Abstract
Background
Hemorrhagic fever with renal syndrome (HFRS) is a zoonosis caused by hantavirus (belongs to Hantaviridae family). A large amount of HFRS cases occur in China, especially in the Heilongjiang Province, raising great concerns regarding public health. The distribution of these cases across space-time often exhibits highly heterogeneous characteristics. Hence, it is widely recognized that the improved mapping of heterogeneous HFRS distributions and the quantitative assessment of the space-time disease transition patterns can advance considerably the detection, prevention and control of epidemic outbreaks.
Methods
A synthesis of space-time mapping and probabilistic logic is proposed to study the distribution of monthly HFRS population-standardized incidences in Heilongjiang province during the period 2005–2013. We introduce a class-dependent Bayesian maximum entropy (cd-BME) mapping method dividing the original dataset into discrete incidence classes that overcome data heterogeneity and skewness effects and can produce space-time HFRS incidence estimates together with their estimation accuracy. A ten-fold cross validation analysis is conducted to evaluate the performance of the proposed cd-BME implementation compared to the standard class-independent BME implementation. Incidence maps generated by cd-BME are used to study the spatiotemporal HFRS spread patterns. Further, the spatiotemporal dependence of HFRS incidences are measured in terms of probability logic indicators that link class-dependent HFRS incidences at different space-time points. These indicators convey useful complementary information regarding intraclass and interclass relationships, such as the change in HFRS transition probabilities between different incidence classes with increasing geographical distance and time separation.
Results
Each HFRS class exhibited a distinct space-time variation structure in terms of its varying covariance parameters (shape, sill and correlation ranges). Given the heterogeneous features of the HFRS dataset, the cd-BME implementation demonstrated an improved ability to capture these features compared to the standard implementation (e.g., mean absolute error: 0.19 vs. 0.43 cases/105 capita) demonstrating a point outbreak character at high incidence levels and a non-point spread character at low levels. Intraclass HFRS variations were found to be considerably different than interclass HFRS variations. Certain incidence classes occurred frequently near one class but were rarely found adjacent to other classes. Different classes may share common boundaries or they may be surrounded completely by another class. The HFRS class 0–68.5% was the most dominant in the Heilongjiang province (covering more than 2/3 of the total area). The probabilities that certain incidence classes occur next to other classes were used to estimate the transitions between HFRS classes. Moreover, such probabilities described the dependency pattern of the space-time arrangement of HFRS patches occupied by the incidence classes. The HFRS transition probabilities also suggested the presence of both positive and negative relations among the main classes. The HFRS indicator plots offer complementary visualizations of the varying probabilities of transition between incidence classes, and so they describe the dependency pattern of the space-time arrangement of the HFRS patches occupied by the different classes.
Conclusions
The cd-BME method combined with probabilistic logic indicators offer an accurate and informative quantitative representation of the heterogeneous HFRS incidences in the space-time domain, and the results thus obtained can be interpreted readily. The same methodological combination could also be used in the spatiotemporal modeling and prediction of other epidemics under similar circumstances.
Author summary
Heilongjiang Province reported the largest number of HFRS cases in China. Previous studies focused on identifying the severe HFRS outbreak regions, exploring the relative impact of environmental factors, forecasting HFRS cases etc. However, the study of the spatiotemporal spread dynamics and patterns of HFRS is still lacking, which is the focus of the present study. This study proposed a novel mapping technique (i.e., class-dependent Bayesian Maximum Entropy, cd-BME) for studying the distribution of HFRS, overcoming the highly heterogeneous features of HFRS data; and, probabilistic logic notions (stochastic indicators) were employed to study the spatiotemporal dependency of HFRS incidence and draw conclusions regarding the HFRS spread under conditions of uncertainty. By dividing the original HFRS data into four classes in terms of percentiles, the cd-BME exhibited better performance in mapping HFRS distribution than the standard (class-independent) BME technique and the mainstream inverse distance technique. Regarding the maps of HFRS distribution, the point outbreak character dominated the HFRS spread at high incidence levels, whereas the lowest incidence level covered more than 2/3 of Heilongjiang Province. Certain HFRS incidence generally occurred between intraclass or neighbor classes. The probabilities of HFRS transition between incidence classes with various spatial distances and temporal instants can be found in the HFRS indicator plots. The above comprehensive information can allow a better understanding of the spatiotemporal HFRS spread mechanisms and further improve HFRS decision-making, management and control.
Introduction
The first cases of hemorrhagic fever with renal syndrome (HFRS) were reported in northeastern China in the early 1930s [1]. During the past seven decades, this rodent-borne zoonosis, caused by Hantavirus, has been spreading southwards to other parts of China. Currently, 31 provinces, autonomous regions, and metropolitan areas of mainland China, are exposed to significant health risks due to this infectious disease. In particular, the reported HFRS cases correspond to approximately 90% of all global number of cases [2, 3]. Specifically, the Hantaan virus (HTNV) and the Seoul virus (SEOV), hosted by Apodemus agrarius and Rattus norvegicus, respectively, are the two predominant sources of HFRS in China (see, e.g., [1, 4, 5]). The hantavirus is transmitted from rodents to humans through inhalation of aerosolized excreta (such as urine and saliva) or direct contact [6]. Infected human specimens suffer from fever, headache, abdominal pain, insufficient renal function, and hemorrhagic episodes [7, 8]. For the period 2004–2008, most HFRS cases reported in China concerned young and middle-age farmers [9] with case fatality rate (CFR) 1.17%, and females experiencing higher CFRs than males in the age groups of 20–39 and >50 years [10]. Also HFRS cases in males were more than three times higher than those reported in females. Evidently, HFRS poses a serious threat to public health in China.
Previous HFRS studies have focused on different aspects of the epidemic, such as the following cases:
Identification of regions with severe HFRS outbreaks. Zhang et al. [2], e.g., used spatial autocorrelation, local indicators of spatial association, and Kulldorff’s space-time scan statistic, to identify distinct cluster areas of outbreak episodes in northeastern, central and eastern China. Similarly, Wu et al. [11] applied cluster analysis, temporal cluster analysis, and space-time cluster analysis, to identify various epidemic clusters in Liaoning Province of China (including a primary cluster in the western part of the province and two secondary clusters in its eastern part).
Quantitative analysis of the impact of physiographic characteristics and environmental variables on HFRS population-standardized incidences. Yan et al. [12], e.g., employed a multivariate logistic regression model to study the relationship between HFRS incidence and various landscape and environmental elements. The study concluded that elevation, Normalized Difference Vegetation Index (NDVI), precipitation, annual cumulative air temperature, semihydromorhic soils, timber forests and orchards, were closely related to HFRS incidence. In a more recent study, Li et al. [13] applied a geographically weighted regression model to Chinese data during the period 2005–2009, and concluded that temperature, precipitation, humidity, NDVI, land use and elevation significantly impacted the spatiotemporal heterogeneity of HFRS incidences. Also, Tian et al. [14] and He et al. [15, 16] used wavelet analysis to study how the dynamics of HFRS are linked to rainfall, temperature, rodents’ density and the multivariate El Niño-Southern Oscillation (ENSO) index.
HFRS incidence forecasting. Liu et al. [17] and Li et al. [18] successfully applied autoregressive integrated moving average (ARIMA) and seasonal ARIMA models to produce forecasts of HFRS in China and Heilongjiang Province, respectively. Moreover, seasonal ARIMA models with exogenous variables (SARIMAX) were also developed for forecasting HFRS in four counties with severe HFRS outbreaks [19].
Clinical manifestation case studies. For example, Zhang et al. [20] compared various clinical indices involving 152 patients in Heilongjiang Province, and showed that SEOV infections are milder and less typical than those caused by HTNV.
