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    <title>DSpace Community:</title>
    <link>http://dspace.dtu.ac.in:8080/jspui/handle/123456789/86</link>
    <description />
    <items>
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        <rdf:li rdf:resource="http://dspace.dtu.ac.in:8080/jspui/handle/repository/22979" />
        <rdf:li rdf:resource="http://dspace.dtu.ac.in:8080/jspui/handle/repository/22690" />
        <rdf:li rdf:resource="http://dspace.dtu.ac.in:8080/jspui/handle/repository/22517" />
        <rdf:li rdf:resource="http://dspace.dtu.ac.in:8080/jspui/handle/repository/21748" />
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    <dc:date>2026-07-23T11:00:20Z</dc:date>
  </channel>
  <item rdf:about="http://dspace.dtu.ac.in:8080/jspui/handle/repository/22979">
    <title>STATUS OF GROUNDWATER QUALITY IN LUDHIANA  DISTRICT OF PUNJAB, INDIA</title>
    <link>http://dspace.dtu.ac.in:8080/jspui/handle/repository/22979</link>
    <description>Title: STATUS OF GROUNDWATER QUALITY IN LUDHIANA  DISTRICT OF PUNJAB, INDIA
Authors: GOYAL, DEEPALI; Singh, S.K. (SUPERVISION); Haritash, A.K. (CO-SUPERVISOR)
Abstract: The present study provides an integrated assessment of groundwater quality in &#xD;
Ludhiana district, Punjab, based on 152 groundwater samples characterized by 18 &#xD;
physicochemical parameters. These were synthesized into a Drinking Water Quality &#xD;
Index (WQI) to evaluate potable suitability. The WQI classification shows that 2.6% &#xD;
of samples are “excellent” and 57.9% “good,” whereas 32.9%, 4.0%, and 2.6% fall &#xD;
into “poor,” “very poor,” and “unsuitable” categories, respectively, indicating spatially &#xD;
heterogeneous degradation in groundwater quality. &#xD;
Hydrogeochemical characterization, supported by facies diagrams, ionic &#xD;
diagnostics, saturation indices, and multivariate statistics, indicates that groundwater &#xD;
chemistry is primarily governed by carbonate and silicate weathering, with active &#xD;
cation exchange. Saturation indices show that groundwater is generally supersaturated &#xD;
with respect to calcite, dolomite, and aragonite, and undersaturated with respect to &#xD;
halite, fluorite, and sylvite. Spatial variability in nitrate and other key parameters &#xD;
reflects localized agricultural and urban influences, while IDW interpolation in QGIS &#xD;
has been used to generate spatial distribution maps of major ions. &#xD;
In the present study, irrigation suitability has been evaluated using salinity, &#xD;
sodicity, and carbonate–bicarbonate hazard indices, including EC, %Na, SAR, and PI. &#xD;
In addition, an Irrigation Water Quality Index (IWQI) is computed using EC, SAR, &#xD;
Na⁺, Cl⁻, and HCO₃⁻ concentrations. Salinity classification indicates that 62.5% of &#xD;
samples fall within the “medium” EC range (250–750 µS/cm), while 37.5% fall within &#xD;
the “high” category. Hazard assessment indicates that 75% of samples fall within the &#xD;
excellent-to-permissible range based on %Na, 97.4% belong to the S1 class (low &#xD;
sodicity) based on SAR, and all samples fall within PI Classes I–II. However, IWQI&#xD;
based classification indicates irrigation constraints, with 21.7% of samples under &#xD;
“severe restriction” (IWQI &lt; 40), 37.5% under “high restriction” (40–55), 33.6% under &#xD;
“moderate restriction” (55–70), and only 7.2% under “low restriction” (70–85). IDW&#xD;
based GIS mapping delineates zones of elevated irrigation risk, particularly in eastern &#xD;
Samrala and Khanna, parts of Ludhiana II and Machhiwara, and southern to western &#xD;
xvi &#xD;
Pakhowal and Sidhwan Bet, whereas low-restriction pockets are confined to limited &#xD;
villages such as Sherpur Kalan, Bardeke, Hathur, and Dholanwal. &#xD;
An ANN-based predictive model for IWQI is developed using the multilayer &#xD;
perceptron architecture in IBM SPSS with standardized inputs. The optimal network &#xD;
includes five input neurons (EC, SAR, Na⁺, Cl⁻, HCO₃⁻), two hidden layers, and one &#xD;
sigmoid-activated output neuron, trained using batch learning and gradient-descent &#xD;
backpropagation. The model achieved RMSE values of 0.09 for training and 0.07 for &#xD;
testing, indicating strong predictive performance and close agreement between &#xD;
observed and simulated IWQI values. Sensitivity analysis shows that Cl⁻ has the &#xD;
