Mapping Hidden Channels with Genesis Live

River channel thalwegs (the line of lowest elevation within a valley or watercourse) are often dynamic, and sometimes hidden features of large river systems.  Especially low slope or impounded systems.  The thalweg is a critical geomorphological feature of river and reservoir systems and affects everything from sediment transport, to fisheries habitat, to algae or invasive plant control.

Thus a good bathymetric contour map is a necessary pre-requisite for effective river and reservoir management.  Here, we walk you through how to use new real time technologies (C-MAP’s Genesis Live) to produce smooth, precise, and accurate maps of hidden river thalwegs all within one trip to the site and with automated post-processing with BioBase’s EcoSound.  We’ll use an annotated image gallery to take you through this process.

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Interpreting bottom hardness in shallow lakes and ponds: digging deeper into the data

BioBase’s EcoSound bottom composition (hardness) algorithm has become quite popular for researchers and lake/pond managers to determine where sedimentation from the watershed may be occurring.  However, interpreting sonar returns in shallow environments (e.g., less than 7 ft or 2 m) with off-the-shelf sonar is challenging, especially if aquatic vegetation is present.  Each situation is different and the objective of this blog is to inform you of how to interpret your EcoSound map in situations when you encounter counter intuitive bottom hardness results.

Here are some high level points to remember.

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Helpful Resources for Getting Started with BioBase

BioBase is a powerful data collection tool for aquatic environments. To get the best results with BioBase – EcoSound, it is important to use proper data collection and management procedures. This post contains links to the resources that will help you get started with BioBase and get great data.

Our quality control team reviews every uploaded trip and looks for glaring issues with the trip like evidence of a slanted transducer, signal loss, poor signal quality. They may email you if they notice any significant issues with your trip, and suggest ways to fix the issue or ways to improve data quality before logging again. The quality control process may cause data edits and offsets to be lost and can “break” merges. Please allow one business day for quality control before applying these changes to your trips, or check the quality control review status by viewing a trip’s report. If there is a quality control reviewer’s name on the report, the trip has been reviewed. You can also see any comments that were not emailed to you on the report.

It is critically important to keep your Lowrance software updated. Software updates can be found here. Outdated software can result in inaccurate or lost data!

Our YouTube channel has many helpful videos, including data editing tutorials.

This post gives an overview on how EcoSound works along with some answers to frequently asked questions that many new users have.

The EcoSound Quick Start Guide shows recommended settings to use while logging sonar. Print this guide and keep it on your survey boat.

The EcoSound Support and Resources page has links to the EcoSound Full Operator’s Guide as well as several tutorials, including guides for using EcoSound data in QGIS.

If you ever need any assistance, contact the BioBase support team at info.biobase@navico.com

Consumer Sonar for Bottom Mapping: Updated Reference List

Another FAQ we get is wondering if there are published studies using BioBase technology? There are many legacy applications on which the BioBase technology is based. Further, now that a sufficient passage of years has accumulated to support the “research to publication” cycle, we’re happy to share several BioBase-specific studies published in the peer-reviewed literature.  This is far from an exhaustive list and we’ve intentionally left out the niche growth in consumer side-scan technology for creating habitat maps.  If there are good published papers you know of that are not on this list, please share in the comments.

Continue reading “Consumer Sonar for Bottom Mapping: Updated Reference List”

FAQ of the year: Does BioBase EcoSound Map Sediment Depth?

Thanks to advances in physical, chemical and biological technologies and funding that are focused on reducing sedimentation or muck depth in waterways, many water resource practitioners are eager to determine how much sediment is in a waterway of interest and how much could be removed. As such, we frequently are asked: “Will BioBase tell you how deep the sediment is?”

Continue reading “FAQ of the year: Does BioBase EcoSound Map Sediment Depth?”

Citizen Lake Mapping: Power of Aggregation!

Ten Mile Lake in Hackensack, Minnesota is one of many crown jewel lakes of Minnesota.  It’s no wonder the Ten Mile Lake Association is serious about lake monitoring and conservation.  When BioBase approached TMLA member and hobby Fisheries Biologist Dr. Bruce Carlson in late 2012 demonstrating how members could passively log their sonar data and map habitat while enjoying a pleasure cruise or fishing, Dr. Carlson jumped at the opportunity.