While, as described above, a significant level of understanding has been reached regarding the specific characteristics of HFRS and its linkage to physiographic variables, its dynamics and associated spatiotemporal spread patterns remain mostly unexplored. The present work aims at bridging this gap, by using the spatiotemporal Bayesian Maximum Entropy theory (BME) to develop a fully probabilistic approach that allows a rigorous quantitative representation of HFRS population-standardized incidences in the space-time domain (BME belongs to the field of modern spatiotemporal geostatistics, [21, 22]). At this point we notice that BME has been successfully applied in the study of several infectious diseases, such as syphilis, hand food and mouth disease, influenza, dengue fever, and Black death [23–28]. Our study area is the Heilongjiang Province, which experiences the highest HFRS population-standardized incidences in China [2, 12, 18], caused by both HTNV and SEOV [20]. In the Heilongjiang case study, the main advantage of the proposed BME-based approach is that it can account for certain crucial aspects of space-time HFRS spread, as follows:
-
i)
Spatiotemporal evolution: The proposed approach not only accounts for the fact that, as is the case with all infectious diseases, the spatiotemporal HFRS evolution can be influenced by several environmental factors, but also for the fact that, as a natural phenomenon, the HFRS spread follows a propagation law with the number of human infections being closely related to human-rodents interactions. In this twofold phenomenological context, when a core area is formed during the disease outbreak, and as time advances, the disease spreads radially from the core center in all directions. The accurate characterization of the spatiotemporal HFRS spread pattern is of essence, and the thus acquired knowledge can be integrated with other information sources (about the disease and its environment) to improve public health management through prevention and control.
-
ii)
Incidence heterogeneity: A crucial observation to be accounted by the proposed approach is that the HFRS infection level varies in a heterogeneous manner across space-time, which means that the adequate distinction between incidence classes can play a significant role in the accurate mapping and risk assessment of regional disease spread during the time period of interest. Furthermore, since infectious disease outbreaks can occur in very short time periods and infect a large number of individuals, and given the highly variable character of disease attributes, it is difficult (both theoretically and practically) and often unrealistic to model simultaneously both the extreme values and the regular values of population-standardized incidences. In other words, a model that considers the distribution of all incidence levels as a single (super) class can neither adequately represent nor fully explain the spread pattern of a specific incidence class, because of smoothing effects and the existence of extreme (high/low) incidence levels in the same setting.
-
iii)
Class transmission and propagation: The probabilistic assessment of the HFRS transmission and propagation patterns among various incidence classes is currently lacking (e.g., the probability of HFRS transmitting from one incidence class to another class at various spatial distances and time separations apart). Yet such an assessment could provide valuable scientific support for HFRS monitoring and control purposes. Accordingly, the adequate representation of the spatiotemporal distributions and operations (transmissions, propagations) between of distinct incidence classes is an important task of any quantitative HFRS study.
In view of the above considerations i-iii, the three main objectives of the present work are as follows:
To overcome data-related methodological and practical difficulties (such as highly heterogeneous data distributions across space-time) by using a cd-BME method that divides the infectious disease dataset into discrete classes (the incidence classes were selected based on variability reduction and mapping coverage criteria).
To generate HFRS distribution maps that account for the real fact that the intraclass and interclass incidence data is subject to uncertainty, and to show that the cd-BME method can produce more accurate incidence estimates at locations and times where no HFRS records are available than standard (class-independent) mapping techniques.
To introduce practical and easily interpretable indicators of spatiotemporal dependency based on probability logic [29]. These indicators exhibit different yet complementary kinds of HFRS dependence (e.g., each indicator captures a different feature of HFRS transition from one class to another so that the combined study of the indicators can result to an improved assessment of HFRS distribution).
Materials and methods
Ethics statement
The present study was approved by (a) the Chinese Center for Disease Control and Prevention, and (b) the Institute of Disease Control and Prevention. All HFRS data were anonymously analyzed.
The HFRS data set and its categorization
During the period January 2005–December 2013, China’s Information System for Disease Control and Prevention (CISDCP) recorded HFRS cases at 130 counties of the Heilongjiang province, with an approximate area of 473 thousand km2, and population of 38.35 million. During this period, the monthly rainfall, temperature and relative humidity ranged from 0.23 to 221.4 mm, -23.12 to 23.12 °C and 38.77 to 83.74%, respectively. The Heilongjiang Province has 38.98, 26.29 and 16.92% croplands, mixed forests and cropland/natural vegetation mosaic, respectively [15]. In addition, the GDP of Heilongjiang Province increased from 551.4 to 1445.5 billion yuan. The monthly HFRS case data were population-standardized using the corresponding demographic data obtained from the National Bureau of Statistics of China. Fig 1 shows the spatial distribution of HFRS population-standardized incidences during the entire study period (i.e., January 2005–December 2013) in the 130 counties of the Heilongjiang Province. The maps in the current study were all made by using the ArcGIS 10.2 software.
The space-time distribution of population-standardized HFRS incidences in Heilongjiang province during the period 2005–2013 are quantitatively represented using a spatiotemporal random field model[22], X(p), where p = (s, t) denotes the spatial coordinate s = (s1, s2) and time instant t (S1 Text). Also, and denote the selected HFRS incidence interval classes at the space-time points p = (s, t) and p′ = (s′, t′), respectively, where the subscripts m, n = 1, 2, 3, 4 are the class identification numbers, and the subscripts l and u denote the lower and upper limit, respectively, of each class interval. Then, these class-based (categorical) HFRS incidences can be denoted as X(p) ∈ Im, which means that the HFRS incidence at point p belongs to the interval class Im, or X(p′) ∈ In, which means that the incidence at point p′ belongs to the class In (S2 Text). Given the high spatiotemporal variability of HFRS incidence values during the period 2005–2013 (the skewness is 6.265 and the kurtosis is 64.007), a twofold methodological choice was made seeking both variability reduction, space-time points coverage and mapping accuracy (S3 Text). In particular:
The data was log-transformed by means of Y(p) = log10(X(p) + 1). The additional advantage of this equation being that it can also account for zero values (such zero values are noteworthy since they may offer important clues to physical characteristics linked to the absence of disease or individual immunity).
The HFRS data set was categorized into four classes in terms of percentiles, as shown in Table 1, i.e., considering that 58% of the original data consist of 0 values, we divided the remaining 42% of the data into four classes by percentile (so that each of them has 10.5% of the data), and, subsequently all 0s (58%) were added to the first class, i.e., 0–68.5%, 68.5–79%, 79–89.5% and 89.5–100%. The selection of four classes was based on the satisfaction of the following quantitative criteria: (i) the variability criterion (i.e., after dividing the original data into a certain number of categories, the incidence variability should be reduced); (ii) the coverage criterion (i.e., the data coverage across the entire study area should decrease with increasing number of categories, and it is suggested to have data that covers more than 60% of the study area); and (iii) the mapping criterion (i.e., based on empirical considerations, to assure mapping accuracy a rigorous technique requires that a certain number of space-time data points around the estimation point should exist in its category).
Table 1. The four HFRS incidence classes and their descriptive statistics.
Class (Im) no. | Percentile | Original dataset X(p) | Log-Transformed data set Y(p) | ||
---|---|---|---|---|---|
Lower limit () | Upper limit () | Lower limit | Upper limit | ||
1 (I1) | 0–68.5 | 0 () | 0.3576 () | 0 | 0.1328 |
2 (I2) | 68.5–79 | 0.3577 () | 0.6830 () | 0.1329 | 0.2261 |
3 (I3) | 79–89.5 | 0.6831 () | 1.5277 () | 0.2262 | 0.4027 |
4 (I4) | 89.5–100 | 1.5278 () | 26.4884 () | 0.4032 | 1.4439 |
Note: Units of min and max of original data are cases/105 capita.
More specifically, as regards criterion i, due to the high HFRS data variability exhibiting a heavy-tailed distribution, it was found that by classifying the data in terms of incidence percentiles, the intraclass data variability was reduced significantly. In response to criterion ii, the particular incidence classes were selected because they allowed a sufficient number of space-time points in each class for further processing (HFRS mapping and indicator analysis). Within these interval classes I1, I2, I3 and I4 (Table 1) there existed, respectively, 9617 space-time points with 130 overlapping locations, 1470 points with 90 locations, 1478 points with 101 locations, and 1475 points with 96 locations. Hence, in the present study there were at least 90 locations in each incidence class (which can be regarded as a spatial data coverage criterion for improved mapping purposes). As regards criterion iii, based on empirical considerations a rigorous mapping technique requires that a certain number of space-time data points around the estimation point should exist in its category for mapping accuracy purposes.
