Squaw Creek, in the uppermost headwaters of the Middle Fork John Day River Basin, may be on the small side, but it isn’t small in terms of its potential importance to native, threatened Mid-Columbia River steelhead and other resident fish and wildlife species. Squaw Creek joins with Summit Creek 3.5 miles above Highway 7 and together these two streams become the Middle Fork John Day River (Middle Fork). Over the last century, Squaw Creek’s productive aquatic habitat slowly declined. Now, with a new restoration project, the Malheur National Forest and Oregon Department of Fish and Wildlife are working to re-intertwine the disconnected pieces of this ecosystem.
Near its headwaters, Squaw Creek once meandered lazily through a 70 acre meadow, a mosaic of fens, wet sedges and dry sagebrush. When the river overtopped its banks in spring, the floodwaters created slow-flowing alcoves, side channels and backwaters ideal for young salmon and steelhead to hide, rest, and feed in. The connection of floodplain to river meant that more nutrients, insects and other food from the land traveled into the water and was available to the growing fish. Steelhead traveled hundreds of miles from the Pacific, unimpeded by weir, dam, or culvert, to spawn here.
Connectivity matters: It’s how a river renews itself. Without longitudinal (upstream-downstream) connectivity, animals like steelhead—whose life cycle depends on the ability to move up and down river systems—can’t access habitat. As flows of nutrients, sediment, wood and gravel from floodplain to river are stopped or slowed through loss of lateral (side-to-side) connectivity, the river’s ability to nourish new generations of fish and wildlife becomes impoverished or lost altogether.
In the case of Squaw Creek, Euroamerican settlement in the Blue Mountains brought beaver trapping, logging, grazing and fire suppression to the watershed, which created a laterally disconnected habitat that is no longer a nurturing environment for young fish to grow and thrive. More recently, road-building and log weir installation longitudinally disconnected Squaw Creek, turning it into a series of semi-isolated segments by blocking fish from getting upstream.
Can connectivity be restored to this once-flourishing stream? That’s where Malheur National Forest Fisheries Biologist Kate Olsen and Hydrologist Hazel Owens come in. Olsen and Owens, in collaboration with Oregon Department of Fish and Wildlife, are leading a multi-year restoration project on Squaw Creek that aims to improve stream habitat, cool stream temperatures, and increase both lateral and longitudinal connectivity. 2015 is Year One. If all goes according to plan, a majority of the project should be finished by 2017—but its effects should last long beyond its completion date, and go much further downstream than the project site.
The restoration team’s strategy to undo the disconnection and knit the isolated pieces of Squaw Creek back together is threefold.
First, the team will return the artificially straightened stream channel to its historically winding, meandering flow path. A stream with more curves and meanders in it helps slow down fast-moving floodwaters, reducing erosion and cooling the water by forcing more of it to flow through gravel bars. The team will also provide places for fish to hide from predators by placing logs and root wads, such as would have been historically present, into the stream. They’ll also create places for fish to rest by making more pools. To help create shade and cool water temperatures for fish, the team is planting aspen, willow, dogwood, and alder near the reconstructed channel.
Second, the team will help reconnect the stream with its floodplain. Currently, the stream runs at the bottom of a deeply carved channel, meaning the floodplain is left high and dry even at high flows, because there simply isn’t enough water to overtop the banks.
To accomplish this lateral reconnection, the team is felling trees, which accomplishes two goals: First, it helps return more water to the stream, because trees use a lot of water. Historically, the trees the team is cutting would not have been present, but a century of fire suppression allowed them to invade the meadow. Secondly, the felled trees will be placed in the channel to help trap sediment and raise the streambed’s elevation. Some trees will be kept on the floodplain to slow the flow of raging floodwaters, reduce erosion, and protect riparian vegetation. Eventually, Squaw Creek will be able to overflow its banks and access the floodplain once again, creating the variety of food-rich, slow-flowing habitats so important to young fish.
