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1 2 LABORATORY AND FIELD EVALUATION OF SODIUM PROPIONATE 3 FOR SNOW AND ICE CONTROL 4 5 6 7 Submitted by: 8 9 10 Naoto Takahashi, Ph.D., P.E. 11 Deputy Team Leader 12 Traffic Engineering Research Team, 13 Civil Engineering Research Institute for Cold Region 14 1-3 Hiragishi, Toyohira-ku, Sapporo, 062-8602, Japan 15 Tel: +81-11-841-1738 16 Fax: +81-11-841-9747 17 E-mail: [email protected] 18 19 Kenji Sato, 20 Researcher 21 Traffic Engineering Research Team, 22 Civil Engineering Research Institute for Cold Region 23 1-3 Hiragishi, Toyohira-ku, Sapporo, 062-8602, Japan 24 Tel: +81-11-841-1738 25 Fax: +81-11-841-9747 26 E-mail: [email protected] 27 28 Roberto A. Tokunaga, Ph.D. 29 Senior Researcher 30 Traffic Engineering Research Team, 31 Civil Engineering Research Institute for Cold Region 32 1-3 Hiragishi, Toyohira-ku, Sapporo, 062-8602, Japan 33 Tel: +81-11-841-1738 34 Fax: +81-11-841-9747 35 E-mail: [email protected] 36 37 Noriyuki Nakajima, Ph.D. 38 Professor 39 Biotechnology Research Center and Department of Biotechnology, 40 Toyama Prefectural University 41 Kurokawa 5180, Izumi, Toyama, 939-0398, Japan 42 Tel: +81-766-56-7500 43 Fax: +81-766-56-2498 44 E-mail: [email protected] 45 46 47
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Page 1: LABORATORY AND FIELD EVALUATION OF …docs.trb.org/prp/17-01094.pdf3 LABORATORY AND FIELD EVALUATION OF SODIUM PROPIONATE 4 FOR SNOW AND ICE CONTROL 5 6 7 8 Submitted by: 9 10 11 Naoto

1

2

LABORATORY AND FIELD EVALUATION OF SODIUM PROPIONATE 3

FOR SNOW AND ICE CONTROL 4

5

6

7

Submitted by: 8

9

10

Naoto Takahashi, Ph.D., P.E. 11

Deputy Team Leader 12

Traffic Engineering Research Team, 13

Civil Engineering Research Institute for Cold Region 14

1-3 Hiragishi, Toyohira-ku, Sapporo, 062-8602, Japan 15

Tel: +81-11-841-1738 16

Fax: +81-11-841-9747 17

E-mail: [email protected] 18

19

Kenji Sato, 20

Researcher 21

Traffic Engineering Research Team, 22

Civil Engineering Research Institute for Cold Region 23

1-3 Hiragishi, Toyohira-ku, Sapporo, 062-8602, Japan 24

Tel: +81-11-841-1738 25

Fax: +81-11-841-9747 26

E-mail: [email protected] 27

28

Roberto A. Tokunaga, Ph.D. 29

Senior Researcher 30

Traffic Engineering Research Team, 31

Civil Engineering Research Institute for Cold Region 32

1-3 Hiragishi, Toyohira-ku, Sapporo, 062-8602, Japan 33

Tel: +81-11-841-1738 34

Fax: +81-11-841-9747 35

E-mail: [email protected] 36

37

Noriyuki Nakajima, Ph.D. 38

Professor 39

Biotechnology Research Center and Department of Biotechnology, 40

Toyama Prefectural University 41

Kurokawa 5180, Izumi, Toyama, 939-0398, Japan 42

Tel: +81-766-56-7500 43

Fax: +81-766-56-2498 44

E-mail: [email protected] 45

46

47

Page 2: LABORATORY AND FIELD EVALUATION OF …docs.trb.org/prp/17-01094.pdf3 LABORATORY AND FIELD EVALUATION OF SODIUM PROPIONATE 4 FOR SNOW AND ICE CONTROL 5 6 7 8 Submitted by: 9 10 11 Naoto

2

Takahashi et al.

