<!DOCTYPE article PUBLIC "-//NLM//DTD JATS (Z39.96) Journal Archiving and Interchange DTD v1.0 20120330//EN" "JATS-archivearticle1.dtd">
<article xmlns:xlink="http://www.w3.org/1999/xlink">
  <front>
    <journal-meta />
    <article-meta>
      <title-group>
        <article-title>A method for evaluating geo-environmental technologies based on a weighted convolution of partial performance criteria in the Mathlab environment.</article-title>
      </title-group>
      <contrib-group>
        <contrib contrib-type="author">
          <string-name>Ekaterina V. Rusanova</string-name>
          <email>rusanovaev@mail.ru</email>
          <xref ref-type="aff" rid="aff0">0</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Evgeniy V. Runev</string-name>
          <xref ref-type="aff" rid="aff0">0</xref>
        </contrib>
        <aff id="aff0">
          <label>0</label>
          <institution>Emperor Alexander I St. Petersburg State Transport University</institution>
          ,
          <addr-line>9 Moskovsky pr., Saint Petersburg, 190031</addr-line>
          ,
          <country country="RU">Russia</country>
        </aff>
      </contrib-group>
      <fpage>92</fpage>
      <lpage>99</lpage>
      <abstract>
        <p>The present paper proposes a model for evaluating geo-ecological protection technologies based on multi-criteria optimization and weighted convolution criteria, on the basis of which the method of calculation is developed, allowing to determine the PQ factor for different objects according to the selected technologies using the Mathlab environment. The work demonstrated the application of the technique in the case of materials made of ash foam concrete with densities and ash content from the incineration of sewage sludge. The determination of the optimum composition of solopenobeton is relevant for the design of noise shields in railway transport. The proposed simulation algorithm in the Matlab environment makes it possible to use the procedure of processing the raw data, using several options of their input: in the form of tables of the format. csv or manual input.</p>
      </abstract>
      <kwd-group>
        <kwd>eol&gt;multi-criteria optimization</kwd>
        <kwd>collation of criteria</kwd>
        <kwd>Matlab</kwd>
        <kwd>geo-ecoprotective technologies</kwd>
        <kwd>PQ index</kwd>
      </kwd-group>
    </article-meta>
  </front>
  <body>
    <sec id="sec-1">
      <title>1. Introduction</title>
      <p>
        In today’s world, the development of waste-free
and low-waste technologies in industrial sectors and
transport infrastructures against the backdrop of the
crises in economic development is particularly
important: An environmentally and economically
sound approach to the development of new waste
management technologies1. [
        <xref ref-type="bibr" rid="ref1">1</xref>
        ], [
        <xref ref-type="bibr" rid="ref2">2</xref>
        ]. Methodologies
for assessing such waste management technologies
are also necessary [
        <xref ref-type="bibr" rid="ref3">3</xref>
        ], [
        <xref ref-type="bibr" rid="ref4">4</xref>
        ].
      </p>
      <p>
        Existing methods for the assessment of
geoenvironmental protection technologies [
        <xref ref-type="bibr" rid="ref5">5</xref>
        ], [
        <xref ref-type="bibr" rid="ref6">6</xref>
        ] do not
provide a complete picture of the technologies
proposed and often address only one group of
criteria. This approach does not provide an objective
assessment of all possible groups of criteria to be
taken into account by decision makers when using
the technology.
      </p>
      <p>Therefore, along with the development of new
geo-environmental protection technologies, an
integrated assessment model based on the full set of
existing criteria (environmental, technological and
other) is needed to provide an objective assessment
of the technology.</p>
      <p>
        A current problem is the creation of recycling
technologies and materials from waste products and
their further use in various industrial and transport
sectors. Waste ash from the incineration of sewage
sludge is one of the types of municipal waste that are
currently under-managed. The ash has an elevated
natural radiation background and is a source of dust
in landfills [
        <xref ref-type="bibr" rid="ref4">4</xref>
        ], [
        <xref ref-type="bibr" rid="ref7">7</xref>
        ].
      </p>
      <p>
        The recycling of such ash is therefore an
important issue in the housing and utilities sectors
and affects the environmental group of criteria for
the use of technologies [
        <xref ref-type="bibr" rid="ref8">8</xref>
        ].
      </p>
      <p>
        The percentage of sand content substituted by
ash, i.e. the replacement of one material - sand, with
another - with ash, is taken into account in the
assessment of the technology to be developed for the
recycling of ash from the incineration of sewage
sludge. The new material received the name ash
foam concrete [
        <xref ref-type="bibr" rid="ref9">9</xref>
        ], [
        <xref ref-type="bibr" rid="ref10">10</xref>
        ], [
        <xref ref-type="bibr" rid="ref11">11</xref>
        ], [
        <xref ref-type="bibr" rid="ref12">12</xref>
        ].
