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  <front>
    <journal-meta />
    <article-meta>
      <title-group>
        <article-title>Method of Using Hazard Criteria for Identifying Hazardous Situations</article-title>
      </title-group>
      <contrib-group>
        <contrib contrib-type="author">
          <string-name>Valery V. Nicheporchuk</string-name>
        </contrib>
        <aff id="aff0">
          <label>0</label>
          <institution>Institute of Computational Modelling of the SB RAS</institution>
        </aff>
      </contrib-group>
      <pub-date>
        <year>2010</year>
      </pub-date>
      <issue>4</issue>
      <fpage>64</fpage>
      <lpage>71</lpage>
      <abstract>
        <p>The paper presents criteria for hazard and threat identification based on the systematization of the parameters of the comprehensive area safety monitoring. The numerical values of the intervals of functional safety of regional social-naturaltechnogenic systems have been obtained based the requirements of regulatory and guidance documents, and expert assessments. A method of using criteria has been proposed for identifying hazardous situations which consists in the comprehensive analytical processing of monitoring data.</p>
      </abstract>
      <kwd-group>
        <kwd>comprehensive monitoring</kwd>
        <kwd>operational environment</kwd>
        <kwd>hazard criteria</kwd>
      </kwd-group>
    </article-meta>
  </front>
  <body>
    <sec id="sec-1">
      <title>Introduction</title>
      <p>
        To fulfill the tasks of ensuring the safe functioning of regional S-N-T systems requires the establishment of allowable
range of parameters controlled by various systems for monitoring natural and anthropogenic processes [1]. A large list of
possible risks characteristic of the territory of Siberia, and their mutual influence which enhances negative effects of the
risk manifestation, justify the need for collecting, consolidating and comprehensive processing of data from the entire
range of active observations [
        <xref ref-type="bibr" rid="ref2 ref3">2, 3</xref>
        ]. The development of a unified approach for identifying hazards and threats allows
creating integrated information and analytical systems allowing one to solve immediate and strategic tasks of the area safety
management [4].
      </p>
      <p>
        Unlike integral risk assessments, which are annually performed, the area safety management authorities are
permanently solving the problems of hazard identification [
        <xref ref-type="bibr" rid="ref5">5</xref>
        ]. Here, virtually the same information resources of comprehensive
monitoring are used, and methods of analytical data processing are similar to those used in solving the problems of
information support for preventive measures for risk reduction.
      </p>
      <p>
        The functionality of most monitoring systems is reduced to on-line visualization of controlled parameters and
analytical processing of observation archives [
        <xref ref-type="bibr" rid="ref6">6</xref>
        ]. The identification of hazards and threats, as a rule, is carried out in manual
mode by selecting the maximum (or minimum) values for the period under consideration. Further decision-making is
performed, which involves additional information resources, and systems of situational and analytical modeling. The use of a
large number of highly specialized systems in decision-making significantly reduces the management effectiveness.
Fragmented software implementation of the tasks of safe development of territories leads to the duplication of
information, while the difference in the regulations of updating causes contradictions, whose resolution would reduce the
efficiency and reliability of management decisions, to result in excessive expenses for ensuring security.
      </p>
      <p>In order to build a universal approach for identifying hazards and threats, criteria have been developed for the
threshold values of parameters for the available types of monitoring the S-N-T systems. A method of using the criteria is
proposed for early detection of precursors of dangerous situations and for timely notification of emergency rescue units,
population, and authorities.</p>
    </sec>
    <sec id="sec-2">
      <title>Systematization of the monitoring parameters</title>
      <p>
        For the systematization of the monitoring parameters PR we introduce the notions of «comprehensive monitoring» and
«current situation» as well as notations of their components [
        <xref ref-type="bibr" rid="ref7">7</xref>
        ]. Comprehensive monitoring is a system of monitoring and
control regularly performed according to a certain procedure for estimating the state of the environment and technosphere
objects representing hazards О1, analysis of the occurring processes and timely identification of the environment changes
as well as collection of data on the characteristics and current state of the protected objects О2 and management objects О3
for further comprehensive processing [
        <xref ref-type="bibr" rid="ref8">8</xref>
        ]. Current situation ST is a collection of factors, conditions and circumstances in
which certain activities are prepared and performed to ensure the safety of objects and areas described by the values of
components of information resources S of multiple types for certain types of situations H [
        <xref ref-type="bibr" rid="ref9">9</xref>
        ].