Shugo Kasamatsu 1

Research Officer, Road Planning Division 2

Construction Department, Hokkaido Regional Development Bureau 3

Kita 8 Nishi 2, Kita-ku, Sapporo, Hokkaido, 060-8511, Japan 4

Tel: +81-11-709-2311(ext. 5357) 5

Fax: +81-11-757-3270 6

E-mail: [email protected] 7

8

9

10

Word count: 4,154 words text + 12 tables/figures x 250 words (each) = 7,154 words 11

12

Revision Date : November 15, 2016 13

Submission Date: August 1, 2016 14

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ABSTRACT 1

To provide the driving public with a safe road surface during winter, large amounts of anti-2

icing and deicing chemicals (deicers) are used. Since there are growing concerns about the 3

impact of chloride-based deicers on motor vehicles, highway infrastructures, maintenance 4

equipment and the environment, the development of alternative deicers and additives serves 5

the public interest. 6

To find a material that can be feasibly used as a deicer, the performance of sodium 7

propionate (SP), which is commonly used as a food additive, was evaluated through a series of 8

laboratory and field tests. Freezing point, metal corrosion, ice melting performance, toxic 9

constituents, and damage to plants were tested in the laboratory, and a field test was conducted 10

to evaluate SP’s deicing performance. 11

SP was found to conform to the standard for toxic substances of deicer in Japan, to achieve 12

more rapid deicing than sodium chloride (NaCl), and to cause almost no corrosion of metal. To 13

reduce costs while taking advantage of SP, the mixing of NaCl and SP, which exhibits 14

performances intermediate between those of NaCl and SP, is considered to be a solution. A 15

mixture of 80% NaCl and 20% SP shows freezing point and ice melting performance equivalent 16

to those of NaCl, mitigates the concentration of chloride ions and the inhibitory effects of NaCl 17

on plants, and is still 80% less corrosive to metal than NaCl is. Considering SP’s high solubility 18

in water and the field test results, it is recommended that SP be used as a pre-wetting material. 19

20

Keywords: Snow and ice control, Sodium propionate, Metal corrosion 21

22

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INTRODUCTION 1

In cold regions, winter weather poses a significant hazard to road transportation. Snow and ice 2

reduce pavement friction, and this can cause traffic delays and increase the risk of traffic 3

accidents (e.g., (1), (2), (3), (4)). To prevent the formation or development of ice, and to break 4

the bond of already-bonded snow and ice, anti-icing and deicing operations have been 5

commonly conducted as a primary snow and ice control strategy (5). 6

As anti-icing and deicing chemicals (hereinafter: “deicers”), chloride-based deicers, such 7

as sodium chloride (NaCl), magnesium chloride, (MgCl2) and calcium chloride (CaCl2) are 8

frequently used (6), (7). To provide a safe road surface for the driving public, large amounts of 9

chloride-based deicers have been applied on winter highways (7), (8), (9), and such use can 10

adversely affect motor vehicles, highway infrastructure, maintenance equipment and the 11

environment (e.g., (9), (10), (11), (12)). 12

Therefore, alternative deicers and additives those promise to be less harmful to highway 13

facilities, motor vehicles and the natural environment have been sought and tested by road 14

agencies and researchers. These include agriculturally derived products (also known as agro-15

based products) (e.g., (13), (14), (15)), compositions formed from organic acids (e.g., (16), (17), 16

(18)), complex chlorides/minerals (CCM) (e.g., (19), (20), (21)), and other deicers (nitrogen 17

products, etc.) (e.g., (22), (23), (24)). Although a considerable amount of research has been 18

carried out and various products are commercially available, chloride-based deicers are still 19

widely used due to their availability, low costs and effectiveness at subfreezing temperatures. 20

Thus, the development of alternative deicers and additives still serves the public interest. 21

This study aims to seek a chemical substance that will be suitable for use as a deicer in 22

terms of cost, corrosion, environmental effect, availability, ease of handling. Most importantly, 23

since the metallic corrosion of motor vehicles, maintenance equipment and infrastructure 24

imposes a lot of costs on both motor vehicle users and highway agencies (25), (26), the 25

substance is required to be much less corrosive to metal than chloride-based deicers are. 26

27

28

METHODOLOGY 29

Selection of the Test Material 30

Chloride-based deicers are known to be highly corrosive to metal because chloride ions (Cl⁻) 31

induce the breakdown of the passive film on iron (27). Compositions formed from organic 32

acids, represented by calcium magnesium acetate (CMA), potassium acetate (KAc) and 33

potassium formate (also known as “acetate/formate-based deicers”) were found to be less 34

corrosive to metal than sodium chloride (16), (17), (18), and even a mixture of acetate and 35

sodium chloride was found to reduce the corrosion of metal relative to sodium chloride (28). 36

