How I taught Streamflow online in Spring 2020

This post is part of a series in which I provide the details of each unit I taught post-transitioning to online in Spring 2020 in the Watershed Hydrology class at Kent State University. For more context about the course and my perspective on it, please read the introductory post. [I’ve added some bracketed notes about things I’d change up for a future online offering.]

Finally, we’ve made it to the stream! This section of the course focuses on water flow in streams (streamflow, discharge, Q). We’ll focus on the following topics:

  1. Why is measuring streamflow important?
  2. Why does streamflow vary over time?
  3. How do we measure streamflow?
  4. How do we find streamflow data?
  5. What are some hydrologic analyses we can do with streamflow data once we have it?

I have a fair number of different resources to cover these five topics, so I’m going to insert some sub-headers in the material below. You can use them to help you keep track of what you are supposed to be focused on.

Learning Objectives

  1. List some of the ways that streamflow data are useful.
  2. Explain why long term stream gauge records are important.
  3. Describe what a water year is and why it starts when it does
  4. Identify whether storms contribute a large fraction of total flow in urban streams
  5. Explain how USGS stream gages work and how stage is measured
  6. Describe why velocity varies in four dimensions and how velocity is measured
  7. Explain the function of a rating curve or stage-discharge relationship
  8. Demonstrate how to identify and download different types of data from the USGS NWIS website
  9. Explain the appropriate uses, units, and graphical conventions for hydrographs, unit hydrographs, and hydro-hyetographs
  10. Describe what a flow duration curve is, how to make one, and how to read the flow percentiles off of one

Why is measuring streamflow important?

Streamflow is of course an important output for watershed’s water balance. Plus, it’s a lot easier to measure that evapotranspiration, so accurate measurements of precipitation and streamflow, combined with some simplifying assumptions, can be used to estimate the actual evapotranspiration of an area.

It’s OK to geek out about streamflow data just because you have fallen in love with all things hydrology. But what are the practical reasons to measure streamflow? Why does the USGS operate over 8000 streamgages around the country? This webpage from the USGS Water Science School lists a bunch of really good reasons to measure streamflow and does a great job of slightly expanding on the topics of the video above.

Why does streamflow vary over time?

Streamflow varies by month and year

This USGS Water Science School webpage gives a brief overview of why we need to measure streamflow every day for many years – because it varies seasonally and interannually (across years). In the associated problem set, I have students look at seasonal and internannual patterns of flow (but their graphs will look a little different than the ones the USGS made here, as I ask them to work in unit discharge in metric units.)

Why we need long-term streamflow data

I’ve teed this video up to a key excerpt about why we need long-term streamflow data. This is followed by some good comments about how climate change adds uncertainty to our understanding of streamflow regimes. (The rest of the video is great too, giving an expanded version of why streamgages are important)

What is a water year and why does it start on October 1st?

In this blog post, I explain the rationale behind the timing of the water year in the United States.

How much water flows during storms?

In this USGS Water Science School webpage, you will learn about the magnitude of peak flow and total stormflow relative to baseflow. The page also talks about the characteristic flow regime of urban streams. Note that some streams, especially those sustained by a lot of groundwater, will have a very ratio of stormflow to baseflow over the course of the year.

How do we measure streamflow?

All the things you need to do to measure streamflow

I created this video during an online office hours session, which means that it is really long (50 minutes), has some hilariously bad attempts at drawing with a mouse and unfunny jokes, and there are slides (30 MB, PDF) to go with it. I advised students that it they didn’t want to watch the whole thing, they should look at the slides carefully and then identify the sections of the video they needed to watch in order to check their understanding or gain additional content.

After watching the above video (or not), you should take a look at the videos below that show actual USGS gages and streamflow measurements. You can also get the TL;DR version of how to measure streamflow on the page linked below.

What does a USGS gage look like and how does it measure stage?

I haven’t found the one perfect video that shows you everything I wished you could see about how a stream gage works, but here are two videos that let you peek inside a USGS gage. The first video gives you a good general overview:

This second video gives you the view from a USGS hydrologic technician as she checks on the gage and makes a streamflow measurement.

It is important to note that both of these videos show gages that operate with a stilling well. But USGS gages also use other technology (bubblers, ultrasonic) to measure depth. I just can’t find a video showing these.

Making streamflow measurements

Too much detail in my 50 minute lecture? Or just want to check to make sure you’ve got the important points? Then read this web page straight from the experts at the USGS for the highlights.

Want to see what it actually looks like to make a streamflow measurement by wading or from a bridge? These two videos from the USGS give you a glimpse of the process.

How do we find streamflow data?

The following videos show how to find and access data from USGS stream gages via the National Water Information System. I designed these to be helpful for my students who are required to find, download, and manipulate USGS data in order to complete the associated problem set.

The USGS National Water Information System is the primary portal to streamgage data in the US. It’s important to understand the different ways you can identify a dataset to investigate – or just to see how much water is in your local stream or river. 

In this video, I take you on a tour of the streamflow information you can find on the USGS NWIS website, using the Cuyahoga River at Jaite as our example gage. I talk you through what the graphs and tables on the current and historical observations page mean, how to see where the gage is located and look at the availability of other types of data, and then…very importantly for the problem set, I show you how to get to the daily data page, select the date range you want to examine, and save the data to your computer in a way that will be useful for opening in Excel or another spreadsheet program.