      </p>
      <p>
        This produced material (ash foam concrete) is
tested according to different process criteria. [
        <xref ref-type="bibr" rid="ref13">13</xref>
        ],
[
        <xref ref-type="bibr" rid="ref14">14</xref>
        ]. The use of recyclable material (ash) in the next
production cycle is also taken into account. The use
is to protect the public from noise in the railway
industry [
        <xref ref-type="bibr" rid="ref15">15</xref>
        ].
      </p>
      <p>The present paper proposes a model for
evaluating geoecoprotective technologies based on
multi-criteria optimization and weighted convolution
criteria. On the basis of this model, a calculation
methodology has been developed, which makes it
possible to determine the PQ factor for different
objects according to the selected technologies using
the Mathlab environment.</p>
      <p>
        The work demonstrated the application of the
technique in the example of materials made of ash
foam concrete, which are dense and containing ash
from incineration of sludge in an amount of 50% of
sand. The definition of the optimum composition of
ash foam concrete is relevant for the application in
the design of noise shields in railway transport [
        <xref ref-type="bibr" rid="ref4">4</xref>
        ].
      </p>
      <p>
        The entire chain of technology is suggested as a
sequence of processes: ash recycling, neutralizing its
harmful properties and reducing noise in populated
areas. [
        <xref ref-type="bibr" rid="ref19">19</xref>
        ].
      </p>
    </sec>
    <sec id="sec-2">
      <title>2. Problem statement</title>
      <sec id="sec-2-1">
        <title>Let’s define by possible groups</title>
        <p>Ws = ws1,...,wsjs – s − я</p>
        <p>W = W k</p>
        <p>s s=1
of criteria.</p>
        <p>the set of
Here</p>
        <p>is
the
group
of
criteria;
wsjs − js – й критерий s − й группы. After that,
 =  1 ,..., m  we mark the number of objects to be
examined using a group of criteria W . Каждому
элементу множества  – исследуемому объекту
сопоставим матрицу размерности k строк и
p столбцов. Здесь p – наибольшее количество
критериев по всем k группам ( p = max s ). The
1sk
elements of the matrix are the value of the
characteristics of the subject of the study according
to natural scale criteria. The rows of the matrix are
the values of the characteristics of the object on
natural scales of groups of criteria.</p>
        <p>Show the view shown here d :  → Mat(k, p) :
d ( j ) = X j =  ...</p>
        <p>
 xk1
... ... ...  (1),</p>
        <p>
... ... xkp 
where among the elements xil ( j ) occur and zero.
This means that there is no feature of the facility in
the group of criteria (such element in the matrix е
X j is replaced by zero).</p>
        <p>Next, each matrix X j compares a matrix Y j , the
elements of which are the values of the
characteristics of the objects on a single scale for all
criteria of the specified groups.</p>
        <p>As a single scale set, a segment is selected 0;1 .
This set is natural for multi-criteria optimization
applications, as the characteristics of the objects are
compared with the given values of the criteria, which
are numerically given by a point per segment 0;1 .</p>
      </sec>
    </sec>
    <sec id="sec-3">
      <title>2.1.Set of model objects</title>
      <p>The objects used are pure ash and molten ash of
different densities with 50% ash content from
incineration of sewage sludge (instead of sand).
