to produce a model?
Secondly, hydroGEOlogy implicitly involves the earth. HydroLUNology, HydoARESology, etc. - these are the subjects that new hydro___ologists will explore. What fun!!!!
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Dear Everyone
I am working in an irrigation department. In this field we need to study hydrogeology. Regarding that I am interested in reading the research paper on current tend and research trend in Hydrogeology. Could anyone suggest me a good review paper on that?
Thanking you
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Dr. David Kreamer has a book posted here on RG that specifically addresses your question.
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Is there an average time (or order of magnitude) that rainwater resides on a soil surface? A kind of residence time or ponding time? I am looking at a natural soil (not urban), normal topography (not too steep, not too flat), moderate vegetation (grass but not trees), made of compacted clay (quite impermeable) in a temperate climate (e.g. Europe)
Thanks!
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Dear Dr Mercedes
I send you an attached thesis, I think you will find answers to your question.
Best reagrds
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Hi all,
I'm gonna study the impacts of the rise of production wells numbers (for irrigation purpose), LU/LC changes on the groundwater in a flat area where  river branch, main canal and many irrigation and drainage canals run through. The main aquifer in this area is recharged from the surface water (i.e. river branch, main canals, and irrigation and drainage canals) and the infiltration of excess irrigation water. The aquifer is semi-confined to phreatic (leaky aquifer). In addition, it is highly conductive with hydraulic conductivity ranging from 80 to 100 m /day, that is because it consists mainly of sand and gravels with clay lenses. Unfortunately, there is no a systematic monitoring for the water level, water chemistry or actual management for this aquifer. There are too many research works in different ways (e.g. geologic, hydrogeology, hydrogeochemistry,..etc.) have been done. There is no actual estimation for recharge quantity, monitoring for the impact of the anthropogonic activities on this aquifer. I have studied some samples from  3 wells, 2 shallow wells (25 m deep and 2.5 inches diameter) and one deep (65 m deep and 8 inches diameter). One of the two shallows is hand pump tube well and located close to the urban area (in agricultural land) with peizometric level, 10.4 m  and nitrate concentration, 6 ppm. And the second shallow well is being pumping using pump machine and located in urban area, north east the first shallow well with approximately distance 1 km long, with peizometric level of 10.3 m and nitrate concentration, 100 ppm. The deep well (the third one) is located north the second shallow well with distance 1 km long, peizometric level is 10.3 m and nitrate concentration is 3 ppm, which located at agricultural land. The second shallow well and the deeper one are both located close to drain canal with its nitrate concentration not more than 40 ppm as literature's result . I believed that the highly pumping rate is the main factor that gives the high nitrate value for the second shallow well. I really need to study the large area with many urban areas surrounded by agricultural lands, and find out the pollutions anomalies. I will measure CFCs as indicator of the recent recharge, GMS model to simulate the nitrate transport and the future prediction of its concentration, main ions, N15  to find the source of the nitrate and total coliforms . I really interested to find a valuable solutions for such problem. So if some one interested to help me in such study or give me advises, ideas and recommendations to how can I study the nitrate pollution anomaly, estimate and quantify the groundwater recharge, and study the impacts of the high density of wells (for irrigation purpose) on the quality and quantity of the groundwater in this area, I will be greatly appreciate.
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I think that a NO3- / Cl- Vs Cl- binary graph can inform you about the probable origin of nitrates.
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Hydraulic tests conducted across ever larger usually yield higher transmissivities/conductivities/permeabilities. There are a lot of theories around what the effect results from. Only to name two: heterogeneity and preferential flow. Thus, my question: Where does the scale effect come from? Do you think it is still controversial?
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In hard rock aquifers we often made the experience that a single investigation measure (pump test in a borehole, packer test in a borehole section...) demonstrates values much too high for a long term draw-down (e.g. by a tunnel), even if well storage and other effects are considered during interpretation of the results. By interpolation of the results on the entire planned underground construction (considering the geological model, obviously), the calculated discharge seems much too high and often exceeds the recharge by precipitation in the entire catchment. The reduction of the prediction, then, starts to be an assumption only and does not base anymore on the test results. We do have, therefore, an important scale problem between the borehole test and the later underground excavation. The reasons for that can be different and, as mentioned by earlier answers, linear effects in the aquifer. We made the experience that groundwater recharge and ductile behavior of rock mass have a stronger influence on the inflow than the fragmentation of the rock mass itself.
