New Alternatives to Online TRO Measurement

New Alternatives to Online DPD Instruments for TRO Measurement_in_RIA/MS

2020

Background

Halogen Systems, Inc. started in 2012 to commercialize its multiparameter sensor technology. From the outset, it sought to eliminate the problems with existing amperometric sensors and develop a robust, alternative
sensor platform with applications across many industries.  Its sensor is radically different other sensors, hence its name, DPI (Direct Pipe Insertion) Amperometric.  This new amperometric sensor was funded, in part, by
Small Business Investment Research (SBIR) contracts from the US Office of Naval Research (ONR) (DoD, 2020). Since 2014, this sensor saw constant improvement and enhancement.  Performance and relative
advantages are described in the sections below:

Executive Summary

The DPI Amperometric is a new alternative to Online DPD Instruments.  When used in Ballast Water Management Systems (BWMS), this alternative eliminates some potential compliance issues.  Unique features include:

There are also installation and service cost advantages:

Extensive Validation in BWMS application:

Third-party evaluation

The Alliance for Coastal Technologies (ACT) conducted an evaluation of Ballast Water TRO Instruments with currently available technology.  While ACT did not directly compare sensors, several points are evident from these reports.

PSU Salinity

HSI

DPD1

DPD2

0.2

0,809

0,809

1.072

0.2

0.962

0,809

0.728

0.2

0.814

0,924

0.777

15

0.779

--

0,762

15

0.825

0.783

0.458

15

0.793

0.859

0.635

30

0.756

--

0.746

30

0.818

0.747

0.456

30

0.717

0.787

0.603

15

Not Tested

0.814

0.585

16

0.778

0.794

0.665

Sample Reading

Reference Method

DPD2

DPD1

HSI

1

3.55

2.3

3.02

3.45

2

3.56

2.41

3.1

3.45

3

3.48

2.39

3.01

3.4

4

3.53

2.39

3.01

3.34

5

3.49

2.29

3.05

3.34

6

3.5

2.3

2.93

3.35

7

3.47

2.31

2.92

3.33

8

3.41

2.33

2.91

3.28

9

3.38

2.32

2.85

3.27

10

3.45

2.3

2.83

3.24

11

3.33

2.32

2.79

3.22

12

3.27

2.27

2.68

3.2

Average STDEV CV (%)

3.45

0.09

2.60%

2.33

0.04

1.90%

2.93

0.12

4.20%

3.32

0.08

2.50%

Relative % Accuracy

-32%

15%

15%

Fast Response from direct pipe installation

This sensor is installed directly in the ballast pipe for rapid TRO readings (<1 min). Online DPD instruments fed by long water sampling lines introduce potential sample contamination as well as a delay (often 3 to 8 minutes on some vessels) before the BWMS receives an updated reading.  A delayed process loop often causes problems with accurate control, resulting in oscillation between over chlorination and under chlorination. Long sampling lines are also often responsible for sample contamination.

Robust Operation in muddy ports

BWMS systems are evaluated using a challenge level of 50 ppm Total Suspended Solids (TSS) (EPA, 2010). However, some ports have much higher suspended solids and the water can even appear “muddy.” As ballast tanks are emptied, silt remaining in the bottom of the tank has a similar effect. To demonstrate the robustness of this sensor, it was evaluated using 40 times the required TSS level (2,000 ppm) (HSI ISO15839, 2020).  These high TSS levels adversely impacted the DPD method (Spectrophotometer) resulting in lower measurements.  This is apparent from Figure 2and Figure 3. To obtain accurate DPD readings the sample required: 1) reaction with the reagent, 2) filtration (5 micron) of the sample to remove the TSS, then 3) measurement. (Hach, 10014). This resulted in both filtered and unfiltered DPD measurements for each TRO level. These should align since the TRO concentration is the same for both samples, however, they start diverging at 200 ppm of TSS, indicating the dirty water is interfering with the spectra in the measurement method.

An online DPD instrument suffers from the same limitation. As seen in Figure 3, lower TRO discharge levels (like the critical Maximum Allowable Discharge Concentration (MADC) of 0.1ppm) result in an even more significant reduction in accuracy.

Ballast water Flow rate changes have no impact on measurement accuracy

Other amperometric sensors are extremely sensitive to flow changes. Halogen’s sensor has proven flow independence. During this test, flow varied from 0, 1.93 meters per second velocity (m/s) to 3.73 m/s.  Sensor accuracy was checked using a laboratory spectrophotometer (Hach DPD) for total chlorine measurement. The sensor measured chlorine accurately at all three flow rates (See Table 3). Figure 4 shows these results (HSI 06, 2020).

Hach DPD values with corresponding Halogen sensor measurements from the time the water sample was taken. The accuracy of the Halogen sensor as compared to the Hach DPD value is given in the last column.

low Operational cost

No chemical reagents or membranes are needed, resulting in lower-cost operation and maintenance labor by the ship’s crew (Table 4). There is only a bi-annual wear kit replacement. According to KRS, DPD instruments also require additional maintenance operations (Korean Register of Shipping (KRS)):

Flow Test

Flowrate (GPM)

Chlorine Concentration (ppm)

Hach DPD

Halogen Sensor

Accuracy of Halogen Sensor

0

8.98

8.96

0%

8.83

9.05

2%

120 (3.73 m/s)

9.49

9.06

-4%

9.48

9.04

-5%

9.02

8.94

-1%

62 (1.93 m/s)

8.64

8.99

-4%

9.06

8.89

-2%

8.87

8.92

1%

0

9.26

8.92

-4%

9.23

8.82

-4%

120 (3.73 m/s)

8.09

8.77

-1%

9.29

8.91

-4%

9.04

8.77

-3%

Flow Test (continued)

Flowrate (GPM)

Chlorine Concentration (ppm)

Hach DPD

Halogen Sensor

Accuracy of Halogen Sensor

62 (1.93 m/s)

8.9

8.8

-1%

9.02

8.91

-1%

8.78

8.84

-1%

0

8.61

8.78

2%

9.05

8.78

-3%

120 (3.73 m/s)

8.77

8.7

-1%

8.82

8.63

-2%

9.14

8.61

-6%

62 (1.93 m/s)

8.96

8.67

-3%

8.71

8.71

-0%

9.07

8.55

6%

0

808

8.63

-2%

8.77

8.48

-3%

From these data, it is clear the flow conditions have a negligible effect on sensor accuracy between 0 and 3.73 m/Sec flow velocity.