This video should help you get data into Excel or Google Sheets to complete the problem set 10. If you use a different browser or spreadsheet program, your may find that things are slightly different than what I do, but you can usually google or find a youtube explainer for how to do the file saving and importing.

If you use Google Sheets, create a new sheet, then go to file –> import data. Locate your saved txt file and then a menu like the one below should pop up. Leave everything as it is and click the big green “import data” button and you will have your data into columns properly. Then you can tidy it up as shown in the video above.

In this video, I show you three ways to examine the field measurements of discharge that underpin the continuous timeseries of streamflow you can find on the US Geological Survey (USGS) National Water Information Service (NWIS) website. I show you how to display the measurements on a graph of streamflow, where to see the actual rating curve, and the way to access the tabular data showing individual field measurements. Put together, all of these things should give you a small sense of how hard USGS hydrologic technicians work to produce good quality streamflow data.

What are some hydrological analyses we can do with streamflow data?

Oregon State University has some excellent tutorials on streamflow analysis techniques. From the page linked here, you can go to pages on: annual analyses; monthly analysis; flow-duration analysis; and flood frequency analysis. These pages have links to examples and tutorials, including with Excel screenshots.

I have adapted these tutorials into my own guide (PDF) to making hydrographs, constructing flow duration curves, and conducting a flood frequency analysis. [Note: I discovered this year that some students got thrown off by the equation that told them to multiply the probability (P) by 100 to get to %. Then, when I told them that recurrence interval was 1 / P their numbers were incorrect. I will fix this in a future year.]

In the video below, I talk through some of the basic ways we can examine and analyze stream discharge data: hydrographs, unit hydrographs, flow duration curves, and runoff ratios. I provide some pointers on how to make effective and visually appealing graphs. This video shows the sorts of graphs students make as they work on the associated problem set.

Just want to look at the slides instead? Here you go (21 MB, PDF).

Assessment

  • 10 question multiple choice quiz, with questions drawn from a larger bank. Students had the opportunity to take the quiz twice.
  • Problem Set in which students download daily USGS data from 2 streams, construct unit hydrographs and flow duration curves and compute some basic metrics. Students are then asked to write a few paragraphs contrasting the streamflow regimes and explaining why they see the patterns they do based on climate and landscape. Students have already delineated the watersheds and computed watershed characteristics using StreamStats in an earlier problem set.
  • Questions on the final exam.

Please respect my work

This work (my videos and blog posts) are licensed under an Attribution-NonCommercial-NoDerivs 3.0 Unported (CC BY-NC-ND 3.0). That means that you need to give appropriate credit if you use or modify anything I’ve posted here. It also means that you can’t use the material for commercial purposes. If you want to use other resources I’ve listed above, please respect the rights of the originators. If you want to use my sequencing of topics and resources in your class, by all means, go ahead.

Categories: by Anne, hydrology, teaching

How I taught Streamflow Generation online in Spring 2020

This post is part of a series in which I provide the details of each unit I taught post-transitioning to online in Spring 2020 in the Watershed Hydrology class at Kent State University. For more context about the course and my perspective on it, please read the introductory post. [I’ve added some bracketed notes about things I’d change up for a future online offering.]

Overview of Streamflow Generation Unit

We’ve talked about how water goes down (precipitation), up (evapotranspiration), and down (infiltration).  Streamflow is the last major term in the water budget – but before we can talk about streamflow we’ve actually got to get the water into the stream (or wetland or lake or …). That’s what we’re going to study now. 

I made a video to introduce you to this topic and define a few key terms. Watch this first and then proceed to work your way down this page watching videos and reading content as you go. 

The slides that accompany this video can be found here.

Learning Objectives

  1. Distinguish between baseflow and stormflow (also called quickflow) and explain when each occurs
  2. Describe the conditions that generate infiltration-excess overland flow and where it is likely to occur
  3. Describe how saturated overland flow works and explain how it is different than infiltration excess overland flow
  4. Explain the requirements for subsurface stormflow and discuss the sequence of events that occurs for it to be produced
  5. Discuss how the variable source area concept is related to subsurface stormflow and saturation overland flow
  6. Illustrate the different connections that can occur between groundwater and streams and lakes
  7. Explain how groundwater pumping can affect streams
  8. Analyze how streamflow generation mechanisms affect stream peak flows and lag times
  9. Define velocity and celerity in the context of hydrology
  10. Discuss how climate, topography, soils, and geology influence the streamflow generation mechanisms that operate in a watershed
  11. Examine how human actions can influence streamflow generation mechanisms and associated hydrograph characteristics

What is streamflow generation?

Terminology note: In the video above and in other resources listed below, you may see the phrase “runoff generation” used. I prefer the term “streamflow generation” because I’m interested in all of the ways that water gets to streams (or other water bodies), not just ways that involve surface runoff or overland flow. I also use the term streamflow generation to talk about how we get baseflow (i.e., water in the stream between storms), which is not runoff. 

Required Reading

The Runoff Processes website (from the COMET international edition) has short pages of text accompanied by good animations of the processes being discussed. You should work your way through:

  • Overview of Runoff
  • Paths to Runoff
  • Basin Properties
  • Soil Properties (this should be a review from our infiltration section)
  • Modeling Concepts (recommended, but not required)
  • Summary

Take the practice multiple choice quizzes at the end of each section to check your comprehension.