In relation to the above, two notions can be used to describe quantitatively the HFRS pattern across space-time: the global size of each incidence class, and the spatiotemporal arrangement of the different incidence classes relative to each other. Individual HFRS incidence classes may visually appear to occupy mutually exclusive “patches” of various sizes within the space-time domain of interest (e.g., any pair of classes Im and In may have or may have not common boundaries). These patches may be spread uniformly throughout the domain of interest, or they may appear to be elongated along a particular direction, in which case the HFRS pattern will be characterized as anisotropic. The distribution pattern of incidence classes is determined by their spatiotemporal dependence, which makes the latter a key notion of a quantitative HFRS study.
Space-time mapping of HFRS incidence distribution using the variant BME method
The spatiotemporal mapping of HFRS incidence distribution was performed using the BME method [21] by simultaneously assimilating the core or general knowledge base (G-KB) and the site-specific or specificatory knowledge base (S-KB) of HFRS in Heilongjiang Province. Specifically, the mean and covariance functions were treated as G-KB and the log-transformed HFRS data Y(p) was regarded as S-KB. The implementation of the BME method (S4 Text) to separately analyze data classes defined in terms of percentiles (Table 1) will be termed class-dependent BME (cd-BME). The cd-BME mapping results will be subsequently superimposed and back-transformed to obtain the final HFRS incidence space-time maps, which provide information about the actual form of the spatiotemporal HFRS spread. For comparison purposes, the standard BME implementation and the mainstream inverse distance weighting (IDW) method were also employed to analyze the original data set without class-decomposition. To evaluate the performance of the different approaches, a ten-fold cross validation analysis was conducted that involved three distinct accuracy indicators: the root mean square error (RMSE), the mean absolute error (MAE), the determination coefficient of the corresponding linear regression (R2). Space-time computational data analysis (BME) used the software library Spatiotemporal Epistemic Knowledge Synthesis-Graphical User Interface (SEKS-GUI, [30]), while the IDW was implemented using R software [31]. An outline of the proposed methodological framework is presented in Fig 2.
Stochastic indicators of space-time HFRS dependency
The spatiotemporal arrangement of the HFRS patches occupied by the different incidence classes can be described by the relative frequencies with which the different kinds of incidence classes occur next to one another, i.e., by the corresponding incidence probabilities across space and time. That is to say, the spatiotemporal dependence of HFRS incidences can be assessed quantitatively in terms of stochastic (probabilistic) indicators linking categorical HFRS incidences at points p and p′ in various yet complementary ways. Similar stochastic indicators have been used to characterize the space-time variation of population health status, environmental pollution and ocean health (e.g., [32–38]). The stochastic HFRS indicators considered in this work are based on the probability logic theory of medical reasoning developed in [29] and provide intuitive measures of relatedness or logical correlations between two categorical HFRS incidences at points p and p′, and they may be estimated along multiple directions (anisotropic relatedness) or omnidirectionally (isotropic relatedness). Specifically:
The joint incidence probability
The joint incidence probability (JIP) is an extension in the stochastic (probabilistic) domain of the joint categorical incidence occurrence X(p) ∈ Im ∧ X(p′) ∈ In at the space-time points p and p′ (the symbol “∧” means “and”), with truth table shown in the first three columns of Table 2, where the T and F denote true (i.e., X(p) ∈ Im or In) and false (i.e., X(p) ∉ Im or In), respectively. The JIP measures the probability that at the points p and p′ the HFRS incidences belong to the specified class intervals Im and In, respectively, i.e., the probability that the incidences X(p) ∈ Im and X(p′) ∈ In occur simultaneously, so that
(1) |
Table 2. Truth table of the joint incidence, the incidence implication and the incidence equivalence.
X(p) ∈ Im | X(p′) ∈ In | X(p) ∈ Im ∧ X(p′) ∈ In | X(p) ∈ Im → X(p′) ∈ In | X(p) ∈ Im ↔ X(p′) ∈ In |
---|---|---|---|---|
T | T | T | T | T |
T | F | F | F | F |
F | T | F | T | F |
F | F | F | T | T |
Otherwise said, the JIP calculates the connectivity (strength of dependency) between the HFRS incidences X(p) ∈ Im and X(p′) ∈ In in the space-time domain of interest. The higher the JIP is, the stronger the connectivity between incidences belonging to the interval classes Im and In (or, equivalently, the higher the probability of HFRS spreading from class m to class n).
The incidence implication probability
The incidence implication probability (IIP) is an extension in the probabilistic domain of the standard logical implication X(p) ∈ Im → X(p′) ∈ In (also known as material conditional) with truth table also shown in Table 2. In this case, the IIP probability can be written as [39],
(2) |
which expresses the strength of the logical implication X(p) ∈ Im → X(p′) ∈ In, i.e., that the categorical incidence X(p) ∈ Im implies logically the categorical incidence X(p′) ∈ In. Sometimes the class Im is called the antecedent class, and In the consequent class. The Im and In in IIP are not interchangeable, due to IIP’s asymmetry. From Table 2 we observe that the logical implication holds when (X(p) ∈ Im ∧ X(p′) ∈ In), i.e., when it is not the case that both incidences X(p) ∈ Im and X(p′) ∈ In occur. As such, IIP measures the probability that X(p) ∈ Im and X(p′) ∉ In do not occur simultaneously across the Heilongjiang province during 2005–2013. Equivalently, the IIP measures the probability that either the categorical incidence X(p) ∈ Im or the incidence X(p′) ∈ In occurs. Obviously, the larger the IIP is, the stronger the spatiotemporal dependence of the HFRS incidence distribution.
The equivalency incidence probability
The equivalency incidence probability (EIP) is an extension in the probabilistic domain of the standard logical equivalence X(p) ∈ Im ↔ X(p′) ∈ In (also known as logical biconditional), with truth table as shown in Table 2. In this case, the IIP probability can be written as,
(3) |
which expresses the strength of the logical equivalence X(p) ∈ Im ↔ X(p′) ∈ In, i.e., it calculates the probability that the categorical incidence X(p) ∈ Im is logically equivalent to the incidence X(p′) ∈ In. From Table 2 we observe that the logical equivalence holds when both or neither of X(p) ∈ Im and X(p′) ∈ In occur simultaneously, i.e.,
(the symbol “∨” means “either, or”). As such, the EIP measures the degree to which the categorical incidences X(p) ∈ Im and X(p′) ∈ In either occur simultaneously or they do not occur simultaneously. The EIP indicates a closer spatiotemporal dependence of the HFRS incidence distribution across the Heilongjiang province during 2005–2013.
Links with statistical incidence conditional
The statistical incidence conditional (SIC) represents the ratio of the number of HFRS distributions in which the categorical incidences X(p) ∈ Im and X(p′) ∈ In occur simultaneously over the number of HFRS distributions in which the incidence X(p) ∈ Im occur, i.e.,
(4) |
which is a conditional categorical incidence probability.
Indicator assumptions and features
If space-time homostationarity is assumed (i.e., the HFRS incidence distribution is space homogeneous and time stationary), the indicators are functions of Δp = p − p′ = (s − s′, t − t′) = (h, τ). For example, the JIP can be written as
(5) |
for all p and p′ such that Δp = (h, τ). Isotropy further implies that the JIP is only a function of the length |h| and time separation τ, i.e., the JIP is a function of |Δp| = (|h|, τ). Similar expressions can be derived for the other three indicators in the case of space-time homostationarity and/or isotropy.
In addition, the four stochastic (probabilistic) HFRS indicators above convey complementary information regarding the intraclass relationship between the same incidence class (i.e., m = n), and the interclass relationship between different incidence classes (i.e., m ≠ n) in Heilongjiang province during January 2005–December 2013 (in fact, intraclass incidence variations can be considerably different than interclass HFRS variations). These stochastic HFRS indicators and their interpretations are summarized in Table 3. Interestingly, the JIP, IIP and EIP indicators can be expressed in terms of the SIC (these relationships are displayed in the third column of Table 3). Further discussion of the characteristics and interpretations of the four stochastic indicators can be found in S5 Text. In practice, these interpretations can be used in a complementary manner to obtain a holistic assessment of the disease situation. Next, the above stochastic HFRS indicators are calculated using space-time maps of HFRS incidence generated by categorized (cd) BME and compared in the case of the Heilongjiang province that is the focus of this work.