Two hundred and twenty four trips spanning two seasons (2013-2014) and 5,065 acres (2,049 ha) later, Dr. Carlson and colleagues have produced the most accurate and detailed map of Ten Mile Lake on the planet (Figure 1)!

Figure 1. Track lines from 224 Lowrance sonar logs uploaded to BioBase and merged (left) and resultant contour map (right) produced automatically for Ten Mile Lake, Hackensack, MN USA.  Ten Mile Lake is a 208-ft (63-m) deep lake with 16-ft (5-m) clarity.

When comparing the hand-made maps of 1947 from the long-dissolved MN Dept of Conservation one has to wonder if creating this map took a dedicated and highly trained survey crew all summer to create this map (Figures 2-4)?  Now a critical mass of anglers or pleasure boaters with no mapping experience can create a community-sourced contour map that rivals anything produced by the most trained hydrologists using the most expensive “survey-grade” echosounders.

Figure 2. Original map of Ten Mile Lake created in 1947 by the MN Department of Conservation (left) next to the aggregated map produced by TMLA volunteers in 2014 after uploading to BioBase.  Maps created in the mid 20th Century remain the only maps offered to anglers and recreationists by a large number State Natural Resource agencies. Often these old maps are digitized and artfully recontoured and shaded for resale.
Figure 3. Close up of the 10-ft contours displayed in the 1947 Department of Conservation map compared with the 2014 aggregated map created by TMLA volunteer uploads to BioBase.
Figure 4. Tight zoom of 10-ft contours from 1947 MN Department of Conservation map (ink blob on top) compared with 3-ft contours from aggregated map created by TMLA volunteer uploads to BioBase.

Not just an improvement in aesthetics!
The efforts of TMLA and volunteers from other Lake Associations across the US (e.g., Lake Paradise, Honeoye, Prior Lake) are producing not only pretty maps but also updated digital maps for the public and highly detailed fish habitat and aquatic plant data for aquatic researchers and managers.

First, public trips uploaded and aggregated both from BioBase and C-MAP Genesis mapping services from anywhere across the globe go to Social Map where they are available for viewing and downloading for free to Lowrance, Simrad, and B&G chartplotters (Figures 5 and 6).

Figure 5.  Insight Genesis Social Map coverage of Sweden.

 

Figure 6. Example map of Anten (Sweden) as viewed from Insight Genesis social map.  Professionals (BioBase) and Anglers (Insight Genesis) can community-source their mapping efforts to “fill-in” unmapped areas and create up to date digital maps for the public.

Second, Fisheries across the globe are threatened by a range of impacts too long to go into detail here and Aquatic Invasive Species are a global pandemic.  Researchers and managers mourn the decline of native aquatic species and often target habitat degradation or loss as a primary driver.  But rarely does information on habitat match the detail of the information on species declines. Citizen Scientists are now helping Natural Resource Agencies fill in the habitat knowledge gaps.  Returning to our example on Ten Mile Lake, now with updated bathymetry provided by TMLA volunteers and data sharing with MN Department of Natural Resources (DNR), Fisheries researchers have precise knowledge about how much cold, well oxygenated water is available for cisco (an important cold-water forage fish for popular gamefish).  Similarly, thanks to the efforts of the Prior Lake Spring Lake Watershed District and citizen volunteers on Prior and Spring Lakes, the response of invasive aquatic plants to watershed and in-lake management actions can be monitored.

Harnessing the power of technology and citizen science to conserve aquatic resources
“Doing more with less” or “working smarter not harder” are common cliché truths that will continue to limit the reach of publicly funded natural resource management programs into the foreseeable future. Through advances in affordable off-the-shelf consumer technology, automation, and the collective enthusiasm of citizen volunteers, good information on aquatic habitat need’nt suffer from declining public natural resource budgets.  Rather, by enrolling the help of citizens and technology such as described here, aquatic biologists and managers can focus their energies on using the information to make wise aquatic resource management decisions.