However, acetate/formate-based deicers are not frequently used due to cost considerations (6), 37

(29). 38

To find a material that can be feasibly used as a deicer, odorless salts of common organic 39

acid were investigated. First, aqueous solutions of each candidate material were prepared, and 40

the freezing point of each solution was determined. The candidate materials, their freezing 41

points and odor in solution are summarized in TABLE 1. 42

43

44

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TABLE 1 Candidate materials, their freezing points and odor in solution 1

2 3

Among the odorless materials, sodium formate and sodium propionate show freezing 4

points equivalent to that of sodium chloride. Sodium formate is hygroscopic and, accordingly, 5

can absorb moisture while in storage. Since this can cause caking and agglomeration, sodium 6

formate was ruled out for this study. Eventually, sodium propionate was chosen as a test 7

material. 8

Compound

classificationMaterial

Concentration of

solution (wt%)

Freezing

point (˚C)Odor

10 -6.00

15 -10.50

20 -22.00

25 -38.90

5 -1.50

10 -8.30

15 -13.50

20 -19.80

20 -14.50

30 -14.40

20 -13.80

30 -23.70

20 -8.00

30 -16.10

40 -21.20

Ammonium carbonate 20 -4.90 Ammonia odor

20 -16.20

30 -24.50

Ammonium formate 20 -15.70 Odorless

Sodium acetate 20 -19.20 Acetic acid odor

Ammonium acetate 20 -16.10 Acetic acid odor

potassium acetate 20 -15.10 Acetic acid odor

Calcium acetate 20 -10.50 Acetic acid odor

Magnesium acetate 20 -8.55 Acetic acid odor

Propionic acid Sodium propionate 20 -17.00Odorless or faint acetic-

butyric acid odor

Butyric acid Sodium butyrate 20 -15.20 Butyric acid odor

Oxalic acidPotassium oxalate

monohydrate20 -6.90 Odorless

20 -10.30

30 -27.10

Disodium succinate 20 -11.60 Odorless

20 -10.60

30 -21.00

Potassium succinate

trihydrate20 -6.30 Odorless

Sodium succinate

hexahydrate20 -5.90 Odorless

20 -6.60

30 -11.20

40 -21.40

Tripotassium citrate

monohydrate20 -5.10 Odorless

Trisodium citrate dihydrate 20 -4.90 Odorless

Diammonium hydrogen citrate 20 -4.50 Odorless

Dipotassium hydrogen citrate 20 -4.00 Odorless

Ammonium dihydrogen citrate 20 -3.80 Odorless

Citric acid 20 -3.20 Odorless

20 -7.50

30 -14.60

40 -27.20

Lactic acid Sodium lactate 20 -5.10 Odorless

Potassium gluconate 20 -3.70 Odorless

Sodium gluconate 20 -3.90 Odorless

Maleic acid Disodium Maleate Odorless

Gluconic acid

Succinic Acid

Diammonium succinate Odorless

Citric acid

Triammonium citrate Odorless

Formic acidSodium formate Odorless

Acetic acid

Malonic acid Disodium malonate Odorless

Ammonium salt

Ammonium carbamate Odorless

Ammonium nitrate Odorless

Chloride

Calcium chloride Odorless

Sodium chloride Odorless

Ammonium chloride Odorless

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Material of Interest 1

Sodium propionate (C3H5NaO2) is the sodium salt of propionic acid. It occurs as colorless, 2

transparent crystals or a granular crystalline powder. It is odorless, or it has a faint acetic-3

butyric acid odor, and it is highly soluble in water (TABLE 2). Since the ingredients meet the 4

specifications of the food chemicals, sodium propionate is used as a food additive in many 5

countries (e.g., (30), (31), (32)). In Japan, the annual consumption of sodium propionate is 6

around 40 tons. 7

8

TABLE 2 General information and properties of sodium propionate (33), (34), (35) 9

