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Ref. No. [UMCES] CBL 2016-013

ACT VS16-04

3

EXECUTIVE SUMMARY

The Alliance for Coastal Technology (ACT) conducted a sensor verification study of in situ

dissolved oxygen sensors during 2015-2016 to characterize performance measures of accuracy and

reliability in a series of controlled laboratory studies and field mooring tests in diverse coastal

environments. The verification including several months of Laboratory testing along with three

field deployments covering freshwater, estuarine, and oceanic environments.

Laboratory tests of

accuracy, precision, response time, and stability were conducted at Moss Landing Marine Lab.

A

series of nine accuracy and precision tests were conducted at three fixed salinity levels (0, 10, 35)

at each of three fixed temperatures (5, 15, 30

o

C). A laboratory based stability test was conducted

over 56 days using deionized water to examine performance consistency without active biofouling.

A response test was conducted to examine equilibration times across an oxygen gradient of 8mg/L

at a constant temperature of 15

o

C. Three field-mooring tests were conducted to examine the

ability of test instruments to consistently track natural changes in dissolved oxygen over extended

deployments of 12-16 weeks. Deployments were conducted at: (1) Lake Superior, Houghton, MI

from 9Jan – 22Apr, (2) Chesapeake Bay, Solomons, MD from 20May – 5Aug, and (3) Kaneohe

Bay, Kaneohe, HI from 24Sep – 21Jan. Instrument performance was evaluated against reference

samples collected and analyzed on site by ACT staff using Winkler titrations following the

methods of Carignan

et.al

. 1998. A total of 725 reference samples were collected during the

laboratory tests and between 118 – 142 reference samples were collected for each mooring test.

This document presents the performance results of Onset’s HOBO U26 Dissolved Oxygen Logger

using the RDO® Basic Technology developed by In-Situ, Inc.

Instrument accuracy and precision for the HOBO U26 was tested under nine combinations

of temperature and salinity over a range of DO concentrations from 10% to 120% of saturation.

The means of the difference between the HOBO U26 and reference measurement ranged from

0.047 to 0.314 mg/L over all nine trials. There was a slight decrease in the magnitude of the

differences with increase of both temperature and salinity levels.

A linear regression of instrument

and reference measurements for all trials combined (n=358; r

2

= 1.00; p<0.0001) produced a slope

of 1.037 and intercept of -0.084.

The absolute precision, estimated as the standard deviation (s.d.)

around the mean, ranged from 0.003 – 0.013 mg/L across trials with an overall average of 0.006

mg/L. Relative precision, estimated as the coefficient of variation (CV% = (s.d./mean)x100),

ranged from 0.036 – 0.268 percent across trials with an overall average of 0.074%.

Instrument accuracy was assessed under a 56 day lab stability test in a deionized water bath

cycling temperature and ambient DO saturation on a daily basis. The overall mean of differences

between instrument and reference measurements was 0.041 (s.d. = 0.339) mg/L for 154

comparisons (out of a potential total of 156). A regression of measurement difference over time

showed a minor drift in response with a slope of -0.004 mg/L/d (r

2

= 0.049; p=0.006). But if two

large negative responses near the end of the test are omitted the regression is not significant

.

A functional response time test was conducted by examining instrument response when

rapidly transitioning between adjacent high (9.6 mg/L) and low (2.0 mg/L) DO water baths,

maintained commonly at 15

o

C. The calculated τ

90

was 27 s during high to low transitions and 26 s

for low to high transitions covering the 8 mg/L DO range.