Color Enhancing your Sonar Log

ciBioBase’s Trip Replay feature that couples bottom depth, aquatic vegetation biovolume, and bottom hardness maps with your actual Sonar Log empowers you with a verification tool that ensures an accurate map in every system you map, every time.  The sonar log also provides users and our Quality Control team helpful information about signal quality and transducer placement that can help both parties diagnose issues.

A little known feature in ciBioBase allows users to reprocess their Lowrance HDS/Elite sonar log at different color and sensitivity settings (Figure 1).

Figure 1. Trip Reprocessing Tab that allows ciBioBase users to reprocess their trips with new edits.  Try reprocessing your sonar log at a higher color (e.g., 240) for “cooling” the colors in your sonar log in ciBioBase and to bring out subtle bottom features.

Sometimes, your Sonar Log may look a little too “hot” making it difficult to distinguish between plants and bottom (Figure 2).

Lowrance, ciBioBase, Sonar Log
Figure 2.  Sonar Log showing colors that may be “too hot” to distinguish between plants and bottom.

Try reprocessing the sonar log at a colorline of 240 (default is 220).  This will bring in “cooler” colors to the sonar log and may help you better distinguish subtle bottom features and gaps in plant beds (Figure 3).

Figure 3.  Sonar Log reprocessed with a colorline of 240.

Alternatively, Lowrance has a powerful free desktop software program called SonarViewer which allows you to replay your Sonar Log with options to dynamically control sensitivity, colorline, zoom, and range (Figure 4).

Figure 4.  SonarViewer is a free download from Lowrance and has a range of tools for enhancing the contrast of bottom features detected by your Lowrance HDS or Elite.

Use SonarViewer to review your files prior to upload to ciBioBase if you suspect possible signal quality issues or are testing different transducer setups for optimal signal quality.  Signal Quality should also be continually monitored by watching your SONAR page on your HDS or Elite while collecting data on the water.  A helpful rule of thumb is that a signal that is clear and crisp to your eyes is most likely clear and crisp to ciBioBase algorithms.

An Unfair War with Aquatic Invasive Species

The Importance of Aquatic Vegetation Abundance Mapping and Long Term Monitoring from a Layman’s Perspective

 

From a layman’s point of view it can be very difficult to understand the importance of lake weeds as they relate to aquatic invasive species (AIS).  I should know . . . I’m a layman.  I started asking questions, and it turns out it’s a bit more complex than I thought.  Sure, I want the Minnesota Lakes I love to be clear with tons of fish, but do we really need these weeds?  Of course we need some “weeds” (“aquatic plants”), and, if you get rid of too many you can throw the entire lake ecology out of balance for years.  When I asked how much is a good amount and how it is being tracked in Minnesota I was disappointed with the answer.  During my time working for the software company Contour Innovations, focusing on automated lake mapping, I’ve had the pleasure of working with some of the most talented aquatic biologists in the Country, both in-house and through our customer base.  I’ve spent the last few years learning the language and attempting to catch on from a neutral, outsider’s perspective.  Slowly, I realized that the complicated topic could be effectively communicated to anyone that cares about and has an interest in water quality . . . which should technically be everyone.

Let’s face it, the DNR has done a great job demonizing invasive species for good reason and with some positive results.  There’s more awareness now and budgets in place to attempt to manage the spread and introduction.  But, eradicating AIS once introduced into a lake is only half the story.  . .
I’ve learned a lot over the last few years but I still had some questions:  Why should our customers really care about the total habitat when Eurasian Water Milfoil has already invaded their lake?  Don’t they just want to know where the Milfoil is so they can get rid of it?  If a monitoring program can’t distinguish between species does it still have a use in aquatic research or management?  I originally thought that identifying where the Milfoil is located is key, but I actually found the opposite to be true.  If we live by the idea that “AIS are bad and should be eliminated at all costs,” wouldn’t the results be easier to obtain? 
The concepts of ecosystem balance are extremely complex but vital.  After early discussions with our biologists it become clear to me that abundance is one of the most important metrics to consider when monitoring water quality and lake health.  This remains true if an invasive species has already been introduced or it’s just knocking on the doorstep.  We need to focus our analysis on total abundance and the overall aquatic habitat instead of speciation as a sole predictor of lake health.  What really matters is knowing if your lake is at risk of the negative impacts from invasive species and if your lake ecology is within certain “healthy” parameters.  A lake’s resilience to invasive species and current water quality regime is going to be a major indicator of lake health and prospects for the future.  It’s also important to quantify your management interventions and determine if they are having their desired effect.  These were difficult questions to answer in the past. 

