Difference between revisions of "IS428 AY2019-20T1 Assign Fresi"

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== Interactive Visualization ==
 
== Interactive Visualization ==
<p>The visualization platform can be accessed here: TO BE UPDATED</p>
+
<p>The visualization platform can be accessed here: https://public.tableau.com/profile/fresi3383#!/vizhome/Fresi_VASTChallenge_MiniProject2/HomeDashboard</p>
  
 
=== Home Dashboard ===
 
=== Home Dashboard ===
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</center>
 
</center>
 
|| <center>[[File:Fresi_Fig2.2.png|600px|center]]</br>Figure 2.2</center>
 
|| <center>[[File:Fresi_Fig2.2.png|600px|center]]</br>Figure 2.2</center>
 
  
 
|-
 
|-
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|| <center>Third, mobile sensors 18, 20, 38, 39, 43, 44, 47 and 48 displayed random variation and spikes of varied radiation measures, which should be within the healthy radiation bound before the quake happened. Also, sensor-id 18 stopped recording from 8 April 2020, 1623 to 9 April 1243. Last, sensor-id 43 showed a discrete drop in radiation from 10 April 1320 to 1535. /center>
 
|| <center>Third, mobile sensors 18, 20, 38, 39, 43, 44, 47 and 48 displayed random variation and spikes of varied radiation measures, which should be within the healthy radiation bound before the quake happened. Also, sensor-id 18 stopped recording from 8 April 2020, 1623 to 9 April 1243. Last, sensor-id 43 showed a discrete drop in radiation from 10 April 1320 to 1535. /center>
 
|| <center>[[File:Fresi_Fig2.3.png|600px|center]]</br>Figure 2.3</center>
 
|| <center>[[File:Fresi_Fig2.3.png|600px|center]]</br>Figure 2.3</center>
 
  
 
|-
 
|-
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</center>
 
</center>
 
|| <center>[[File:Fresi_Fig2.4.png|600px|center]]</br>Figure 2.4</center>
 
|| <center>[[File:Fresi_Fig2.4.png|600px|center]]</br>Figure 2.4</center>
 
 
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|| <center>Easton and East Parton possessed high uncertainty as they are located right beside the Safe Town. Also, being the centre position of St. Himark city, regions such as Weston, Easton, Southton, West Parton, and East Parton has higher uncertainty as the radiation in these regions seem lower as compared to how almost all vehicles pass through these areas. </center>
 
|| <center>Easton and East Parton possessed high uncertainty as they are located right beside the Safe Town. Also, being the centre position of St. Himark city, regions such as Weston, Easton, Southton, West Parton, and East Parton has higher uncertainty as the radiation in these regions seem lower as compared to how almost all vehicles pass through these areas. </center>
 
|| <center>[[File:Fresi_Fig2.6.png|600px|center]]</br>Figure 2.6</center>
 
|| <center>[[File:Fresi_Fig2.6.png|600px|center]]</br>Figure 2.6</center>
 
  
 
|-
 
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|| <center>Wilson Forest region should be one of the higher uncertainty areas as there are no radiation measures records in this region. Furthermore, it is located right beside the Wilson Forest Highway which displayed one of the highest radiation records based on Figure 2.7. Last uncertainty area is the Old Town, with the highest concentrated mobile sensors travelled in and out of the area especially it is located near to the Jade Bridge which recorded the highest radiation level on 8 April 2020 at around 2000.  /center>
 
|| <center>Wilson Forest region should be one of the higher uncertainty areas as there are no radiation measures records in this region. Furthermore, it is located right beside the Wilson Forest Highway which displayed one of the highest radiation records based on Figure 2.7. Last uncertainty area is the Old Town, with the highest concentrated mobile sensors travelled in and out of the area especially it is located near to the Jade Bridge which recorded the highest radiation level on 8 April 2020 at around 2000.  /center>
 
|| <center>[[File:Fresi_Fig2.7.png|600px|center]]</br>Figure 2.7</center>
 
|| <center>[[File:Fresi_Fig2.7.png|600px|center]]</br>Figure 2.7</center>
 
 
|}
 
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  </center>
 
  </center>
 
|| <center>[[File:Fresi_Fig2.8.png|600px|center]]</br>Figure 2.8</center>
 
|| <center>[[File:Fresi_Fig2.8.png|600px|center]]</br>Figure 2.8</center>
 
  
 
|-
 
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|| <center>Mobile sensor-id 12 recorded the highest radiation measure as compared to other sensors on 9 April 2020 at around 0243 yet the subsequent measures showed a high density of very low radiation value within the healthy range. Hence, it increased the uncertainty of the radiation level. </center>
 
|| <center>Mobile sensor-id 12 recorded the highest radiation measure as compared to other sensors on 9 April 2020 at around 0243 yet the subsequent measures showed a high density of very low radiation value within the healthy range. Hence, it increased the uncertainty of the radiation level. </center>
 
|| <center>[[File:Fresi_Fig2.9.png|600px|center]]</br>Figure 2.9</center>
 
|| <center>[[File:Fresi_Fig2.9.png|600px|center]]</br>Figure 2.9</center>
 
 
|}
 
|}
  
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|| <center>For mobile sensors, the possible areas of contamination are (1) Old Town, (2) Scenic Vista, and (3) Wilson Forest Highway. </center>
 
|| <center>For mobile sensors, the possible areas of contamination are (1) Old Town, (2) Scenic Vista, and (3) Wilson Forest Highway. </center>
 
|| <center>[[File:Fresi_Fig3.2.png|600px|center]]</br>Figure 3.2</center>
 
|| <center>[[File:Fresi_Fig3.2.png|600px|center]]</br>Figure 3.2</center>
 
  
 