highest normalized importance (100%), followed by SAR (59.7%), Na⁺ (58.5%), &#xD;
HCO₃⁻ (53.1%), and EC (27.2%), confirming the dominant influence of salinity and &#xD;
sodicity on irrigation water quality. &#xD;
Additionally, nitrate distribution has been examined to distinguish regional &#xD;
hydrogeological controls from localized anthropogenic influences. The weak &#xD;
statistical association between nitrate concentration and hydraulic parameters indicates &#xD;
that regional groundwater flow is not the principal control on nitrate occurrence. The &#xD;
lack of a coherent downgradient nitrate plume suggests that nitrate distribution is &#xD;
governed mainly by localized recharge and anthropogenic inputs. A conservative &#xD;
nitrate-transport scenario simulated by coupling the calibrated transient MODFLOW &#xD;
flow model with MT3D-USGS shows a decline in mean nitrate concentration from &#xD;
8.86 mg/l in Year 1 to 6.51 mg/l in Year 10 (~27% reduction), contraction of the &gt;45 &#xD;
mg/l footprint from ~1.70% to ~0.88%, and a reduction in peak concentrations to a &#xD;
maximum simulated value of ~69.95 mg/l after 10 years.</description>
    <dc:date>2026-05-01T00:00:00Z</dc:date>
  </item>
  <item rdf:about="http://dspace.dtu.ac.in:8080/jspui/handle/repository/22690">
    <title>STUDY OF AEROSOLS IN INDOOR - OUTDOOR MICROENVIRONMENTS FOR URBAN HOUSEHOLDS OF DELHI</title>
    <link>http://dspace.dtu.ac.in:8080/jspui/handle/repository/22690</link>
    <description>Title: STUDY OF AEROSOLS IN INDOOR - OUTDOOR MICROENVIRONMENTS FOR URBAN HOUSEHOLDS OF DELHI
Authors: SHARMA, MONIKA; Mishra, Rajeev Kumar (SUPERVISOR); Khare, Mukesh (CO-SUPERVISOR)
Abstract: Rapid urbanization increases the population density in urban regions, which&#xD;
compromises the standard of living. Indoor air quality in urban regions is a serious&#xD;
concern. To understand the indoor air quality in residential homes of one of the India’s&#xD;
most polluted cities, Delhi. This is a region where detailed studies remain scarce,&#xD;
especially in residential context. This study analyzed the concentration of indoor&#xD;
particulate matter and particle number concentration in urban clusters where significant&#xD;
socioeconomic differences exist within the same geographical domain. To understand&#xD;
the indoor air quality in residential homes of one of the India’s most polluted city, Delhi.&#xD;
This is a region where detailed studies remain scarce, especially in residential context.&#xD;
This study also estimated the seasonal variations of indoor and outdoor particle number&#xD;
concentrations in different socioeconomic household conditions in the urban city Delhi.&#xD;
This study investigated the impact of festival activities on household indoor air quality&#xD;
in megacity Delhi. The study included different phases and activities during the festival&#xD;
and normal conditions and analysed the impact of different emissions. The portable&#xD;
aerosol spectrometer was employed to measure quasi-ultrafine, sub-fine, fine, and coarse&#xD;
particle concentrations in the kitchen, bedroom, and outdoor conditions. Indoor air&#xD;
quality is crucial for the well-being of residents, as people spend 80% of their time&#xD;
indoors.&#xD;
Particulate matters (PM10, PM2.5, and PM1) were measured in two major indoor&#xD;
microenvironments (kitchen and bedroom) along with outdoors of the selected&#xD;
households during winter, summer, and monsoon seasons. Four major income groups&#xD;
were considered for the study. A poorly ventilated kitchen was found to have higher&#xD;
concentrations of PM10 (247 μg/m3), PM2.5 (200 μg/m3), and PM1 (153 μg/m3),&#xD;
respectively. Indoor, PM1 contributed ~40 to 85 % to PM10. During winter, the seasonal&#xD;
mean I/O ratio of PM10, PM2.5, and PM1 ranged between 1.1 and 1.8 in bedroom and&#xD;
between 0.8 and 2.2 in kitchen. The influence of outdoor particulate matter concentration&#xD;
on indoor air was observed to be high during winter, followed by summer and monsoon.&#xD;
The higher concentration in kitchen leads to an exposure of 0.10 μg, and in bedroom, it&#xD;
was 0.11 μg for adults with a higher breathing rate. The exposure depends on the&#xD;
xi&#xD;
concentration and exposure time. The PM2.5 depositions were found more in the lower&#xD;
lung regions.&#xD;