You should also read Chapter 5 pages 125-138 in your Brooks et al. textbook, if you haven’t already done so.

Details of the Streamflow Generation Mechanisms

I created video lectures discussing infiltration-excess (Hortonian) overland flow (HOF), saturation overland flow (SOF) and the variable source area concept, and subsurface stormflow (SSF). I’ve already posted those videos in a separate blog post, with some wrap-around text. You can read the blog post here.

If you or your students just want the slides I used, you can get the HOF ones here, SOF ones here, and SSF ones here. If you use them, please credit me and Cornell University’s Dr. Todd Walter for the animated sequences. Dr. Walter also has an excellent page with more details of infiltration-excess overland flow and one on saturation overland flow.

More about Groundwater and How it Interacts with Streams

Every year, some students in my class have had a full hydrogeology course, while others know nothing about groundwater. I have struggled to find the right approach to teaching groundwater basics within the confines of a broader watershed hydrology class, while not boring/overwhelming my students depending on their background. I’ve decided that focusing on groundwater-surface water interactions is the way to go. The video below by Ken Bradbury provides an excellent introduction to the topic and I think hits the mark better and more concisely than I have ever done in person.

The video was produced by the American Geosciences Institute (AGI) and is actually part of one of three that together make a nice hour-long seminar on Water as One Resource, with multiple presenters. You can access all three parts, the associated slides, and even quizzes through the AGI Geoscience Online Learning Initiative website. Ideally, I’d love to have students complete the whole sequence, which I think would be appropriate for both those with and without a hydrogeology course under their belt. But in the interest of simplifying log-ins and content during this highly unusual semester, I opted for just the video shown above.

How flow generation controls stream hydrographs

I’ve written this as a blog post to help you make the connection between what’s happening on/in the hillslopes to what happens in the stream. The different flow generation mechanisms affect the way a stream responds to rainfall. How quickly does the water start to rise? And how high do the peak flows get? (Estimated reading time: 10-15 minutes)

Zooming Out: How climate and landscapes control flow generation

This is another blog post I wrote, in which I try to put the flow generation mechanisms in context of watershed characteristics. We’ve been talking about watershed characteristics all semester long, and here is yet another way that they are important for understanding (or even predicting) what happens in the streams. (Estimated reading time: 7-10 minutes)

Masterclass on Streamflow Generation

This is totally optional and not in any way required for anyone, but if you think that streamflow generation mechanisms are just about the coolest thing that you’ve ever heard of, then you can learn so much more about them from one of the world’s leading experts on hillslope hydrology: Jeff McDonnell in this 3 hour short course (requires flash).

When I was a graduate student I got to take a 10 week hillslope hydrology class with Dr. McDonnell and it changed the way I think about the world beneath my feet. Listening to 3 hr recorded presentation isn’t nearly as good, but you could still learn a lot if you want to do a deep dive.

Assessment

  • A 10 question multiple choice quiz, drawn from a bank of more than 10 questions, which students had the opportunity to take twice.
  • Questions on the final exam.
  • I don’t have a problem set that accompanies this unit, but I’d love to hear how others treat this topic quantitatively or in terms of data interpretation in a similar course.

Please respect my work

This work (my videos and blog posts) are licensed under an Attribution-NonCommercial-NoDerivs 3.0 Unported (CC BY-NC-ND 3.0). That means that you need to give appropriate credit if you use or modify anything I’ve posted here. It also means that you can’t use the material for commercial purposes. If you want to use other resources I’ve listed above, please respect the rights of the originators. If you want to use my sequencing of topics and resources in your class, by all means, go ahead.

Categories: by Anne, hydrology, teaching

How I taught Soil Moisture and Infiltration online in spring 2020

This post is part of a series of posts in which I provide the details of each unit I taught post-transitioning to online in Spring 2020 in the Watershed Hydrology class at Kent State University. For more context about the course and my perspective on it, please read the introductory post. [I’ve added some bracketed notes about things I’d change up for a future online offering.]

Learning Objectives:

By the time you’ve worked your way through these materials, I expect you to know how to:

  • Explain the relationships between the concepts of gravity drainage, capillary water, adsorbed water, saturation, field capacity, and wilting point.
  • Give examples of how a sponge can be used to demonstrate infiltration and soil moisture concepts
  • Diagram a vertical profile from the land surface to the saturated zone, identifying important zones for hydrologic processes
  • Describe how volumetric water content, matric potential, and pressure potential change throughout the vertical profile.
  • Discuss how soil properties influence infiltration capacity.
  • Explain why hydraulic conductivity is affected by the water content of the soil
  • Recall the key difference between the Horton Equation and Green-Ampt equation
  • Summarize the key assumptions and features of the Green-Ampt equation
  • Explain why each of the variables in the Green-Ampt equation (for vertical infiltation with ponding) appears where it does in the equation.
  • Describe how a Guelph permeameter and double ring infiltrometer work

“Lecture Slides”

“Lecture Slides” for Soil Moisture and Infiltration(18 MB, PDF). [Note: These are the slides I was planning to use and had posted for my class before we went online. I keyed the resources I posted for my students to the slide numbers here, so student could cross-reference my slides and whatever video or blog post they were looking at. After this unit, I abandoned unit-long slide decks.]