10 11

The price of sodium propionate as a food additive is US$2.3/kg for purchases of 10 tons at a 12

time. This is about 10 times as expensive as sodium chloride for deicer in Japan. To reduce the 13

cost but still benefit from the positive effects of sodium propionate, mixtures of sodium 14

propionate and sodium chloride were also tested in this study. 15

16

17

Description of laboratory tests 18

Freezing point 19

A test tube that contains specimen (solution of the test material) is put into acetone which is 20

kept at 0°C in a stainless steel dewar bottle. Then, the specimen was gradually cooled. The 21

temperature decrease was set to be approximately 1°C/min. The temperature of the specimen 22

is measured and recorded periodically. Measurement was conducted three times, and the 23

average value was adopted in this study. The freezing point is taken as the intersection of 24

projections of the cooling curve and the freezing curve. If the solution supercools, the freezing 25

point is the maximum temperature reached after supercooling. 26

Since the freezing points of sodium chloride (hereinafter: “NaCl”) and sodium propionate 27

(hereinafter: “SP”) are already known, a mixture of sodium chloride and sodium propionate 28

(hereinafter: “NaCl/SP mixture”) are additionally tested. 29

30

31

32

Appearance

Chemical Formula

C3H5NaO2

CAS* Registry Number 137-40-6

Molar Mass 96.060 g/mol

Solubility in Water 995 kg/m3 (20 ˚C)

Potential of hydrogen (pH) 8 - 9.5

Food Additive Price** (USD/Kg) 2.3

* CAS: Chemical Abstracts Service issued by American Chemical Society

** For purchase of 10 tons at a time. 1USD = 110JPN

o

o-+NaH3C

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Corrosion of metal 1

The corrosiveness of test material on metal was evaluated by the procedures below: 2

3

Preparation of test solutions: 3.0 g of test material is dissolved in 100 cc of distilled water. 4

The test materials are NaCl, calcium chloride (hereinafter: “CaCl2”), SP, and NaCl/SP mixtures. 5

6

Preparation of test specimen: A steel sheet used as the cathode panel for the Hull Cell Test 7

(36) is cut into strips (67 mm x 50 mm x 0.3 mm). Zinc film is stripped off and the weight of 8

each specimen is measured. 9

10

Immersion and aeration of test specimen: Test specimens are immersed in the solutions 11

for 24 hours, and then the specimens are taken out from the solutions and aerated for 24 hours. 12

This immersion-aeration cycle is repeated for 7 days. That means the specimen is immersed in 13

the solution 4 times and aerated 3 times. The immersion-aeration cycle for distilled water is 14

also conducted as the control. 15

16

Calculation of corrosive effect for each solution: After the immersion-aeration cycle 17

described above, the test specimen was immersed in a cleaning solution of hydrochloric acid 18

(HCl) at 5.0 wt% containing propargyl alcohol (1.0 wt% to the HCl). Propargyl alcohol was 19

added to the HCl to stop further oxidization once the resulting rust was removed. Then, the test 20

specimen was removed from the cleaning solution and rinsed with ethanol. The corrosion rate 21

(Cr) is determined by the following equation. 22

23

𝐶𝑟 = (𝑊𝑖 − 𝑊𝑓)

𝐴 × 𝐷 (1) 24

25

where 26

Wi = initial weight of the test specimen (mg), 27

Wf = final weight of the test specimen (mg), 28

A = surface area of the test specimen (dm2), and 29

D = duration of immersion-aeration cycle (day) 30

31

32

Ice melting performance 33

The test method in this study was modeled after the “Ice Melting Test (SHRP H-205.1 and 34

H-205.2)” (37). The test was conducted in a temperature-controlled chamber. TABLE 3 shows 35

the test conditions. 36

First, 200 ml of water is frozen in a stainless steel tray of 185 mm in width, 140 mm in 37

depth and 27 mm in height. After the initial weight of the test specimen was measured, 5 g of 38

test material (grain size: 0.3 - 1.0 mm) was evenly applied over the specimen. 5, 10, 20, 30, 60, 39

120, 180 and 360 minutes after application, the liquid and undissolved test material were 40

completely removed, and then, the weight of the test specimen was measured. The weight of 41

ice melted can be determined by measuring the change in the weight of test specimen. The test 42

was conducted at -2°C, -5°C, -8°C, and -15°C, with triplicate samples tested for each 43

combination of test material, time and temperature. 44

45

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TABLE 3 Conditions of the ice-melting test 1