Table 3. Stochastic HFRS indicators and their links to the statistical conditional.
HFRS indicator | Probability that the categorical HFRS incidences | Relationship with statistical incidence conditional |
---|---|---|
X(p) ∈ Im and X(p′) ∈ In occur simultaneously | ||
X(p) ∈ Im and X(p′) ∈ In do not occur simultaneously | ||
X(p) ∈ Im and X(p′) ∈ In either occur simultaneously or do not occur simultaneously | ||
X(p′) ∈ In occurs given that X(p) ∈ Im occurred |
Results
In what follows, the categorical HFRS incidence representation will be considered in terms of the four selected incidence interval classes, Im, m = 1, 2, 3, 4. In the context of the categorical HFRS representation used in this work, two kinds of HFRS spread patterns were assumed for comparison purposes: outward HFRS spread that links a specific incidence class to the entire set of incidence classes, and inward HFRS spread that is concerned with incidence transition from the entire set of classes to a specific class.
Space-time mapping of HFRS incidences using class-based BME
Spatiotemporal correlation (covariance model) of HFRS incidences
Monthly spatial correlations of the original HFRS incidence X(p) were first calculated (108 covariances, in total). The temporal variation of the HSRF mean is smooth and periodic, fluctuating constantly around the 0.25 incidence value (Fig 3a). The covariance sill values explain the variance of HFRS incidence in the Heilongjiang Province during the same month, exhibiting certain noticeable peaks at twelve months period, the size of which reduce with time (Fig 3b). The interpretation of these high peaks is that they imply the presence of high uncertainty (or the presence of outbreaks at specific locations) in the HFRS variation during the peak times. The correlation ranges determine the HFRS domain of influence, showing a rough variation with time, which, like the HFRS mean variation, it also exhibits a periodic character (Fig 3c). The minimum and maximum values of the correlation range during the period 2005–2013 are 21,700 meters and 897,650 meters, respectively. The functional shapes of the HFRS mean, covariance sill and range are remarkably similar (e.g., in Fig 4 large (small) HSRF mean values are directly linked to long (short) correlation ranges). Interpretationally, the two distinct peaks of the HSRF mean plot during June and November, which coincide with the corresponding peaks of the mean sill plot, detect the HFRS outbreaks that occurred during these months.
Subsequently, the empirical space-time covariance values and the fitted theoretical models of the log-transform HFRS incidences Y(p) (shown in Fig 5) were derived separately for each interval class of Table 1. It is noteworthy that the space-time dependence ranges of HFRS incidences vary with the incidence level (S2 Table). Moreover, all theoretical covariance models, cX(Δp) = cX(|h|, τ), are space-time separable. However, the spatial part of the covariance model in class I4 (corresponding to the highest incidence level) is more complicated than the other three, further indicating the different space-time variation pattern of class I4.
Some key space-time variation features of the empirical covariance values (red circles) and the corresponding theoretical models (lines) can be observed in Fig 5:
For all HFRS incidence classes considered, the non-zero slopes of the spatial covariance components at the origin indicate that the log-transformed HFRS incidence fields exhibit intense localized variations across space. Regarding the temporal HFRS covariance components, except for the incidence class 1, the slopes of these covariances at the origin are zero, implying (based on the underlying spatiotemporal random field theory) that the temporal incidence variation is apparently much smoother than the spatial incidence variation.
Visual inspection of the temporal and spatial covariance plots of the HFRS incidence in the Heilongjiang province, obtained for different incidence classes, reveals that the spatiotemporal structure of incidence distributions embodied in the shape of the space-time covariance functions depends on the HFRS incidence level, with dependencies in time being stronger than those in space.
The spatial and temporal covariance lags beyond which HFRS incidence dependencies are negligible (usually referred to as spatial and temporal correlation ranges, respectively) vary among the different incidence classes selected.
Beyond the corresponding spatial and temporal ranges, the spatial and temporal components of the covariance functions of the four HFRS incidence classes are approximately zero-valued, indicating that the log-transformed incidence is spatially homogeneous in space and stationary in time. Also, the selected theoretical models (see S2 Table of the SI section) provide good fits to the empirical covariance values, thus validating the adequate theoretical representation of the actual HFRS variation in Heilongjiang province.
Accuracy performance of cd-BME mapping
The ten-fold cross validation analysis shows that the cd-BME outperforms the standard (class-independent) BME and IDW techniques in terms of the corresponding RMSE, MAE and R2 values calculated using the entire HFRS incidence dataset (S3 Table). Moreover, in order to test the robustness of the cd-BME, the original data set was also divided into 3 classes (with percentile ranges 0–72%, 72–86% and 86–100%), in which case the 10 fold-cross validation results showed that the cd-BME with 3 classes also outperforms the standard BME and IDW, although it is inferior to the cd-BME with 4 classes selected in this work (see, optimal selection of number of classes discussed in S3 Text). By looking into each individual HFRS interval class, the performance of both ways of BME implementation (cd and standard) decreases with increasing incidence level (i.e., from incidence class 1 to class 4) but, in all cases, the performance of the cd-BME implementation remains superior (S4 Table). In terms of the MAE indicator, the accuracy improvement when using the cd-BME implementation instead of the standard BME implementation is 65.16%, 82.13%, 72.32% and 42.18% for the four incidence classes considered, respectively.
Space-time mapping of HFRS incidences
The 108 spatiotemporal HFRS distribution maps with resolution 5 km × 5 km × 1 month were obtained for each interval class (i.e., 108 × 4 = 432 maps were generated, in total), and subsequently superimposed to produce the final HFRS distribution maps (S2–S10 Figs). For illustration purposes, S5 Fig shows the selected HFRS incidence map for the year 2008. One observes the following: (a) The HFRS incidences in Heilongjiang province exhibited two noticeable peaks during the months of June and November. (b) The first peak triggers the rapid spread of HFRS cases during the August-November period toward the western part of Heilongjiang province and also toward some counties in the eastern part of the province. (c) After November, the HFRS incidences decrease at some counties, and the number of counties suffering high levels of HFRS infections also decreases. (d) The western part of the Heilongjiang province exhibits a lower number of HFRS incidences than the eastern part.
Alternatively, an informative visualization of HFRS spread over the Heilongjiang province during 2008 is provided by the categorical space-time maps in terms of the four different incidence interval classes defined earlier, and shown in Fig 6. Specifically, the maps of Fig 6 present to scale the monthly distribution of “patches” with incidence classes I2, I3 and I4 amidst class I1. An apparent feature of Fig 6 is that some parts of the Heilongjiang region are dominated by small patches of HFRS incidence, whereas in some other parts the HFRS patches seem to be large. These incidence patches are mutually exclusive, bounded and they have varying sizes. Certain HFRS patches seem to be distinctly elongated toward some preferred direction, indicating the presence of anisotropy. Sometimes the HFRS patches are clearly separated from one another, some other times they share common boundaries, and yet some other times they are completely surrounded by another class (e.g., in various monthly maps the classes I2, I3 and I4 occur as patches within the class I1). The proportions of regional cover by each incidence class shows the dominance of class I1 within which all the other classes are embedded, so that class I1 acts like a background class.
