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*Energies*
**2016**,
*9*(11),
954;
https://doi.org/10.3390/en9110954

Article

Study on Insulator Flashover Voltage Gradient Correction Considering Soluble Pollution Constituents

^{1}

State Key Laboratory of Power Transmission Equipment & System Security and New Technology, Chongqing University, Shapingba District, Chongqing 400044, China

^{2}

State Grid Chongqing Electric Power Co. Electric Power Research Institute, Yubei District, Chongqing 401121, China

^{*}

Author to whom correspondence should be addressed.

Academic Editor:
Issouf Fofana

Received: 11 September 2016 / Accepted: 8 November 2016 / Published: 15 November 2016

## Abstract

**:**

Natural polluted insulator surfaces are always coated with various kinds of soluble constituents, and those constituents affect flashover performance differentially. Currently, this fact is not considered either in laboratory experiments or field pollution degree measurements, causing the existing insulation selection method to be deficient. In this paper, a systematic study on insulator flashover voltage gradient correction involving different types of soluble pollution constituents is presented. Using a typical type glass insulator as the sample, its flashover tests, polluted by typical soluble chemicals (NaCl, NaNO

_{3}, KNO_{3}, NH_{4}NO_{3}, MgSO_{4}, Ca(NO_{3})_{2}and CaSO_{4}), were carried out. Then, the flashover gradient correction was made by combining the flashover performance of each soluble constituent, the equivalent salt deposit density (ESDD) contribution of the seven constituents, and the saturation performance of CaSO_{4}. The correction agreed with the flashover test results of insulator polluted by three types of soluble mixture. Research results indicate that the flashover gradient correction method proposed in this paper performs well in reducing the calculating error. It is recommended to carry out component measurements and flashover gradient correction to better select outdoor insulation configuration.Keywords:

insulator; pollution flashover; equivalent salt deposit density (ESDD); soluble constituent; flashover voltage gradient## 1. Introduction

External insulation equipment on transmission lines or in substations are frequently subjected to various kinds of contamination such as industry emissions, natural salt, dust, bird droppings, and other contaminants [1]. Due to pollution source features, geographical environment, and weather conditions, there is a great diversity of chemical constituents deposited on insulator surfaces during contamination [2].

Plenty of researches have been carried out so far to obtain the main constituents of insulator surface pollution. To sum up, insulator surface pollution is mainly made up of several conductive materials including NaCl, NaNO

_{3}, KCl, KNO_{3}, Mg(NO_{3})_{2}, MgSO_{4}, NH_{4}NO_{3}, NH_{4}Cl, (NH_{4})_{2}SO_{4}, Ca(NO_{3})_{2}, CaSO_{4}, and other contaminants, according to the research data in [3,4,5].All these constituents must affect an insulator’s electrical properties differentially [6,7], which will probably bring errors to the flashover voltage calculation. Currently, insulator flashover voltage is commonly calculated using an empirical negative exponent formula as follows [8,9,10]:

$${U}_{f}=A\times ESD{D}^{-n}$$

The main symbols of this paper were described in Table 1. In this formula, equivalent salt deposit density (ESDD) is derived from converting the pollution solution conductivity to the weight of NaCl, and A and n are obtained through laboratory tests using NaCl as the soluble pollution. So, the formula neglects the influence of other soluble constituents on flashover voltage, which causes deficiency.

In light of this, researches concerning different soluble constituents were carried out to further reveal insulator flashover voltage characteristics.

In literature [6], researchers studied the flashover performance of insulator polluted by different soluble materials, and proposed that, according to kinetic theory and permeation theory, a lower flashover voltage may be a function of the type of salt.

Researchers in [7] studied the dependence of flashover voltages on the chemical composition of the insulator surface contaminants, and put forward that the limiting flashover voltage of a contaminant containing several salt types may be computed from that of each salt type measured independently:

$${U}_{LFOV\sum}=({\displaystyle \sum {\rho}_{ESDDi}{U}_{LFOVi}})/{\rho}_{ESDD\sum}$$

In literature [11], researchers recommended that when calculating the critical flashover voltage and critical current, appropriate arc constants (A and n) should be selected for different chemical compositions of the pollutants.

Researchers in literature [12] showed the influence of pollution under 12 types of chemical constituents. It is proposed by the authors that in the case of simple salts and salts mixtures, the critical voltages are insensitive to the chemical nature of pollution. The critical currents are influenced by the chemical constitution of pollution for both polarities.

