Error in distributed temperature sensing (DTS) water temperature measurements may be introduced by contact of the fiber optic cable sensor with bed materials (e.g., seafloor, lakebed, streambed). Heat conduction from the bed materials can affect cable temperature and the resulting DTS measurements. In the Middle Fork John Day River, apparent water temperature measurements were influenced by cable sensor contact with aquatic vegetation and fine sediment bed materials. Affected cable segments measured a diurnal temperature range reduced by 10 % and lagged by 20–40 min relative to that of ambient stream temperature. The diurnal temperature range deeper within the vegetation–sediment bed material was reduced 70 % and lagged 240 min relative to ambient stream temperature. These site-specific results illustrate the potential magnitude of bed-conduction impacts with buried DTS measurements. Researchers who deploy DTS for water temperature monitoring should understand the importance of the environment into which the cable is placed on the range and phase of temperature measurements.
Distributed temperature sensing (DTS) allows averaged temperature measurement at 0.25–2 m intervals along a fiber optic cable. The utility of DTS to characterize a wide variety of environmental systems has been demonstrated (e.g., Selker et al., 2006; Lowry et al., 2007; Henderson et al., 2009; Sayde et al., 2010). Accurate measurement requires that the temperature of the fiber optic cable equilibrates with the temperature of the measured media. Heat fluxes that are external to that media can significantly impact cable temperature, depending on media properties, surrounding system characteristics, and the physical placement of the cable within the media. For instance, Neilson et al. (2010) reported bias in DTS water temperature measurements due to solar heating of the submersed fiber optic cable. Under conditions of minimal water turbulence and shallow depth, cable absorption of shortwave solar radiation caused significant measurement error. A valuable contribution of the work was to quantify this temperature biasing effect based on water velocity and depth.
Conduction or convection of heat from external media to the fiber optic cable is another biasing influence on DTS measurements. Researchers who used DTS to measure pore-water temperature below streambeds have sought to increase measurement accuracy by burying fiber optic cable within the bed, rather than by placing it on top, where contact with the stream water introduced an external heat flux (Lowry et al., 2007; Krause et al., 2012). Conversely, heat conduction from bed materials may influence apparent water temperature measurements. For DTS measurements in hydrologic systems, fiber optic cable has been deployed to the bottoms of estuaries, lakes, and rivers. The cable used in these installations is typically selected to be denser than water to keep the cable at the bottom of the water column and limit exposure to the air–water interface and solar radiation (e.g., Petrides et al., 2011). However, cable contact with seafloor, lakebeds, and streambeds introduces the potential for conduction heat flux from the bed material. In some cases, the bed material may partially or fully envelop the cable (Fig. 1), reducing and delaying the diurnal range of the water temperature measurements due to the heat transfer processes in the sediments.
The impact of bed conduction on DTS measurements depends on
the degree of fiber optic cable burial within bed materials, including
DTS stream temperature measurements taken at 08:00, 10:00, 13:00, 15:00 and 17:00 PST (Pacific standard time) along 375 m of the Middle Fork John Day River are shown on the left, with segments that intersected vegetation–sediment layers (centered at 129, 152, and 208 m downstream) highlighted in purple. On the right, these temperature measurements within the layers were plotted temporally with average ambient stream water temperature (distance-averaged temperature from 96 to 116 m downstream).
Two days of point temperature measurements from above, within and below the vegetation–sediment layer.
Factors affecting bed conduction are themselves determined by several variables. First, equilibration of bed temperature and water temperature varies seasonally and diurnally, and also depends on bed material type and composition. Second, the surface area of cable contact with the bed depends largely on bed material type. Harder bed materials (stone, concrete, packed fine sediment) contact the cable minimally, while softer materials (loose fine sediment, aquatic vegetation) can partially or fully envelop the cable. Other factors, such as solar exposure and stratified water systems, are not treated here. Additionally, for a rich set of literature on phase and amplitude patterns in thermal signals as a function of depth, refer to Hatch et al. (2006) and Luce et al. (2013).
This paper presents observed thermal impacts on DTS data arising from contact with the streambed based on fluvial temperature data from the Middle Fork John Day River, Oregon, USA. Supplementary temperature measurements made within and above the bed material quantified the differences in diurnal temperature signals of the bed and ambient stream water.
In the summer of 2011, stream temperature was monitored on a 375 m reach
(“study reach”) of the Middle Fork John Day River using DTS. The upstream
end of the study reach was located at 44.642362
The installation employed a custom-built fiber optic cable manufactured by
AFL Telecommunications, consisting of two Giga-Link 600 multimode fibers
protected by a 1.0 mm o.d. stainless steel loose tube, a resin-stabilized
fiberglass sheath, and a meter-marked polyurethane jacket, completing the
cable to a 2.5 mm diameter. The cable was installed in the stream
channel thalweg and was observed to sink and remain stable on the riverbed
in all water conditions except the most turbulent. Alluvial rocks were
placed to secure the cable where the risk of cable movement was high. A
SensorTran Gemini DTS instrument was used for data collection. The
installation was powered by a photo voltaic system and housed in a 2
Visual assessments of cable position, channel bed type, and flow conditions
were made. Channel bed material beneath most of the study reach consisted of
cobbles and a few sections of hard-packed fine sediments. The only recorded
exception to these bed conditions consisted of three 5 to 20 m long
segments where aquatic vegetation growing in beds had trapped fine sediments
to create thick, soft and porous layers of suspended vegetation and mineral
matter over the buried hard bed. The fiber optic cable (density: 1.6 g cm
The apparent temperature dynamics of cable sections that intersected the vegetation–sediment layers were altered (purple-highlighted segments in Fig. 2) relative to adjacent sections of cable. The range of diurnal temperature variation was reduced typically by 10 % and lagged in time by 20–40 min relative to that of the ambient stream water.
To establish the magnitude of DTS stream temperature bias relative to cable
position within the vegetation–sediment layer, temperatures within and above
a layer were continuously monitored at three vertically distributed
locations. The monitored vegetation–sediment layer was located at
44.596325
Over the two monitored days (24–26 August 2010), the temperature range at Location 1 was reduced by 70 % relative to the range of the stream temperature, and the extrema lagged those of stream temperature by 180–240 min (Fig. 3). At the top of the vegetation–sediment layer (Location 2), the diurnal temperature range was less affected, reduced by just 10 % and lagged by 10 to 20 min.
Vegetation–sediment layers on the Middle Fork John Day River streambed impacted DTS water temperature measurements by reducing the measured diurnal temperature range by 10 % and by causing a 20–40 min lag. If the cable had been placed deeper within the layers, the diurnal range reduction may have been as high as 70 % of the stream temperature range, and the lag may have been as long as 240 min. While these impacts were site-specific (unique to the location and streambed material), DTS water temperature measurements in other hydrologic systems may be affected by related bed material effects. Researchers who deploy DTS to streambeds, seafloor, or lakebeds for water temperature monitoring would do well to understand the environment into which the cable is placed and to flag potential measurement error due to conduction from bed materials.
This work was made possible by the generous collaboration of the Confederated Tribes of the Warms Springs Reservation of Oregon (CTWSRO) and funded by the Oregon Watershed Enhancement Board and the National Science Foundation award 0930061. Most of the data described herein were collected on CTWSRO property, and all field workers were housed within the CTWSRO research station in Bates, Oregon. Other collaborators include The River Design Group and the US Forest Service. Edited by: L. Vazquez