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Interaction between surface water and groundwater in karst is so strong that in most cases it is not possible to split hydrological from hydrogeological approaches and methods .
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I agree with Prof. Bonacci. The point to note is the use of the term "Karst", which points to the geologic media. Hence, hydrology and hydrogeology in this sense are synonymous. Similarly, for a karst system with active variable area hydrology, surface and groundwater systems work as an integrated system and are inseparable. Consequently, there is no distinction from a systems view between surface and groundwater.
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im looking for an hydrogeological methods of interpreting the activity istopes of radium in groundwater and some relation of this isotops with the other physical and chemical parameters, cations, anions, pH, TDS, temperature ....
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I am currently running a master program in Hydrogeology and i want to do a project which incorporates hydro and environmental geology.. i will appreciate any suggestions regarding a topic for my project.
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Following
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Dear Researchers!
It is known that methods such as: GOD (Foster) and DRASTIC (Aller et al) and others are widely used. But are there new methods developed to evaluate the intrinsic vulnerability of the physical environment to loads or pollutants? and with easy application (accessible parameters)?
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There is no method that can fit every case of study. DRASTIC request several factors that are not available in many countries; the spatial resolution of data is another problem. GOD is made for aquifers that have a large extension; it is not the best solution for small aquifers or where lateral and vertical lithological variations are frequent. SINTACS is the italian little brother of DRASTIS; it has thus the same shortcomings. AVI is based on permeability which is generally not available or the measurement points are poorly distributed...
Since geophysical data are mostly available or surveys could be done, we suggest a geophysical method for countries where data are lacking.
Please check this recent paper:
Regards
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Researchers in hydrogeology, hydrogeochemistry, environmental geology
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Dear Dr. Nwanosike
Bone char is a good option, there are several studies of groundwater fluorine removal using this material:
Best Regards.
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Our new textbook:
"GROUNDWATER ENGINEERING A Technical Approach to Hydrogeology, Contaminant Transport and Groundwater Remediation"
was finaly publishedby Springer.
This textbook employs a technical and quantitative approach to explain subsurface hydrology and hydrogeology, and to offer a comprehensive overview of groundwater-related topics such as flow in porous media, aquifer characterization, contaminant description and transport, risk assessment, and groundwater remediation. It describes the characterization of subsurface flow of pristine and polluted water and provides readers with easily applicable tools for the design of water supply systems, drinking-water source protection, and remediation interventions. Specific applications range from groundwater exploitation as a drinking water supply to the remediation of contaminated aquifers, from the definition and safeguarding of drinking-water sources to the assessment of human health risks in connection with groundwater contamination events.
The book represents an ideal learning resource for upper-undergraduate and graduate students of civil engineering, environmental engineering, and geology, as well as practitioners in the fields of water resource management and environmental protection who are interested in groundwater engineering and technical hydrogeology.
for more details:
if you are an instructor and you want to request a complimentary copy :
-> https://lnkd.in/dsZe2ju ISBN 978-3-030-20516-4
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Je suis aussi tres interesse pour la version gratuite. C'est tres important dans
domaine de recherche !.
Me interesa bastante el libro, mis felicitaciones !. Los académicos en Venezuela Estamos pasando pour una situación de recursos extra-limitados!.
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The vadose zone is the first groundwater protection line, what are the main physical, chemical, biological and other elements capable of attenuating the potential contaminants released on the ground surface?
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Well,
Text book, Groundwater Science / Fitts, 2006.
Regards
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What is the difference between the hydrogeological system and the aquifer system?
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Well,
hydrogeological system simply means regional hydrogeologic basin including recharge, transition and discharge zone, while aquifer system is a part of the hydrogeologic system. see the attached links.
Regards
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We are currently characterizing aquifer in an area where there is paucity of hydrogeologic data and need some sort of secondary data to combine with our geophysical information and what is available is rainfall data.
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Dear Ebong D. Ebong , I believe you have already done some review by now. Nothwithstanding, if you are still looking for an answer, I'd like to suggest you and anyone who is interest in start studying this topic, to start at the following reference:
Healy, R.W., Scanlon, B.R., 2010. Estimating groundwater recharge. Cambridge University Press. 256p.
There are many methods for estimating groundwater recharge and this little book presents a comprehensive review on most of them. You will be convinced by the authors that using a single method may not be enough in order to achieve reasonable recharge rate estimates.