Noise-proofing screens along the railways were
made of various densities of autoclave ash foam
concrete to protect the population from railway
noise:
1 – ashes from incineration of sewage sludge;
 2 –autoclave ash foam concrete, density of the
3
substance 500 kg m ;
 3 –autoclave ash foam concrete, density of the
3
substance 600 kg m ;</p>
      <p>3
substance 800 kg m .</p>
      <p> 4 –autoclave ash foam concrete, density of the
Thus, the set of objects being
 = 1,..., 4  is composed of four elements.</p>
    </sec>
    <sec id="sec-4">
      <title>2.2.Groups of criteria and criteria</title>
      <p>studied
model</p>
      <p>In the model of assessment of geo-ecological
technologies of manufacture autoclave ash foam
concreteya distinguish the following groups of
criteria:</p>
      <p>W – Environmental group;</p>
      <p>1
W2 – Technological group;</p>
      <p>W3 –Operational group.</p>
      <p>Several of the most relevant criteria for decision
makers are identified in each group.</p>
      <p>For an environmental group, these are:
w11 – content of natural radionuclides
w12 – dust content</p>
      <sec id="sec-4-1">
        <title>For the technology group, this is:</title>
        <p>w21 – thermal conductivity
w22 – strength
w23 – frost resistance
w24 – ash content
w25 – sound insulating ability
For the operating group it is:
w31 – noise level in built-up area</p>
      </sec>
    </sec>
    <sec id="sec-5">
      <title>2.3.Scale of criteria</title>
      <p>Consider the display d :  → Mat(k, p) (1) from
a set of objects to a set of matrices whose elements
set the properties of objects according to criteria
scales.</p>
      <p>Each object
matrix X j with
strings and
columns (here – number of groups of criteria, –
number of criteria per group, p = max s . In the rows
1s3
of the above matrix, the values of the characteristics
of the object are arranged according to groups of
criteria. In the case , for the set of investigated
objects referred to in paragraph 2.1  = 1,..., 4  ,
we have the following groups of criteria:
first group – s1 = 2 criteria;
second group – s2 = 5 criteria;
third group – s3 = 1 criteria.</p>
      <p>Here p = m1sax3 sk = max2,5,1 = 5 .</p>
      <p>To harmonize the dimensions, we assume that if
one or more criteria are not present in a group, the
corresponding matrix elements are replaced by 0.</p>
      <p>General type of such matrix for the case:
first group – s1 = 2 criteria; second group – s2 = 5
criteria; third group – s3 = 1 criteria; p = m1sax3 sk = 5
has the form:
d ( j ) = X j =  x21

 x31</p>
    </sec>
    <sec id="sec-6">
      <title>2.3.1. The numerical values of criteria characteristics</title>
      <p>The numerical values of the characteristics
according to the scale of criteria for objects of study
- samples from materials 1-4 are given in table 1
below.</p>
      <p>
        Standard methods conforming to the
requirements of the GOST were selected for
qualitative and quantitative analysis of the research
materials [
        <xref ref-type="bibr" rid="ref9">9</xref>
        ], [
        <xref ref-type="bibr" rid="ref10">10</xref>
        ].
      </p>
      <p>The data in table 3 are sample averages derived
from a series of sample experiments. The statistical
processing was done using the Mathlab environment.</p>
      <p>All the research was carried out in the centre
«Socrates» of the PGUPS; in the test laboratory
«Center of testing and certification of SPB»; in the
test laboratory of the radiation control of the Test
Center «PKTI-Stroistat». All organizations are
licensed.</p>
    </sec>
    <sec id="sec-7">
      <title>2.3.2. Natural scale according to criteria of objects</title>
      <p>The starting point in the search for an optimum
object that satisfies the groups of criteria and the
decision on the basis of which it can be used in
geoecological protection technologies is the
systematization of natural scales.</p>
      <p>Natural scales are to be understood as
measurements of the characteristics that determine
the physical properties of the materials of the tested
samples. Table 2 shows the natural scales with
measurement units for the criteria variables.</p>
      <p>Units of the international SI system and units of
measurement according to the GOST test standards
were used as units of change.</p>
      <p>Table 2 Natural scales of variables describing
criteria
)
)
)
s
t
i
n
u
Bq/kg
mg/m3
)
)
)
)
)
)
s
t
i
n
u
W/m2 °C</p>
      <p>MPa
cycles
kg/m3
dB
)
)
dB
s
t
i
n
u</p>
    </sec>
    <sec id="sec-8">
      <title>2.3.3. Limit values of the measurement scales</title>
      <p>In order to construct a universal scale with an
area of variation, the ranges of measurement
boundaries for each characteristic were fixed for all
criteria.</p>
      <p>For all the criteria, the following range
boundaries were selected:</p>
      <p>
        1) Natural radionuclides content (NRC) was
reviewed at intervals from 29 Bq/kg (the best value
of the interval is the background value
corresponding to the plaster natural stone as the
cleanest) until 740 Bq/kg (the worst value of the
interval corresponds to the samples allowed for use
in urban construction [
        <xref ref-type="bibr" rid="ref9">9</xref>
        ]). Best natural radionuclide
content criterion (29 Bq/kg) coincides with the right
limit of the universal scale, i.е. 1.
      </p>
      <p>2) The dust content was considered in the range
of 0 mg/m3 to 0.3 mg/m3 (norm maximum
permissible concentration). The best value
(corresponding to the ideal state of the system - total
absence of dust)- 0 mg/m3 is assigned a value of 1 in
the universal scale, the worst value (0.3 mg/m3) is
the value of 0 in the universal scale. The best (0
mg/m3) coincides with the right bound on the
universal scale.</p>
      <p>3) The thermal conductivity of the samples
shall be considered in the range of 0.07 W/m2 °C to
0.20 W/m2 °C. The best value for the heat
conductivity criterion (0.07 W/m2 °C) corresponds
to the right boundary of the universal scale.
