Real-time nodes permit adaptive management of endangered species of fishes
© The Author(s) 2017
Received: 24 May 2017
Accepted: 29 August 2017
Published: 13 September 2017
Currently acoustic tag-detecting autonomous receivers must be visited periodically to download the files of tag detections. Hence, the information about the whereabouts of tagged fishes is not available to make prompt regulatory decisions to reduce entrainment. In contrast, real-time receivers can detect the signal from a transmitter on a passing fish and immediately transmit its identity and time of detection to a website, where they can be viewed on either a computer or cellular telephone. Real-time nodes can aid regulatory biologists in making important decisions. This is a powerful new tool for resource managers and conservation biologists.
We describe a network of real-time, fish-tracking nodes on the Sacramento River, California. Two case studies illustrate the value of the nodes. The first entails detecting the arrival of migrating winter-run Chinook salmon near a water diversion and alerting regulatory biologists to keep the diversion closed to increase the migratory success. The second study involves the detection of green sturgeon at potential stranding sites, alerting biologists of the need to transport them from that site to the main channel of the river so they can continue their upstream migration to their spawning sites.
Individually coded acoustic tags and tag-detecting stationary receivers were developed in the 1980s to describe site fidelity of sharks at coral reefs  and seamounts [2, 3]. Although this technology was first used to ascertain the degree of residency of highly mobile species at biotic “hot-spots” in the ocean , it has been used even more frequently to determine rates of movement and reach-specific survival of adult anadromous fishes on their upstream migrations to their spawning sites within rivers and juveniles migrating downstream to the ocean . By 2012, there were 378 published studies utilizing this methodology .
Autonomous receivers allow the collection of detection data from remote sites without personnel being present. However, the files of tag detections stored in the receivers must be downloaded periodically, and for this reason equipment failure and the resulting loss of data are not detected until these infrequent visits are made. In contrast, real-time receivers can record the passage of tagged fish and immediately transmit their identities and times of detection at a particular location to a website, where they can be viewed on either a computer or cellular telephone. Regulatory biologists can access the data on the website to help them make important decisions. The viewer can find out whether the receiver is operating by simply checking whether a full is voltage displayed on the website. A real-time node must be distinguished from an autonomous receiver. The former is composed of a variety of receivers, a mooring within the river, a submersible cable, a circuit board, modem, and battery enclosed within a waterproof box, with a cable leading from it to an array of solar cells. This is an emerging capability, which has recently been used in remote area of the ocean to monitor the residence times and depth preferences of four species fishes at a fish aggregating device (FAD) . An acoustic receiver transmitted behavioral information to via the Argos satellite to a base station in real time.
There is a critical need for real-time detection of fishes in the Sacramento River. There are two runs, winter and spring, of Chinook salmon (Oncorhynchus tshawytscha) that are listed as endangered and threatened by the Environmental Protection Act (ESA). Both encounter numerous water diversions as they migrate down the river and through the delta. Furthermore, the green sturgeon (Acipenser medirostris) migrate to the upper river to spawn and can become disoriented and stranded within these diversions.
In response to the current extended drought conditions in California, state and federal agency regulators must balance the competing needs of endangered and threatened fish species for limited water resources with the needs of society to use water for urban, industrial, and agricultural demands. During the winter of 2015, water levels in the Sacramento–San Joaquin Delta became very low, and there was pressure to open the Delta Cross Channel (DCC) radial gates to import more water into the interior Delta to be exported to Southern California through the state and federal water diversions. However, at the same time it was imperative that this action would not jeopardize the safe passage of Chinook salmon smolts to the ocean. Perry et al. , using coded acoustic tags and an array of tag-detecting receivers, determined route-specific survival of the smolts through the main channel and three routes through the Delta. A higher rate of survival was recorded during December 2006 when the DCC gates were open than during January 2007 when they were closed. Furthermore, Steel et al. , using a 2-D tracking array, showed that juvenile salmon were diverted from the main channel of the Sacramento River into the Delta when the gates of the DCC were open. Based on these two studies, regulatory biologists recommended the closure of the DCC gates when winter-run smolts arrive in their vicinity.