2 3

4

Toxic constituents 5

Since large amounts of deicers are used, deicer must not contain toxic substances. In Japan, 6

deicer must conform to the standard for toxic substances of deicer (TABLE 4). This standard 7

was defined by referring to the industrial effluent standards in Japan, based on the idea that 8

substantial amounts of deicer can be finally discharged from the road by surface runoff, 9

infiltration, and outflow from the drainage system. 10

As shown in TABLE 4, 16 items and their standard values (i.e., maximum allowances) 11

are defined. Since deicer may accumulate in drainage basins, the content of each item in a 12

saturated solution is evaluated. Although SP is used as a food additive and its properties are 13

shown in Material Safety Data Sheets (MSDS), the toxic constituent test was conducted to 14

determine whether SP conforms to the standards. 15

16

TABLE 4 Standard for toxic constituents of deicer 17

18 19

20

21

NaCl

SP

NaCl/SP mixture (weght ratio 8:2)

Test temperature (°C) -2, -5, -8, -15

Measurement time (min) 5, 10, 20, 30, 60, 120, 180, 360

Test material

(A)* (B)**

mg/L ≤ 0.03 ≤ 0.01

mg/L ≤ 1 Not detectable***

mg/L ≤ 1 Not detectable***

mg/L ≤ 0.1 N/A

mg/L ≤ 0.5 ≤ 0.05

mg/L ≤ 0.1 ≤ 0.05

mg/L ≤ 0.005 ≤ 0.0005

mg/L Not detectable*** N/A

mg/L ≤ 0.003 N/A

mg/L ≤ 0.06 N/A

mg/L ≤ 0.03 N/A

mg/L ≤ 0.2 N/A

mg/L ≤ 0.1 N/A

mg/L ≤ 10 N/A

mg/L ≤ 8 N/A

mg/L ≤ 100 N/A

Note:

* ***** "Not detectable " means that the amount of the substance is less than the limit of detection.

UnitStandard values

Item

Cadmium

Total cyanide

Organic phosphorus

Lead

Hexavalent chromium

(B): Stringent standard applied to vulnerable area designated by ordinance

Ammonia, Ammonia compound,

Nitrous acid compound and Nitric

acid compound

(A): National uniform standard

Thiobencarb

Selenium

Boron

Fluorine

Arsenic

Total mercury

Alkyl mercury

PCB

Thiram

Simazine

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Takahashi et al.

Damage to plants 1

The test method in this study is modeled after a test method determined by the Ministry of 2

Agriculture, Forestry and Fisheries of Japan (38). FIGURE 1 summarizes the basic steps of the 3

test and the test conditions. 4

- 500 ml of sieved air-dried soil is filled in a Neubauer pot (113 mm inside diameter x 65 5

mm height) and a defined quantity of water is added. 6

- 0, 1, 2, 4, and 8 g of test material is applied over the soil, with duplicate samples for each 7

dosage. 0 g is the control. 8

- 20 seeds of the test plant are placed in a pot to allow them to germinate. 9

- The test plants are cultivated in a temperature-controlled chamber for 21 days. 10

11

12 FIGURE 1 Basic steps of the test and the test conditions 13

14

15

Description of field test 16

A field test was conducted to evaluate the deicing performance of the test materials. The test 17

was conducted at a test track of our institute. The test track is 2,700 meters in circumference, 18

and the straightway of the test track paved with dense-graded asphalt was used. 19

The test track layout, the application method, and the basic steps of the test are 20

summarized in FIGURE 2. Section 1 was set to serve as the control section (i.e., no treatment 21

was performed) to compare the differences in friction values to the treated sections (sections 22

No. 2 - No. 5). In between the treated sections, dry-surface sections were set to prevent the 23

vehicles from dragging the test material to the next test section. 24

Since the granularity of salt is known to affect its deicing performance (39), molded 25

granules of SP were prepared such as to have the same granularity of NaCl used as deicer. 26

27

The basic steps of the field test are listed below. 28

- Icy surfaces were artificially created by applying water to the dry surface with a road 29

sprinkler when the surface temperature was below 0 °C. 30

- Test materials were spread on the icy surfaces (test sections No. 2 - No. 5). 31

- Friction values were measured immediately after test material spreading. 32

(a) Basic steps of the test

Growth of test plant

MeasurementCultivation

Seeding

(b) Test conditions

NaCl

SP

NaCl/SP mixture (weght ratio 8:2)

Dosage (g) 0 (no application), 1.0, 2.0, 4.0, 8.0

Test plant Brassica rapa var. perviridis

Germination rate (%)

Length of test plant (mm)

Weight of test plant (g)

Growth condition (leaf scorch etc.)