The findings of the study revealed that quasi-ultrafine (250 to 500 nm) particle&#xD;
concentration was high (2.1×106 #cm-3) in urban poor households during the winter&#xD;
season. Indoor quasi-ultrafine particle concentration ranged between ~105–106 #cm-3 in&#xD;
the kitchen and bedroom. In a properly ventilated kitchen, a significant reduction in&#xD;
indoor particle number concentration (1.2×106 #cm-3 to 7.1×105 #cm-3) was observed.&#xD;
The number concentration of coarse particles was found to be the lowest (&lt; 1.1×103 #cm-&#xD;
3) among other sizes. However, indoor sources resulted in a higher I/O ratio of 40. Lower-&#xD;
income group kitchens exhibited a higher number concentration of different-sized&#xD;
particles, which also influenced bedroom concentration.&#xD;
During the festival period, the indoor ultrafine particle concentration was found to be 6.7&#xD;
× 104 #cm-3, which was the highest observed indoor concentration throughout the study.&#xD;
The particle number concentration of the nanoparticles in indoor environment ranged&#xD;
from 104 to 105 #cm-3. Ultrafine size range particles contributed up to 85% to the total&#xD;
particle numbers. Fireworks contributed to higher particle numbers in indoors, followed&#xD;
by cooking, dusting, and worshiping. The size distribution pattern of the particles emitted&#xD;
during cooking activities and fireworks were found to be different. Particle size range 10&#xD;
to 30 nm contributed 31 % to total particle numbers on fireworks day, whereas on a&#xD;
normal day, it contributed only 13 %. During a normal day, 100 to 1000 nm size particles&#xD;
contributed ~50 % to the total particle numbers. The diurnal pattern of the indoor&#xD;
environment was different to the outdoor. The outdoor fireworks activities also&#xD;
influenced indoor pollutants with respect to trace metals, which makes the indoor air&#xD;
quality more toxic and affects the occupants' health.&#xD;
Indoor particle number concentration (PNC) varies significantly in different&#xD;
microenvironments. Cooking, dusting, and incense stick burning are major indoor&#xD;
activities that generate different-sized particle numbers. The number concentration of the&#xD;
quasiultrafine particles (qUFP) was found to be a maximum of (106 #cm-3), followed by&#xD;
subfine (105 #cm-3), fine (104 #cm-3), and coarse (103 #cm-3) particles. The winter season&#xD;
exhibits a higher decay period of particles in indoor. The number concentration of&#xD;
xii&#xD;
particles observed during nighttime was higher than the concentration during daytime.&#xD;
The particles generated during cooking took more time to decay, up to 320 minutes,&#xD;
followed by dusting (120 to 300 minutes) and incense stick usage (&lt; 200 minutes).&#xD;
Roasting, stir frying, and gravy preparation emit a higher concentration of qUFP (4 to&#xD;
5×106 #cm-3) and sub-fine (6 to 8×105 #cm-3) particles. More fine particles were&#xD;
generated during stir-frying (3×104 #cm-3) and coarse particles (2×103 #cm-3) were&#xD;
emitted at high levels during roasting. The boiling method of cooking generates a very&#xD;
less number of qUFP and subfine particles (&lt; 105 #cm-3). The measured particle number&#xD;
concentration linearly correlated with particulate matter, and the influence of indoor&#xD;
sources was found to be more in the studied microenvironments. Indoor number&#xD;
concentrations were found to be higher than in the outdoor environment. Households&#xD;
with good infrastructure conditions were found to have less influence on one&#xD;
microenvironment than another. Improving indoor air quality relies not only on sources&#xD;
but also on ventilation status, built infrastructure, occupants’ behaviour, and the influence&#xD;
of outdoor air. Since people spend the majority of their time indoors, it will be more&#xD;
vulnerable to residents. Indoor pollution in households needs to be mitigated and&#xD;
regulated for a better standard of living.</description>
    <dc:date>2026-02-01T00:00:00Z</dc:date>
  </item>
  <item rdf:about="http://dspace.dtu.ac.in:8080/jspui/handle/repository/22517">
    <title>A COMPARATIVE STUDY ON SIZE SEGREGATED ULTRAFINE PARTICLE CONCENTRATION AND ITS TEMPORAL DISTRIBUTION IN URBAN AND BACKGROUND REGIONS</title>
    <link>http://dspace.dtu.ac.in:8080/jspui/handle/repository/22517</link>