In this work we also calculated the mean distances across patches during each month of the period 2005–2013 using the centers of each incidence patch. Given that the area of class I1 in Fig 6 is the background domain that is not consisting of patches, a relevant center of class I1 cannot be recognized in Fig 6, and, hence, mean distances could not be calculated for class I1. The plots of mean distances across patches during each month of the period 2005–2013 are shown in S11 Fig (e.g., the mean distance between the incidence class I2 and the class I3 during March 2008 is 258.3 Km). These mean distances across patches may be interpreted as effective ranges beyond which the transition probabilities remain essentially constant. As we observe in S11 Fig, the temporal variations of the mean distances across patches are stationary, i.e., they fluctuate around certain constant values, as follow: 272 Km (mean distance across I2 patches), 304 Km (across I2 − I3 patches), 340 Km (across I2 − I4 patches), 255 Km (across I3 patches), 273 Km (across I3 − I4 patches), and 273 Km (across I4 patches). I.e., the longest mean distance during 2005–2013 occurred across patches of class I2 to I4, and the shortest mean distance across patches of class I2. The reciprocals of the mean distances between incidence patches can also serve as the intensity parameters of the four classes. As the numerical results above demonstrate, nevertheless, there are small differences among the intensity parameters of the four HFRS classes, with the relatively most intense being the I3 patches (4 × 10−4 Km-1), followed by the I2, I4 and I3 − I4 patches (3.6 × 10−4 Km-1), and with the least intense being the I2 − I3 (3.3 × 10−4 Km-1) and I2 − I4 (2.9 × 10−4 Km-1) patches. The mean coefficients of variation of the HFRS incidence during the period 2005–2013 were equal to 57.6532, 0.0232, 0.0824 and 0.2997 for the I1, I2, I3 and I4 class, respectively.
It would be interesting to calculate the varying frequencies and dynamics of adjacent and non-adjacent HFRS classes in the Heilongjiang province during 2005–2013, as well as the probabilities of incidence transition from one class to another. This is the concern of the stochastic (probabilistic) HFRS indicators to be discussed next.
Spatiotemporal dependence pattern of HFRS incidence spread in Heilongjiang province during 2005–2013
The global size of each incidence class during Jan 2005-Dec 2013 was first calculated (S6 Text). At time t let denote the spatial mean of the HFRS incidence X(s, t) averaged over the Heilongjiang region. For each time t (month), the probability represents the geographical fraction of the Heilongjiang region with (m = 1, 2, 3, 4).S12a–S12d Fig present the temporal variation of for each of the four HFRS classes. The values for m = 1, 2, 3 and 4 fluctuate around the constant probability values, ℘1 = 0.6767, ℘2 = 0.2314, ℘3 = 0.0736, ℘4 = 0.0184, respectively. Clearly, the HFRS class I1 is the most dominant in the Heilongjiang province (covering about 68% of the total area), followed by the classes I2, I3 and I4.
The spatiotemporal arrangement of the different HFRS incidence classes relative to each other and their relationships were assessed based on the different perspectives offered by the four stochastic indicators considered in this work (their detailed calculation can be found in S7 Text). The obtained results are presented next.
The JIP perspective
Assuming that the space-time points p and p′ were randomly selected in the study domain, the surfaces of Fig 7 express the joint probability of occurrence of both HFRS incidences X(p) ∈ Im and X(p′) ∈ In as a function of the spatial distance h between these two points and their time separation τ. Otherwise said, given that τ = t′ − t > 0, the JIP value is equal to the probability that the HFRS incidence moves from an incidence patch of class Im at p to a patch of class In at p′.
We observe that the surfaces in Fig 7 representing the distribution of intraclass HFRS dependence (i.e., m = n) start from their highest value at h = 0, τ = 0, and gradually decrease to a stable, for all practical purposes value. At large space-time lags, this value should be equal to . The lag h and separation τ corresponding to this stable value defines the spatial and temporal ranges representing the distance and time of self-dependence of the Im class. The height of the JIP surfaces also drops gradually from class I1 to class I4, i.e., the space-time dependence is higher among smaller incidences than among larger ones, and the incidence class I1 has the most significant contribution to the strength of the space-time HFRS dependence measured by JIP compared to the other three classes. In fact, the probability between categorical incidences of class I1 is higher than between incidences in any other class, even at long h and τ (compare the cyan surfaces in Fig 7a with the purple, orange and green surfaces in Fig 7b, 7c and 7d, respectively). Similarly, for classes I1 and I2, there is a higher probability of decreasing intraclass HFRS dependence with increasing h and τ (Fig 7a and 7b), whereas for classes I3 and I4 the intraclass HFRS dependence is the strongest at small temporal lags τ (Fig 7c and 7d).
As regards interclass variation (i.e., m ≠ n), the JIP measures the probability of moving from an incidence patch of class Im to one of class In. The interclass JIP plots represent the change in transition probabilities between two different classes from one point to another point with increasing h and τ. The JIP probability surfaces representing the space-time distribution of interclass HFRS dependence are higher between neighboring classes, i.e., the JIP surface of any incidence classes m and n drops with increasing difference |n − m| (e.g., the JIP surface of class pair I1 and I2 is higher than that of the pair I1 and I3, which, in turn is higher than that of the pair I1 and I4). The probability of HFRS dependence between class I1 and the other four classes decreases with increasing HFRS incidence in class I1. Also, when either X(p) ∈ I4 or X(p′) ∈ I4 occur, the corresponding joint incidence probabilities or are the smallest among the values with m, n = 1, 2, 3 or 4 (see the green surface in Fig 7a–7c and the four other colors surfaces in Fig 7d). Visually, class I1 exhibits the simplest space-time patterns of HFRS dependency among all four incidence classes considered, since the JIP surfaces in Fig 7a do not overlap. Lastly, the HFRS incidences of class I4 exhibit the lowest connectivity with the other incidence classes, as indicated by the lower JIP values in Fig 10d relative to the other classes in Fig 7a–7c), followed by class I3. (More characteristics of JIP values can be found in S8 Text).
The IIP perspective
Fig 8 shows the IIP probability of X(p) ∈ Im → X(p′) ∈ In as a function of the distance lag h and the time separation τ.
The intraclass incidence surfaces represent the change in probabilities of an incidence class Im from one space-time point to another point with increasing lag h and separation τ. At large space-time lags, the should be equal to 1 + ℘m(℘m − 1). More specifically, Fig 8a shows that, overall, among the four classes considered the highest IIP probability of intraclass HFRS incidence dependence at distance and time lags h and τ occurs between incidences of the same class I1, i.e., ; whereas the lowest IIP probability occurs between incidences of classes I1 and I4, i.e., . These results confirm that for all h and τ, the influence of the categorical HFRS incidence at location s and time t on the incidence at location s + h and time t + τ is much stronger for class I1 than for class I4. Fig 8b shows that at small h and τ the incidence of class I2 at location s and time t has a higher probability of influencing incidence of the same class I2 at location s + h and time t + τ than of the other three classes. But, at larger h and τ the HFRS incidence of class I2 at location s and time t has higher probability of influencing the incidence of class I1 at location s + h and time t + τ than the incidence of the other three classes. Similar conclusions can be drawn from Fig 8c and 8d.
The EIP perspective
Fig 9 shows the probability surfaces representing the event that the categorical incidence X(p) ∈ Im is logically equivalent to the incidence X(p′) ∈ In, i.e., X(p) ∈ Im ↔ X(p′) ∈ In. In general, it holds that . The EIP plots are the only one among the four indicators in which the surfaces associated with the different classes clearly overlap (see, e.g., Fig 9a). Further, by comparing the four Fig 9a–9d, we found that X(p′) ∈ I4 exhibits a high EIP probability of logical equivalence with X(p) ∈ Im for m = 2, 3, 4, which also confirms the low connectivity between X(p) ∈ I1 and X(p′) ∈ I4 detected by JIP and IIP.
The SIC perspective
The SIC perspective focuses on the conditional probability that a patch of HFRS incidence class In lies next to one of species Im. Accordingly, Fig 10 shows the probability surfaces , i.e., the probability of X(p′) ∈ In occurrence given that X(p) ∈ Im occurred. Hence, SIC is the ratio of the number of HFRS distributions in which the categorical incidences X(p) ∈ Im and X(p′) ∈ In occur simultaneously over the number of HFRS distributions in which the incidence X(p) ∈ Im occur. The intraclass plots start from their highest value at h = 0, τ = 0, and gradually decrease to a stable, for all practical purposes, value, which, at large space-time lags is approximately equal to ℘m. On the other hand, the interclass plots start from their lowest value at h = 0, τ = 0, and then increase to a stable value, which, at large space-time lags is approximately equal to ℘n. The generally differs from , the probability of X(p) ∈ In occurrence given that X(p′) ∈ Im occurred, because ℘m ≠ ℘n (i.e., the classes Im and In are not necessarily equiprobable).