Finally, the team will focus on restoring longitudinal connectivity by addressing 85 fish passage barriers over the life of the project. In summer 2015 alone, fourteen log weirs throughout Squaw Creek were removed, along with a culvert that blocks both adult and juvenile steelhead passage. This barrier removal will allow fish to access more habitat where they can effectively spawn or feed and grow.
The Forest Service is monitoring the local impact of the project. Meanwhile, other researchers, part of the Middle Fork Intensively Monitored Watershed collaborative, will monitor downstream of the project site to see if, and how, the Squaw Creek project impacts habitat downstream in the Middle Fork.
After all, this is what connectivity is all about. What goes on upstream in the headwaters of a river can often have a profound impact on the conditions downstream. Planting shade trees to cool water temperatures for fish, for example, might not work if there is no streamside vegetation for miles upstream of the project, meaning the water flowing through your shaded project is already too hot. On the other hand, if you effectively restore enough miles of upstream habitat, your downstream restoration project might work. This is what biologists call ‘cumulative impact’—smaller impacts adding up to a whole that is bigger than the sum of its parts. This is part of why connectivity matters so much.
By knitting together a headwater stream with its floodplain, and splicing its isolated segments back together with barrier removals, the Squaw Creek restoration team is restoring part of the inherent nature of this dynamic system: connectedness. Stay tuned for future updates on the Squaw Creek restoration as the project progresses!
- Emily Davis
Monitoring Coordinator, Oxbow & Forrest Conservation Areas
Confederated Tribes of the Warm Springs Reservation of Oregon
The Middle Fork John Day River, one of the last core strongholds for mid-Columbia steelhead and spring Chinook, is much warmer these days than it used to be, due to historic removal of shading streamside vegetation and straightening of the river channel. This can translate to lethally warm water, as biologists saw first-hand during the devastating summer fish kills of 2007, 2013 and 2015. Salmon and steelhead are cold-water fish: Warm water stresses these fish’s immune systems, putting them at higher risk of infection and disease. One urgent goal of restoration activities in the Middle Fork is to cool water temperatures to improve this crucial salmon habitat.
But how do we know that our stream restoration strategies are working to cool down the river?
To answer this question, the Selker Water Resources Lab at Oregon State University’s Department of Biological and Ecological Engineering has studied stream temperature in the Middle Fork since 2008. Their goal: to learn what factors, such as shade, stream channel shape, groundwater, and weather, influence stream temperature, and how we can leverage that information to get the most water-cooling bang for our buck out of our restoration projects. Their strategy? A futuristically high-tech approach involving—no joke— lasers.
For many years, the only option for monitoring water temperatures was just to stick a waterproof data logger in the river at just one place, in order to record temperatures at that single place over a time period. But these point measurements don’t give us all the information, because stream temperatures also change continuously over space as a river channel changes shape, as water moves faster or slower, and as vegetation cools the water by shading.
To solve this problem, the OSU scientists are looking at how temperatures change continuously along the stream length. They do this by laying fiber-optic cables along the riverbed. Fiber-optic cables, normally used for long-distance telecommunications, have now been adapted for all kinds of applications, including sensing water temperature. By using the cables—also called Distributed Temperature Sensing, or DTS— the Selker Lab can get very high-resolution temperature data. DTS works by shooting a laser down the length of the fiber optic cable. The laser’s light behaves slightly differently depending on the temperature of the water, and the researchers use this information to translate into temperature data. Starting in 2013, large-scale installations of these cables have gathered data in the Middle Fork of the John Day River, collecting temperatures over about 8 miles of river.