    <description>Title: A COMPARATIVE STUDY ON SIZE SEGREGATED ULTRAFINE PARTICLE CONCENTRATION AND ITS TEMPORAL DISTRIBUTION IN URBAN AND BACKGROUND REGIONS
Authors: MOHAN, VIGNESH
Abstract: In developing countries like India, air pollutants have become a serious issue.&#xD;
Industrialization and urbanization have greatly boosted the Indian economy. On the&#xD;
other hand, they have also brought about a drastic change in the environment. Due to&#xD;
various natural and anthropogenic activities, different pollutants are released into the&#xD;
atmosphere. Air pollution is still a major problem faced by the whole world, resulting&#xD;
in 6.2 million deaths throughout the world and 6,20,000 premature deaths in India&#xD;
alone. The alarming increase in air pollutants, with its intensity on the higher side, has&#xD;
resulted in numerous health issues and lung diseases, including chronic respiratory&#xD;
disorders, pneumonia, acute asthma, and shortness of breath. Although technological&#xD;
advancements have improved our understanding of ultrafine particles and air quality,&#xD;
many environmental conditions and scientific problems remain unresolved. Ultrafine&#xD;
particles in the atmosphere are formed due to natural and anthropogenic activities,&#xD;
including photochemical reactions and combustion processes. Atmospheric aerosols&#xD;
persist in solid or liquid form and significantly impact a region’s air quality,&#xD;
contributing to climate change and affecting human health. The concentration of the&#xD;
ultrafine particles in a region is highly dependent on the intensity of the emission&#xD;
sources, represented by the number concentration. The ultrafine particle concentration&#xD;
is quantified in terms of particle number concentration (PNC) per unit volume of air,&#xD;
expressed as the number of particles per cubic centimeter (cm3). Ultrafine particles are&#xD;
considered a universal carrier of a wide variety of toxic chemicals to humans. The&#xD;
deposition of particles in the human respiratory system varies based on the size of the&#xD;
particles, which are categorized into nucleation, Aitken, and accumulation modes.&#xD;
Also, the concentration of these particles signifies the emission sources in a particular&#xD;
region. These can enter the deeper regions of the respiratory system, such as the&#xD;
alveoli, and can be transported to the circulatory system, allowing them to reach any&#xD;
organ in the body. This study analyzes the year-long measurements of particle number&#xD;
size distribution (10.21-1090.23 nm) in 2022 in the urban traffic corridor of the&#xD;
megacity Delhi. The study examined particle number concentration in the ultrafine&#xD;
(&lt;100 nm) and accumulation (100-1000 nm) ranges during both day and night, in terms&#xD;
of the source's intensity, emission patterns, and local meteorological conditions.&#xD;
Further, the ultrafine particles (&lt; 100 nm) are separated into three mode size fractions&#xD;
xi&#xD;
(Nnuc, Natk, and Nacc) were also considered, and the data set was analyzed for the&#xD;
different meteorological periods and day and night time in terms of sources and type&#xD;
of emission (from CNG, petrol, and diesel vehicular exhaust) and meteorology.&#xD;
Nucleation mode particles (Nnuc, 10-30 nm) contributed ~50% during the daytime in&#xD;
the summer period due to increased fresh traffic emissions. During the daytime,&#xD;
particle concentration was dominated by smaller sizes, such as nucleation mode&#xD;
particles (Nnuc, 30-100 nm), while at nighttime, the particles were found in the Aitken&#xD;
and Accumulation (Nacc, 100-1000 nm) modes. Nnuc and Natk were reduced by ~45%&#xD;
and 4% at night, while Nacc increased by ~34%. The mean normalized particle number&#xD;
size distribution confirmed these findings, showing clearly that Nnuc dominated during&#xD;
the daytime, especially during peak rush hours, and at night, particle concentration&#xD;
increased up to the size of 300 nm particles. The particle number size distribution and&#xD;
the changes experienced in the percentage concentration of the different particle size&#xD;
ranges highlight the role of engine exhaust emissions in the atmospheric particles&#xD;
contributed in urban areas. The study's findings help identify the intensity and behavior&#xD;
of different sources during the day and nighttime, which can inform policy formulation&#xD;