Long interval between Maintenance cycles

Following the ISO 15839 methodology for a “Field Test” Halogen Sensors operated 24 hours a day, for a total of 33 cycles over 80 days, yet required no maintenance or calibration. This corresponds to 66 weeks or 1.2 years of shipboard operation and over 792 hours of actual sensor operation. This accelerated test was based on assumptions shown in Table 5. During a typical two-week voyage, a ballast/deballast cycle occurs in which the sensors run for ~8 hours and remain off for the rest of the voyage. During the deballast cycle sodium sulfite was used as a chlorine neutralizer to lower the TRO level ~0.1 ppm. Chlorine levels were measured at several points during the deballast cycle, including at 0.1 ppm. The sensor would have been recalibrated if at any time it deviated from the DPD reading by 15% or more. An example of a cycle is shown in Figure 5 (HSI 04, 2020).

Service

DPI,Amperometric

DPD

Reagents

None

Reagents every 30 to 60 days of operation

Replace Wear parts

24 months

NA

Annual Costs USD

$120

~$600

Annually

NA

Pump requires overhaul every year due to corrosion by chemicals and seawater

Monthly

NA

Checking and Cleaning T-strainer

Quarterly

NA

Checking and Cleaning check valve and pump tubing

Semi- annually

NA

Two-way solenoid valve cleaning

Installation cost

Installation costs for the Halogen Sensor are much lower than DPD instruments since there are no sampling lines, waste lines, remote valves, sample conditioning, or pumps (See Table 6). Estimated savings are over $2,200 per instrument.

Tyoical BWMS Maintence period

Typical Voyage (days)

14

Ballasting Time per Voyage (hours)

10

Ballasting Time per month (hours)

21.4

Calibration Check (days)

60

Typical Sensor Operation (hours) in 60 days

42.9

Ease of Service

The Halogen Hot Tap Valve allows for easy sensor mounting in a ballast pipe and can be equipped with a removal tool for either permanent attachment or intermittent service.

Figure 6 Sensor installed without optional Remover

Figure 7: Remover installed to retract sensor to:

1. Valve close point

2. Then removal point

Figure 8: Slide sensor out of the Remover plate

Figure 9: Remove saddle clamps to separate sensor from junction box

Item

DPT Instrument

Amperometric Sensor

Cost Comparison

Pump

909

0

Valves

Waterlines Run shipboard

Skid mounting

Sample conditioning and filtration

1,763

0

0

0

0

Hot Tap Valve & Remover

NA

0

Total Added Installation Cost

$2672 Estimated

0

Hazardous and Non-Hazardous Models

There are four sensor models available. Both Hazardous (Zone1 Group IIC) and non-hazardous model types are available with three mounting options. The sensor’s smaller size and rapid removal make it suitable to carry as a spare on board, reducing potential downtime (See Figure 10). The sensor is easily separated from the junction box for quick replacement or service Figure 9. A side stream version is also available that does not require pressure or flow regulation (See Table 8). Customers have installed this version without a sampling pump by using a pressure differential in the ballast pipe to circulate water through the chamber. The models can also be installed on Open Deck.

Item

In Pipe (Hot Tap)

Side Stream

Non-Hazar

Self-cleaning

The sensor is covered by seven US Patents and five foreign patents. The integrated pump Figure 11 increases velocity across the sensor electrode surfaces and increases the signal, thereby increasing the signal to noise (S:N) ratio. This feature also makes constant cleaning of the electrodes possible. Cleaning beads are captured in a cavity within the sensor the flow and moves them about to abrade the electrodes. This pump is driven by a motor with a 20,000-hour life. In addition to TRO, the sensor measures salinity, temperature, ORP, and pH. Three of these parameters are used to compensate for signal changes in fresh and brackish water.

Item

IECEX Sensor

Side stream chamber with IECEx sensor with sampling port

Hazardous-Zone1 Group IIC

Integrated salinity sensor

All sensors come with an integrated salinity sensor. This may reduce the need for another instrument (savings of >$3,000). This function enables sensor compensation in freshwater ports.

Conclusion

As stated in the 2014 report (Tamburri, 2014): “Amperometric sensors are not commonly used in BWMS but offer some potential advantages over other instruments. Amperometric sensors are reagentless and if applied to BWMS would allow for the direct immersion of the sensor in a sampling inlet, ending the need for sampling pumps and reagents associated with DPD online analyzers.”

Designed specifically for BWMS type applications, Halogen’s amperometric sensor is a unique combination of technologies that serve the Ballast Water applications in a cost-efficient manner eliminating some potential compliance issues.

References

Alliance for Coastal Technologies HF. (2020). PERFORMANCE VERIFICATION STATEMENT For the SSR-Ex Total Residual Oxidant (TRO) and Chlorine Monitor. Baltimore, MD: Alliance for Coastal Technologies. Retrieved from (http://www.act-us.info/evaluations.php

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