Specifically, we observe that the SIC probability surfaces representing the space-time distribution of intraclass HFRS incidence dependence (i.e., m = n) drop gradually from class I1 to class I4. Moreover, the SIC values of intraclasses decrease with increasing h and τ (see the cyan, purple, brown and green surface in Fig 10a, 10b, 10c and 10d, respectively). Also, at large h and τ the SIC probability related to class I1 is always higher than that of the other three classes (see the cyan surfaces in Fig 10a–10d); whereas at small h and τ with m = n, the surface shows higher values than the surfaces with m ≠ n. Lastly, the SIC probability surfaces representing the space-time distribution of inter-class HFRS dependence (i.e., m ≠ n) are higher between neighboring classes, i.e., the SIC surface of any incidence classes m and n drops with increasing difference n − m ≥ 0 (e.g., the SIC surface of classes 1 and 2 is higher than that of classes 1 and 3, which, in turn is higher than that of classes 1 and 4, shown in Fig 10a). On the other hand, the SIC surface increases with increasing difference (n − m ≤ 0) at large h and τ (e.g., the is higher than , whereas the is higher than ). The shapes of the SIC plots differ, depending on the spatiotemporal distribution of the Im and In classes. For example, in Fig 10d the plot first exhibits certain peaks and then reaches its stable (asymptotic) value, which means that the incidence class I1 frequently occurs adjacent to classes I4. On the other hand, in Fig 10b the plot initially exhibits a low-value section and subsequently reaches its stable value, which means that the incidence class I3 seldom occurs close to the incidence class I2.
In theory it should hold that, JIPX < EIPX < IIPX, and JIPX < SICX, which are also confirmed in practice by the numerical results obtained in this study (S9 Text). Moreover, the space-time averaged values of the four stochastic HFRS indicators (i.e., JIPX, IIPX, EIPX, SICX) lead to the following probability assessments (see, also, S10 Text):
the probability of “both the interclass HFRS incidences occur at p and p′” is very low (with probability 0.132),
the probability of “either the HFRS incidence occurs at p′ or it does not occur at p” is very high (0.878),
the probability of “either both HFRS incidences occur or both do not” is moderate (0.368); and
the probability of “the HFRS incidence occurs at p′ given that it occurs at p” is relatively high (0.517).
The four different probabilities calculated above offer complementary quantitative assessments of the HFRS incidence dependency between any pair of points in the space-time domain of interest, with relative significance depending on the HFRS perspective adapted.
Discussion
In this work, the spatiotemporal distribution of HFRS incidences in Heilongjiang province during the period 2005–2013 was studied quantitatively using spatiotemporal random field modeling that accounts for both the structural and uncertain aspects of HFRS spread. In this modeling context, key attributes of the HFRS incidence distribution were quantified by means of covariance functions, shedding light on the predominant HFRS spread patterns in space and time. A methodological advancement of the present study is that a cd-BME technique was introduced to reduce skewness effects in the spatiotemporal distribution of HFRS incidence data. This technique demonstrated a significant ability in modeling the pronounced variability in HFRS data caused by infection outbreaks that result in skewed distributions. Further, a moving windows configuration (Akita et al. [40]2012) was used that focuses mainly on local information (this configuration provides an HFRS variability representation that is closer to the real-world infectious disease spread pattern and less variable than the global pattern). The original dataset was optimally divided into four classes based on percentiles, which while maintained all advantages of BME modeling of spatiotemporal dependencies and correlations, it made HFRS predictions more accurate and robust.
In this work we considered several models, before concluding that BME is the best one for the Heilongjiang study. For example, due to the presence of disease data with a considerable number of 0 values, the zero-inflated model with spatial random effect was considered, because it has been designed to handle over-dispersed data [41]. We first noticed that after applying this model, the distribution of the original data will change and the data values will be also modified as a result. Second, this model usually either requires certain impact factors (e.g., environmental or gender population features) for regression purposes or the neighbor disease data should be assumed to be the independent variable (regressor). The former possibility is not applicable in the present study because of the lack of such data. As regards the latter possibility, taking the neighbor data as input could account to a limited extent for purely spatial dependency. Yet, these ad hoc approximations are not necessary here, since the BME method not only can handle data with any kind of distribution but it also rigorously accounts for the spatial, temporal and composite space-time dependency of the data. Other drawbacks of the zero-inflated model with spatial random effect is that it is a “naïve” interpolator (i.e., it does not account for the varying distances between data locations, and it is impossible to obtain informative space-time maps with finer resolution compared to the original dataset), and it cannot incorporate the disease spread indicators based on probability logic. BME has none of the above drawbacks (it is an adequate interpolator, i.e. it generates accurate estimates at unsampled locations that account for the varying distances between data locations and between the data and the interpolated locations, it generates informative space-time maps with fine resolution, and it incorporates the probabilistic disease indicators).
We concluded that the living conditions of rodents can dominate HFRS epidemics, as they influence the rodents-human interaction rate. As regards the space-time mapping of HFRS incidences in Heilongjiang Province during 2005–2013, the western part exhibits lower HFRS incidences than the eastern part. This is mainly due to environmental factors, as water resources expedite growth of plants, which serve as food and facilitate reproduction of rodents [42]. The aforementioned findings are in agreement with the broader picture of the river network in the region. More precisely, in Heilongjiang Province, only Neng River is located in the western part of Heilongjiang Province (i.e. lower HFRS incidences), whereas Wusuli River, Songhua River and Mudan River locate in the eastern part of the province (i.e. higher HFRS incidences) [15]. Moreover, the eastern and southeastern parts of Heilongjiang Province exhibit mixed land types with forests, favoring rodents’ reproduction. As a result, the eastern part of Heilongjiang Province demonstrates a consistently high level of HFRS infections throughout the year, whereas, the HFRS incidences in the western part of the province are dominated by monthly outbreaks. This is due to the fact that large proportions of the western part of the province are croplands, which remain flooded for crop growth purposes during the entire farming period, preventing rodents’ reproduction. A general overview of HFRS spread patterns in Heilongjiang Province can be obtained from Fig 5, as well as by the space-time maps in the supporting information (i.e. S2–S10 Figs).
Another contribution of this work is in filling the gap in the quantitative modeling of the spatiotemporal HFRS transition mechanisms based on probability logic. In other words, the present study provides a solution to the problem of calculating HFRS spread across space-time. In this context, the proposed stochastic HFRS indicators were applied to estimate the probability of HFSR transmission between space-time domains exhibiting different infection levels as a function their spatial distance and time separation. The results of the Heilongjiang study suggested that the proposed stochastic HFRS indicators summarize well the space-time incidence patterns, and their physical meanings and interpretations of the proposed HFRS indicators provide useful information about the HFRS spread mechanisms in the Heilongjiang province during Jan 2005-Dec 2013. Some HFRS classes were found to be cross-correlated with apparent correlation ranges, but some classes were not cross-correlated in the usual sense (i.e., if classes occur at two distant parts of the Heilongjiang province, it may be appropriate to characterize their interclass relationship as non-adjacent). Each HFRS class has a relationship with any other class in the Heilongjiang province during Jan 2005-Dec 2013, and quantifying the spatiotemporal relationships between HFRS classes and incorporating them into disease analysis and mapping are help us realistic assessment of the real HFRS situation in the space-time domain of interest. The transition probabilities provided by the HFRS indicators describe the spatiotemporal arrangements between incidence classes and suggest interactions that can be explored further in detail.
