1. Introduction
Arctic sea ice has been a sensitive indicator of climate change and has declined dramatically in recent decades [
1,
2,
3]. Melt pond can be considered as one of the most significant and important features of Arctic sea ice in the summer [
4,
5,
6,
7,
8]. The positive net surface energy balance of the sea ice results in the surface melting on Arctic sea ice, which starts from late spring, and some of the meltwater is retained on the ice surface. The continuous absorption of solar radiation leads to severe localized melting and meltwater area expanding both horizontally and vertically, which eventually forms melt ponds. Melt pond can dramatically reduce the ice albedo and promote more energy into the upper ocean [
9,
10,
11].
The evolution of a melt pond can be divided into four stages, based on the results of observations and pond behavior and control mechanisms [
12]. In the first stage, pond coverage rapidly increases and meltwater accumulates on the surface. During the second stage, horizontal transport dominates the process of water loss, and percolation through the ice is also one of the significant causes. High ice permeability and open flaws cause the meltwater to be freely lost to the ocean, with some melt ponds even directly melting through to the ocean during the third stage. The fourth stage is defined as a refreezing period, which is not restricted to the end of the ice season. In this stage, the freezing of the melt ponds can stop meltwater transportation. Numerical modeling is the most widely used and most effective research method to depict the features of sea ice conditions in the Polar Regions. The seasonal evolution of melt ponds is a predominant control of albedo and solar energy partitioning [
13], and can be used as an important variable in melt pond modeling [
14,
15,
16,
17,
18], as the accuracy of sea ice numerical models depends largely on the assimilation of the results of long-term in situ observation.
The observation of the evolution process of the melt pond mainly includes the melt pond coverage, melt pond depth, albedo, melt pond shape and size, and melt pond temperature. Field observation and remote sensing can usually be used to study the morphological changes and physical properties of melt ponds [
19,
20,
21]. In situ observations, aerial surveys and synthetic aperture radar were used together to evaluate the physical, radiative, and electrical properties of the melt ponds of first-year ice and multiyear ice [
22]. Under-ice diving observations from 8 June 2008 to 11 June 2008 provided results that melt pond size and shape distributions may affect the regional transmittance of sea ice [
9]. Aircraft videography can be used to reveal sea ice surface types, including melt ponds of different colors [
23]. Observations of pond coverage, albedo, and ice properties and terrestrial lidar measurements were made on landfast Arctic sea ice to quantitatively identify the mechanisms of pond coverage [
5]. A terrestrial laser scanner, snow and sea ice sampling, and surface meteorological characterization were used to study the evolution of melt pond coverage, surface topography, and mass balance on landfast sea ice, estimating the contribution of surface melting to the net radiative flux [
24]. Ice mass balance buoy (IMBs) and the Scottish Association of Marine Science (SAMS) sea ice mass balance for the Arctic (SIMBA) have been widely deployed in the Arctic Ocean to automatically observe the sea ice mass balance [
25,
26,
27,
28]. The ice mass balance buoy with radiometers (IMB-R) were deployed in a freshwater pond and a saline pond, respectively, revealing the salinity control of thermal evolution of melt ponds [
29]. For the first time, continuous observation by ice mass balance instruments provided the formation of a deep melt pond and subsequent false bottom evolution [
30]. A two-stream radiative transfer model was proposed and applied to ponded sea ice in the Arctic to examine the upwelling irradiance from the pond surface and provided a potential method to obtain ice thickness through melt pond color [
31]. The “LinearPolar” algorithm was proposed based on the polar coordinate transformation and the proposed algorithm had higher accuracy and precision [
32].
In these contexts, this paper focused on designing an ice-tethered observation system for melt pond evolution with vision and temperature profile measurements used in the Polar Regions.
Section 2 describes the system composition, design of ice-tethered buoy, freeze-resistant camera, and the thermistor chain.
Section 3 gives research results on the low-light image enhancement method in the Arctic. In
Section 4, the results of field experiments in the Yellow River enable us to evaluate the performance of the thermistor chain, and the effectiveness of the low-light image enhancement algorithm is compared and evaluated. The conclusions and future works are present in final section.
3. Low-Light Image Enhancement in Arctic
The images of sea ice or melt pond cannot achieve the quality of images under ideal lighting conditions, and some substances in the air can also cause light attenuation and scattering, resulting in low brightness, low contrast, and severe noise in the collected images. Therefore, a low-light image enhancement algorithm in Arctic is proposed.
The sparrow search algorithm (SSA) is an intelligent search algorithm, which can simulate sparrow foraging behavior and antipredation behavior [
33,
34]. In this algorithm, some of the sparrows with better fitness can be used as producers and the rest are followers. A certain proportion of individuals in the population are selected for detection and early warning.
The location update formulas of the producers, followers, and alerter of the sparrow search algorithm are as follows:
The location update formula of the discoverers in SSA is described as follows [
35]:
where
Xti,j represents the
jth dimension of the
ith sparrow of generation
t;
Tmax is the maximum number of iterations;
α is the uniform random number in the range of (0, 1];
Q is a random number that follows the standard normal distribution;
L is the
d-dimensional row vector, where every entry is 1.
The follower location update formula can be described as follows:
where
Xti,j is the best position occupied by the producer;
Xtworst is the worst position;
A is a 1 × D matrix; and each element is randomly assigned 1 or −1; and
A+ =
AT(
AAT)
−1.
The position update formula for the investigator is described as follows:
where
Xtbest is the best global optimal location;
β is a step size control parameter and satisfies the normal distribution random number, with the mean value of 0 and variance of 1.