The Selker Lab has focused much of their effort on stream sections within two major restoration project sites (Phase 2 and Phase 3*) on the Confederated Tribes of Warm Springs’ Oxbow Conservation Area. In 2012, the Phase 2 project consolidated the river channel from two channels back into its single, historic channel, while plugging the old, man-made channel. Whereas before the water ran through two shallower channels, with roughly twice the surface area, the current single channel means a deeper stream with less exposed surface area, reducing the ability of the sun to warm up the water. The lab found that within and downstream of the Phase 2 project site, temperatures swung less wildly from one extreme to the other between day and night. This means that during the make-or-break time of day when it really matters for salmon—the hottest hours, between 2 and 5 pm— the restored channel is doing its job by keeping the water cooler. Meanwhile, at night, the temperatures in the new channel cool off less dramatically than they would have in the old channels. The ability of the restored channel to buffer dramatic swings in temperature and keep the stream cooled during the day is a potential win for fish.
By contrast, Oxbow’s Phase 3 project, completed in 2014, is projected to actually increase stream surface area. That’s because it took an artificially straightened channel and added bends and meanders. Re-meandering the river does a number of beneficial things: it slows down the water during high flows, decreasing bank erosion; allows the river to flood its banks and exchange sediment and nutrients with its floodplain; and creates more pools and alcoves for fish to rest and feed. In the short term, the increased stream surface area is predicted to actually warm the water slightly—at least until the thousands of newly planted willows and alders get taller and provide some shade. The team predicts that if restoration changes the river channel by making it wider, it will need taller vegetation to shade it effectively than a narrow channel would. These predictions help determine if and where planting vegetation is most effective for achieving cooler water temperatures. In the long term, the Selker team predicts that the taller and denser the riparian canopy gets, the more shaded the channel will be, and the cooler the water.
But just because Phase 3 is predicted to slightly warm temperatures in the short term does not mean this restoration project won’t be successful. These results illustrate the challenging trade-offs that large-scale, comprehensive river restoration poses. Though warm temperatures are one of the most limiting factors for salmon in the Middle Fork, another obstacle is the lack of space for juvenile fish to thrive and survive so they can successfully return as adults to spawn. Even if all of the Middle Fork were shaded and cooled off, helping more adult salmon survive the summer and spawn in the fall, there still wouldn’t be enough space to support increased numbers of juvenile fish—the very problem that much of the Oxbow restoration is designed to address.
What’s next for DTS in the Middle Fork? As global climate change continues to heat up our summers, DTS data is being used to “virtually” compare pre- and post-restoration stream temperatures under potential future climate scenarios, to predict which restoration efforts might work best in the future.
And meanwhile, salmon and steelhead are cooling off from the hot summer sun in the restored river channels.
* A multi-year, multi-phase restoration effort on the Oxbow Conservation Area has been split into five phases. Three phases are completed; Phase IV is currently underway.
Before restoration (top photo), the river was split into two channels (North and South)
and Granite Boulder Creek (top middle of both photos) flowed into the North channel
After restoration (bottom photo), flow was redirected to the historic South channel and Granite Boulder Creek was once again able to contribute its cold water and effectively cool down the river
- Emily Davis
Monitoring Coordinator, Oxbow & Forrest Conservation Areas
Confederated Tribes of the Warm Springs Reservation of Oregon
By Emily Davis
What do you think of when you hear the word ‘engineer’? For many, the term conjures an image of activity, of working hard to build or change something. An ecosystem engineer is a living thing that dramatically changes its surrounding environment, influencing habitat for many other critters along the way. Beavers are a classic example of an ecosystem engineer. Their dam-building floods valleys, transforming running streams into deep, still ponds and wetlands, often creating lush oases in the middle of otherwise arid lands. River restoration practitioners applaud beavers because they save us a lot of work.
But what if a plant—a sedentary being— could be an engineer? The humble torrent sedge (Carex nudata), a water-loving plant native to many rivers in Oregon and California, may be just such an unsung hero. In the Middle Fork John Day River, the torrent sedge has been quietly changing its landscape just as much as any busy beaver, but without all the hustle and bustle and fanfare.