      </p>
      <p>The main types of ST are meteorological, hydrological, seismic, radiation, forest fire, sanitary and epidemiological
conditions. The consolidation of the parameters of different types of monitoring allows one to take into account the
mutual effect of ST. For example, adverse weather conditions increase the scale of hazards for almost all types of dangerous
situations while the phytopathological environmental factors determine the risk of natural fires.</p>
      <p>The primary source of the control parametric data O1 is instrumental monitoring. Nowadays devices allow measuring
the values of physical parameters, such as temperature, pressure, velocity, substance concentration, radiation power, size
change, etc., and transmit data for processing at arbitrarily small intervals. Instrument monitoring also includes alarms
transmitting signals about a dangerous event based on internal processing of measurement results. The information
resources of monitoring include the results of instrumental measurements with various levels of processing (error
correction, aggregation, etc.). However, for direct monitoring of the equipment functioning at the object level, devices are the
only method of immediate identification of hazards and threats.</p>
      <p>
        The most important source of information on the conditions of large areas is the data of remote sensing of the Earth
[
        <xref ref-type="bibr" rid="ref10">10</xref>
        ]. In addition to the parameters listed above, spacecraft control a wide range of electromagnetic radiation, albedo, and
spatial surface characteristics [
        <xref ref-type="bibr" rid="ref11">11</xref>
        ]. Depending on the spatial resolution of the received channels, and the periodicity of
shooting, earth remote sensing systems are used to provide information support for management and control in almost all
types of dangerous situations [12]. Unlike ground monitoring, in order to be used for the hazard and threat identifying,
satellite imagery data require complex processing with the use of highly specialized software [13].
      </p>
    </sec>
    <sec id="sec-3">
      <title>Criteria for identifying hazards and threats</title>
      <p>The solution for the hazard identification problem is based on real-time analytical processing of data streams of
comprehensive real-time monitoring of the environment and objects of the technosphere. The identification of hazards and
threats consists in comparing the observed or calculated parameters with the criteria unique for the type of situations H.</p>
      <p>The main document used as the basis for the development of the criteria for hazards and threats identification is the
Order of the Ministry of Emergencies of Russia No. 329 dated July 8, 2004 “Concerning the Implementation of the List of
Criteria for Information on Emergency Situations”. In addition, use was also made of departmental methods and
regulatory acts of Roshydromet, Ministry of Natural Resources of the Russian Federation, Ministry of Transport of the Russian
Federation, Ministry of Energy of the Russian Federation and others.</p>
      <p>General criteria are used for all points of observation of seismic, and radiation conditions while unique ones are used
for the hydrological situation (data of critical water levels), functioning of techno-sphere objects, etc. Group criteria of the
meteorological situation are applied for various climate zones - areas located in temperate latitudes, Arctic zone, and
highlands.</p>
      <p>Hazard criteria are reviewed at different time intervals: limits for the discharges of hydropower plants are set monthly,
depending on the hydro and meteorological conditions; critical water levels - once every five years. Longer periods of
action are characteristic for the criteria of radiation hazard which depend on lengthy medical research as well as for the
criteria for identifying technogenic acci-dents. Since some types of situations H are of seasonal character, their control is
performed in certain months of the annual cycle. For natural emergencies which depend on air temperature, there are daily
intervals of hazard control. For example, rising water levels and fires in the forest are most likely to occur during the day
between 1 to 5 pm. It is appropriate that the seasonal and daily intervals for other types of situations are based on the
analytical processing of catalogs of emergency situations.</p>
      <p>The values of the threat criteria in the absence of specific data in literature or results of field observations were
determined by expertise as a fraction of the dangerous value. Most hazard criteria rep-resent the maximum or minimum
possible value of the monitored parameter, and the threat criteria represent a percentage of the critical value. In addition, the
criteria can represent the sum of the values for a certain period, difference of consecutive measurements, as well as the
number of objects having certain properties, or changed properties during the period. For technogenic objects, hazard and
threat criteria may be in the middle of the operation intervals (for example, the rotation velocity of the hydroengines of a
power station).</p>
      <p>Decision making on emergency response to hazards and threats has a multi-level character. The real-time monitoring
of the state of the environment is carried out at the regional level. The monitoring of technosphere objects is performed by
duty dispatch services at the object level, the information is presented to higher-level management bodies in a
summarized form. This is due not only to the large amount of control information concerning units and modules of industrial
facilities and infrastructure of the areas, but also to the need for special knowledge to interpret signals as signs of a
nonroutine or emergency situation.</p>
      <p>Thus, in most cases, hazard criteria are necessary but not sufficient conditions for a hazardous event to occur. After
double-checking the signal using other sources of information and depending on the type of situation H, a decision is
made on the response of operative services or their transfer into high-alert regime. The full cycle of management
information support using identification criteria consists in the successive solution of the following tasks:
 identification of hazards or threats in terms of the current or forecasted state of any situation ST at the observation
point PO, with notification (informing) of response services and population for a particular area;</p>
      <p>
         identification of risk indicators exceeding the allowable values with the fulfillment of the tasks of planning
preventive measures for the territory with an increased level of emergency risk [
        <xref ref-type="bibr" rid="ref12">14</xref>
        ].