Invasive species are coming.   We can try to stop it but more likely we’re just delaying it.  The reason these species are thriving is because they’re designed to thrive.  With the right conditions they can easily steal the resources required to grow from other plants, effectively eliminating competition from the lake.  They’re opportunistic and the microscopic amount required for infestation is astonishing.  We should accept this fact and be realistic about what we’re dealing with.  It doesn’t mean we roll over and stop the cleaning stations or citations for failing to drain your bilge, but a proactive management and monitoring plan is a good idea.   

Let’s understand our lake’s resilience and identify if it’s at risk.  Let’s get our resource managers identifying which lakes need close attention and devote our stretched budgets to the ones that need it.  The chips are already stacked against us and without good quantitative data, they’re stacked even further.   With mismanaged resources it becomes a war we can’t win.

At a certain level of productivity, an invasive species will win the war against a diverse ecological aquatic habitat and turn into a lake of a single species.  This isn’t a good thing for any lake ecosystem or water quality.  It’s all about balance and a healthy lake habitat can help keep an infestation in check.  It’s also possible that certain management techniques could push a lake towards a higher risk scenario if decisions were made without quality abundance data.  Understanding the risks of this happening are key in designing a management plan to be proactive instead of reactive.  Identifying hot spots in abundance and potential causes could be more important than identifying where the invasive species exist.  The best thing is that it’s never too early or late to start. 

The entire ecosystem is tied together.   The cumulative effect of lake stressors can lead to the low resilience required for an invasive species to thrive.  Identifying the stressors and dealing with them could prove more valuable than eliminating an invasive species.  Much like a healthy body can deal with the flu virus better than an unhealthy one, a lake with good shorelines, healthy fish communities, and healthy diversity of plant abundance can keep an infestation in check.  In certain conditions, taking plants out of the lake might be a bad decision that could have a negative effect on lake ecology depending on the lake regime and characteristics of the lake.  
In fact, there are ideal targets and optimal or idea habitat levels and conditions.  Our own Ray Valley, a 10 year veteran of the Minnesota DNR, has devoted a majority of his career to habitat monitoring and interactions between plant abundance, fish, lake resilience and relationships to water quality.  His research on ecosystem balance, namely lake resilience, is instrumental in understanding what’s really happening in a lake and when lakes are at risk.  Much of this is actually tied to plant abundance and changes over time.
Through a long term monitoring program it’s possible to identify the red flags.  Plant abundance growing at deeper depths from year to year could show an increase in water clarity allowing more light penetration.  This might be caused by a recent zebra mussel infestation or a shift in the lakes ecology.  Regardless, something as simple as the depth aquatic plants grow tells us a ton about the direction the lake is going.  In another example, unusual increases in plant abundance in specific areas could indicate, among other things, a home with a leaking septic tank on the lake, a change in the landscape, changes in sedimentation, a run-off issue or a bigger problem upstream.  All of these, left unchecked, could cause more problems for the lakes balance and resilience leading to higher risk of negative impacts of an invasive species introduction.   These changes don’t show up in a visual reconnaissance, presence/absence surveys with a rake, or a single map.   But getting these items resolved could be the management technique that keeps an invasive species from dominating a lake habitat in the future and early detection of these problems could prevent an unfair fight against AIS in the future.
Complete dominance of an invasive species is another story but it’s also the exception.  I’ve seen a number of groups continue to dump massive amounts of money into management without quantitative goals or the ability to effectively quantify the whether they are meeting their management expectations.  Maybe we’re not asking the right types of questions or maybe the technology didn’t exist to get the information we need.  No one is at fault yet.  Once the dialog shifts away from hysterical talking points and towards pragmatic management approaches, we’ll start making real strides in getting ahead of AIS and start achieving improvements in our precious lakes.