and decision-making to mitigate air quality and its associated health impacts.&#xD;
The study measured and analysed the particle number concentration of&#xD;
particles ranging from 10 nm to 800 nm in urban and background sites. The aim of the&#xD;
study is to estimate the role of anthropogenic sources in urban regions in terms of&#xD;
number concentration. The study finds that the particle number concentration in an&#xD;
urban site is ~8 times higher than in the background sites. At the urban site, the Aitken&#xD;
and Nucleation modes contributed more to the total particle concentration, whereas at&#xD;
the background site, it was the Aitken and Accumulation modes. The annual average&#xD;
concentrations at the urban and background sites were 2.5 x 104, 2.9 x 103 cm-3,&#xD;
respectively. Aitken-mode particles dominated both in the urban and background sites,&#xD;
with the lowest concentrations observed in the summer (6.4 x 102 cm-3) and monsoon&#xD;
periods (1.09 x 102 cm-3), respectively. The diurnal concentration illustrates the role of&#xD;
transportation emissions at the urban site and the natural process of particle&#xD;
condensation at the background site. The long-range transportation of sources&#xD;
indicates that during the winter and autumn seasons, the westerly and north-westerly&#xD;
winds bring biomass burning emissions smoke to the urban region, which is less visible&#xD;
xii&#xD;
in the background conditions.&#xD;
Road traffic emissions are often identified as the leading source of ultrafine&#xD;
particles in urban environments. However, recent international studies have revealed&#xD;
that in cities with elevated solar radiation, the occurrence of new particle formation&#xD;
events may also significantly contribute to the levels of ultrafine particles. To assess&#xD;
the frequency and effects of these events, a comprehensive study was carried out in&#xD;
Delhi from January to December 2022. The analysis showed that the highest mean&#xD;
concentration of total particle number concentration (Ntot) followed the order of Post-&#xD;
Monsoon &gt; Winter &gt; Monsoon &gt; Summer. The Aitken particle contribution (Natk) to&#xD;
Ntot was approximately 52% on event days and 46% on non-event days. Throughout&#xD;
the year, 23 new particle formation (NPF) events were identified, accounting for 6%&#xD;
of the total days, which included 2 nocturnal and 21 midday occurrences. During the&#xD;
nocturnal events, ammonia levels increased by about 34%, which aids in the growth&#xD;
of newly formed particles. The remaining NPF events predominantly occurred during&#xD;
daylight hours, when solar radiation was a crucial factor in particle generation. The&#xD;
highest growth rates were observed in winter (12.07 ± 1.07 nm h-1), while the&#xD;
condensation sink (cs) was highest in the post-monsoon period (0.087 ± 0.039 s-1). The&#xD;
presence of larger pre-existing particles during the post-monsoon season appeared to&#xD;
hinder formation rates but enhance particle growth. An increase in particle numbers&#xD;
was associated with a decrease in the condensation sink throughout the day. Winds&#xD;
from the northwest direction were conducive to new particle formation, coinciding&#xD;
with increased solar radiation and temperature, alongside a decrease in relative&#xD;
humidity. In summary, although traffic remains the predominant source of ultrafine&#xD;
particles (UFP) in urban areas, urban nucleation events also represent a significant&#xD;
source of UFP. A future decline in traffic-related particle concentrations is expected;&#xD;
however, an increase in nucleation events in urban areas is likely due to the reduced&#xD;
capacity of urban condensation sinks.&#xD;
The festival of Diwali, characterized by extensive fireworks displays in India,&#xD;
significantly contributes to the increase of atmospheric particles over a brief period,&#xD;
thereby compromising air quality. Implementing short-term measures, such as&#xD;
prohibiting the use of firecrackers during these celebrations, can enhance urban air&#xD;
quality. This study examined particle number concentrations ranging from 10 nm to&#xD;
xiii&#xD;
1000 nm during the years 2021 and 2022. A notable decrease in particle number&#xD;
concentration was recorded, dropping from 3.8 x 104 cm-3 to 3.1 x 104 cm-3, following&#xD;