Soil Moisture Concepts and Measurement (slide 2)

This 25 minute video was recorded in 2018, and was part of a several year effort to shift the time I was spending in class talking about measurement techniques out of the classroom. I wanted to make more time for fundamental concepts and hands-on explorations during our 75 minute class periods. In a normal year, I would go over the concepts in class, and then send them to the video for review of the concepts and info about the measurement techniques. I have a question on the problem set that asks the students a question about the measurement techniques that is very answerable if they’ve watched the video and paid attention.

Soil Water Potential (slides 4-6)

This 17 minute video introduces the concepts related to soil water potential and provides a worked example of a simple problem.

How wet is the unsaturated zone? (blog post, slide 7)

The link above is to a blog post I wrote that steps you through a diagram of the unsaturated zone and the relevant water content and water potential states of each part of the vertical profile. 

There is also a short video, by Oregon State’s John Selker, that talks about the unsaturated zone more generally and it may be helpful if you are feeling a bit lost.

Sponges as Models for Soils (slides 8-16)

On our last day of in-person class, we broke out a bunch of sponges, water, and cafeteria trays for catching the mess and played with simulating the various moisture states of soils. We also watched how the wetting front propagates downward during infiltration and used some strangely water-repellent sponges to discuss hydrophobicity. The website linked above has photos and descriptions for those not able to take part in class, but I think this activity is one that could fairly easily be done by students at home (as long as they have a sponge) in an online course.

Hydraulic Conductivity – Saturated and Unsaturated (slides 20-22)

The link above is to a blog post I wrote on hydraulic conductivity. The blog post contains a nice video explanation by John Selker of why unsaturated hydraulic conductivitiy is lower than saturated hydraulic conductivity. The blog post also contains another video by John Selkerthat tells you more about the soil water characteristic curves shown in slide 15. [We talked a little bit about soil water characteristic curves, but they are an example of the sort of content that I expect graduate students to spend more time learning than the undergraduates in this course.]

Soil Bulk Density Increases and Hydraulic Conductivity Decreases with Depth (slide 26)

Up near the surface, soils tend to be “fluffy” – plant roots and animal burrows make lots of big pore spaces and there isn’t much pushing down to compact them. So near the surface, soils tend to be low density (1 g/cm3 is common – and that’s the density of water) and they tend to have relatively high hydraulic conductivity.

As you go deeper, plant roots and animal burrows go away and the overlying soil starts to squeeze and compact the pore spaces. As a result, soils get denser and have lower hydraulic conductivity. The soils are still a lot less dense than solid rock though – quartz has a density of 2.6 g/cm3. But once you get past 1.4 g/cm3 plant roots have a hard time getting through the soil . 

Of course, what happens at the surface can really change the vertical profile. In the images in the slide, notice how the grazed soils have higher bulk density and lower hydraulic conductivity near the surface. Animal feet are good at squishing those fluffy surface soils.

How do soil properties affect infiltration and water movement through soils? (slides 26-28)

Read through the five very short web pages (linked above) on how soil properties affect infiltration and runoff generation. You’ll learn about soil texture classification, soil composition, soil profiles, and surface properties. There are even some review questions you can use to check your understanding. [These web pages were produced by the COMET program, international edition. We also came back to this website when we discussed runoff generation in greater detail.]

Macropores (preferential flowpaths that influence infiltration) (slides 28-29)

Macropores are some of my favorite things. The link above takes you to a page built by Cornell’s Todd Walter. It does a really nice job of explaining what macropores are, why they are important, and it provides some pictures. If you want to know more about other types of preferential flow (finger flow, funnel flow), you can follow the links at the bottom of that page. 

The video below was taken by one of my former graduate students, at his field site. I love to see classroom knowledge being applied in the real world. And the excitement!

Infiltration equations (slides 33-35)

This video by Oregon State’s John Selker talks about the Horton Infiltration equation (slides 33-34) and how it is empirical – which means that it based on measured data and relationships, without reference to any physics. Other infiltration equations (like the Brutsaert one in the video), the Richards Equation (slide 35), and the Green-Ampt equation (slides 36-44, Problem Set 8) are fundamentally rooted in physical understanding of how infiltration works. So the Horton equation can give you a good answer (if you have the data to put into it), but it can’t tell you *why* infiltration works the way it does. For that we need a physically based equation. 

Introduction to Green-Ampt (slides 36-39)

This video by John Selker does a pretty good job of setting up the Green-Ampt equation and the assumptions that make it a physically reasonable, but not mathematically impossible representation of reality.  Note that in the video, he focuses on the horizontal case (like near an irrigation furrow) which simplifies the math a little bit relative to the case of vertical infiltration (like for rainfall), that is shown in your slides. [I wish that there was a similarly excellent video for the vertical case, which is more relevant to the natural phenomena of infiltration.]

More Green-Ampt (slides 40-41)

This video by John Selker goes into a bit deeper detail mathematically about how the Green-Ampt equation works. Again, he uses the horizontal case, which simplifies things further than I do on the slides. But he does show some of the math involved in getting the equation into a useful form.

[I encouraged graduate students to work their way through the video and the derivation linked below, but made the material optional for undergraduates this semester. I didn’t feel confident that students could watch and read the material without much chance at interaction – in a different form than in the slides and textbook – and not come away with some confusion and/or apprehension. If I were to teach this unit online again, I would make sure to align my content with Selker’s videos and/or make my own.]