In literature [13], researchers studied the flashover performance of insulator string polluted by CaSO

_{4}and NaCl, and reduced the flashover voltage calculation error through considering the slight solubility of CaSO_{4}. It is concluded by the authors of the paper that the current ESDD method may fail to reflect specific effects of insulator contamination on its electrical property.The above studies contributed towards the knowledge of pollution flashover principles and provide a theoretical basis for contamination constituents’ effects on the insulation property. However, during laboratory artificial tests, pollution degree measurements, as well as field insulation design, NaCl is still used as the only representation of a conductive constituent. Moreover, few of the previous works proposed a procedure for flashover voltage gradient correction that considers various characteristics of soluble constituents.

This paper presented a systematical research on insulator flashover voltage gradient correction considering soluble pollution constituents. Firstly, flashover tests of typical type insulator string polluted by NaCl, NaNO

_{3}, KNO_{3}, NH_{4}NO_{3}, MgSO_{4}, Ca(NO_{3})_{2}, and CaSO_{4}were carried out, respectively. Then, with the flashover test data, the flashover gradient corrections basing on ESDD contribution of seven types of constituents and the saturation performance of CaSO_{4}were analyzed. The corrected flashover gradients agreed with insulator flashover test results under three types of soluble mixtures. This research is intended for contributing to the better design of outdoor insulation in field transmission lines.## 2. Sample, Experimental Setups, and Procedure

#### 2.1. Sample

The samples were typical type glass insulators. The technical parameters and profile of the sample are shown in Table 2.

#### 2.2. Experimental Setups

The tests were carried out in a multifunction artificial climate chamber. The artificial climate chamber, with a diameter of 7.8 m and a height of 11.6 m, can simulate steam fog conditions. The power was supplied by a 500 kV/2000 kVA pollution test transformer, of which the maximum short current is 75 A and the frequency is 50 Hz. The test circuit is shown in Figure 1, where B is the voltage regulator, T is the test transformer, R

_{0}is the protective resistance (10 kilo ohms), G is the wall bushing, D is the capacitive voltage divider (1000:1), E is the climate chamber, C is the leakage current measurement system, and S is the sample shown as an insulator string. The setups meet the requirements of pollution flashover test.#### 2.3. Test Procedure

#### 2.3.1. Preparation

Before the tests, all the samples were carefully cleaned by Na

_{2}PO_{3}solution so that all traces of dirt and grease were removed. The samples were left to dry naturally indoors to avoid dust or other pollution, and the relative humidity surround was less than 70% RH (Relative Humidity).#### 2.3.2. Polluting

The dipping method was applied to pollute the sample. The pollution solution was made strictly referring to standards [14,15]. Firstly, the soluble constituent was added until the volume conductivity reached a predetermined value, and then kaolin was added to make the solution into clay suspension. The samples were carefully dipped into and then taken out of the pollution mixture to get a uniform pollution layer coated on the surface.

After each dipping procedure, three pieces of the sample were randomly selected and the average value of their ESDD and non-soluble deposit density (NSDD) was measured, as was the ESDD and NSDD of the soaked samples. Based on IEC standard, 300 mL deionized water was used to wipe off the contaminants when measuring the ESDD.

NaCl and the other six soluble constituents (KNO

_{3}, NH_{4}NO_{3}, NaNO_{3}, Ca(NO_{3})_{2}, CaSO_{4}, and MgSO_{4}) were used in this study to make the pollution solution.#### 2.3.3. Flashover Test

The polluted insulators were firstly precharged by a predicted voltage level and then wetted by steam fog. The fog was generated by a 1.5 t/h boiler, for which the rate was 0.05 ± 0.01 kg/h·m

^{3}. During the flashover test, the temperature in the chamber was maintained between 30 °C and 35 °C through control of the refrigeration system, and the atmospheric pressure was 98.6 kPa in all the experiments.In the tests, up-and-down method was adopted to get a 50% withstand voltage U

_{50}. Each contaminated sample was subjected to at least 10 “valid” individual tests. The applied voltage level in each test was varied through up-and-down voltage. The voltage step was approximately 5% of the expected U_{50}. The first “valid” individual test was selected as being the first one that yields a result different from the preceding ones. Only the individual test and at least 9 following individual tests were taken as useful tests to determine U_{50}.It is very important to obtain the predicted flashover voltage level for the first up-and-down evaluation. Firstly, a small voltage on the suspended samples was applied, and then the steam fog was opened; the wetting condition of the surface was judged by observing the surface water film situation as well as the variation of recorded leakage current waveform. When the surface water films were formed and connected with each other, or the leakage current reached a high value and then started decreasing, the insulator pollution surface was treated as wholly wetted. Then, the voltage was lifted until flashover. The final voltage value was taken as the predicted flashover voltage.