In contrast, the Sacramento River during wet years will flow over the Fremont Weir at the northern end of the Yolo Bypass and move in a southerly direction through the bypass avoiding the City of Sacramento . The fast moving waters in the bypass serve as a false attractant to the green sturgeon moving upstream during their spawning migrations. They become trapped at the top of the Yolo Bypass south of the Fremont Weir when the Sacramento River recedes from flood stage, and the elevation of the river falls below the crest of the weir . The California Department of Fish and Wildlife (CDFW) was notified by local fishermen during 2011 that numerous sturgeon were stranded in shallow pools behind the Fremont and Tisdale Weirs after a series of rain storms. The sturgeon were trapped when the flows in the Sacramento River subsided, consequently lowering the height of the river below the crest of the weirs. A total of 24 green sturgeon were captured, transported, and released into the Sacramento River above the weirs .
Fisheries biologists have advocated on an international level using real-time biotelemetry to make management decisions . Real-time information about water temperature and rate of flow in the Fraser River, Canada, is currently being used to make within-season management decisions, and there is keen interest in relating these environmental drivers to the movement rates and reach-specific survival of fishes using similar tag-detection nodes . Some have argued that telemetry is not relevant to conservation . The approach described here alleviates this concern, providing specific examples where biotelemetric data have been used to make important management decisions.
We will first describe the components of real-time nodes that provided real-time reporting of the passage of fishes during the drought in the Sacramento River and Delta in California. Two examples will be given illustrating the value of these nodes. The first involves the two runs of Chinook salmon, winter- and spring-run. Regulatory biologists were alerted during winter 2015 of the arrival of hatchery-raised winter-run Chinook salmon near a water diversion, which was kept closed based on this information. Furthermore, the absence of the detection of tagged spring-run by a real-time node in Sacramento led regulatory biologists to increase the pulse of water coinciding with the release to enhance the survival of the smolts. The second example consisted of alerting rescue crews of the passage of adult green sturgeon (A. medirostris) past the Yolo Bypass, a potential stranding site, during their upstream spawning migration during spring 2016.
Architecture of real-time node
The first-generation real-time, tag-detection system was an expansion of “Environet,” a website devoted to the display of environmental data hosted by Netronix Inc. This site can be accessed at https://environet.com by entering the following email address: firstname.lastname@example.org and password “getdata.” The second-generation real-time, tag-detection system was developed by the biologists of the Biotelemetry Laboratory in conjunction with the engineers of Teknologic Engineering and named the Biotelemetry Autonomous and Real-Time Database (BARD). To access this site, use the following address: http://sandbox5.metro.ucdavis.edu/landingmap.
Advantages and disadvantages of the first- and second-generation real-time stations
Biotelemetry Autonomous and Real-Time Database (BARD)
Detection times stamped by node GPS (m/d/y hh:mm)
Detection times stamped by receivers (m/d/y hh:mm:ss:ms)
If offline, all detections are stamped with time of next successful polling
If offline, all detections get original time stamp from receiver at time of detection
Polling limited to minute polling rate due to cellular node time stamping
Greater temporal resolution, since time is independent of cellular node
Netronix server space limited
SQL space permits 4 tBytes; “unlimited” space with Amazon cloud
Limited to 20 detections per minute
Unlimited detections per polling interval; 196 kByte limit, which equals about 2000 detections per polling
Web interface not adaptable
Web interface with SQL database is adaptable to visualize any query
Displays single monitor location
Displays multiple locations for comparison
Unable to input a list of unique IDs
Can provide list of specific IDs
Current database, 101 gBytes with 52.7 million detections
Website of real-time node
Further development of this telemetric portal is ongoing. We would like to add additional capabilities. We will be deploying an environmental sonde from Eureka Sensors, which has sensors of temperature, salinity, pH, dissolved oxygen, turbidity, and chlorophyll A. It is our intention to eventually display these data upon the website. Also addition diagnostic metadata will be displayed such as the voltage of the communication control center in order to know that the battery is charged and the solar panel is connected and functional.
Real-time node geographical distribution
During the winter of 2016, 16 real-time nodes were established at a ten sites in the watershed. On the Sacramento River upstream to downstream, paired nodes were set up at Colusa, Tisdale Weir, Knights Landing, Feather River, The I-80 and Tower Bridges near the city of Sacramento. The last two paired nodes were less than a kilometer apart, permitting a final determination of probability of detection. Those winter-run that migrated this far downstream were detected at both paired nodes, providing a 100% detection efficiency, and this facilitated the estimation of the rate of survival between the successive paired upstream real-time nodes. Arnold Ammann gave sixteen biweekly updates with the percentage of fishes reaching the successive pairs of nodes downstream of the release site ending on March 3, 2016. These nodes are currently being upgraded to the second-generation architecture.