Potential of hydrogen (pH)

Chloride ion (Clˉ) concentration (mg/mg)

Test material

Measurement item

for test plant

Measurement item

for soil

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- Vehicles ran on these surfaces to duplicate traffic flow. 1

- Friction values were measured after 50, 100, 150, 200, 250 and 300 vehicle passes. 2

3

Friction values were measured using a RT3 (Halliday Technologies Inc., RT3 GRIP) (40). 4

A friction value determined by the RT3 is referred to as a Halliday friction number (HFN), and 5

HFN values can be converted to coefficient of friction (μ) (41). 6

7

8 FIGURE 2 Test track layout, the application method and the basic steps of the field test 9

10

11

TEST RESULTS 12

Results of laboratory tests 13

Freezing point 14

TABLE 5 shows the freezing points of the test materials. The freezing point of SP is 2.8°C 15

higher than that of NaCl. Mixing NaCl and SP gives the mixture a freezing point intermediate 16

between those of NaC and SP. The freezing point of a NaCl/SP mixture (weight ratio 8:2) is -17

18.9°C. This means the mixture is expected to have a low-temperature performance 18

comparable to that of NaCl. 19

20

TABLE 5 Freezing points of the test materials. 21

22 23

24

SpreadingWatering Vehicle running Measurement

Dry surface

100m 50m 50m 50m 50m 50m 50m 50m

Icy surface

1 2 3 4 5

(a) Basic steps of the test

(b) Application method and application rate for each test section

(c) Basic steps of the test

Section No.Type of spreading

operationApplication rate

1 - No treatment (control section)

2 Dry NaCl (solid) 20g/m2

3 Dry NaCl (solid) 16g/m2 + SP (molded granule) 4g/m2

4 Pre-wetted NaCl (solid) 18g/m2 + 30wt% SP solution 2g/m2

5 Pre-wetted NaCl (solid) 18g/m2 + 30wt% CaCl2 solution 2g/m2

Specimen (20 wt% aqueous solution) Freezing point ( ˚C)

NaCl -19.8

SP -17.0

NaCl/SP mixture (weight ratio 8:2) -18.9

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Metal corrosion 1

FIGURE 3 shows the metal corrosion test results for distilled water and the test materials. SP 2

aqueous solution is found to cause almost no corrosion. And the aqueous solution of NaCl/SP 3

mixture (weight ratio 8:2) is found to be 49% less corrosive to metal than distilled water and 4

80% less corrosive than NaCl. Even the aqueous solution of NaCl/SP mixture (weight ratio 5

9:1) is able to reduce metal corrosion by 45% relative to the NaCl aqueous solution. SP 6

demonstrates significant corrosion-inhibiting performance. 7

8

9 FIGURE 3 Metal corrosion rates of distilled water and the test materials 10

11

12

Ice melting performance 13

Figure 4 shows the amount of ice melted (g) over time at each test temperature. 14

15

16 FIGURE 4 Results of ice melting test for NaCl, SP and NaCl/SP mixture 17

Co

rro

sio

nra

te(C

r)

NaCl/SPmixture(19:1)

Distilled water

NaCl CaCl2 SPNaCl/SP mixture

(8:2)

NaCl/SPmixture

(9:1)

25

20

15

10

0

30

5

8.6

22.5

27.5

0.3

4.4

12.5

14.6

(a) Test temp.: -2 ºC (b) Test temp.: -5 ºC

(c) Test temp.: -8 ºC (d) Test temp.: -15 ºC

0

20

40

60

80

100

0 60 120 180 240 300 360

Ice m

elted (

g)

Time (minutes)

0

20

40

60

80

100

0 60 120 180 240 300 360

Ice m

elted (

g)

Time (minutes)

0

20

40

60

80

100

0 60 120 180 240 300 360

Ice m

elted (

g)

Time (minutes)

0

20

40

60

80

100

0 60 120 180 240 300 360

Ice m

elted (

g)

Time (minutes)

0

100

0 360

Ice

me

lte

d (

g)

Time (minutes)

NaCl

SP

NaCl+SP

NaCl

SP

NaCl/SP mixture

0

100

0 360

Ice

me

lte

d (

g)

Time (minutes)

NaCl

SP

NaCl+SP

NaCl

SP

NaCl/SP mixture

0

100

0 360

Ice

me

lte

d (

g)

Time (minutes)

NaCl

SP

NaCl+SP

NaCl

SP

NaCl/SP mixture

0

100

0 360

Ice

me

lte

d (

g)

Time (minutes)

NaCl

SP

NaCl+SP

NaCl

SP

NaCl/SP mixture

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Takahashi et al.