So where do we start?  With crowd-sourced solutions like ciBioBase.com we can all start getting the volume of data we really need to have this realistic and proactive discussion.  With cloud computing we’ve broadened the base of individuals that can participate allowing passionate home owner groups to take matters into their own hands instead of waiting for an understaffed DNR.   Aquatic plant abundance maps that took a highly trained hydrographer a week or more and to complete can be done by anyone with a boat, a depth finder and GPS, and 20 minutes for computers do the work of processing the collected data.  This is the future of monitoring and lake management.  There are no longer barriers to getting the kind of data we need for identifying the red flags, eliminating stressors and improving lakes across Minnesota and the globe.
So, let’s understand the lakes heartbeat first.  Let’s get a clear picture of the lakes resilience and its current status for optimal health.  Then we move forward to a future with cleaner lakes.

This article represents and aggregation of my thoughts as I’ve journeyed through this industry and tried to learn the ropes.   This is merely an appeal to think differently about our lakes, expectations, and what the future holds.  The future of our most important resource is brightest if we take a step back, think about what we’re doing and where we need to go.
 
Let’s have those realistic and proactive discussions with real data . . .
                                                         -Matt Johnson, CEO, Contour Innovations, LLC

 

CONTOUR INNOVATIONS AND CIBIOBASE

ciBioBase (ciBioBase.com) removes the time and labor required to create aquatic maps! ciBioBase leverages log file formats recorded to SD cards using today’s Lowrance™ brand depth finders and chart plotters. Data you collect while on the water is uploaded to an online account where it is processed by our servers automatically! We rely on automation to make vegetation mapping cost effective by reducing the technical skills, staff, and hours to produce vegetation abundance maps from raw sonar collection. With the human element gone, you get accurate and objective mapping at lightening speeds! The result is a uniform and objective output all over the world!
I’m proud to be a part of this step in the right direction of a positive future for lake management and overall quality of our most precious resource.  We’re shaking things up and this is a time when everyone benefits.  We work as a huge team to define the best uses and features of one of our products, BioBase, to change the lake management industry.  We’re using expert opinions and powerful cloud computing to create amazing contour and vegetation maps and gain important quantitative metrics of lake health.

Our Company has a culture that considers its social responsibility and contribution.  Our sales team is motivated by how they are changing the future of lakes and resources management.  I was most intrigued by what we might be contributing to the future of a resource that means so much to me.  I’m still intrigued!

Aquatic Plant Abundance Mapping and Resilience!

Merriam-Webster Defines resilience as an ability to recover from or adjust easily to misfortune or change.  Eminent University of Wisconsin-Madison Ecologist Dr. Steve Carpenter further adds that resilience is the ability for a system to withstand a “shock” without losing its basic functions, http://www.youtube.com/watch?v=msiIV5NdLVs

Resilience is a relatively easy concept to understand, but it can be difficult to measure in lakes without monitoring subtle changes over time.  This stresses the importance of long-term monitoring and being on guard for new changes to water quality, aquatic plants, and fish.  Volunteer networks and agencies across the country are making great strides in monitoring water quality by dropping a disk in the water and scooping up some water and sending it to a lab for analysis.  In essence, taking the lake’s “blood” sample.  Indeed, water quality samples can be very telling.  But what is happening to the rest of the lake “body”?  How is it changing in relation to its liquid diet of runoff or medication to treat invasive species?  Unfortunately, until now, natural resource agencies, lake managers, and volunteers have not had the capabilities to objectively and efficiently assess these changes without time-intensive, coarse surveys of vegetation cover.

Your body’s immune system is the engine of resilience.  When your immune system becomes compromised, you become vulnerable to a wide range of ailments that may not be a threat to someone with a healthy immune system.  The same goes for lakes.  In the glaciated region of the Upper Midwestern US and Canada, healthy lakes are those that have intact watersheds where the hydrologic cycle is in balance.  Without going into great depth, keeping water where it falls (or at least slowing it down), goes a long way in keeping the hydrologic cycle in balance.  Healthy glacial lakes also have clear water, a diverse assemblage of native aquatic plants, and balanced fish communities.  When humans or the environment alter any one of these components, the lake must adjust in order to compensate for those alterations and remain in a healthy state.  The ability of the lake to do so is this concept of resilience (Figure 1).