the ban on firecrackers in Delhi. The concentration range shifted from 105 cm-3 to 104&#xD;
cm-3. The analysis of various size categories, Nucleation (10 nm to 30 nm), Aitken (30&#xD;
nm to 100 nm), and Accumulation (100 nm to 1000 nm), revealed that on Diwali day,&#xD;
Accumulation mode particles accounted for approximately 60% to 83% of the total&#xD;
particle number concentration. Furthermore, the total inhalable particle concentration&#xD;
exposure on Diwali day was reduced by about 18%, equating to 1.6 million particles&#xD;
per day. The findings of this study indicate that significant reductions in emissions&#xD;
within urban environments can be achieved through effective policy implementation&#xD;
and active citizen engagement. Lowering particle emissions is crucial for enhancing&#xD;
air quality, minimizing health risks, and promoting sustainability. The overarching&#xD;
sustainability objectives emphasize the necessity of clean air for all, while health&#xD;
improvements in polluted areas represent achievable interim goals through the&#xD;
execution of appropriate mitigation strategies, which also contribute to combating&#xD;
climate change.</description>
    <dc:date>2025-11-01T00:00:00Z</dc:date>
  </item>
  <item rdf:about="http://dspace.dtu.ac.in:8080/jspui/handle/repository/21748">
    <title>STUDY OF NANO-SIZE PARTICLE DYNAMICS IN URBAN ROAD  MICROENVIRONMENT IN DELHI</title>
    <link>http://dspace.dtu.ac.in:8080/jspui/handle/repository/21748</link>
    <description>Title: STUDY OF NANO-SIZE PARTICLE DYNAMICS IN URBAN ROAD  MICROENVIRONMENT IN DELHI
Authors: RAJAGOPAL, KANAGARAJ
Abstract: Due to rapid urbanization, Delhi experiences frequent pollution events, and the particulate &#xD;
matter load exceeds the prescribed limit often. This study analyzes nanoparticle (10 to &#xD;
1090 nm) during different emission scenarios, seasonal and meteorological conditions in &#xD;
two phases: April to June 2021 (Period I) and October to November 2021 (Period II). &#xD;
Period I experienced around 31% less concentration of particles (~2.4 × 104&#xD;
cm-3&#xD;
) due to &#xD;
lockdown restrictions and, on the other hand, particle concentration increased by 35% &#xD;
compared to normal conditions due to the sudden rise in firework emissions in Period II. &#xD;
Except for the post-Diwali phase (104&#xD;
cm-3 to 105&#xD;
cm-3&#xD;
), the concentrations lie between &#xD;
103&#xD;
cm-3&#xD;
and 105&#xD;
cm-3&#xD;
. The Aitken modes contribute 10 to 30% of total concentration in &#xD;
both periods. Particles in nucleation and accumulation modes contribute 30 to 40%, 20 to &#xD;
30%, 15 to 25%, and 35 to 50% in Periods I and II, respectively. Concentration and &#xD;
behavior of nano particles in different seasons (winter, spring, summer, monsoon, and &#xD;
autumn) are examined, for the first time. Concentration of particles is classified into four &#xD;
different sizes as Nnuc (10 to 30 nm, nucleation), Nsatk (30 to 50 nm, small Aitken), Nlatk&#xD;
(50 to 100 nm, large Aitken), and Nacc (100 to 1000 nm, accumulation mode), and the &#xD;
total (10 to 1000 nm) particle number concentration (PNC) as Ntotal. PNC ranges between &#xD;
104&#xD;
cm-3&#xD;
and 106&#xD;
cm-3&#xD;
over Delhi during the year, and the highest concentration occurs in &#xD;
winter. Winter concentration is 2 times higher than monsoon, summer, autumn and spring &#xD;
concentrations, respectively. Nnuc, Nsatk, Nlatk and Nacc and their respective contributions &#xD;
to total PNC exhibit significant seasonal variations. During winter Nlatk and Nacc&#xD;
contribute more to total PNC due to coagulation, with Nacc alone contributing &gt;40% to &#xD;
total PNC. Nnuc, Nsatk, and Nlatk are higher in spring and summer during mid-day due to &#xD;
nucleation and/or ultrafine particle burst events. The direct primary emissions from &#xD;
engine exhaust produce a prominent double hump structure during morning and evening &#xD;
ix&#xD;
peak hours in winter and autumn. PNC and their contributions exhibit day-night &#xD;
variations as they are influenced by emission sources and variations in meteorological &#xD;
parameters (wind speed, relative humidity, temperature, solar radiation and boundary &#xD;
layer height) between day and night. Carbon monoxide correlates positively with Nacc in &#xD;
all seasons (R2~0.5) as fossil fuel emission is predominant source for gases and particles &#xD;