K is a random step size control parameter in the interval [−1, 1];
σ is a minimum constant to prevent the numerator being zero;
fi is the fitness value of the
ith sparrow;
fg is the optimal fitness value of the current sparrow population; and
fw is the worst fitness value of the current sparrow species.
Considering the characteristics of the Arctic, bilateral gamma correction is used to enhance the low brightness areas while suppressing the local bright areas of low light images. Bilateral gamma adjustment can be expressed as follows [
36]:
The result of Equation (16) can be calculated by two gamma functions
G1(
x) and
G2(
x).
α and
β are two variables, the values of which can be found in [0, 1]. Assuming that the gray value range of the image is normalized to the range of [0, 1]. The two gamma functions can be described as follows:
where
x is the gray value of image;
γ is an adjustable variable to adjust the degree of image enhancement;
G1(
x) is a convex function for enhancing dark areas;
G2(
x) is a concave function for suppressing bright areas of the image.
where
I(
x,
y) is the acquired image matrix; (
x,
y) represents the pixel cells of the image matrix;
I′(
x,
y) is the results after being carried out progress of normalization;
I″(
x,
y) is the output corrected by the bilateral gamma adjustment function.
The range of the gray value after the bilateral gamma adjustment function can be adjusted to [0, 255] as follows:
In this study, the optimization strategy was determined based on a trade-off between three aspects. Therefore, the objective function is the maximum sum of
Eimage,
Sedge, and
STV.
Figure 6 shows the schematic diagram of the proposed strategy for a low-light image enhancement in the Arctic.
The objective function is formulated as follows:
where
φ,
η, and
μ are the weighting factors and the sum of them should be equal to 1.
Eimage is the entropy value of the enhanced image;
Sedge is the edge content of the enhanced image;
STV is the gray standard variance of the enhanced image.
The entropy value of the image
Eimage indicates the information in the image and can be expressed as follows:
where
P(
i) is the probability of the
ith gray value in the enhanced image.
Sedge can be calculated using the ratio of the sum of non-zero pixels and the total number of pixels in the image.
5. Conclusions and Future Work
In this study, an ice-tethered observation system for melt pond evolution was designed and presented. This system includes meteorological instruments, as well as instruments for observation for the ice mass balance, the visual observation of the melt pond, and the thermodynamic observation of melt pond. A power supply module, a controller, and a data logger are installed inside the main buoy of the ice-tethered buoy. In order to improve the survival ability of the system, the main buoy and floating body are small and can be easily deployed in sea ice through ice drilling. The morphological changes of the melt pond and sea ice can be studied using the freeze-resistant camera in this observation system. For the seasonal observation of the melt pond in the Arctic, a serial port camera is installed in a designed sealed shell and electric heating wires are wrapped around the camera, increasing the temperature to around the camera to reduce the impact of low temperatures. A DC-powered pan-tilt platform is used to realize the automatic rotation for observation of changes in surface morphology of sea ice and melt pond within a certain range. The design of the thermistor chain is based on the master–slaves mode and the construction of the data transmission bus. The function of the temperature observation of thermistor chain is achieved through a bridge circuit and high-precision temperature measurement sensors realize temperature observation, which can reduce the error of temperature inversion. An interface recognition algorithm designed specifically for the thermistor chain relies on the vertical temperature profile after heating and can improve the efficiency of the inversion of the internal structure of melt ponds. A low-light image enhancement strategy is proposed and applied based on the sparrow search algorithm and bilateral gamma correction. Field experiments were completed and the thermistor chain can be proved high precision and high stability in the temperature profile in the second reservoir of Fen River, Yellow River. During the field experiment on ice, an artificial freshwater pond of 1 m × 0.7 m × 0.3 m was built using drilling and cutting methods. The observation results of new ice thickness, pond depth, and ice thickness under the freshwater pond were evaluated and analyzed. The results showed that the average growth rates of new ice thickness and ice thickness under the freshwater pond were 1.2 cm/d and 1.1 cm/d, respectively. The pond depth decreased from 24.2 cm to 15.8 cm from 21 January to 27 January. For the low-light images, the processing results of the proposed visual enhancement algorithm, single-scale retinex (SSR), multiscale retinex (MSR), multiscale retinex with a color recovery factor C (MSRCR), and contrast-limited adaptive histogram equalization (CLAHE) were assessed and verified. The mean square error (MSE), peak signal-to-noise ratio (PSNR) and feature similarity index (FSIM) between the original and enhanced images indicate that the proposed algorithm is suitable for low-light image enhancement in the Arctic based on comparative analysis of image quality, ability to suppress noise and feature similarity between the processed images and the original images.
More design optimization can be realized to overcome potential risks in Arctic observations. In future work, the application of renewable energy in polar regions is a key point, which can provide guarantees for the seasonal observation of melt pond. More observation plans for the different types of melt ponds should be considered and more sensors with different parameters, such as chlorophyll and dissolved oxygen can be assembled into the system to observe the impact of melt pond evolution on the marine environment.
Obtaining meaningful information by extracting specific features from images is still a challenge [
38]. Images obtained from ice-tethered observation system for melt pond evolution can provide a wealth of information, requiring feature extraction detection and recognition. Entropy plays a pivotal role in image processing. A method for establishing an automatic and efficient image retrieval system is designed and can improve the retrieval ability and accuracy of feature extraction [
39]. Image encryption is necessary to protect the digital image transmission and image data security should be considered [
40].