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Ref. No. [UMCES] CBL 2015-010

ACT VS15-03

EXECUTIVE SUMMARY

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

situ pH sensors during 2013 and 2014 to characterize performance measures of accuracy and

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

environments. A ten week long laboratory study was conducted at the Hawaii Institute of

Marine Biology and involved week long exposures at a full range of temperature and salinity

conditions. Tests were conducted at three fixed salinity levels (0.03, 22, 35) at each of three

fixed temperatures (10, 20, 30

o

C). Ambient pH in the test tank was allowed to vary naturally

over the first five days. On the sixth day the pH was rapidly modified using acid/base additions

to compare accuracy over an extended range and during rapid changes. On the seventh day the

temperature was rapidly shifted to the next test condition. On the tenth week a repeated seawater

trial was conducted for two days while the temperature was varied slowly over the 10 – 30

o

C

range. Four field-mooring tests were conducted to examine the ability of test instruments to

consistently track natural changes in pH over extended deployments of 4-8 weeks. Deployments

were conducted at: Moss Landing Harbor, CA; Kaneohe Bay, HI; Chesapeake Bay, MD; and

Lake Michigan, MI. Instrument performance was evaluated against reference samples collected

and analyzed on site by ACT staff using the spectrophotometric dye technique following the

methods of Yao and Byrne (2001) and Liu et al. (2011). A total of 263 reference samples were

collected during the laboratory tests and between 84 – 107 reference samples were collected for

each mooring test. This document presents the results of the Idronaut Ocean Seven 305 Plus

CTD which uses a potentiometric pH sensor consisting of two electrochemical cells including

the measuring sensor and the Ag/AgCl reference sensor filled with a saturated KCl gel.

ACT wants to acknowledge that this particular performance verification was not

conducted under ideal conditions. One significant factor was that the company did not have the

resources to send a representative for direct face to face training, and none of the ACT staff had

any prior experience with this instrument. This lack of direct training contributed to one of the

programming errors which caused a loss of test data. In addition, the company acknowledges a

lack of full understanding of the extent of the testing and that refurbishment of the instrument

between test sites could have been done better. It was felt more care should have been taken to

address biofouling and confirmation of the functionality of the reference electrode. It should be

noted the instrument was re-serviced by the company only prior to the Great Lakes field test

since the initial receipt by ACT more than a year earlier. However, the performance verification

was conducted according to the signed testing protocols and at a minimum the instrument was

exposed to some form of CRM prior to deployment to confirm proper working order.

The Idronaut 305 Plus was not operating at the start of the laboratory deployment due to a

battery short, but the error was not discovered and corrected until January 13

th

, which was about

6 days into the brackish water test. Because no seawater results were obtained initially, a brief

additional seawater exposure test was performed at the end of the study. After redeployment on

January 13th, the instrument operated continuously for the next 33 days and generated 3162 pH

measurements at 15 minute intervals. The total range of pH measured by the Idronaut 305 Plus

was 6.899 to 8.276, compared to the range of our reference pH of 6.943 to 8.502. The Idronaut

305 Plus measurements tracked changing pH conditions among all water sources and

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