      </p>
      <p>Table 1 shows the hazard criteria for the parametric monitoring of different types of hazards.</p>
      <sec id="sec-3-1">
        <title>TECHNOGENIC HAZARDS</title>
        <p>Md &gt; 0,6
Md &gt; 1,2</p>
        <sec id="sec-3-1-1">
          <title>One-time value</title>
        </sec>
      </sec>
      <sec id="sec-3-2">
        <title>Radiation situation</title>
        <p>MED (Md, mSv)</p>
      </sec>
      <sec id="sec-3-3">
        <title>Collapse of buildings and constructions</title>
        <sec id="sec-3-3-1">
          <title>Snow level on large-span buildings</title>
          <p>(LS, cm)</p>
        </sec>
      </sec>
      <sec id="sec-3-4">
        <title>Accidents in housing and utility sector</title>
        <sec id="sec-3-4-1">
          <title>Hot water pressure in the heat supply chamber (PW, atm)</title>
        </sec>
        <sec id="sec-3-4-2">
          <title>Hot water temperature in the heat sup</title>
          <p>ply chamber (TW, C)</p>
        </sec>
      </sec>
      <sec id="sec-3-5">
        <title>Weather hazards</title>
        <sec id="sec-3-5-1">
          <title>Temperature (t, C)</title>
        </sec>
        <sec id="sec-3-5-2">
          <title>Wind velocity (SW, m/s)</title>
        </sec>
        <sec id="sec-3-5-3">
          <title>Precipitation (Pre, mm)</title>
        </sec>
        <sec id="sec-3-5-4">
          <title>Wet snow diameter (DS, mm)</title>
        </sec>
        <sec id="sec-3-5-5">
          <title>Fire hazard class, CFD</title>
        </sec>
        <sec id="sec-3-5-6">
          <title>Snow level in the avalanche-prone area (LS, cm)</title>
          <p>LS &gt; 20
PW &lt; 6
TW &lt; 90
DS &gt; 20
CFD = 3
LS &gt; 30
LS &gt; 30
PW &lt; 4
TW &lt; 70
crossing 0
t ≤ -40
SW ≥ 25
DS &gt; 30
CFD ≥ 4
LS &gt; 50</p>
        </sec>
        <sec id="sec-3-5-7">
          <title>Can change depending on a particular object</title>
        </sec>
        <sec id="sec-3-5-8">
          <title>Direct feed</title>
        </sec>
        <sec id="sec-3-5-9">
          <title>Direct feed</title>
        </sec>
        <sec id="sec-3-5-10">
          <title>Can vary depending on the climate zone</title>
        </sec>
        <sec id="sec-3-5-11">
          <title>Estimated based on air temperature and humidity, duration of the period without precipitation</title>
        </sec>
        <sec id="sec-3-5-12">
          <title>Can vary depending on the slope and exposure</title>
        </sec>
      </sec>
      <sec id="sec-3-6">
        <title>NATURAL HAZARDS</title>
        <p>30 ≤ t &lt; 35 or -40 &lt; t ≤</p>
        <p>-35
t ≥ 35
15 ≤ SW &lt; 25
Pre ≥ 30 per 1 Pre ≥ 50 per 12 Pre ≥ 120 per For solid and liquid
precipitah. h. 42 h. tion
DD &gt; 7</p>
        <p>DD &gt; 14</p>
        <sec id="sec-3-6-1">
          <title>RL ≥ Starting level of flood</title>
          <p>Kh1 0,8</p>
        </sec>
        <sec id="sec-3-6-2">
          <title>RL ≥ Starting level of flood Kh1</title>
          <p>dRL &gt; 100</p>
        </sec>
      </sec>
      <sec id="sec-3-7">
        <title>BIOLOGICAL AND SOCIAL HAZARDS</title>
        <p>Сp ≥ maxD
Сp ≥ maxD24
С ≥ maxD  Nс or С ≥ maxD24  Nс</p>
        <sec id="sec-3-7-1">
          <title>Can vary depending on the climate zone</title>
        </sec>
        <sec id="sec-3-7-2">
          <title>Unique criteria Khi</title>
          <p>for each point of observation</p>
          <p>PO
maxD – maximum one-time
concentration; maxD24 –
maximum day exposure
concentration</p>
        </sec>
        <sec id="sec-3-7-3">
          <title>Nс  [3; 10] depending on the</title>
          <p>control parameter</p>
        </sec>
        <sec id="sec-3-7-4">
          <title>Long drought (DD, days)</title>
        </sec>
      </sec>
      <sec id="sec-3-8">
        <title>Hydrological hazards</title>
        <sec id="sec-3-8-1">
          <title>Water level in rivers (RL, cm)</title>
        </sec>
        <sec id="sec-3-8-2">
          <title>Daily variation of the water level (dRL, m)</title>
        </sec>
      </sec>
      <sec id="sec-3-9">
        <title>Mass diseases</title>
        <sec id="sec-3-9-1">
          <title>Concentration of the contaminating substance, Сp</title>
        </sec>
      </sec>
    </sec>
    <sec id="sec-4">
      <title>Using the criteria of hazards and threats</title>
      <p>
        The software implementation of automatic indication of emergency and unfavorable parameters of the situation is