When testing, the polluted insulators were firstly precharged by a predicted flashover voltage level, and then the steam fog was opened. If flashover occurred, the voltage applied in the next test was set 5% lower; however, if the current recorded peaks had decreased to values permanently lower than 70% of the maximum peak [14], the withstand of the insulator was considered definitive and the test was stopped—in this case, the applied voltage was set 5% higher in the next test. The U
where U

_{50}and relative standard deviation error (σ) are calculated as follows:
$${U}_{50}=\frac{\sum ({U}_{i}{n}_{i})}{N}$$

$$\sigma =\sqrt{({\displaystyle \sum _{i=1}^{N}{({U}_{i}-{U}_{50})}^{2}})/(N-1)}/{U}_{50}\times 100\%$$

_{i}is an applied voltage level, n_{i}is the number of tests carried out at the same applied voltage U_{i}, N is the total number of “valid” tests, and σ is the relative standard deviation.## 3. Test Results and Analysis

The insulator flashover voltage gradient can be expressed by:

$${E}_{L}={U}_{50}/L$$

Test results are shown in Table 4, where it can be seen that:

- (1)
- The relative errors were lower than 7%, so the dispersion degree of the data acquired by the test procedure is very small. Besides, NSDD was controlled narrowly within 0.08–0.12 mg/cm
^{2}through the dipping method, which means that the effects of NSDD on flashover voltage can be neglected. - (2)
- Insulator flashover performance is quite different under different soluble constituents. For example, when the constituent is NaNO
_{3}and ESDD is 0.031 mg/cm^{2}, insulator E_{L}is 55.5 kV/m; however, when the soluble constituent is MgSO_{4}and ESDD increases to 0.049 mg/cm^{2}, the E_{L}increases to 57.3 kV/m. A higher ESDD value does not always mean a lower flashover voltage when the soluble constituent is different. - (3)

The curves fall into the 3% error bars of the data points, meaning the fit is good. It can be seen from the figure that different soluble constituent corresponds to different E

_{L}–ESDD variation trends. Given the same ESDD, the flashover gradient of slightly soluble salt CaSO_{4}is always the highest, and it decreases the most slowly with the increase of ESDD. The flashover gradient of NaCl is always the lowest, and it decreases the fastest with the increase of ESDD.For the seven kinds soluble constituents, the A value of the insulator sample varies within 15.5–36.2, n varies within 0.19–0.34. It indicates that different soluble constituent corresponds to very different E

_{L}-ESDD relationship, and A is also associated with pollution chemical type. In summary, consideration of chemical compositions is necessary when calculating insulator pollution flashover voltage.Flashover tests of the insulator sample polluted by soluble constituents’ mixture were also carried out. The components and their weight percentage of the pollution mixtures were determined basically according to the data in [16,17,18]. In this study, three types of pollution mixtures were simulated, which represented a highway area, chemical plan area, and seaside, respectively. Test results are shown in Table 6.

It can be seen from Table 6 that under different types of pollution mixtures, the flashover performance varies. For example, when ESDD was about 0.081 mg/cm

^{2}, the E_{L}under Type I pollution was 50.6 kV/cm, while that under Type II was 47.8 kV, a decrease of 6%.Using the traditional method, which is only based on insulator flashover performance under NaCl (shown in Equation (1)), the flashover voltage gradient under pollution mixture was calculated. Calculation results and relative errors are shown in Table 7.

The relative errors are very high, meaning that the traditional flashover voltage calculation method leads to serious deviation in guiding external insulation design of field operating lines which are inevitably polluted by various kinds of constituents. A correction procedure should be proposed to consider the factors of soluble constituents and to optimize the flashover voltage calculation results.

## 4. Correction of Flashover Gradient Considering Soluble Pollution

#### 4.1. Correction Based on Equivalent Salt Density Contribution Ratio

According to Equation (2) which was provided by literature [7], flashover voltage gradient under a salt mixture can be expressed by:
where E

$${E}_{LM}=\frac{{\displaystyle \sum _{i=1}^{m}SD{D}_{i}\times {E}_{Li}}}{{\displaystyle \sum _{i=1}^{m}SD{D}_{i}}}=({\displaystyle \sum _{i=1}^{m}SD{D}_{i}\times {E}_{Li}})/ESD{D}_{M}$$