4) The compression strength of the samples
shall be considered between 0 MPa and 35 MPa. The
best value on the compression strength criterion (35
MPa) corresponds to the right boundary of the
universal scale.</p>
      <p>5) Frost resistance, the property of the material
to damage resistance from the freezing-thaw cycle, is
measured in the number of cycles that will withstand
the material without damage. The scale of the
criterion in natural units of measurement ranges
from 5 cycles to 30 cycles. The best value for the
cold resistance criterion (30 cycles) corresponds to
the left boundary of the universal scale.</p>
      <p>6) The ash content of 1 m3 of material is
considered in the range of 0 to 500 kg/m3. The best
value for the ash content criterion (500 kg/m3)
corresponds to the right boundary of the universal
scale.</p>
      <p>7) The soundproofing capability of sound
shields from autoclave ash foam concreteA of
different density and thickness is determined by a
calculated method. It accepts values on a natural
scale from 0 dB to 49 dB. The best value for the
soundproofing capacity of the sample (49 dB)
corresponds to the right boundary of the universal
scale.</p>
      <p>8) Noise in populated areas was measured
before and after installation of the noise shield. This
criterion adopts values on a natural scale ranging
from 20 dB to 120 dB. The best value according to
the criterion «noise level in populated areas» (20 dB)
corresponds to the right border of the universal scale.</p>
      <p>Table 3 presents all boundaries with the specified
criteria measurement areas .</p>
      <p>For each criterion with a natural scale and a range
of values of a variable criterion, we construct a
display , here – number of groups of criteria,
– number of criteria, the field in a universal for all
criteria region-segment [0;1].</p>
      <p>Said map exhibits the property of strict
monotonicity and compares the lowest (highest)
value according to the natural scale of the lowest
(highest) according to universal:
strictly increasing function;
strict function.</p>
      <p>The type of monotony is determined by the
physical characteristics underlying the criteria.
– in the case of a
– in the case of a</p>
    </sec>
    <sec id="sec-9">
      <title>2.4.Matrix shapes</title>
      <p>Each object in the set Ѳ is a comparable matrix
, whose elements are the values of the variables of
all model criteria on a universal scale from a
segment [0;1]:</p>
      <p>где – a display introduced in 2.3.3,
which has the monotonicity pattern property.</p>
      <p>Here, the matrix is the variable
matrix for the groups of criteria of an object j.
.</p>
      <p>For sample 1 material, the matrix will be as
follows:
 0,249

Y1 =  0
 0,274
0
0
0
0
0
0
0
0
0
0 </p>
      <p>
0 
0 </p>
      <p>For sample 2 material, the matrix will be as
follows:
 0,964 1 0 0 0 
 
Y2 =  1 0,356 0,213 0,312 0,936
 0,861 0 0 0 0 </p>
      <p>For sample 3 material, the matrix will be as
follows:
 0,961 1 0 0 0 
 
Y3 =  0,962 0,520 0,524 0,437 0,944 
 0,876 0 0 0 0 </p>
      <p>For sample 4 material, the matrix will be as
follows:
 0,995 1 0 0 0 
 
Y4 =  0,740 0,842 0,860 0,685 0,956  .</p>
      <p> 0,891 0 0 0 0 </p>
      <p>The above matrices show experimental
measurement data (table 1) for the subjects of the
study, translated into a universal scale.
criteria
target</p>
      <p>The map , built
in the preceding paragraphs has a vector character. It
compares an object matrix whose elements are
characteristic values in natural scales to an object
matrix whose elements take values from a segment
[0;1] on a universal scale.</p>
      <p>the vector objective function whose
components are strictly monotone scalar functions.