Green-Ampt Equations Written Out (slides 36-42)

The link above takes you to Todd Walter’s course notes on the Green-Ampt equation. This is a pretty thorough, yet well organized and digestible treatment of the math. As noted above, I made this material optional for undergraduates this year.

The main Green-Ampt Equation to know (slide 42-44)

Concerned I might be overwhelming students with Green-Ampt derivations, I wanted to draw their attention back to a fairly simple form presented in my course slides. Make sure you’ve followed the slides and videos enough to know where K and L come from and why Sw  and Ho are in the equation.

Green-Ampt infiltration equation for conditions with ponding, presents equation and defines terms.

Measuring infiltration capacity in the field (slides 45-48)

The above link takes you to a blog post where I explain how double ring infiltrometers and Guelph permeameters work, and remind you about the definitions of infiltration capacity and equilibrium infiltration capacity. I also have some nifty videos of them in action, including one of my students from a previous year.

Assessments

Students’ understanding of the material in this unit was assessed in three ways:

  • a problem set with four parts: (1) presenting soil moisture data time series and asking for interpretation of it; (2) using an Excel spreadsheet (that I provide) with the Green-Ampt equation embedded to change soil properties and assess the effects on infiltration; (3) using the same Excel spreadsheet to conduct a sensitivity analyses on the effects of initial water content and rainfall rate and explain their results; and (4) sending them to the Web Soil Survey and a target area of interest to assess what information relevant to the Green-Ampt equation they can find readily versus what requires assumptions of appropriate values (e.g., from a textbook table) or specialized measurements.
  • a 10 question multiple choice quiz that I wrote to align with the learning objectives. There were more than 10 questions in the test bank and students could take the quiz 2 times.
  • questions on a midterm exam that spanned evapotranspiration and this unit.

Special thanks to

Many of the amazing videos for this unit were made by Dr. John Selker of Oregon State University. You can learn even more about soil hydrology and biophysics from him at https://www.youtube.com/channel/UCoMb5YOZuaGtn8pZyQMSLuQ/playlists
And thanks also to Dr. Todd Walters of Cornell University for his clear images and explanations linked above. You’ll see more from him in the next unit on streamflow generation mechanisms.

Please respect my work

This work (my videos and blog posts) are licensed under an Attribution-NonCommercial-NoDerivs 3.0 Unported (CC BY-NC-ND 3.0). That means that you need to give appropriate credit if you use or modify anything I’ve posted here. It also means that you can’t use the material for commercial purposes. If you want to use other resources I’ve listed above, please respect the rights of the originators. If you want to use my sequencing of topics and resources in your class, by all means, go ahead.

Categories: by Anne, hydrology, teaching

Moving Watershed Hydrology online in 3 days: how I did it, how it went, and how I’m working to make it better next time

When Kent State “pivoted to online” in mid-March, I was about half-way through my Watershed Hydrology class. For context, this class typically has about 20-25 undergraduate students, from geology, environmental studies, and conservation biology majors, and about 5-8 graduate students from geology and geography. I use the first part of the Brooks et al “Hydrology and the Management of Watersheds” textbook, which students have access to as an e-book through the Kent State library, but I don’t rely heavily on assuming the students are reading it. My goal for the 2020 edition of my class was to feature a hands-on activity in the classroom approximately weekly. That unfortunately, went out the window when we pivoted online in mid-March.

Side note: I really appreciated that Kent State and other universities distinguished between our suddenly online classes (which we called “remote instruction”) and classes that were intentionally designed to be delivered 100% online. But for simplicity’s sake, I’m just going to call it online on the blog.

What I did

When we went online, I decided to use an asynchronous approach so that students could work through the material at times that worked best for them, and then use class time for “online office hours” where students could optionally come and get help with concepts and problem sets. I used a mix of videos I created and those by others, blog posts I wrote and existing web pages to support their learning. I wrote out learning objectives for each unit (~1 week of material) and created a multiple choice quiz that they could take 2 times to check their understanding of the material. Each week the students also had to a problem set tied to the concepts of the unit, but I made those deadlines soft, recognizing that it would be easy for students to get overwhelmed with everything going on during this turbulent semester.

We start the semester talking about the topographic definition of watersheds and water and energy balances. Then we spend the rest of the semester working our way through the water cycle, starting with precipitation and evapotranspiration. So by mid-March, we were in the midst of discussing soil moisture and just moving into infiltration. Because of the disruption associated with moving online, I essentially just started the unit over when classes resumed. Following that material, I had fully online units on streamflow generation, streamflow, and floods.

Watch for upcoming blog posts to provide the resources and materials I used for each of the units that I taught on line.

Looking back

Am I happy with how the online portion of Watershed Hydrology played out in Spring 2020? More or less. I think given all of the constraints surrounding the rapid transition and circumstances of the online period meant that both I and my students did the best we could. I provided content, support, and grace for students to achieve what they wanted to achieve in my class this spring. To me, that’s the most important outcome.

Would I do the exact same thing if I had to teach Watershed Hydrology online again? No. I hope never to find myself in a position to pivot to online so suddenly again, without childcare, in the middle of a pandemic, so this was clearly not a thoughtful, best-case scenarios for teaching Watershed online. I am generally happy with the content I provided, though I might scaffold it differently in a future offering, as well as add/drop some things. I would certainly write a different syllabus in terms of expectations for a fully online class.