_{LM}is the flashover voltage gradient under a pollution mixture composed of m kinds soluble constituents, kV/m; ESDD_{M}stands for the measured equivalent salt deposit density (ESDD) of the mixture pollution solution; SDD_{i}stands for equivalent salt deposit density contributed by soluble constituent i, mg/cm^{2}; and E_{Li}is the flashover voltage gradient corresponding to single soluble constituent i under ESDD_{M}.E

_{Li}can be obtained based on the fitting results in Table 5:
$${E}_{Li}={A}_{i}\times {{ESDD}_{M}}^{-{n}_{i}}$$

So, if ESDD

_{M}and SDD_{i}are determined, Equation (6) can be solved. For a certain pollution mixture, its ESDD_{M}is directly the measured equivalent salt deposit density of the mixture solution. However, SDD_{i}of each soluble constituent in the given pollution mixture is uncertain, because the existing chemical test techniques can only determine the ion component and weight of each chemical constituent in the soluble mixture [16,17,18].Suppose β

_{i}is the weight percentage of soluble constituent i in the pollution mixture, α_{i}is the contribution ratio of a certain weight of constituent i to equivalent salt deposit density, and W_{M}is the total weight of the soluble mixture:
$$SD{D}_{i}={\alpha}_{i}\times {\beta}_{i}\times {W}_{M}$$

With Equation (8), Equation (6) can be simplified and rewritten as:
where η

$$\begin{array}{l}{E}_{LM}=\frac{{\displaystyle \sum _{i=1}^{m}({\alpha}_{i}{\beta}_{i}\times {A}_{i}\times {{ESDD}_{M}}^{-{n}_{i}})}}{{\displaystyle \sum _{i=1}^{m}{\alpha}_{i}{\beta}_{i}}}={\displaystyle \sum _{i=1}^{m}({\eta}_{i}\times}{A}_{i}\times {{ESDD}_{M}}^{-{n}_{i}})\\ {\eta}_{i}=\frac{SD{D}_{i}}{ESD{D}_{M}}=\frac{{\alpha}_{i}{\beta}_{i}}{{\displaystyle \sum _{i=1}^{m}{\alpha}_{i}{\beta}_{i}}}\end{array}$$

_{i}stands for the ESDD percentage of soluble constituent i. It can be seen from Equation (9) that if α_{i}and β_{i}corresponding to each soluble constituent are determined, the flashover voltage gradient can be solved.Equivalent salt density is basically derived from the conductivity of a certain solution, thus, soluble constituent conductivity tests were carried out. During the tests, the volume conductivity of each electrolyte solution under different concentrations was measured, and then the results were converted to the standard temperature (20 °C), as shown in Figure 4:

It can be seen that the volume conductivity presents an almost linear relationship with the increment of electrolyte concentration. It is known that ESDD is calculated based on the NaCl conductivity-weight relationship:

$$ESDD=\frac{{S}_{a}V}{A}$$

S

_{a}can be calculated by volume conductivity, expressed as:
$${S}_{\mathrm{a}}={\left(5.7{\sigma}_{20}\right)}^{1.03}$$

It can be seen that ESDD is almost linear with the volume conductivity. So, the contribution ratio of soluble constituents to ESDD can be obtained through comparing the conductivity curves’ slopes to the NaCl conductivity curve slope, as shown in Table 8.

With Table 8 and the weight percentage of each constituent given in 6, Equation (9) can be solved, as is shown in Table 9.

It can be seen from the table that when considering the equivalent salt density of each soluble constituent, the relative errors between calculated and tested values decreased a lot. Two of the errors were already within 7%, which is acceptable for the prospective of practical engineering.

However, when it comes to a Type III pollution mixture, the relative error is still not acceptable. For Type III pollution, the amount of CaSO

_{4}makes up to 60%, and the ESDD reaches 0.251 mg/cm^{2}. In this circumstance, a large amount of CaSO_{4}cannot be dissolved during the insulator wetting process, which means the ESDD contribution ratio of CaSO_{4}needs to be reconsidered, given its easy saturation feature.#### 4.2. Correction Based on Calcium Sulfate’s Slight Solubility

The contribution of CaSO

_{4}to ESDD is different from other soluble constituents, of which the solubilities are much higher, and the volume conductivities are linear with concentration. CaSO_{4}is slightly soluble, with a solubility of about 2 g/L at 20 °C. The CaSO_{4}on the surface of an insulator cannot dissolve sufficiently during the actual insulator wetting process in a steam chamber.Under normal circumstances, one standard suspension insulator unit can only be coated by approximately 20 mL water [13], and this volume is much smaller than the 300 mL water used when measuring the ESDD. This fact will not affect the contribution of good diffluent constituents, but does bring obvious error when hard-to-dissolve salt CaSO