Monotonicity is determined by the property of the
natural physical evaluation of the object (sample).</p>
      <p>As scalar target functions the continuous
bit-linear functions are selected. The choice of this
function class is motivated by the fact that the
investigated objects are classified into several
applications (e.g., materials in construction). The
number of sites where these functions are
continuously introduced according to the standards
of the application areas of the facilities under study.</p>
      <p>Based on the above conditions, two types of
functions are possible to satisfy scalar target
functions.</p>
      <p>Type 1: Piece-line, rigidly increasing functions
,
where – positive real numbers, –
range number .</p>
      <p>Type 2: Piece-by-piece - linear descending
functions
,
where – positive real numbers, –
range number .</p>
      <p>Ratios are defined from a system
of linear algebraic equations that results from the
bilateral continuity of functions at the
boundary points of the scale split ranges. Number of
equations in the system quantity equal .</p>
    </sec>
    <sec id="sec-10">
      <title>2.6.Weighted criteria consolidation of</title>
      <p>
        The next step in constructing the target function
using the criteria consolidation is to determine the
folding weights [
        <xref ref-type="bibr" rid="ref17">17</xref>
        ],[
        <xref ref-type="bibr" rid="ref18">18</xref>
        ],[
        <xref ref-type="bibr" rid="ref19">19</xref>
        ].
      </p>
      <p>In each group of criteria, the weight of the
criterion is determined taking into account the
importance of the criterion in the group.</p>
      <p>The relevance of the criterion is determined by
the method of peer review, the decision maker based
on standards, legislation, worldwide practice and
other technical information.</p>
      <p>For the weighting coefficients, the natural
(additive) normalization condition shall be met:
the sum of all weights in a fixed index shall
be one:
p
 kl = 1.</p>
      <p>l=1</p>
      <p>For the four objects considered in the work, for
which three groups of criteria are applied, and
weights have been determined, the data are listed in
table 4.</p>
      <p>The result of the weighted collation of criteria in
each group is the targeted collation function :
,
где – weight vector of criteria
in k group, аnd – rows of matrix
function with bit-linear components.</p>
      <p>Each component is defined by linear
functions defined on separate ranges of the scales of
the corresponding criteria.</p>
      <p>The result of applying weighted convolution of
criteria to the samples under consideration is given
in table 5.</p>
      <p>In table 6 the values of the folding functions are
specified for k groups of criteria. Because
there are large computations with multivariate
datasets in work (k groups, criteria in the group,
line functions, linear function coefficients),
the numerical values of the folding functions were
obtained using the Mathlab environment.</p>
    </sec>
    <sec id="sec-11">
      <title>2.7.Weighted grouping of criteria</title>
      <p>Consider the weight vector of the groups of
criteria , where weights are
derived from the ratio
 j = ks j
 s j
j=1
where s j - peer review group of criteria number j.</p>
      <p>For multiple objects to be considered with three
(k=3) the groups of criteria are shown in the table
(table 6) weight vector values .</p>
      <p>Table 6 shows that when materials are used in
geo-ecological protection technologies, the
environmental group of criteria has the greatest
weight. This should be borne in mind by decision
makers.
где - weight vector of criteria in
group number j.</p>
      <p>Calculations with the specified bundles for
different objects are carried out in the Mathlab
environment using algorithms for processing
multivariate data arrays.</p>
      <p>
        These algorithms allow the data to be used
immediately after measurement experiments and to
find target function values for any number of
experimental samples. It saves time and
computational complexity [
        <xref ref-type="bibr" rid="ref23">23</xref>
        ].
      </p>
    </sec>
    <sec id="sec-12">
      <title>2.8.Optimal solution</title>
      <p>On the Figure 1 shows the weighted totals of the
criteria groups as a column chart.</p>
      <p>The proposed model, based on weighted totals of
criteria, makes it possible to compile as a method of
calculating the target functions of PQ-factors
according to individual optimality criteria. And how
to calculate the PQ factors of the group of criteria
with the aim of constructing an optimal solution for
recommending a decision on the use of materials in
the creation of geo-environmental protection.</p>
      <p>The final result of the work is an algorithm
implemented in the Mathlab environment with
processing of multivariate data sets, which can be
used for a wide class of tasks of estimation of
different technologies under conditions of
decisionmaking with full information on different groups of
criteria.</p>
    </sec>
    <sec id="sec-13">
      <title>3. Acknowledgements</title>
      <p>The authors express their gratitude to their
colleagues at the University of Petersburg for the
communication ways of Emperor Alexander I for
many years of fruitful cooperation, which led to the
emergence of interesting ideas in approaches to
solving various applied problems, particularly
relevant in today’s environment, such as modelling
the reliability and stability of systems/</p>
      <p>We also express our gratitude to the departments
«Water supply, drainage and hydraulics»,
«Engineering chemistry and natural history»,
«Higher mathematics», «Informatics and
information security» for the friendly warm
atmosphere, Continuous discussion and creative
search in solving emerging applications.</p>
      <p>We shall mark the high contribution to the
organization and holding of the seminar «Models
and Methods for Researching Information Systems
in Transport» by the employees of the department
«Information and computing systems».</p>
    </sec>
  </body>
  <back>
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