The biggest thing I would change is that I would add a larger synchronous component to the online course, particularly if the entire semester would be online. I did have an optional synchronous component to my 2020 class, that I billed online office hours, but held during the previously scheduled class period. During that time I was available via Blackboard Collaborate Ultra and able to answer questions about problem sets and other course content. Several students regularly attended those online office hours and found them very valuable, but other students never participated and only experienced the course asynchronously after the transition online. I was very sensitive to limitations in high speed internet access, increased family care and work responsibilities, and illness, and I want to acknowledge that those limitations will continue to exist. But I would like to find a way to have broader (if not complete) participation in synchronous sessions in any future online offering. I can envision using the synchronous sessions as an opportunity not just for students to get homework help, but also for students to work collaboratively on virtual “hands-on activities” involving data exploration (e.g., via Shiny apps) or internet-hosted modeling interfaces) or have group discussions based on videos that students had watched ahead of time.

Looking ahead

While I don’t think that an online Watershed Hydrology class can offer the same experience for students and instructors as safely being in the classroom, field, or laboratory, I do think that we can offer a rich and rewarding experience online, with the right preparation and the right community infrastructure and resources. That’s why I’m thrilled to be part of an NSF-funded team working to rapidly develop and deploy such infrastructure resources for distance education in the hydrologic sciences.

In the midst of the chaos of spring 2020, a dream team of hydrologic scientists and educators, lead by Adam Ward of Indiana University, assembled to propose the RAPID and then immediately (even before funding) began to roll out community resources, including CUAHSI-hosted virtual forums and cyberseminars for discussing strategies and challenges for online hydrology education, a new Hydroshare collection of educational resources (where my course materials will go), and a virtual guest lecturer database (sign up here). Look for these activities to continue and expand through the summer and fall as we contemplate what our courses will look like in the next academic year and beyond.

While spring 2020 was incredibly rough on us as faculty and on our students, we can make future online hydrology experiences better for everyone by collaborative developing the needed tools and sharing our knowledge and resources.

Categories: by Anne, hydrology, teaching

A Riverine Flooding Cookbook, Volume 1: Meteorological Floods

Legendary fluvial geomorphologist Reds Wolman once said “Floods come from too much water,” and that’s the phenomenon distilled to its core essence. But this bit of wisdom doesn’t give us much to go on if we want to understand what creates floods or why some areas are more flood-prone than others. It’s the cooking equivalent to “Bread comes from flour.” How do we turn the flour into bread? How do we turn too much water into a flood?

In this blog post, I’ll create a cookbook for riverine floods, explaining the different phenomenon that generate floods and linking to examples that I or others have written about. I’ll be drawing heavily from the framework of a 2002 book chapter by O’Connor, Grant, and Costa called “The Geology and Geography of Floods” and as such I won’t be focused on the particulars of flood hydraulics or routing as the meteorologic, hydrologic, and geologic factors that are preconditions for floods. In a sense then, I guess I’m writing ingredients lists, not the full cookbook.

The first and most obvious ingredient you need for a flood is water. A lot of water. But if you have a lot of water draining slowly over time, that’s not a flood. It’s a river. So we need to have a lot of water, stored somewhere, and then release it quickly. Since the ways water can be released quickly are closely tied to where the water is stored, let’s start with storage.

Water can be stored as vapor in the atmosphere, liquid at the earth surface (in some sort of reservoir), or solid at the earth surface (i.e., ice or snow). That gives us a universe of three main types of floods: meteorological floods, dam break floods, and snow or ice melt floods. But those types are not absolute and bounded. You can have cross-overs. It can rain so hard as to burst a dam or rain on top of snow, melting the snow. But some floods are caused simply by too much rain, and these meteorological floods are the most common. That’s what I’ll cover in this blog post. (Look for volume 2 of the cookbook to cover how terrestrial water storage can lead to floods at some point after the semester is over.)

Meteorologial floods

Meteorological floods are closely tied to the four mechanisms of atmospheric lifting (convection, frontal systems, convergence, and orographic) that produce cooling, saturation, and precipitation. As climate change warms the atmosphere, enabling it to hold more water, and shifts atmospheric circulation patterns, there is the potential for more severe flooding and flooding in new places to result from any of these lifting mechanisms.

Convective rainfall + steep topography +/- human land use change = localized flash flooding

Convective lifting is associated with localized thunderstorms. These storms affect small areas (25 km2) over short time scales (a few minutes to a few hours). In these short periods, convective thunderstorms can produce staggeringly high rainfall intensities. (50 to >100 mm/hr) that generate localized flooding. For example, in July 2016, a convective storm dumped ~114 mm (4.5″) in an hour and 150 mm total on Ellicott City, near Baltimore, Maryland. This intense rainfall produced flash flooding that caused millions of dollars in damage and several deaths. Unbelievably, less than 2 years later, another convective storm dumped 220 mm of rain on the same area and the town flooded again.

Red-green map of precipitation showing some rain fell overmuh of the Baltimore-Washington area, but the most extreme precipitation was near Ellicott City

Precipitation that generated the 2016 Ellicott City flood. Ellicott City is in the reddest area, just to the west of Baltimore. (Image from the NWS.)