The plots of the four indicators offer complementary visualizations of the variation of the different probabilities of transition between incidence classes, i.e., the probabilities with which the different levels of HFRS incidences occur next to each other and so they describe the dependency pattern of the space-time arrangement of the HFRS patches occupied by the different incidence classes. Specifically, key features of interclass HFRS incidence relationships observed in this work are the space-time dependency, level of juxtaposition, and directional asymmetry of class patterns. The categorical HFRS incidences in the Heilongjiang province during Jan 2005-Dec 2013 exhibit rather smooth intraclass but complex interclass relationships. The complementary character of HFRS indicators of intraclass and interclass incidence transition and the estimated proportions of regional cover by each incidence class showed the dominance of the incidence class I1 with which all the other classes are associated. Indeed, the HFRS incidence class I1 covered about 68% of the total area, wheres the fact that the transition probabilities from the classes I2, I3 and I4 individually to class I1 are high suggests that the incidence class I1 dominated the Heilongjiang region. This phenomenon indicated that, independently of the particular infection level, the HFRS spread is dominated by point outbreaks with relatively small spatial ranges of influence. In other words, if an HFRS outbreak occurs at one location, it is necessary for the public health management to focus on in-situ HFRS prevention and control, as a measure to prevent further spread. This also reflects that the main pathway of HFRS infection is from rodents to humans, rather from person-to-person interaction [6]. In the latter case, an HFRS outbreak would spread in much larger areas. Using the findings of spatiotemporal HFRS spread patterns, public health management can also determine the critical temporal and spatial scales for HFRS prevention and control. For example, if HFRS incidences at some location are identified to belong to class 2, effective measures should be taken for a period of approximately three months and within a radial distance of approximately 50 km (see Fig 7b).
Certain quantitative findings of this work are in line with previous qualitative assessments. For example, based on the finding of the previous studies HFRS incidences are closely associated with environmental factors, a finding that confirms, in part, the suggestions made by [4, 19, 43, 44]. Given BME’s methodological features to assimilate secondary information and auxiliary variables (e.g., [45]), future work should focus on integrating environmental factors into BME analysis, to better understand HFRS spread patterns and provide more accurate predictions. The approach introduced in this work is likely to be valuable in comparisons of spatiotemporal incidence patterns at other regions of China or worldwide. Also, the same methodology could be used in the spatiotemporal modeling and mapping of other epidemics under similar in situ conditions, in which case the choice of the disease incidence classes could be linked to the specific public health purposes.
Future work should also focus on the current shortcomings of the proposed approach. One of them is the need for developing HFRS transition probabilities tests that could lead to stronger inferences regarding the interclass interactions suggested by these probabilities. Another is the relaxation of the space-time homostationarity assumption concerning HFRS spread, which may allow a more detailed assessment of the spatial anisotropy of transition probabilities as described by the HFRS indicators. Lastly, it must be kept in mind that real-world computations usually process datasets of potentially widely varying levels of uncertainty. As a result, in most cases the computational results may not satisfy exactly the theoretical assumptions. Instead, they are expected to strike a balance between theoretical rigor and computational cost is acceptable for practical purposes, which leaves room for potential improvement of the computational component of the proposed analysis.
Supporting information
Data Availability
Patient data are protected by the China CDC and are unsuitable for public sharing. The HFRS data is not allowed to be publicly shared due to local infection disease law. Interested parties can apply for the data by contacting the Data-center of China Public Health Science (http://www.phsciencedata.cn/Share/ky_sjml.jsp?id=59761d3e-ca3c-4c65-a6a5-67be1d2fb692) or email data@chinacdc.cn.
Funding Statement
This research was supported by grants from the National Natural Science Foundation of China (Grant Nos. 41671399 and 11501339), the China Scholarship Council (201706320278) and the National Mega-Project for the Prevention and Control of Infectious Diseases (No. 2018ZX10713003). The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
References
- 1.Zhang Y-Z, Zou Y, Fu ZF, Plyusnin A. Hantavirus Infections in Humans and Animals, China. Emerging Infectious Diseases. 2010;16(8):1195–203. 10.3201/eid1608.090470 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 2.Zhang W-Y, Wang L-Y, Liu Y-X, Yin W-W, Hu W-B, Magalhaes RJS, et al. Spatiotemporal Transmission Dynamics of Hemorrhagic Fever with Renal Syndrome in China, 2005–2012. PLOS Neglected Tropical Diseases. 2014;8(11):e3344 10.1371/journal.pntd.0003344 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 3.Zou L-X, Chen M-J, Sun L. Haemorrhagic fever with renal syndrome: literature review and distribution analysis in China. International Journal of Infectious Diseases. 2016;43(Supplement C):95–100. 10.1016/j.ijid.2016.01.003. [DOI] [PubMed] [Google Scholar]
- 4.Zhang W-Y, Guo W-D, Fang L-Q, Li C-P, Bi P, Glass GE, et al. Climate Variability and Hemorrhagic Fever with Renal Syndrome Transmission in Northeastern China. Environmental Health Perspectives. 2010;118(7):915–20. 10.1289/ehp.0901504 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 5.Hansen A, Cameron S, Liu Q, Sun Y, Weinstein P, Williams C, et al. Transmission of Haemorrhagic Fever with Renal Syndrome in China and the Role of Climate Factors: A Review. International Journal of Infectious Diseases. 2015;33(Supplement C):212–8. 10.1016/j.ijid.2015.02.010. [DOI] [PubMed] [Google Scholar]
- 6.Jiang H, Du H, Wang LM, Wang PZ, Bai XF. Hemorrhagic Fever with Renal Syndrome: Pathogenesis and Clinical Picture. Frontiers in Cellular and Infection Microbiology. 2016;6:1 10.3389/fcimb.2016.00001 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 7.Rusnak JM, Byrne WR, Chung KN, Gibbs PH, Kim TT, Boudreau EF, et al. Experience with intravenous ribavirin in the treatment of hemorrhagic fever with renal syndrome in Korea. Antiviral Research. 2009;81(1):68–76. 10.1016/j.antiviral.2008.09.007 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 8.Krautkrämer E, Zeier M, Plyusnin A. Hantavirus infection: an emerging infectious disease causing acute renal failure. Kidney International. 2012;83(1):23–7. 10.1038/ki.2012.360 [DOI] [PubMed] [Google Scholar]
- 9.Wang Q, Zhou H, Han Y-h, Wang X-f, Wang S-w, Yin W-w, et al. Epidemiology and surveillance programs on hemorrhagic fever with renal syndrome in Mainland China, 2005–2008. Zhonghua liuxingbingxue zazhi. 2010;31(6):675–80. . [PubMed] [Google Scholar]
- 10.Klein SL, Marks MA, Li W, Glass GE, Fang L-Q, Ma J-Q, et al. Sex Differences in the Incidence and Case Fatality Rates From Hemorrhagic Fever With Renal Syndrome in China, 2004–2008. Clinical Infectious Diseases. 2011;52(12):1414–21. 10.1093/cid/cir232 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 11.Wu W, Guo J, Guan P, Sun Y, Zhou B. Clusters of spatial, temporal, and space-time distribution of hemorrhagic fever with renal syndrome in Liaoning Province, Northeastern China. BMC Infectious Diseases. 2011;11(1):229 10.1186/1471-2334-11-229 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 12.Yan L, Fang L-Q, Huang H-G, Zhang L-Q, Feng D, Zhao W-J, et al. Landscape Elements and Hantaan Virus–related Hemorrhagic Fever with Renal Syndrome, People’s Republic of China. Emerging Infectious Diseases. 2007;13(9):1301–6. 10.3201/eid1309.061481 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 13.Li S, Ren H, Hu W, Lu L, Xu X, Zhuang D, et al. Spatiotemporal Heterogeneity Analysis of Hemorrhagic Fever with Renal Syndrome in China Using Geographically Weighted Regression Models. International Journal of Environmental Research and Public Health. 2014;11(12):12129 10.3390/ijerph111212129 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 14.Tian H-Y, Yu P-B, Luis AD, Bi P, Cazelles B, Laine M, et al. Changes in Rodent Abundance and Weather Conditions Potentially Drive Hemorrhagic Fever with Renal Syndrome Outbreaks in Xi’an, China, 2005–2012. PLOS Neglected Tropical Diseases. 2015;9(3):e0003530 10.1371/journal.pntd.0003530 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 15.He J, Christakos G, Zhang W, Wang Y. A Space-Time Study of Hemorrhagic Fever with Renal Syndrome (HFRS) and Its Climatic Associations in Heilongjiang Province, China. Frontiers in Applied Mathematics and Statistics. 2017;3(16). 10.3389/fams.2017.00016 [DOI] [Google Scholar]