At the test temperatures of -2°C and -5°C, SP melts more ice in the first 45 minutes than NaCl 1

and the NaCl/SP mixture (weight ratio 8:2) do. After 60 minutes, NaCl exhibits the highest ice 2

melting performance. Although SP is able to melt less ice than NaCl, the NaCl/SP mixture 3

(weight ratio 8:2) demonstrates almost the same ice melting performance as NaCl. 4

At the test temperature of -8°C or below, there are no large differences in the amount of 5

ice melted. 6

7

8

Toxic constituents 9

TABLE 6 shows the results of the toxic constituents test for sodium propionate. It is 10

confirmed that SP conforms to the standard for toxic substances of deicer in Japan. Since 11

organic compounds in general have been found to elevate biological oxygen demand (BOD) in 12

adjacent waterways (42), further study on the toxicity of the effluents is required. 13

14

TABLE 6 Results of toxic constituents test for sodium propionate 15

16 17

18

Damage to plants 19

FIGURE 5 summarizes the test results. Although almost all of the seeds germinate when 2.0 g 20

of NaCl is applied, growth inhibition and leaf scorching of the test plant are observed. No seed 21

is able to germinate when 4.0 g or more of NaCl is applied. The test plants show better growth 22

when 1.0 g of SP is applied than when 1.0 g of NaCl is applied. However, no germination is 23

observed when 2.0 g or more of SP is applied. 24

When the NaCl/SP mixture is applied, the test plant exhibits good growth relative to that 25

when NaCl is applied: Even 10% of the seeds germinate when 4.0 g of the mixture is applied. 26

We cannot conclusively determine the impact of SP on plants due to diversity of vegetation 27

and soil conditions, but the NaCl/SP mixture is found to mitigate the inhibitory effects of NaCl 28

on the germination and growth of Brassica rapa var. perviridis. Considering the diversity of 29

the vegetation and soil conditions, further laboratory and field studies on the impacts on plants 30

are required. 31

32

(A)* (B)**

mg/L ≤ 0.03 ≤ 0.01 Not detected

mg/L ≤ 1 Not detectable*** Not detected

mg/L ≤ 1 Not detectable*** < 0.02

mg/L ≤ 0.1 N/A Not detected

mg/L ≤ 0.5 ≤ 0.05 < 0.05

mg/L ≤ 0.1 ≤ 0.05 Not detected

mg/L ≤ 0.005 ≤ 0.0005 Not detected

mg/L Not detectable*** N/A Not detected

mg/L ≤ 0.003 N/A Not detected

mg/L ≤ 0.06 N/A < 0.001

mg/L ≤ 0.03 N/A < 0.001

mg/L ≤ 0.2 N/A Not detected

mg/L ≤ 0.1 N/A Not detected

mg/L ≤ 10 N/A 0.22

mg/L ≤ 8 N/A 0.5

mg/L ≤ 100 N/A 0.18

Note:

* ***** "Not detectable " means that the amount of the substance is less than the limit of detection.

UnitStandard values

Item

Cadmium

Total cyanide

Organic phosphorus

Lead

Hexavalent chromium

(B): Stringent standard applied to vulnerable area designated by ordinance

Ammonia, Ammonia compound,

Nitrous acid compound and Nitric

acid compound

(A): National uniform standard

Results

Thiobencarb

Selenium

Boron

Fluorine

Arsenic

Total mercury

Alkyl mercury

PCB

Thiram

Simazine

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Takahashi et al.