We will now present two examples where information about tagged fish from the real-time nodes proved useful to resource managers. It is not our intent in this communication to present the detailed scientific results from the studies of these fish but to illustrate how the real-time detection of fish can be used by managers in making regulatory decisions. This same approach could be used with terrestrial species that aggregate at sites.
Detecting winter- and spring-run smolts in real time
The regulatory biologists did not anticipate the rapid arrival of the hatchery fish at the Sacramento. The winter-run hatchery releases during 2014 took a much longer time to reach Sacramento. These smolts were released at Caldwell on February 10, 2014, in anticipation of a pulsed flow that increased 5000 cfs from 5000 to 10,000 cfs measured 2 days later. However, the peak of 48 smolts did not occur until 20 days on March 2, 2014, coinciding with a second 6000 cfs increase from 4000 to 10,000 cfs. Based on this prior information, resource agencies planned to open the gates throughout February to divert water into the interior Delta to improve water quality. The agencies believed that the fish would take 3 weeks to a month to reach the DCC gates. The prompt arrival of winter-run smolts at Sacramento on February 6, 2015, convinced the agencies to keep the DCC closed through March 2015, reducing additional mortality to the 2015 hatchery winter-run releases due to diversion into the Delta. During winter 2016, we deployed 16 real-time nodes at a ten sites in the watershed. On the Sacramento River upstream to downstream, paired nodes were set up at Colusa, Tisdale Weir, Knights Landing, Feather River, The I-80 and Tower Bridges near the city of Sacramento. Ammann gave sixteen biweekly updates with the percentage of fishes reaching the successive pairs of nodes downstream of the release site ending on March 3, 2016.
Real-time reporting proved useful also in monitoring downstream migration of the spring-run smolts during 2015 and 2016. The Feather River Fish Hatchery released smolts at two locations, Gridley and Boyds Pump Boat Ramps, on the Feather River late March 2015. A subsample of 75 acoustically tagged fish accompanied each release of hatchery fish to permit immediate monitoring of their downstream migration success. A supplemental pulse of water of 440 cfs was released from Oroville Reservoir to stimulate downriver migration. Only one tagged individual from the upstream release at Gridley and seven from the downstream release site at Boyds Pump, or 5.3% of the total, reached the single real-time node near the city of Sacramento (Arnold Ammann, NMFS, unpub. data). The Feather River Hatchery Oversight Team decided to release the rest of the hatchery-raised spring-run on 2 April rather than the traditional mid-April date and to accompany them with a larger release of water of 1400 cfs (Jeffrey Stuart, NMFS, pers. commun.). A total of 12 (8.0%) of the 150 tagged smolts released at the two sites were detected at the Sacramento node (Arnold Amman, NMFS, unpub. data.). During the El Niño conditions of spring 2016, 54 (27%) of 200 tagged smolts were detected at the Sacramento nodes (Colin Purdy, CDFW, pers. commun.). These smolts not only exhibited higher migratory success but also moved downstream faster than smolts during spring 2015. This higher survival and faster movement coincided with the higher flows in the Sacramento River during 2016.
Detecting green sturgeon in real time
Researchers in Washington and California have pleased long-term coded tags beacons within the abdominal body cavities of nearly 400 Green Sturgeon over the past 10 years. The information on sizes, weights, timing of tagging and release are contained in the California Fish Tracking Consortium database. The batteries with lives ranging from 3 to 10 years have made it possible to monitor repeated upstream migrations of green sturgeon in the Sacramento River system. Adults return to spawn in the Sacramento River approximately every 2–5 years (unpub. data, Michael Thomas).
This success led CDFW to support the development of the real-time node. One real-time node was immediately situated in the Yolo Bypass downstream of Lisbon Weir and one on the main stem of the Sacramento River downstream of the Tisdale Weir, where green sturgeon might strand (nodes 5 and 4 in Fig. 5). These two nodes enable CDFW now to better respond to sturgeon stranding at the two bypasses. The nodes detected 23 green sturgeon during their spawning season from late February to late June 2015. The passage of tagged fish are indicated by solid circles superimposed on a hydrograph of the river stage, or height in meters (Fig. 5). The river height, measured at the Fremont gage, ranged from 5.2 m from the end of February to 3.5 m by the end of June, well below the 12 m height that would result in flooding. Regulatory biologists concerned with the protection of this species were given weekly alerts by Matt Pagel, the Database Manager in the Biotelemetry Laboratory, during the spawning season.