based on the “semaphore principle” [
        <xref ref-type="bibr" rid="ref13">15</xref>
        ]. The detection of threats is done by verifying the correspondence of the
monitoring data to the established threshold values or revealing their discrepancy. The data are evaluated by comparing the
current values of the parameters being controlled with the criteria given in Table 1. Filtration is done to determine the levels
of the conditions of the objects under control. Depending on its results, the parameters under control have the following
colors:
      </p>
      <p> «green» - the conditions correspond to the norm, the values of the parameters under control are within the allowable
limits;</p>
      <p> «threat» – the identification of a threat when the parameters approach the critical values, or dramatic changes are
detected, or else a prolonged deviation is observed from the average standard values;</p>
      <p> «red» – the identification of a hazard, increased risk of a situation connected with damages or interruption of the
activities in the area. In this case, the parameters are equal or exceed the critical values.</p>
      <p>The grey color of the indicator shows the absence of the current data for the estimation and the necessity to verify the
source of information and channel of data transmission.</p>
      <p>The application of the three-color gradation has been shown to be optimum for prompt decision making by the
authorities of the Emergency Ministry of Russia using the earlier developed response scenarios. The scenarios describe the
consequences and actions in a dangerous situation, depending on its type, and scale; and they are adjusted to a particular area
and arising conditions.</p>
      <p>The algorithm of using the criteria for the hazard and threat identification is presented in Figure 1. The process
includes three cycles: taking into account the types of situations ST, observation points PO and measured parameters PR.
The content of the monitoring information depends on the type of the information source. The data package of the
instrumental monitoring can be represented by the vector of the parameters PR. The data from the observation systems and
web-portals integrate the information from all the observation points PO (matrix PO PR).</p>
      <p>Most situation types ST depend on the weather conditions and forecast, thus, in analyzing the situations
meteorological parameters are to be taken into account. The range of the allowable values for the situations with the unfavorable
values of the meteorological parameters decreases. Some of the parameters PR require preliminary calculation, for example,
the precipitation sum Pre for the period or the fire hazard class in the forests CFD. In the process of comparison of the
current PR with the criteria of hazards and threats Kr the array Signal is filled. In the cases of varying values of the
elements of the array Signal[st, po, pr] the tasks of prompt response t21 and t22 are solved according to the earlier developed
scenarios of actions.</p>
      <p>
        Automatic indication of hazards and threats for the situation as a whole has been developed with the help of the
operation of aggregation. The situation is assigned a level of hazard corresponding to the worst of the levels from multiple
analytical indicators. Notification of hazards and threats occurs at the level of the whole area and the function of the
refinement of the analytical model OLAP allows one to check the observation point and parameter whose values exceed the
allowable level. The given function is implemented in the system ESPLA-M included into the automated working place
of an operator at the Regional Monitoring Center of the Krasnoyarsk Region [
        <xref ref-type="bibr" rid="ref14">16</xref>
        ].
      </p>
    </sec>
    <sec id="sec-5">
      <title>Conclusions</title>
      <p>Criteria for the hazard and threat identification have been developed based on systematizing the parameters of
comprehensive monitoring of the area safety. The numeric values of the intervals, which correspond to the safe functioning of
the regional social- natural-technogenic systems have been developed taking into account the regulations and guidance
documents and expert estimates. A method of using the criteria for the identification of hazardous situations has been
developed consisting in comprehensive analytical processing of the monitoring data.</p>
    </sec>
  </body>
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