Clearly, convective storms can produce floods, and Ellicott City has terrible luck. But is it all bad luck? While the rainfall amounts from these storms are really big, if they’d happened in flat, sandy, forested areas, the resulting floods would have been much smaller. Unfortunately, historic downtown Ellicott City sits at the bottom on a locally steep valley that gathers runoff from three little tributary streams. And upstream, there is a lot of urban development. Ellicott City’s floods illustrate that the topography matters – the faster water runs down slope and gets collected into channels, the worse the flood will be, because more water will be entering the stream at once. Land use also matters, but for really extreme events, its signal is a little harder to parse, because if it rains hard enough or long enough, few landscapes will be able to infiltrate all of the water. Land use matters more for small floods.

Mesoscale convective complexes = flash flooding in multiple streams + downstream floods

Some convective storms are much larger than normal, and we call these “mesoscale convective systems” or “mesoscale convective complexes.” Mesoscale systems can have diameters of 10s to 100s of kilometers, and they can be major flood generators with impacts over much larger area than the isolated convective storms. The worst floods occur when large-scale atmospheric circulation patterns cause a mesoscale convective systems to stall out over a particular area, with thunderstorms popping up over and over again for hours or days. Isolated convective storms generally only cause floods for small streams, but an important feature of floods caused by mesoscale convective systems is that they affect more than one localized area, so they can create floods on larger river systems within or downstream of the area where rainfall occur.

A stalled out mesoscale convective system over Colorado’s Front Range in September 2013 caused over 450 mm of rainfall in one week, resulting in over $2 billion dollars in flood damage and hundreds of landslides. Flooding started in mountain canyons where over 300 mm of rain fell in one 24 hour period alone. As all of that water drained onto the flat-lying plains, flooding continued for days in the South Platte River and its tributaries. Flooding occurred because of infiltration-excess and saturation-excess overland flow. Rainfall probabilities for this event are estimated to be >1/1000 years (though that’s extrapolating well beyond the data), but flooding probabilities are not quite that extreme, with most of the places where gages exist or estimates made having floods with a 1/50 to 1/500 year probability.

Eroded road, house off its foundation, flooded river

Damage from the 2013 Colorado floods in Boulder County, Colorado. (FEMA photo via Wikipedia)

flooded highway and fields

Flooding near Greeley, Colorado from the South Platte River, September 19, 2013 (EPA photo via Flickr)

As with isolated convective systems, mesoscale systems can create bigger floods where topography is steep and there are lots of channels to quickly move precipitation falling on land into a stream network, resulting in more water arriving in the same part of a river at the same time.

Tropical and extra-tropical cyclones = flooding for miles and days

Tropical cyclone is the general term for hurricanes (wind speeds >74 mph), tropical storms (wind speeds 39-73 mph), and tropical depressions (wind speeds

Tropical cyclones are notorious flood generators, and inland flooding is the leading cause of death from these storms in the US. Hurricane categories only consider wind speed, not rainfall, so people may under-estimate the hazard associated with lower category storms. Immense rainfall totals can result as moisture is supplied to the storm by nearby ocean waters or by flooded and saturated soils on land. This makes slow moving hurricanes particularly dangerous flood generators, and it’s a reason that people are very concerned with the possibility that climate change could be contributing to slower hurricane movement after landfall. The most sobering example of slow-moving hurricane flooding in the recent past is Hurricane Harvey and its impacts on Houston in 2017. I wrote about the climate change connection and the land use connection at the time. Many fingers were pointed as Houston’s urban sprawl for worsening the disaster, and in some ways that’s fair (houses in floodplains are bad), but in other ways it’s not (almost nowhere can receive 1270 mm of rainfall in a few days without experiencing saturation and flooding).

Isohyetal map showing over 40" of rain in some areas

Rainfall from Hurricane Harvey in the Houston area. By David M. Roth; NOAA WPC – http://www.wpc.ncep.noaa.gov/tropical/rain/harvey2017.html, Public Domain.

When tropical cyclones produce flooding in flat areas, like coastal plains along the East Coast and Gulf of Mexico, the floods can last for weeks. We’ve seen this repeatedly in the US, including prominently in North Carolina in 2016, following Hurricane Matthew.

Where tropical cyclones meet steep topography, spectacular flood destruction can result, such as when Hurricane Irene hit Vermont in 2011. Even though Irene dumped less rain on Vermont than where it first made landfall in North Carolina, the flood effects were much worse. A similar phenomenon happened just a week later in the Susquehanna River watershed, as a result of Tropical Storm Lee. In fact, those two storms prompted my first “recipe” for flooding: Take a tropical cyclone and add steep topography.

Atmospheric rivers + orographic lifting = a major source of floods for California and the Pacific Northwest

Atmospheric rivers are narrow bands of concentrated moisture coming off the ocean and onto land. They are an area of active research as we increasingly recognize how important they are for generating floods and building snowpacks in the Western US. Here’s a great explainer video:

A key thing about atmospheric rivers as flood generators is not just how much water they carry, it’s what happens as they are orographically lifted over steep terrain like the Coast Range, Cascades, and Sierra Nevadas. That lifting and cooling causes the moisture to come out of the sky and fall as rain and snow. If conditions are cold enough to form snow, skiers rejoice and hydrologists and emergency managers let out a sigh of relief. But often, the atmospheric rivers are coming from the tropical ocean, in what we call a “pineapple express”, so the moisture is not just abundant, it’s warm. Then, the precipitation falls as rain, even at high elevations, and we get floods. If an atmospheric river happens after snow accumulates in the mountains, it will melt some or all of the snow and we get even bigger floods.