- 16.He J, Christakos G, Wu J, Cazelles B, Qian Q, Mu D, et al. Spatiotemporal variation of the association between climate dynamics and HFRS outbreaks in Eastern China during 2005–2016 and its geographic determinants. PLOS Neglected Tropical Diseases. 2018;12(6):e0006554 10.1371/journal.pntd.0006554 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 17.Liu Q, Liu X, Jiang B, Yang W. Forecasting incidence of hemorrhagic fever with renal syndrome in China using ARIMA model. BMC Infectious Diseases. 2011;11(1):218 10.1186/1471-2334-11-218 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 18.Li C-P, Cui Z, Li S-L, Magalhaes RJS, Wang B-L, Zhang C, et al. Association between Hemorrhagic Fever with Renal Syndrome Epidemic and Climate Factors in Heilongjiang Province, China. The American Journal of Tropical Medicine and Hygiene. 2013;89(5):1006–12. 10.4269/ajtmh.12-0473. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 19.He J, He J, Han Z, Teng Y, Zhang W, Yin W. Environmental Determinants of Hemorrhagic Fever with Renal Syndrome in High-Risk Counties in China: A Time Series Analysis (2002–2012). The American Journal of Tropical Medicine and Hygiene. 2018;99(5):1262–8. 10.4269/ajtmh.18-0544 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 20.Zhang X, Chen H-Y, Zhu L-Y, Zeng L-L, Wang F, Li Q-G, et al. Comparison of Hantaan and Seoul viral infections among patients with hemorrhagic fever with renal syndrome (HFRS) in Heilongjiang, China. Scandinavian Journal of Infectious Diseases. 2011;43(8):632–41. 10.3109/00365548.2011.566279 [DOI] [PubMed] [Google Scholar]
- 21.Christakos G. Modern spatiotemporal geostatistics: Oxford University Press; 2000. [Google Scholar]
- 22.Christakos G. Spatiotemporal Random Fields: Theory and Applications: Elsevier, Amsterdam, the Netherlands; 2017. [Google Scholar]
- 23.Christakos G, Olea RA. New space-time perspectives on the propagation characteristics of the Black Death epidemic and its relation to bubonic plague. Stochastic Environmental Research and Risk Assessment. 2005;19(5):307–14. 10.1007/s00477-005-0236-6 [DOI] [Google Scholar]
- 24.Gesink Law DC, Bernstein KT, Serre ML, Schumacher CM, Leone PA, Zenilman JM, et al. Modeling a Syphilis Outbreak Through Space and Time Using the Bayesian Maximum Entropy Approach. Annals of Epidemiology. 2006;16(11):797–804. 10.1016/j.annepidem.2006.05.003 [DOI] [PubMed] [Google Scholar]
- 25.Choi K-M, Yu H-L, Wilson ML. Spatiotemporal statistical analysis of influenza mortality risk in the State of California during the period 1997–2001. Stochastic Environmental Research and Risk Assessment. 2008;22(1):15–25. [Google Scholar]
- 26.Yu H-L, Yang S-J, Yen H-J, Christakos G. A spatio-temporal climate-based model of early dengue fever warning in southern Taiwan. Stochastic Environmental Research and Risk Assessment. 2011;25(4):485–94. 10.1007/s00477-010-0417-9 [DOI] [Google Scholar]
- 27.Angulo J, Yu H-L, Langousis A, Kolovos A, Wang J, Madrid AE, et al. Spatiotemporal Infectious Disease Modeling: A BME-SIR Approach. PLOS ONE. 2013;8(9):e72168 10.1371/journal.pone.0072168 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 28.Angulo JM, Yu H-L, Langousis A, Madrid AE, Christakos G. Modeling of space–time infectious disease spread under conditions of uncertainty. International Journal of Geographical Information Science. 2012;26(10):1751–72. 10.1080/13658816.2011.648642 [DOI] [Google Scholar]
- 29.Christakos G, Wang J, Wu J. Stochastic Medical Reasoning and Environmental Health Exposure: Imperial College Press, London, UK; 2014. [Google Scholar]
- 30.Yu H-L, Kolovos A, Christakos G, Chen J-C, Warmerdam S, Dev B. Interactive spatiotemporal modelling of health systems: the SEKS–GUI framework. Stochastic Environmental Research and Risk Assessment. 2007;21(5):555–72. 10.1007/s00477-007-0135-0 [DOI] [Google Scholar]
- 31.Pebesma E, Graeler B. Gstat package: https://cran.r-project.org/package=gstat; 2018.
- 32.Christakos G, Hristopulos DT. Stochastic Indicators for Waste Site Characterization. Water Resources Research. 1996;32(8):2563–78. 10.1029/96WR01393 [DOI] [Google Scholar]
- 33.Christakos G, Hristopulos DT. Characterization of atmospheric pollution by means of stochastic indicator parameters. Atmospheric Environment. 1996;30(22):3811–23. [Google Scholar]
- 34.Christakos G, Hristopulos DT. Stochastic indicator analysis of contaminated sites. Journal of Applied Probability. 1997;34(4):988–1008. Epub 07/14. 10.2307/3215012 [DOI] [Google Scholar]
- 35.Christakos G. Space-Time Stochastic Modelling in Human Exposure. Encyclopedia of Environmetrics 2013. [Google Scholar]
- 36.Yang Y, Christakos G. Spatiotemporal Characterization of Ambient PM2.5 Concentrations in Shandong Province (China). Environmental Science & Technology. 2015;49(22):13431–8. 10.1021/acs.est.5b03614 [DOI] [PubMed] [Google Scholar]
- 37.He J, Yang Y, Christakos G, Liu Y, Yang X. Assessment of soil heavy metal pollution using stochastic site indicators. Geoderma. 2019;337:359–67. 10.1016/j.geoderma.2018.09.038. [DOI] [Google Scholar]
- 38.Jiang Q, He J, Wu J, Hu X, Ye G, Christakos G. Assessing the severe eutrophication status and spatial trend in the coastal waters of Zhejiang province (China). Limnology and Oceanography. 0(0). 10.1002/lno.11013 [DOI] [Google Scholar]
- 39.Christakos G. On a deductive logic-based spatiotemporal random field theory. Teor Imovir Mat Stat. 2002;66:46–57. [Google Scholar]
- 40.Akita Y, Chen J-C, Serre ML. The moving-window Bayesian maximum entropy framework: estimation of PM2.5 yearly average concentration across the contiguous United States. Journal Of Exposure Science And Environmental Epidemiology. 2012;22:496 10.1038/jes.2012.57 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 41.Agarwal DK, Gelfand AE, Citron-Pousty S. Zero-inflated models with application to spatial count data. Environmental and Ecological Statistics. 2002;9(4):341–55. 10.1023/a:1020910605990 [DOI] [Google Scholar]
- 42.Li J, Chen Z, Hou T, Xing Y, Cai Z, Yang Y. Study on the risk factors of hemorrhagic fever with renal syndrome in Xi’an city. Chin J Dis Control Prev. 2013;17:564–6. [Google Scholar]
- 43.Guan P, Huang D, He M, Shen T, Guo J, Zhou B. Investigating the effects of climatic variables and reservoir on the incidence of hemorrhagic fever with renal syndrome in Huludao City, China: a 17-year data analysis based on structure equation model. BMC Infectious Diseases. 2009;9(1):109 10.1186/1471-2334-9-109 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 44.Xiao H, Liu H-N, Gao L-D, Huang C-R, Li Z, Lin X-L, et al. Investigating the Effects of Food Available and Climatic Variables on the Animal Host Density of Hemorrhagic Fever with Renal Syndrome in Changsha, China. PLOS ONE. 2013;8(4):e61536 10.1371/journal.pone.0061536 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 45.He J, Kolovos A. Bayesian maximum entropy approach and its applications: a review. Stochastic Environmental Research and Risk Assessment. 2018;32(4):859–77. 10.1007/s00477-017-1419-7 [DOI] [Google Scholar]
Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Supplementary Materials
Data Availability Statement
Patient data are protected by the China CDC and are unsuitable for public sharing. The HFRS data is not allowed to be publicly shared due to local infection disease law. Interested parties can apply for the data by contacting the Data-center of China Public Health Science (http://www.phsciencedata.cn/Share/ky_sjml.jsp?id=59761d3e-ca3c-4c65-a6a5-67be1d2fb692) or email data@chinacdc.cn.