_{4}makes up a large part of the pollution mixture, because in this case a greater portion of the CaSO_{4}does not act as conductive electrolyte if the insulator surface is wetted by just 20 mL water.Considering this, the conductivity performance of high concentration CaSO

_{4}solution was measured, and then a comparison was made between the ESDD contribution of CaSO_{4}in 20 mL solution and in 300 mL solution, as shown in Figure 5.It can be seen from Figure 4 that the ESDD contribution of CaSO

_{4}is overrated, considering the limited volume of insulator surface water absorbed. The saturated ESDD contribution (ESDD_{S}, as shown Figure 5) of CaSO_{4}is only equal to 0.038 mg/cm^{2}if the water volume is 20 mL, which is much lower than the ESDD contribution for a volume of 300 mL.The ESDD contribution of CaSO

_{4}under 300 mL solution (ESDD_{i}^{300}) can be calculated using the measured ESDD_{M}, based on Equation (9):
$$\begin{array}{cc}{{ESDD}_{i}}^{300}={\eta}_{i}\times ESD{D}_{M}& i=CaS{O}_{4}\end{array}$$

Then, according to Figure 5, the corrected CaSO
where ESDD

_{4}ESDD contribution, considering slight solubility and limited wetting amount, can be expressed as follows:
$$\begin{array}{l}{ESDD}_{i}^{20}=\{\begin{array}{c}ESD{D}_{i}^{300},ESD{D}_{i}^{300}<ESD{D}_{S}\\ ESD{D}_{s},ESD{D}_{i}>ESD{D}_{S}\end{array}\\ i=CaS{O}_{4},ESD{D}_{S}=0.038mg/c{m}^{2}\end{array}$$

_{i}^{20}is the corrected value, assuming the largest surface-coated volume of water is 20 mL.The measured ESDD value of the pollution mixture should also be corrected to the 20 mL situation:

$$\begin{array}{l}ESD{D}_{M}^{*}=ESDD-ESD{D}_{i}^{300}+ESD{D}_{i}^{20}\\ i=CaS{O}_{4}\end{array}$$

Then, the ESDD percentage of each constituent should be modified:

$${\eta}_{i}^{*}=\{\begin{array}{c}\begin{array}{cc}\frac{{\eta}_{i}\times ESD{D}_{M}}{ESD{D}_{M}^{*}}& i\ne CaS{O}_{4}\end{array}\\ \begin{array}{cc}ESD{D}_{i}^{20}/ESD{D}_{M}^{*}& i=CaS{O}_{4}\end{array}\end{array}$$

Considering the slight solubility of CaSO

_{4}, and using Equations (14) and (15) to correct the measured equivalent salt deposit density (ESDD_{M}) and ESDD percentage (η_{i}) of each constituent, the results are as shown in Table 10.It can be seen from the table that for the Type III pollution mixture, its actual equivalent salt deposit density and constituent ESDD percentage are changed obviously after correction. This is because the weight of CaSO

_{4}in the Type III pollution mixture is much greater than those in the other two types.As the table shows, for the Type III pollution mixture, its actual equivalent salt deposit density should be 0.164 mg/cm

^{2}, decreased by 34.6% compared to the measured value using 300 mL water; the ESDD percentage of CaSO_{4}should be 0.232, decreased by 54% compared to the measured value using 300 mL; and for other soluble constituents, their ESDD percentage increased a bit. This indicates that the traditional method of measuring ESDD will overrate the influence of slightly soluble constituents on flashover voltage.Using the corrected data of Table 10 to correct the E

_{LM}value:
$${E}_{LM}^{*}={\displaystyle \sum _{i=1}^{m}({\eta}_{i}^{*}\times}{A}_{i}\times {{ESDD}_{M}^{*}}^{-{n}_{i}})$$

The corrected flashover voltage gradient values and corresponding relative errors are as shown in Table 11.

It can be seen obviously that the relative error for the Type III pollution mixture decreases from −20.4% to −4.4%, which means the correction, when considering the slight solubility of CaSO

_{4}, does lower the calculated error, making the flashover voltage gradient calculation more accurate and scientific.## 5. Discussion

The flashover tests in a laboratory climate chamber cannot actually reflect the real flashover of a natural polluted insulator, making the voltage calculating error inevitable. However, through the correction process proposed in this paper, the error can be significantly reduced. It is important to calculate the ESDD contribution ratio of each soluble constituent when predicting flashover voltage of natural polluted insulator, because different soluble constituents on an insulator surface correspond to different flashover performances. Also, consideration of CaSO

_{4}saturation performance is a necessary step due to CaSO_{4}always occupies the largest proportion of natural contaminants.Currently, the effects of pollution constituents have been brought to the attention of relative research institutes. They conducted plenty of measurements on field insulator surface chemical components, and the most commonly used method is IC (ion chromatograph) analysis [4,16,17,18]. This method provides accurate categorization of negative and positive ions, as well as their mass percentage in the pollution solution. Then, the soluble constituents and their weights in the pollution solution can be easily determined by pairing the ions. Based on this, the flashover gradient of an insulator under natural pollution conditions can be better determined through a systematical correction procedure shown in Figure 6.