Since the 1990s, the Middle Fork has been the focus of enormous and complex restoration efforts to repair the damage done by previous logging, gold dredging, and cattle grazing. In 2001, the Confederated Tribes of Warm Springs acquired the Forrest and Oxbow Conservation Areas on the Middle Fork, and promptly built fences to exclude cows from the river. Simply as a result of removing cattle grazing from the riverbanks, torrent sedge exploded across the landscape. And when that happened, it didn’t escape the notice of Dr. Patricia McDowell, from the University of Oregon’s Department of Geography.
McDowell, a geomorphologist, had been working on the Middle Fork for awhile, and had her eye on torrent sedge the whole time. For years, she wondered about its potential role in restoration. When PhD student Matthew Goslin expressed an interest in torrent sedge, a long-awaited research project was finally able to begin.
“The first time I saw torrent sedge in the Middle Fork, I just thought it was an incredibly beautiful plant, and I wanted to learn more about it,” says Goslin. “Lots of researchers focus on problems, on negative issues or what’s going wrong. I was really drawn to the idea of learning about this plant that seemed to be doing positive things [in the river].”
Until recently, fluvial geomorphology—the study of rivers, their shape and how they change—focused on physical processes like the movement of water and sediment. Plants were more or less ignored as agents of change. But that line of thinking is beginning to change. These days, researchers acknowledge plants as playing a role in changing river shapes, flow, erosion and sedimentation in complex ways. Goslin’s research aims to advance this idea that the plant-river relationship is reciprocal: that plants can alter the shape of the river just as the shape of the river can influence plant communities.
When it comes to standing up to the power of the river, torrent sedge is tough. The plants build small, impenetrable fortresses, called ‘tussocks,’ with their dense root systems. These root balls are so tenacious that McDowell and Goslin began imagining them as ‘organic boulders.’ These ‘organic boulders’ are immobile objects in the river that can withstand fast currents and redirect flows; but that also grow and reproduce, building islands as they do so. As a result, torrent sedge appears to be changing the shape of the river from a simple, single-thread channel to a complex multi-threaded channel, creating a rich diversity of habitat for fish and other creatures.
River restoration practitioners, like those working on the Oxbow Conservation Area, increasingly think of the unassuming torrent sedge as a positive contributor to the river landscape. Torrent sedge is now being transplanted into restoration projects, but with only a vague understanding of its potential function. Understanding how exactly it may change the river is essential for using it effectively in restoration work.
To do the very same channel-shaping work as this modest plant, human engineers require heavy machinery like excavators, hundreds of thousands of dollars, dozens of meetings, and detailed blueprints of how to reconfigure the river. But all the torrent sedge needs is time.
And, bonus feature: It does its work for free.
By Emily Davis
If you live on or near the Middle Fork John Day River (Middle Fork), you know that the amount of water in the river fluctuates widely throughout the year—from the roar of spring runoff to the quieter trickle of late summer. But did you know that measuring river flow is an important piece in the puzzle of salmon restoration? High flow measurements are key to understanding how restoration actions in the Middle Fork are affecting fish habitat, so being able to keep track of flow is important.
The North Fork John Day Watershed Council (NFJDWC) routinely takes river and stream flow measurements in the Middle Fork. NFJDWC staff usually take these flows during times of the year when it’s easy to wade in the river, such as the low-flow season of early fall. Because of the dangers of trying to wade the river when the water is high, the NFJDWC crew was unable to collect data during these times in the past. But why bother with taking flow measurements during high water, if we already have measurements during low water? Without these measurements year-round, we’re only seeing part of the picture of what river scientists call the ‘hydrograph’, the story of what a river does over the course of a year. It’s like putting together a quarter of a jigsaw puzzle and trying to infer what you might see on the rest of the puzzle, based on the corner you have in front of you.