Figure 1.  Conceptual diagram of a resilient system.  The height of the slope and the deepness of the valley are the compensatory mechanisms that bring a lake back to some resilient baseline condition after a short-term “shock” like a flood or a temporary septic failure.  Lakes with forested watersheds, clear water, native aquatic plants, and balanced fish communities are typically in this condition.

Slowly, as more curb and gutter goes in, green lawns replace native grasses, personal swimming beaches replace marshes, fish are overharvested or overstocked, or invasive species are introduced, the lake slowly loses its ability to compensate (Figure 2).  All of a sudden you hear “I’ve never seen that before” become more common when people describe a phenomenon on the lake that well, they’ve never seen before.   You may start to observe more algae blooms, more attached algae on rocks and plants, plants growing where they’ve never grown before, invasive species taking hold and thriving.  This is an example of the lake losing resilience and succumbing to the vagaries of the environment.  Under these circumstances, the lake can’t compensate anymore and you never know what you will see from year to year.  With no baseline, objective assessment of aquatic plant abundance and no monitoring of change in abundance and cover from year to year, it makes it even harder to know how much the lake has actually changed and what you need to try to get back to with implemented best management practices .

Figure 2.  An example of the consequences of the cumulative impacts of environmental and human stressors on lake resilience.  As lakes become more impacted by various watershed and in lake practices and invasive species, resilience is slowly worn away.  The valley becomes more shallow and a new “domain” enters the picture.  Lake conditions slosh around from one state to the next depending on the vagaries of weather and other disturbances.  Not knowing to expect from one year to the next becomes the norm.

A demonstration of the difference between a resilient lake and one that is losing resilience can be found in a paper published by Valley and Drake in Aquatic Botany in 2007 entitled “What does resilience of a clear-water state in lakes mean for the spatial heterogeneity of submersed macrophyte biovolume?”  Valley and Drake found very consistent patterns of vegetation growth from one sampling period to the next over three years in a clear lake (Square Lake, Washington Co. MN USA; Figure 3).  Each survey in Figure 3 took two days to survey and another week to make these plots.  Not including time on the water, ciBioBase produces these same plots in an hour.
 

Figure 3.  Submerged aquatic plant biovolume (% of water column inhabited by plants) as a function of depth in Square Lake, Washington Co., MN USA.  Notice the consistency of the pattern of vegetation growth from one time period to the next (study took place for 3 years from 2002-2004; Valley and Drake 2007).  Water clarity in Square Lake is high with diverse aquatic plants.

In contrast, patterns of vegetation growth were quite variable in a moderately turbid lake with abundant Eurasian watermilfoil; West Auburn Lake, Carver Co. MN USA; Figure 4).  For example, in summer 2003, a bloom of attached algae formed on Eurasian watermilfoil stems and effectively weighed down the stems and prevented them from reaching the surface.  This bloom was unique to 2003 and was not observed at any other time during the study.

Figure 4.  Plant growth as a function of depth in a moderately turbid Minnesota Lake with abundant Eurasian watermilfoil (West Auburn Lake, Carver Co. MN USA; Valley and Drake 2007).  Plants grew shallower and more variable in this more disturbed lake. 

If stressors continue unabated, then the lake can “tip” into a new, highly resilient domain of poor health (Figure 5).  The feedback mechanisms that used to keep the lake in a healthy state have now switched to new feedback mechanisms that are keeping it in an unhealthy state.  Algae begets more algae, carp beget more carp, stunted bluegill beget more stunted bluegill, if invasive plants are lucky enough to grow, they beget more invasive plants.  Getting the lake back to the original state is nearly impossible at this point.  It’s like Sisyphus rolling the rock uphill only to have it roll right back down again!  Although controversial, at some point, citizens, regulators, and lake managers need to start rethinking expectations and adapting management approaches in highly degraded systems.  Rather than trying to restore a lake to a Pre-European settlement condition through expensive, risky, and Draconian measures, it may be more reasonable to ask: “How can we have good enough water quality to support naturally reproducing stocks of game fish?”  “Can we manage invasive plants in a way that maintains fish habitat AND recreational opportunities?”  After the wailing and gnashing of teeth subsides and some agreement is reached on objectives and management strategies, then it becomes essential to determine whether implemented management practices are having their desired effect.  It doesn’t take two weeks and $10’s of thousands of dollars to do a vegetation survey.  Volunteers can do it, lake consultants can do it, state agencies can do it and they’ll all do it the same objective way with ciBioBase and they can all work together!