You must be aware of two things: (1) the nomenclature of the recharge rates and mechanisms; and (2), the specific spatial and temporal scales that limits each method as well as the inherent uncertainties of each method. For example, some methods can give you average multiannual rates in a specific point of your watershed (e.g. Chloride Mass Balance, peak displacement methods), while others will give you event based areal distributed recharge estimates (e.g. water table fluctuation). Some are quite objective (e.g. water budgets), while others can be very prone to subjectivity (e.g. WTF). You must have a sound understanding of the assumptions and limitations of each method in order to chose those that are most suitable for your hydrogeological and climatic system and database.
The suggestion you received from Jean-Pierre Faillat may be quite useful if you only have meteorological data (and a few other easily obtainable parameters). But it will provide you only a gross estimate of the (maximum) potential recharge, i.e., the average water surplus that escapes evapotranspiration and is available to infiltrate further towards reaching the aquifer system. Surely better than nothing.
Best of luck.
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I need to construct my 3D conceptual model considering the geometry (boundary conditions), topography, fluxes (precipitation, evapotranspiration, runoff, etc.), flow directions and so on...
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Walter Antolinez got it. We typically use Adobe Illustrator, Leapfrog, or MVS, which are not freeware, to put together graphics like this. I suggest looking at this researchgate thread that covers this topic:
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How discharge is unsually conceptualized for catchments under arid or semiarid environments with no springs and only ephemeral rivers, in a context that could not be explained exclusively by evapotranspiration (i.e. no salinization, TDS increase, etc)? Could you suggest any reviews or insightful literature about this topic? Kindest regards to all.
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Hydro(geo)logic lierature on recharge/discharge processes is predominantly based on experiences observed in humid regions of the world and appears to be biased toward humid understanding of hydrogeoloical phenomenon.
You may consider reviewing the following:
Happy Reading!
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Hydrogeology
Hydrology
Petrophysics
Well logging
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it is illegal way
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Submarine groundwater discharge is a very common topic of research nowadays and there are a lot of studies investigating about it but when was this term invented and by who?
Looking in published papers the first time that I can find it was in 1991 by Vladimir Vanek and David Robert Lee in Limnology and Oceanography but maybe it has been used before?
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If I remember correctly, neither Jan Ghijben nor Alexander Herzberg ever used the term "Submarine Groundwater Discharge". The fact that their reports were respectively in Dutch and German does not help either ;-) I think Carlos is specificly interested for this discussion in the term "Submarine Groundwater Discharge" and no so much in the history of research on salt water intrusion in general.
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I'm looking for codes that can do this for saturated and/or unsaturated porous media. I expect there are a few that can handle the porosity changes easily, but predicting permeability changes seems much more complicated.
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Dear Spencer,
In this benchmark exercise you have 5 codes that can do so:
In this other benchmark you have a couple of codes more:
I hope this helps you
Best regards
Vanessa
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Dear scientists of noble gas and hydrology,
Would equilibrium and/or excess concentrations of noble gases change after isolation from gas exchange with atmosphere? (Non-atmospheric noble gas was not taken into consideration in this question.)
Relationship of solubilities of noble gas and salinity were found and reported by Weiss (1970 and 1971), Weiss and Kyser (1978), Clever (1979 and 1980), Benson and Krause (1976), and Smith and Kennedy (1983). The higher salinity would lead to lower gas concentration if other parameters like temperature and pressure stay unchanged.
However, reported data was from air-water exchange interface like in unconfined aquifers or surface water system. Would it be available for groundwater in CONFINED aquifers? That is to say, would dissolved noble gas degas in confined groundwater due to the increase of salinity? Or would gas concentration stay undisturbed in groundwater flow system after isolation from gas exchange with air?
Any feedback, answers or discussions would be welcomed. And I would greatly appreciated for that.
Kind regards
Dan
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Good discussion....Following
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These terms (sustainable yield and safe yield of an aquifer) are the most debatable terms in hydrogeology. People sometimes report their predicted yields of aquifer systems that show no considerable negative impact of the available groundwater potential of the aquifer system as "sustainable yield" and some experts report it as "safe yield". On the other hand, there are also confused reported that also confuse readers in terms of defining these terms. So, do they really have similar meanings? Is there any justifiable difference between these terms? Can we make an agreement on how/where to use these terms?
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"sustainable yield" = recharge = maximum quantity of water that can be supplied by the aquifer without depletion
"safe yield" = quantity of water lower than recharge and that can be supplied by the aquifer in a safe way
So, "safe yield" is lower than "sustainable yield" and even though the definitions look similar in terms of quantity of water that can be exploited, their respective values are different.