The winter-run race is classified as endangered under the Endangered Species Act. Winter-run adults migrate up river from December through July, with a peak during the period between January and April. Adults hold in a section of the Sacramento River between Keswick Dam and approximately the location of the Red Bluff Diversion Dam until they commence spawning. They spawn between late-April and mid-August, with a peak in June and July as reported by CDFW annual escapement surveys. Young of the year winter-run Chinook Salmon begin to emigrate downstream from their natal river reaches in fall into the lower Sacramento River and typically reach the area of the DCC gates starting in late winter (mid-January and February). Elevated river flows associated with storm events stimulate this downstream movement.
Thank you so much for all your daily reporting. I want to let you know how helpful it is to get this kind of “real-time” information, as the Directors of the five agencies continue to meet by conference call every morning at 8 am to go over all information and decide on the best balance of water exports and fish protection for the day. …I really appreciate you accommodating the management needs in the continuing drought (Maria Rea, pers. communication).
In conclusion, real-time information about the whereabouts of winter- and spring-run smolts is enabling resource managers to make more timely decisions with regard to the closure of a water diversion and the magnitudes of supplementary water releases.
Thanks again for these detailed updates and apologies for the confusion on metadata. The white sturgeon rescued on 31 March 2016…is moving downstream (≈40 river miles). We believe this was a spawned out female so this downstream behavior seems appropriate. I am always glad to get reports of fish moving around after being rescued as it shows they survived and our efforts were not in vain (Colin Purdy, pers. commun.).
The two case studies presented within illustrate a real success story of researchers from the resource agencies working closely with researchers in academia to utilize conservation-based information in protecting listed species. In the first case, the information was rapidly transmitted to the regulatory division of NMFS, which quickly disseminated it to the other federal and state resource agencies for timely management decisions. In the second case, the information was relayed to the lead biologist of a sturgeon rescue crew at CDFW. This real-time technology permits resource managers to take an adaptive approach to balancing the public’s need for water with the needs of migratory fishes. The success of the case studies presented here relied heavily on a mutual cooperation among researchers and resource managers during this period of drought in Central California.
APK obtained the funding, oversaw the development and deployment of the real-time nodes, and wrote the paper. AJA provided the detection data for winter- and spring-run Chinook smolts. TVA led the team deploying and maintain the array of real-time detection nodes. RDB deployed and maintained the real-time monitors. MDP maintained a SQL database of tag detections, provided weekly updates of sturgeon detections during their spawning season, and edited a draft of the paper. MJT developed a prototype real-time node working closely with engineers from VEMCO-Amerix, Netronix, and Teknologic Industries, and helped in their deployment and maintenance. All authors read and approved the final manuscript.
Jeffrey Stuart, a Fisheries Biologist in the California Central Valley Area Office of NMFS, participated in the development of the manuscript. Brent Smith of Teknologic Engineering added the real-time capability to the 416-kHz-sensitive JSATS monitors and is currently working with Biotelemetry Laboratory of UC Davis to improve the real-time monitoring stations. Dale Webber of VEMCO-Amerix oversaw the integrated cabling of the 69 and 180 kHz receivers to provide similar outputs. Vaseilios Nasis of Netronix added the capability of displaying tag detections in graphical and tabular format on Environet. We want to express our gratitude in particular to the second reviewer of this manuscript for giving us guidance in reorganizing the flow of the article.
The authors declare that they have no competing interests.
Availability of data and materials
The records of spring-run Chinook smolt detections plotted in Fig. 8 are available from Mr. Arnold Ammann, Research Scientist at the Southwest Fisheries Center, Santa Cruz. The records of green sturgeon presented in Fig. 9 are available from Mr. Matthew Pagel, Database Manager at the Biotelemetry Laboratory at UC Davis.
Consent for publication
All of the authors consent to this role in the preparation of this article.
The real-time stations were developed by members of the Biotelemetry Laboratory of the University of California working closely with the engineers from the above-mentioned companies. The systems were designed, the individual components purchased, and assembly completed with a grant to APK entitled, “Expanding fish tracking array with real-time monitoring of tagged sturgeon and salmonids” (E1183018) from the California Department of Fish and Game’s Ecosystem Restoration Program.