This procedure remedies the deficiency of the traditional ESDD method by considering the soluble constituents of insulator surface contaminants, and it is easy to implement in engineering practice.

## 6. Conclusions

In this paper, a systematic study on insulator flashover gradient correction involving different soluble pollution constituents was presented, and the conclusions are as follows.

- (1)
- Insulator flashover performance is quite different with differently soluble constituents. A higher ESDD value does not always mean a lower flashover voltage when the soluble constituent is different.
- (2)
- For the seven kinds constituents with different solubilities presented in this paper, the A value of the insulator sample varies within 15.5–36.2 and n varies within 0.19–0.34. Different solubilities of constituents correspond to very different E
_{L}-ESDD relationships. - (3)
- The proposed flashover gradient correction method, which considers a soluble constituent’s ESDD contribution and CaSO
_{4}saturation characteristic, performs well for reducing the calculating error. It is recommended to carry out component measurements and flashover gradient correction to better select outdoor insulation configuration.

## Acknowledgments

This work was supported by the Funds for Innovative Research Groups of China (51321063), Chongqing University Postgraduates’ Innovation Project (2015, No. CYB15031) and State Grid Corporation Science Project (SGTYHT/14-JS-188).

## Author Contributions

The authors gratefully acknowledge the contributions as following: Xingliang Jiang and Zhijin Zhang conceived and designed the experiments; Dongdong Zhang, Zhongyi Yang and Jiayao Zhao performed the experiments; Dongdong Zhang and Zhongyi Yang analyzed the data; Yongfu Li contributed reagents; Dongdong Zhang wrote the paper.

## Conflicts of Interest

The authors declare no conflict of interest. The founding sponsors had no role in the design of the study; in the collection, analyses, or interpretation of data; in the writing of the manuscript, and in the decision to publish the results.

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**Figure 1.**Schematic diagram of the alternating current (AC) test circuit, B—the voltage regulator, T—the test transformer, R

_{0}—the protective resistance, G—the wall bushing, D—the capacitive voltage divider, E—the climate chamber, C—the leakage current measurement system, and S—the insulator string sample.

Symbol | Description | Unit |
---|---|---|

U_{f} | flashover voltage | kV |

ESDD | equivalent salt deposit density | mg/cm^{2} |

A | coefficient related to the shape of the insulator, insulator surface material, air pressure, power source type, etc. | N/A |

n | characteristic exponent characterizing the influence of ESDD on U_{f} | N/A |

i | a certain soluble chemical contained in insulator pollution | N/A |

U_{LFOVΣ} | limiting flashover voltage of mixture electrolyte solution | kV |

U_{LFOVi} | the limiting flashover voltage of single electrolyte solution of i | kV |

ρ_{ESDDΣ} | the ESDD of the mixture electrolyte solution | mg/cm^{2} |

ρ_{ESDDi} | the ESDD of single electrolyte solution of i | mg/cm^{2} |

U_{50} | 50% withstand voltage | kV |

E_{L} | flashover voltage gradient | kV/m |

L | insulator string’s creepage | m |

V | volume of the suspension used to collect insulator pollution | mL |

A | the area of insulator surface | cm^{2} |

S_{a} | salinity of the collected suspension | kg/m^{3} |

σ_{20} | volume conductivity at a temperature of 20 °C | S/m |

ESDD_{M} | the measured ESDD value of insulator surface pollution mixture | mg/cm^{2} |

η_{i} | ESDD contribution percentage of soluble constituent i in mixture | N/A |

Limiting flashover voltage: the lowest flashover voltage occurs during flashover tests. | ||

Critical flashover voltage: the theoretical value of the applied voltage when flashover. | ||

50% withstand voltage: a voltage value under which the withstand probability is 50%. |

**Table 2.**Profile parameters of the insulator sample, h is the configuration height, l is the leakage distance, and d is the diameter of insulators.