I’ve written about the effects of atmospheric rivers on Oregon’s Mt. Hood on more than one occasion. Flooding in 2011, was relatively minor as far as these things go. In 2006, a similar storm caused more extensive flooding and landslides on Mt. Hood, affecting my own research. The same storm, caused problems from Central Oregon all the way up to Mt. Rainier, south of Seattle. That gives you some idea of the scale of these systems and their effects.

Californians care a lot about atmospheric rivers, because they depend on mountain snowpacks and reservoirs to provide water for farms and people living in lower, warmer, and drier locations. But too much of a good thing is a flood. And climate change is projected to increase the intensity of atmospheric rivers affecting California and could even set up a scenario called the ARkstorm (for 1/1000 probability, atmospheric river storm). Watch the video below, because the consequences of this possible event are too big just to put into words, and yet, what could happen is based on state-of-the-art science and historical records of the 1861-1862 flood that inundated nearly the entire Central Valley.

Monsoons = Weeks-long rains and sometimes floods

As the Intertropical Convergence Zone (ITCZ) shifts north and south across the Equator, the direction of air flow towards it changes too. Whichever way the wind is blowing, where the warm moist air from over the oceans blows onto even hotter land, it rapidly rises, cools, and begins to rain. The seasonally shifting wind direction and associated wet-dry periods is called a monsoon climate, and monsoon climates are particularly pronounced around the Indian Ocean. In the northern hemisphere winter, the ITCZ causes monsoon rains in northern Australia, while in northern hemisphere summer, the rains are affecting south Asia. During the Asian monsoon, orographic effects as air lifts over the Himalayas increase the intensity of the rainfall. If you’ve spent time in the southwestern United States, you may also be familiar with monsoon rains in that region.

Monsoon rains bring an average of 900 mm of rain to India each year. Spread out over the months of June to September, the rains are an important water source for crops, livestock, and humans, and helps offset the opposite season, when hardly any rain falls.

But when monsoon rains come in intense downpours, flooding can result.  Some years, more rain falls or a lot of rain falls in the space of a few weeks, rather than more evenly spread out over months. In ways that we don’t completely understand, climate change seems to be making the monsoon rainfall less moderate and more sporadic. Dry periods interspersed with extreme precipitation periods are becoming more likely and that means that floods are becoming a more frequent part of the monsoon climate.

Monsoon flooding was a major problem in India in 2019, and this article (not by me) does an amazing job of linking monsoon dynamics to climate change and increasing risks experienced by growing urban populations.

In 2010, monsoon flooding hit Pakistan hard. Monsoon rains poured over one mountain region for weeks, causing flooding and landslides, followed by slow downstream flood wave propagation along the Indus River for weeks longer. More than 18 million people were affected by this flood alone, and it appears that the location of the flood-producing rains was shifted relative to historic patterns, yet another flood-related consequence of climate change.

Monsoon flooding along the Chao Phraya River in Thailand, with July 2011 (left) and October 2011 (right) compared. Images are from NASA, via Wikipedia.

Monsoon flooding along the Chao Phraya River in Thailand, with July 2011 (left) and October 2011 (right) compared. Images are from NASA, via Wikipedia.

Important notes and take away points

These aren’t the only ways to cook up floods. First, I’ve only covered meteorological floods on rivers in this post, and then, I haven’t even covered all of those. Frontal systems can produce floods too, particularly if the ground is wet to begin with or if infiltration capacity is low. And rain-on-snow is a significant flood generator (even without the concentrated fire power of an atmospheric river) because the heat from the rain can melt large amounts of snow, dramatically increasing the volume of water contributing to a flood.

Climate oscillations like the El Niño-Southern Oscillation and Pacific Decadal Oscillation will exacerbate these flood generation recipes in some years and some regions, and mute them in other places. The climate oscillations don’t create flooding in-and-of themselves, but they can make things better or worse.

The recipes above will generate floods that vary in space and time scale of impact – from affecting headwater streams for a few hours to affecting huge river basins for months. In general, the highest intensities of rainfall will only affect a fairly small area for a fairly short amount of time, but mechanisms that produce more prolonged rainfall can cause widespread flooding, even if the intensity is lower.

Topography matters. Steep slopes route water quickly into streams producing high peak flows, while flat areas drain slowly resulting in floods that last much longer.

Land use matters – to some extent. In really extreme rainfall, it may make little difference in the peak flow and total flood volume, because the landscape would have been overwhelmed regardless of landcover. For smaller floods, land use, including deforestation and urbanization, definitely matters, and land use also matters quite a bit for things like landslides which often accompany floods.  Regardless of size, a flood is a disaster when people are in the way, and land use is one rough proxy for how many lives and how much property is likely to be affected.

Climate change is affecting the frequency and/or severity of floods across all of these recipes, even if we can’t always detect the signal of climate change in a particular event. In general, we are seeing – and expect to continue to see – increases in extreme rainfall, the key ingredient in all of these recipes. And extreme rainfall intensity is increasing much faster than the overall increase in atmospheric moisture and mean precipitation.  We are also seeing shifts in timing and location of flood-generating storms.

Categories: by Anne, geohazards, hydrology