Now, for the first time, the NFJDWC is able to get flow measurements during dangerous high-water events, and start putting together the rest of the puzzle. Using specialized equipment, and working with partners from the Bureau of Reclamation and the Malheur National Forest, NFJDWC staff successfully measured stream discharge this winter at flows that would have almost certainly knocked someone trying to use the traditional method right off their feet. The traditional method is simple: a researcher wades across the channel with a current velocity and depth meter, taking measurements every few feet. In the Middle Fork, at twenty cfs (cubic feet per second), the river slides lazily by and the water comes up to a researcher’s ankles; at seventy cfs, it becomes difficult to stay on your feet; and at several hundred cfs even the hardiest hydrologist would avoid stepping foot in the channel.
The new method follows the same principles. It takes a little more time, but is much safer at high water. Flows are measured with a sounding reel from a bridge near the usual flow measurement site. A sounding reel is a specialized cable on a winch with a crank. Weights are put on the end of the cable to keep it steady in the current; the cable can then be lowered into the water to measure depth. A current velocity meter can also be attached to the cable and used to measure velocity from the safety of the bridge.
The additional high flow measurements create a more complete picture of year-round flow in the Middle Fork. By understanding the changes the river undergoes during all seasons, we can get one step closer to understanding how to improve watershed health and support thriving fish populations.
North Fork John Day Watershed Council, Bureau of Reclamation, and Malheur National Forest staff
using a sounding reel to measure high flows in the Middle Fork John Day River
By Emily Davis
On September 4th 2014, a giggly and squirmy group of twenty-five 2nd and 3rd grade students from Prairie City loaded into a school bus and made the journey over Dixie Summit into the Middle Fork John Day Basin. There, Jeff Neal at Oregon Department of Fish and Wildlife and Kristen Coles at Confederated Tribes of Warm Springs led the kids on a Tour de Middle Fork, including a fish ladder at Bates State Park, a fish screen and a pool of adult Chinook salmon on the Middle Fork Forrest Conservation Area (MFFCA) and the newly completed Phase 3 Tailings Restoration Project on the Oxbow Conservation Area (OCA).
“The kids loved being outside,” said Coles. “They were really interested in the Chinook redds we saw when we walked down to the river. And of course they all wanted to play in the water and on the logs."
Neal told the kids that they were seeing the project from the beginning, and they could come back in ten years when they are teenagers and see how much bigger the plantings had grown and how much more the river would be shaded.
“In fifteen or twenty years, the management of the Middle Fork will be in the hands of these kids, so it’s important that we give them the chance to build a connection to this place now,” explained Emily Davis, current Monitoring Biologist for the Forrest and Oxbow Conservation Areas. “Even if they don’t understand every detail of the science or the restoration project, we can help nurture their curiosity by letting them explore.”
Researchers use low-cost techniques to produce high-resolution images of new river channel construction in the Oxbow Conservation Area
By Emily Davis
Aug 24, 2015
Researchers use low-cost techniques to produce high-resolution images of new river channel construction in the Oxbow Conservation Area
The Oxbow Conservation Area (OCA) on the Middle Fork John Day River (Middle Fork) has been the site of some ambitious and impressive river channel restoration projects in the last few years. The big question on everyone’s mind is: How can we monitor our restoration projects to see what kind of change takes place over time, and hopefully connect that to changes we see in fish populations? And how can we do it effectively, without expending too much money or time? Researchers at the University of Oregon think they may have the answer to this riddle. Using a creative approach and a unique assortment of tools, scientists from the McDowell Geomorphology Lab are using a technique that, in just an afternoon, can collect more data than an army of students could collect in a whole summer.
Decades of gold dredging and other channel straightening activities made this reach of the Middle Fork an unfriendly place for fish. The channel reconstruction project on the OCA took a straight, relatively uniform stretch of river and turned it into a more natural meandering channel with more deep pools. The hope of the channel reconstruction project was to provide the nooks, crannies, and diversity of habitat types that fish—especially juvenile salmon— need to rest, feed, and hide from predators.