in study environment. The concentration of UFP size range particles is dominantly higher &#xD;
(70 to 80%) during peak hours than the non-peak hours. The variations in particle number &#xD;
concentration depend on the intensity and emissions of sources during peak, and non peak hours. UFP contributes ~60 to 80% to the total particle number concentration in the &#xD;
urban roadside microenvironment, and its contribution increases during peak hours. &#xD;
During the winter season, the average total particle number concentration was observed &#xD;
to be maximum (4.1 × 104&#xD;
cm-3&#xD;
) with a higher surface area of particles of 3.5 × 10-3 mm2m 3&#xD;
. Compared to the monsoon season, the concentration of NOX was 5 times higher in &#xD;
winter. The boundary layer height in the study region ranged from 600 to 2400 m during &#xD;
different seasons, and the maximum ventilation coefficient was observed to be &gt;3000 &#xD;
m2s-1 during summer. Precipitation reduced the concentration of particles by half, from &#xD;
2.2 x 104&#xD;
to 1.1 x 104&#xD;
cm-3&#xD;
, due to wet scavenging. The study revealed that the &#xD;
concentrations of particles depend not only on primary emissions but also are influenced &#xD;
by local meteorology and other co-emitted pollutants. The Multiple Path Particle &#xD;
Dosimetry (MPPD) model simulated values show that the order of deposition goes as &#xD;
alveoli &gt; bronchiole &gt; bronchus. The deposition in the study area ranges between 10 and &#xD;
18 million nanoparticles during different hours of the day, whereas the estimated &#xD;
inhalable particles vary between 0.5 to 1 billion. The concentration of total inhalable &#xD;
particles and the actual particles deposited in the lung varies. The seasonal sequence of &#xD;
deposition of nanoparticles is winter &gt; monsoon &gt; summer &gt; autumn &gt; spring. The &#xD;
x&#xD;
deposition of nanoparticle in adults is 30 to 40% higher than in children and infants, and &#xD;
further, the deposition is higher in the alveolar region than in the bronchiole and trachea &#xD;
regions. About 90% of the particles get deposited in the alveolar regions, 6 to 8% in the &#xD;
bronchiole region, and 2% in the trachea region. The estimated deposition of &#xD;
nanoparticles for an individual working 8 hours a day in the near road conditions is 338 &#xD;
µg/year in Delhi. The deposition increases almost linearly as a function of time, and is 3 &#xD;
times higher (1016 µg/year) for a person residing near the road throughout the day (24 &#xD;
h). The deposition fraction of particles ranges between 0.05 and 0.10 µg/day in alveolar &#xD;
region, &lt;0.05 µg/day in the bronchiole region, and lies between 0.02 and 0.04 µg/day in &#xD;
the trachea. The nanoparticles deposited in the respiratory system can lead to the &#xD;
development of various diseases such as asthma, chronic obstructive pulmonary disease, &#xD;
and can lead to carcinogenicity. Number concentration-based studies are essential for &#xD;
estimating the potential impacts on human health due to air pollution. The study provides &#xD;
information regarding vehicle emission-based particle concentration under various &#xD;
emission scenarios in urban cities, which is crucial for estimation of emissions, health &#xD;
impact assessment, future policy formulation and strategy measures. These quantitative &#xD;
results on seasonal variations of air pollutants together with the knowledge on seasonal &#xD;
variations in meteorological parameters and atmospheric dynamics provide a foundation &#xD;
which can positively contribute to the planning and devising mitigation measures aimed &#xD;
at improving air quality and public health. The study provides new insights on inhalable &#xD;
particle concentration during the day that are crucial for strategy development, emission &#xD;
mitigation, and health hazard assessment for the citizens. Understanding the dynamics of &#xD;
atmospheric nanoparticles in urban roadside environments provides on the deposition of &#xD;
nanoparticles in humans residing near roadside conditions are crucial to estimate the &#xD;
xi&#xD;
human health risk potential, and to formulate mitigation measures for exposure reduction &#xD;
which can result in a better and sustainable future.</description>
    <dc:date>2025-05-01T00:00:00Z</dc:date>
  </item>
</rdf:RDF>