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The question is that, how much can we trust the indicators like SPI and GRI and the other indicators that analyze the changes in groundwater levels in relation to precipitation? Due to the fact that in many regions, including arid and semi-arid regions, the water table is very low and most likely due to high evaporation, rain does not play a role in groundwater recharge. Based on my Experiences in the assessment of groundwater in Kashan, located in the center of Iran in an arid and semi-arid region, precipitation does not feed the groundwater (based on the analysis of tritium and carbon-14 isotopes). It seems that in the subject of the effect of meteorological drought on the hydrogeological drought, isotope investigation could be so important. I think the meteorological and hydrogeological indicators such as SPI and GRI, are more reliable for moderate regions with high precipitation and sallow aquifers. I look forward to receiving your valuable opinions about this matter.
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Are we receiving necessary information for amply assessing the groundwater pollution potential?
OR
Are we biased towards the hydro-geological settings (that potentially decides the transport of pollutants)
than
the socioeconomic conditions and the anthropogenic activities (that potentially release the pollutants)?
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Well,
thanks for discussion Dr Suresh Kumar Govindarajan , the first part about geogenic source was examined in details in the following articles,
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The sand body on the river bed is 9 meters thick. It consists of medium and coarse sand. The stream course on the river changes course and hence direst pumping stations for irrigation are adversely affected. The base flow is the only alternative left for exploitation.
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Thanks for your valuable comments. Further work being on going, I will post the findings later on.
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I am looking to obtain the Kfs of only the top 30cm of a beach profile and I am not sure which model to use.Ideally, I would like to use something more simplistic for ease of computation. would something general and  simplistic like the Philips (1956) two-term model work or should i use something more complex, like the Reynolds and Elrick (1990) two-ponding head approach. 
Thanks for your advice.
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Dear respected Lee Allen Sean Britton,
I would Prefer Phillips (1956) two term model as you identified. Double ring infiltrometer would be used to collect the field data.
Best regards
Kifilideen
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I am having difficulty understanding what in-situ variables i will need to measure to predict saturated hydraulic conductivity using the Philip's (1957) two-term model and a double-ring infiltrometer?
Rate infiltration Eqn. i(t)=1/2St1/2+A 
Cumulative Infiltration Eqn. I(t)=St ½+At 
Where S is sorptivity and A is dependent upon the soil properties as well as initial and boundary water contents.
what information do i need to gather to calculate A and S, and in turn, how do I calculate it?
Thanks for any help you may be able to provide,
Lee 
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I want to know if it is possible to construct a 3D structural model for a certain area using "Midland Valley Move software" by utilizing boreholes only.
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You can construct a 3D structural model using boreholes in Move software. Indeed, you can construct it in other free or cheaper-licenced programs. However, the most important thing to bear in mind or what you should ask yourself is: what is the purpose of this "3D structural model" and what really means for you a "3D structural model".
One thing is to construct a fence diagram (which usually is in 3D or quasi-3D) using formation tops or stratigraphic information (e.g., lithology, thickness, etc) from the boreholes, a fence diagram like that one suggested by Bayan Hussien, which is very useful to correlate stratigraphically. However, from a fence diagram, you will hardly construct a reliable structural model even a 2D structural model!. So, a reliable structural model must be at least balanced or geometrically consistent, in this way, you should have more structural data and a seismic line will be very useful to interpret structures.
Another important thing is the space between boreholes, you must consider that the greater spacing the greater unknown information in between (uncertainty increase dramatically).
Please consider the below examples (image) constructed from borehole data. In case #1, from the stratigraphic correlation in the fence diagram, you can infer a simple structural model with horst and graben structures related to planar normal faults. However, in case #2, from the same data/information you could interpret another structural model related to listric faults. So, the important point is, what is the detail or purpose of your work, depending on the latter, you can assess if move software is what really do you need or the advantages/disadvantages of constructing a (likely complex) "3D structural model" using only a limited borehole data.
Move software is very useful when you have a seismic line or very dense structural information.
Anyway, I hope I have understood your question correctly and be able to help a little.
Huber
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Suggest me drought monitoring through remote sensing and GIS with combination of Hydrogeology.
Thank you..................
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Thank you sir Saikat Das
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I am a Congolese hydrogeologist. Groundwater resources of the DRC are unknown. I am making a database of existing Wells and borehole with hydrogeology data.
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