1 FIGURE 5 Growth conditions of the test plants, and the measurement results 2

3

4

Field test results 5

FIGURE 6 shows the changes in the coefficient of friction (μ) as a function of the number of 6

vehicle passes. The μ value remains low on section No.1 (no treatment). On section No.2 (solid 7

NaCl applied), the μ value gradually increases with increases in the number of vehicle passes, 8

finally reaching around 0.7. On section No.3 (solid NaCl/SP mixture applied), although the μ 9

value rapidly increases, it gradually decreases with increases in the number of vehicle passes 10

after 150 vehicle passes. On section No.4 (solid NaCl pre-wetted with SP solution applied), the 11

μ value gradually increases even after 150 vehicle passes, finally approaching 0.7 at 300 vehicle 12

passes. On section No.5 (solid NaCl with pre-wetted CaCl2 solution applied), although the μ 13

value is the highest at 100 vehicle passes, it levels off after that. 14

Although the friction patterns may change when tested under different environmental 15

parameters, the field test suggests that application of the NaCl/SP mixture is as effective as 16

conventional application methods. Considering its high solubility in water, it is recommended 17

to use SP as a pre-wetting material. 18

19

(a) NaCl

0 g

1.0 g 2.0 g 4.0 g 8.0 g

(b) SP

0 g

1.0 g 2.0 g 4.0 g 8.0 g

(c) NaCl/SP

mixture0 g

1.0 g 2.0 g 4.0 g 8.0 g

Dosage (g)

0.0 1.0 2.0 4.0 8.0

Germinaton rate (%) 100 100 97.5 0 0

Lengt of test plant* (mm) 128.0 96.6 53.0 0 0

Weight of test plant* (g) 7.73 6.29 1.13 0 0

Potential of hydrogen (pH) 5.2 5.1 5.3 5.5 5.3

Clˉ concentration (mg/mg) 16 800 1900 4400 9200

NOTE: * Germinated test plants were measured and averaged

Dosage (g)

0.0 1.0 2.0 4.0 8.0

Germinaton rate (%) 100 100 0 0 0

Lengt of test plant* (mm) 128.0 122.0 0 0 0

Weight of test plant* (g) 7.73 7.87 0 0 0

Potential of hydrogen (pH) 5.2 6.4 7.7 8.6 9.3

Clˉ concentration (mg/mg) 16 17 34 39 26

NOTE: * Germinated test plants were measured and averaged

Dosage (g)

0.0 1.0 2.0 4.0 8.0

Germinaton rate (%) 100 100 100 10 0

Lengt of test plant* (mm) 128.0 105.0 84.8 8.5 0

Weight of test plant* (g) 7.73 5.42 4.52 0.26 0

Potential of hydrogen (pH) 5.2 5.3 5.5 6.1 6.5

Clˉ concentration (mg/mg) 16 860 1700 4200 6900

NOTE: * Germinated test plants were measured and averaged

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Takahashi et al.

1 FIGURE 6 Changes in μ as a function of the number of vehicle passes 2

3

4

CONCLUSIONS 5

In this study, a series of laboratory and field tests were conducted to investigate the performance 6

of SP as a deicer. SP was found to conform to the standard for toxic substances of deicer in 7

Japan, to achieve more rapid deicing than NaCl, and to cause almost no corrosion of metal. To 8

reduce costs while taking advantage of SP, the mixing of NaCl and SP, which exhibits 9

performances intermediate between those of NaCl and SP, is considered to be a solution. A 10

mixture of 80% NaCl and 20% SP shows freezing point and ice melting performance equivalent 11

to those of NaCl, mitigates the concentration of chloride ions and the inhibitory effects of NaCl 12

on plant germination and growth, and is still 80% less corrosive to metal than NaCl is. 13

Considering SP’s high solubility in water and the field test results, it is recommended that SP 14

be used as a pre-wetting material. This application method is as effective as conventional 15

application methods, and it can be applied using existing facilities and equipment. 16

In order to add SP as a choice of snow and ice control materials, quantitative field 17

observations regarding deicing performance, impact on environmental systems, and impact on 18

highway infrastructures and maintenance facilities are required. 19

20

21

22

No.1: No treatment

No.2: NaCl (solid) 20g/m2

No.3: NaCl (solid) 16g/m2 + SP (molded granule) 4g/m2

No.4: NaCl (solid) 18g/m2 + 30wt% SP solution 2g/m2

No.5: NaCl (solid) 18g/m2 + 30wt% CaCl2 solution 2g/m2

Air temp. (ºC) Surface temp. (ºC)

-16.0

-14.0

-12.0

-10.0

-8.0

-6.0

-4.0

-2.0

0.0

0.0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

1.0

0 50 100 150 200 250 300

Air &

su

rfa

ce

te

mp

era

ture

(▫C

)

Co

eff

ien

t o

f fr

ictio

n

Number of vehicle passes

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Takahashi et al.

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