Figure 5.  Example of a lake that has flipped into a degraded regime regulated by new feedback mechanisms that keep it in the degraded state. 

The Upshot

Resilience is an easy concept to understand on a basic level, but hard to measure in lakes and changes slowly over time.  This stresses the importance of long-term monitoring and being on guard for those things “you’ve never seen before.”  Uploading data to ciBioBase every time you are on the water gives an objective and quantitative snapshot of the current conditions in your lake of interest.  Be watchful for anomalies in monitored areas.  Vegetation growth should follow a relatively predictable pattern from year to year and if it doesn’t, that may be the first indication that the lake is losing resilience and precautionary conservation measures should be taken.  Conservation measures may include better onsite storm water infiltration (e.g., rain gardens, nearshore vegetation buffers), maintaining a modest amount of aquatic plant growth in the lake, maintaining a balanced fish community in terms of species, size, and abundance.  These efforts will go a long way in protecting the long-term integrity of our beloved lakes!

Suggested Readings:

Carpenter, S.R., 2003. Regime shifts in lake ecosystems: pattern and variation. In: Excellence in Ecology, vol. 15, Ecology Institute Oldendorf/Luhe, Germany.

Scheffer, M., 1998. Ecology of Shallow Lakes. Chapman and Hall, London.

Valley, R.D. and M.T. Drake 2007.  What does resilience of a clear-water state in lakes mean for the spatial heterogeneity of submersed macrophyte biovolume? Aquatic Botany 87: 307-319.


Auto Blue Scale Bathymetry Mapping

Contour Innovations (CI) is announcing the addition of a new feature of our BioBase System.  As many of you know, each trip uploaded to your account is processed for depths and plant canopy heights to automatically create maps and output the layered data in your interactive online account.  From now on, depth contours will be displayed in blue scale after launch of our new blue scale image feature.  When loading your vegetation layer, blue scale will disappear but transparent contour lines will display beneath the % biovolume output. 
This feature is great for lake and pond managers that are interested in getting a quick assessment of any sized water body to understand where the deep spots are for diffuser placement and overall management.  We still employ a TIN anlysis for accurately estimating total water volume.  On a pay per upload plan, our customers can get this data quickly for as little as $100 per water body and in as short as 10 minutes.   You collect the data with your low cost Lowrance HDS depth finder, upload it to a secure account from your computer, and the raw sonar is processed in the cloud in minutes.  Images of the blue scale can be exported with ease to be included in management plans (images in this blog are direct exports from the BioBase System).  State agencies are using the System for bathymetric output to update their existing lake maps provided to anglers.    This is just another great feature added to the powerful BioBase System.
To further demonstrate the power of automation and centralization anyone that has already uploaded trips to the BioBase System can now get blue bathymetry for those uploads with little effort.  To try it out, log into your account and click the interactive viewer for any trip.  Using the REPROCESS tab, check “contours” and resend the trip to our servers.  Within minutes you will get an email letting you know that your reprocess has been completed and blue scale will be provided for this trip.  Using an online account there are no software updates or manual processing of older trips.  Let our servers do the work.  That’s what they’re there for.  Anytime we add a new feature to BioBase, anything you’ve already uploaded to your account can be updated.   It’s pretty cool stuff!

Please contact us with any questions at matt@ContourInnovations.com or 715.864.9347.  Pond managers can contact our exclusive partner, Aquatic Eco-Systems (Orlando, FL) at mattr@aquaticeco.com or 407.462.4697.  Let us know what you think!