Statement of ethics approval
The implantation techniques used for JSATS beacons used in this study were reviewed by the veterinarian staff of UC Davis and are covered by UC Davis Animal Care Protocols #16819, “Migration and Movement of Fall and Spring Run Chinook Smolts” and #18744, “Spring Run Chinook Salmon Smolt Movement in the San Joaquin River.”
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- McKibben JN, Nelson DR. Patterns of movement and grouping of gray reef sharks, Carcharhinus amblyrhynchos, at Enewetak, Marshall Islands. Bull Mar Sci. 1985;38:89–110.Google Scholar
- Klimley AP, Butler SB. Immigration and emigration of a pelagic fish assemblage to seamounts in the Gulf of California related to water mass movements using satellite imagery. Mar Ecol Progr Ser. 1988;49:11–20.View ArticleGoogle Scholar
- Klimley AP, Butler SB, Nelson DR, Stull AT. Diel movements of scalloped hammerhead sharks (Sphyrna lewini Griffith and Smith) to and from a seamount in the Gulf of California. J Fish Biol. 1988;33:751–61.View ArticleGoogle Scholar
- Klimley AP, Voegeli F, Beavers SC, Le Boeuf BJ. Automated listening stations for tagged marine fishes. Mar Technol Soc J. 1998;32:94–101.Google Scholar
- Cooke SJ, Midwood JD, Thiem JD, Klimley P, Lucas MC, Thorstag EB, Eiler J, Holbrook C, Ebner BC. Tracking animals in freshwater with electronic tags: past, present, and future. Anim Biotelemetry. 2013;1:1–34.View ArticleGoogle Scholar
- Kessel ST, Cook SJ, Heupel MR, Hussey NE, Simpfendorfer CA, Vagle S, Fisk AT. A review of detection range testing in aquatic passive acoustic telemetry systems. Rev Fish Biol Fish. 2014;24:199–218.View ArticleGoogle Scholar
- Dagorn L, Pincock D, Girard C, Holland K, Taquet M, Sancho G, Itano D, Aumeeruddy R. Satellite-linked acoustic receivers to observe behavior of fish in remote areas. Aquat Living Resour. 2007;20:307–12.View ArticleGoogle Scholar
- Perry RW, Brandes PL, Sandstrom PT, Klimley AP, Ammann A, MacFarlane B. Estimating Survival and migration route probabilities of juvenile Chinook salmon in the Sacramento–San Joaquin River Delta. N Am J Fish Manag. 2010;30:142–56.View ArticleGoogle Scholar
- Steel AE, Sandstrom PT, Brandes PL, Klimley AP. Migratory route selection by juvenile Chinook salmon at the Delta Cross Channel, and the role of water velocity and individual movement patterns. Environ Biol Fish. 2013;96:215–24.View ArticleGoogle Scholar
- Sommer TR, Harrell WC, Nobriga ML. Habitat use and stranding risk of juvenile Chinook salmon on a seasonal floodplain. N Am J Fish Manag. 2005;25:1493–504.View ArticleGoogle Scholar
- Thomas MJ, Peterson ML, Friedenberg N, Van Eenennaam JP, Johnson JR, Hoover JJ, Klimley AP. Stranding of spawning run green sturgeon in the Sacramento River: post-rescue movements and potential population-level effects. N Am J Fish Manag. 2013;33:287–97.View ArticleGoogle Scholar
- Lennox RJ, Aarestrup K, Cooke SJ, Cowley PD, Deng ZD, Fisk AT, Harcourt RG, Heupel M, Hinch SG, Holland KN, Hussey NE, Iverson SJ, Kessel ST, Kocik JF, Lucas MC, Mills Flemming J, Nguyen VM, Stokesbury MJW, Vagle S, VanderZwaag DL, Whoriskey FG, Young N. Envisioning the future of aquatic animal tracking: technology, science, and application. BioScience. 2017. doi:10.1093/biosci/bix098 (in press).Google Scholar
- Young N, Gingras I, Nguyen VM, Cooke SJ, Hinch SG. Mobilizing new science into management practice; The challenge of biotelemetry for fisheries management, a case study of Canadas Fraser River. J Int Wildl Law Policy. 2013;16:331–51.View ArticleGoogle Scholar
- McGowan J, Beger M, Lewison RL, Harcourt R, Campbell H, Priest M, McMahon C. Integrating research using animal-borne telemetry with the needs of conservation management. J Appl Ecol. 2017;54:423–9.View ArticleGoogle Scholar