Material | Profile | Parameters (mm) | ||
---|---|---|---|---|

h | d | l | ||

Glass | 146 | 280 | 400 |

Sample | Pollution Type | Test Records | U/kV, (Flashover ○; Withstand ●) | ||||
---|---|---|---|---|---|---|---|

3-unit LXY_{4}-160 String | NaCl, ESDD: 0.045 mg/cm ^{2}NSDD: 0.107 mg/cm ^{2} | String 1 | Test No. | 1 | 2 | 3 | 4 |

Records | 54.1 ○ | 52.5 ○ | 50.6 ● | 54.0 ○ | |||

String 2 | Test No. | 1 | 2 | 3 | 4 | ||

Records | 51.2 ● | 53.7 ● | 56.4 ● | 60 ● | |||

String 3 | Test No. | 1 | 2 | 3 | 4 | ||

Records | 56.7 ○ | 52.7 ● | 56.4 ● | 60.3 ● | |||

String 4 | Test No. | 1 | 2 | 3 | 4 | ||

Records | 52 ● | 55.1 ○ | 53.4 ● |

(1) For this example, 54.1 kV is the predicted value, and only the 11 bold voltage values are the valid data; (2) Each sample string was only subjected to 3–4 evaluations to avoid pollution loss by a long duration of fog wetting; (3) The 60 kV and 60.3 kV data points are the odd data which may be caused by pollution loss during wetting; (4) It is impossible to control voltage step to ±5% accurately. In actual tests the voltage step was basically 4%–6%.

Soluble Constituent | Flashover Parameters | Test Results | ||
---|---|---|---|---|

NaCl | ESDD (mg/cm^{2}) | 0.027 | 0.045 | 0.078 |

NSDD (mg/cm^{2}) | 0.132 | 0.107 | 0.103 | |

E_{L} (kV/m) | 51.9 | 44.8 | 36.2 | |

σ (%) | 5.2 | 3.8 | 3.4 | |

KNO_{3} | ESDD (mg/cm^{2}) | 0.032 | 0.055 | 0.072 |

NSDD (mg/cm^{2}) | 0.074 | 0.078 | 0.087 | |

E_{L} (kV/m) | 51.8 | 45.4 | 43.5 | |

σ (%) | 5.4 | 5.2 | 3.3 | |

NH_{4}NO_{3} | ESDD (mg/cm^{2}) | 0.024 | 0.039 | 0.073 |

NSDD (mg/cm^{2}) | 0.123 | 0.119 | 0.124 | |

E_{L} (kV/m) | 57.5 | 51.6 | 46.2 | |

σ (%) | 4.3 | 4.6 | 4.9 | |

NaNO_{3} | ESDD (mg/cm^{2}) | 0.031 | 0.056 | 0.100 |

NSDD (mg/cm^{2}) | 0.105 | 0.092 | 0.084 | |

E_{L} (kV/m) | 55.5 | 48.5 | 43.3 | |

σ (%) | 4.7 | 3.6 | 4.4 | |

Ca(NO_{3})_{2} | ESDD (mg/cm^{2}) | 0.026 | 0.051 | 0.109 |

NSDD (mg/cm^{2}) | 0.090 | 0.086 | 0.100 | |

E_{L} (kV/m) | 61.7 | 51.4 | 44.7 | |

σ (%) | 4.7 | 3.3 | 3.2 | |

MgSO_{4} | ESDD (mg/cm^{2}) | 0.049 | 0.082 | 0.160 |

NSDD (mg/cm^{2}) | 0.142 | 0.133 | 0.151 | |

E_{L} (kV/m) | 57.3 | 48.5 | 44.3 | |

σ (%) | 4.7 | 4.8 | 3.2 | |

CaSO_{4} | ESDD (mg/cm^{2}) | 0.055 | 0.145 | 0.028 |

NSDD (mg/cm^{2}) | 0.092 | 0.088 | 0.079 | |

E_{L} (kV/m) | 65.3 | 56.9 | 72.8 | |

σ (%) | 5.1 | 5.6 | 5.3 |

Salt | E_{Li} = A_{i} × ESDD^{−ni} | ||||||
---|---|---|---|---|---|---|---|

NaCl | NH_{4}NO_{3} | KNO_{3} | Ca(NO_{3})_{2} | CaSO_{4} | MgSO_{4} | NaNO_{3} | |

A | 15.5 | 27.4 | 23.8 | 26.9 | 36.2 | 29.5 | 26.4 |

n | 0.34 | 0.19 | 0.22 | 0.22 | 0.18 | 0.21 | 0.21 |

**Table 6.**Test results of insulator strings polluted with three types of soluble constituents mixture.

Pollution Mixture Based on Weight Percentage | Parameters | Test Results |
---|---|---|