So how has the river channel changed since the project was implemented? To find out, UO graduate students working in the McDowell Lab attached an ordinary digital camera to a heli-kite flown over a portion of the reconstructed channel during the course of an afternoon. A heli-kite is a deceptively simple device: just a small helium balloon with two ropes attached and a place to attach the digital camera. It can be easily operated by two people. With one person standing on either side of the river channel, each holding a rope attached to the heli-kite, and the helium balloon holding the camera overhead in the middle, the crew then walks down the stretch of river they are interested in analyzing. As the camera passes overhead of the channel, it snaps a multitude of overlapping images, about one every second. The images are later analyzed using special computer software that matches up the overlapping photos, creating a digital image of the structure of the riverbed. In essence, the software creates a 3-D ‘tour’ of the channel shape using the photos. “It’s analogous to what you might see if you went to a realtor’s website and got a 3-D tour of the inside of a house for sale,” says project leader Dr. Pat McDowell. “Just way more precise, of course.”
What can an interested researcher do with this 3-D tour of the riverbed? For one, it allows restoration practitioners to more easily track how their projects are changing the physical landscape over time. Such monitoring has historically relied on very time-intensive field methods, requiring lots of personnel and money to complete. Initial results from 2014 (photo 3) show increased channel bed complexityextensive restoration project. More channel bed complexity could mean improved aquatic habitat for fish and other critters in the Middle Fork. The heli-kite method is unique and simple—and it means monitoring the success trajectory of restoration at the Oxbow Conservation Area and elsewhere on the Middle Fork could get a whole lot easier in the future.
One of the most popular methods to measure salmon numbers in a watershed is to monitor spawning adults and their redds (nests). Mature Chinook salmon return each year to the Middle Fork John Day River during May and June. They spend the summer months seeking cool water while holding in deep pools. When the weather starts to cool in September they begin spawning by digging redds and laying their eggs in the gravel. These redds are easily observed and are a common method to measure the abundance of spawning salmon. Each year Oregon Department of Fish & Wildlife (ODFW) fish biologists walk the Middle Fork John Day River to count redds to estimate the number of spawning adults (for details, see Bare et al. 2014).
Redd counts for the 2014 spawning season were impressive. ODFW biologists estimated that > 500 redds were constructed within the Middle Fork IMW area during 2014. This is a 350% increase from 2013 counts and the highest on record since 2000. Redd counts throughout the John Day River basin were similarly high.
The detection of this high abundance of redds demonstrate the potential for salmon in the Middle Fork John Day River. However, our previous data has shown that high abundance of redds does not directly translate into more juvenile offspring, suggesting that the freshwater environment in the Middle Fork is limiting the potential for increasing the salmon population. Summer water temperatures in the Middle Fork have also killed many adult salmon in 2007 and 2013 resulting in very low redd counts for those years. The inability of the freshwater environment to produce more offspring despite high numbers of spawning adults and their deposited eggs is a central reason for continued restoration actions within the Middle Fork IMW.
LONG CREEK, OR. – The North Fork John Day Watershed Council’s (NFJDWSC) intensive monitoring efforts on the Middle Fork of the John Day River have collected an invasive species, previously un-recorded in eastern Oregon or the John Day River system. The “European ear snail” was collected by NFJDWC Project Coordinator, Valeen Madden, on September 24, 2014 in a drift net during regular macroinvertebrate monitoring activities on the Middle Fork John Day River. The European ear snail was positively identified in the drift net sample by Rithron Laboratories of Missoula, MT.
European ear snails (Radix auricularia) are in the family of lymnaeid snails which are scrapers and gatherers. They are native to both Europe and Asia. The species generally grow to about 15 mm in height and 13 mm in width. The mantle has dark spots along its edge and 4 to 5 whorls in the shell. The snails generally prefer fresh water lakes and slow moving rivers. Ear snails feed on detritus, algae, and sand. Their common name is derived from the “ear” shaped shell in which they live.