Type I: CaSO_{4} 57.5%, NaCl 13.1%, KNO_{3} 9%, NaNO_{3} 8.7%, NH_{4}NO_{3} 6.4%, MgSO_{4} 3.7% | ESDD (mg/cm^{2}) | 0.081 |

NSDD (mg/cm^{2}) | 0.117 | |

E_{L} (kV/m) | 50.6 | |

σ (%) | 5.1 | |

Type II: CaSO_{4} 54.3%, NaCl 10.3%, NaNO_{3} 2.2%, KNO_{3} 6.3%, Ca(NO_{3})_{2} 20.7%, MgSO_{4} 4.2% | ESDD (mg/cm^{2}) | 0.082 |

NSDD (mg/cm^{2}) | 0.128 | |

E_{L} (kV/m) | 47.8 | |

σ (%) | 4.7 | |

Type III: CaSO_{4} 59.4%, NaCl 13.6%, KNO_{3} 9.5%, Ca(NO_{3})_{2} 7.8%, MgSO_{4} 7.9% | ESDD (mg/cm^{2}) | 0.251 |

NSDD (mg/cm^{2}) | 0.112 | |

E_{L} (kV/m) | 32.8 | |

σ (%) | 4.6 |

**Table 7.**Test results of insulator strings polluted with three types of soluble constituents mixture, E

_{L}* means the calculated value of flashover gradient.

Mixture Type | ESDD (mg/cm^{2}) | Calculated Value E _{L}* (kV/m) | Relative Error Δ (%) |
---|---|---|---|

Type I | 0.081 | 33.8 | 33.2 |

Type II | 0.082 | 35.2 | 26.3 |

Type III | 0.251 | 22.5 | 31.4 |

Δ = (E_{L} − E_{L}*)/E_{L} × 100% |

Salt | NaCl | NH_{4}NO_{3} | KNO_{3} | Ca(NO_{3})_{2} | CaSO_{4} | MgSO_{4} | NaNO_{3} |
---|---|---|---|---|---|---|---|

α_{i} | 1.000 | 0.885 | 0.733 | 0.550 | 0.485 | 0.462 | 0.784 |

Mixture Type | ESDD (mg/cm^{2}) | Calculated E_{LM} Using Equation (9) (kV/m) | Relative Error Δ (%) |
---|---|---|---|

Type I | 0.081 | 49.9 | 1.5 |

Type II | 0.082 | 51.0 | −7.0 |

Type III | 0.251 | 39.5 | −20.4 |

Δ (%) = (E_{L} − E_{LM})/E_{L} × 100% |

**Table 10.**Correction of measured equivalent salt deposit density and ESDD percentage of each soluble constituent.

Pollution Type | Type I | Type II | Type III | |||
---|---|---|---|---|---|---|

ESDD_{M} correction | ESDD_{M} | ESDD_{M}* | ESDD_{M} | ESDD_{M}* | ESDD_{M} | ESDD_{M}* |

0.081 | 0.081 | 0.082 | 0.082 | 0.251 | 0.164 | |

η_{i} correction | η_{i} | η_{i}* | η_{i} | η_{i}* | η_{i} | η_{i}* |

CaSO_{4} | 0.451 | 0.451 | 0.468 | 0.468 | 0.503 | 0.232 |

NaCl | 0.212 | 0.212 | 0.183 | 0.183 | 0.237 | 0.363 |

KNO_{3} | 0.107 | 0.107 | 0.082 | 0.082 | 0.122 | 0.186 |

NaNO_{3} | 0.110 | 0.110 | 0.031 | 0.031 | 0.000 | 0.000 |

NH_{4}NO_{3} | 0.092 | 0.092 | 0.000 | 0.000 | 0.000 | 0.000 |

MgSO_{4} | 0.028 | 0.028 | 0.034 | 0.034 | 0.064 | 0.097 |

Ca(NO_{3})_{2} | 0.000 | 0.000 | 0.202 | 0.202 | 0.075 | 0.115 |

Pollution Mixture Type | ESDD (mg/cm^{2}) | Calculated E_{LM}* Use Equation (9) (kV/m) | Relative Error Δ (%) |
---|---|---|---|

Type I | 0.081 | 49.9 | 1.5 |

Type II | 0.082 | 51.0 | −7.0 |

Type III | 0.251 | 34.3 | −4.4 |

Δ = (E_{L} − E_{LM}*)/E_{L} × 100% |

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