The European ear snail is not considered a “noxious” species, only an invasive species. That indicates that the snail is exotic to North America, and it is increasing its population density, but it is not outcompeting or having any detrimental effect on native species in the lakes and rivers where it is found. The nearest prior discovery to the west was in Lake Billy Chinook in central Oregon and to the east in Idaho’s Snake River and Owyhee drainages. Significant populations occur in southwestern Oregon.
The NFJDWC will seek additional funding to search upstream and downstream from the capture site to determine the level of prevalence of the population. Additional investigation by the Oregon Department of Fish and Wildlife Invasive species coordinator will seek to determine the source of the new species. Elaine Eisenbraun, Executive Director of the NFJDWSC, stated, “Rivers are such a dynamic element of our environment. It is important to keep an eye on the changes that take place naturally and as a result of human activity. Our staff is working diligently to gather relevant information about the health and constant changes in the waterways that we monitor. It is a tribute to the diligent work of our monitoring staff that their efforts revealed a critical change in the system biota.”
For more information:
Elaine Eisenbraun, Executive Director
North Fork John Day Watershed Council
For more information about the European ear snail, visit:
Additional links about European ear snail discovery:
Since 2010 samples of insects living in the water (aquatic macroinvertebrates) have been collected at 15 locations in the Middle Fork John Day IMW by the North Fork John Day Watershed Council. Sample locations include sites that have had active restoration and locations that have not had any restoration activity. After collection, samples are sent to a lab where macroinvertebrates are identified and classified. Certain macroinvertebrates are only found in extremely healthy streams, while others are signs of poor water quality or disturbance. This data can be used to assess the ”biotic integrity,” or health, of the stream ecosystem.
In 2014, Washington State University Tri-Cities graduate student Robin Henderson began analyzing three years of macroinvertebrate data from the Middle Fork John Day River IMW and the South Fork John Day River. Robin tested different models of biotic integrity for accuracy in prediction and then used those results to assess if restoration has improved the health in the Middle Fork John Day River. Robin’s initial analysis produced a highly accurate predictive model of biotic integrity. Her modeling results indicate macroinvertebrates respond to variables related to forest health and integrity, land use, habitat fragmentation and the riparian buffer zone, confirming that restoration activities implemented in the Middle Fork John Day river affect the biotic integrity of the watershed, at least in the short term. Supplementary data collection and additional analysis is needed to understand the longer term biological response.
Macroinvertebrate collection will continue for several years and Robin’s model will be used again to determine if restoration activities have increased biotic integrity. Further research has also been proposed to characterize between-year variability of biotic integrity and to determine the regional climate drivers which may impact the biotic integrity of regional streams.
For more detailed information on Robin’s research refer to the following resources…
Henderson, Robin M. Measuring the Biotic Integrity of Stream Ecosystems with Restoration. MS Thesis. Washington State University, Richland. 2014.
Henderson, Robin M. and James R. Pratt. Measuring the Biotic Integrity of Stream Ecosystems with Restoration. Washington State University Academic Showcase. 2014.
A total of 95 temperature data loggers were deployed in the Middle Fork John Day River IMW area in 2014. The North Fork John Day Watershed Council (NFJDWC) (http://nfjdwc.org/) deploys and maintains 43 of the loggers and the remainder are deployed and maintained by various IMW partners, including the Warm Springs Tribe and The Nature Conservancy. All temperature logger data is shared with and managed by the NFJDWC.
Water temperature is measured every hour from approximately late April through November. The goal of collecting water temperature data is to identify tributaries that are water temperature limited and may be candidates for restoration activities.
In addition, the NFJDWC deploys 10 “level loggers” which, in addition to measuring temperature, measure water pressure above the logger. Water pressure measurements, coupled with flow measurements taken at each “level logger” site, and further analysis, allow the NFJDWC to identify how each tributary contributes to the river system in both volume and water quality/temperature.