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The official should be worried about the contamination of cars travelling within the city as it increases the chance of more contamination to other objects and citizens. There are also possibilities that contamination will be spread out of St. Himark city as these vehicles travelled in and out via Jade Bridge and Wilson Forest Highway. </center>
 
The official should be worried about the contamination of cars travelling within the city as it increases the chance of more contamination to other objects and citizens. There are also possibilities that contamination will be spread out of St. Himark city as these vehicles travelled in and out via Jade Bridge and Wilson Forest Highway. </center>
 
|| <center>[[File:Fresi_Fig3.3.png|600px|center]]</br>Figure 3.3</center>
 
|| <center>[[File:Fresi_Fig3.3.png|600px|center]]</br>Figure 3.3</center>
 
 
|}
 
|}
  
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|| <center>Mobile sensor-id 10 logged the highest radiation value in Jade Bridge. </center>
 
|| <center>Mobile sensor-id 10 logged the highest radiation value in Jade Bridge. </center>
 
|| <center>[[File:Fresi_Fig3.5.png|600px|center]]</br>Figure 3.5</center>
 
|| <center>[[File:Fresi_Fig3.5.png|600px|center]]</br>Figure 3.5</center>
 
  
 
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|| <center>Moving on to the sensors that might have left the areas, we see, there are 2 possibilities of events where vehicles have left the city. First, based on Figure 3.5, we see sensor-id 10 travelled out of the city via Jade Bridge. Second, based on Figure 3.8, all the mobile sensors mentioned in the picture enter and then leave the city via the Wilson Forest Highway.  </center>
 
|| <center>Moving on to the sensors that might have left the areas, we see, there are 2 possibilities of events where vehicles have left the city. First, based on Figure 3.5, we see sensor-id 10 travelled out of the city via Jade Bridge. Second, based on Figure 3.8, all the mobile sensors mentioned in the picture enter and then leave the city via the Wilson Forest Highway.  </center>
 
|| <center>[[File:Fresi_Fig3.8.png|600px|center]]</br>Figure 3.8</center>
 
|| <center>[[File:Fresi_Fig3.8.png|600px|center]]</br>Figure 3.8</center>
 
 
|}
 
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<p>By analysing the data as a stream, we will monitor the change in radiation reading over time to (1) identify the sensors with highest radiation measure, (2) identify the areas with high radiation, and (3) identify vehicles with high contamination. The dynamic nature of radiation contamination required continuous monitoring in real-time to determine the next solution. Therefore, treating the data as the stream will be more suitable as compared to analyse the data as a static collection.  
 
<p>By analysing the data as a stream, we will monitor the change in radiation reading over time to (1) identify the sensors with highest radiation measure, (2) identify the areas with high radiation, and (3) identify vehicles with high contamination. The dynamic nature of radiation contamination required continuous monitoring in real-time to determine the next solution. Therefore, treating the data as the stream will be more suitable as compared to analyse the data as a static collection.  
 
</p>
 
</p>
 
  
 
== References ==
 
== References ==
 +
* Live real-time monitoring map of radiation counts in the USA - https://wattsupwiththat.com/2011/03/17/live-real-time-monitoring-map-of-radiation-counts-in-the-usa/
 +
* Background Radiation - https://en.wikipedia.org/wiki/Background_radiation
 +
* Geospatial analysis made easy with two new spatial functions: MakePoint and MakeLine - https://www.tableau.com/about/blog/2019/6/geospatial-analysis-made-easy-two-new-spatial-functions-makepoint-and-makeline
  
 
== Comments ==
 
== Comments ==

Revision as of 22:27, 13 October 2019

Contents

Problem & Motivation

St. Himark is a vibrant community with a population of 246,839 people located in the Oceanus Sea. It also home to the Always Safe nuclear power plant, a 200 Megawatts electric (MWe) pressurized water reactor (PWR). The Always Safe nuclear power plant provides 72% of the city’s electricity and provides jobs for 700 highly skilled professionals. It has always been the pride of the city, yet it was not quite built to be compliant with the recommended safety standards developed by international organizations and is now ageing.

The nuclear plant sustained moderate (but not life-threatening) damage during the earthquake resulting in some contamination being released. Further, a coolant leak sprayed employees’ cars and contaminated them at varying levels. The city has installed stationary sensors which could be used to determine affected areas, but they don’t cover all parts of the city. Luckily, the Himark Science Society has stepped in with citizen scientists to help crowdsource this important task. Utilize these various sensors to understand which parts of the city are most affected. Meanwhile, mayor Jordan, city officials, and emergency services are overwhelmed and are desperate for assistance in understanding the true situation on the ground and how best to deploy the limited resources available to this relatively small community.

With the huge amount of contamination data collected from the sensors reading, there is a need to build an interactive comprehensive visualization platform to monitor which parts of the city are the most affected.

The interactive visualization will focus on:

  • The monitoring of Static sensors reading, one at the entrance to the Always Safe nuclear power plant and eight dispersed around the city.
  • The monitoring of 50 mobile sensors that travel in and out of the city.
  • Understanding the observation and identify the anomalies from the static and mobile sensor reading.
  • Identifying the area/s that are heavily affected by the contamination and dispatch necessary help for its citizens.

Dataset Analysis & Transformation Process

The data zip folder contains 1 shapefile folder, 4 maps of St Himark city, and 3 CSV files.

The 3 CSV files are:

  • StaticSensorLocations.csv
  • StaticSensorReadings.csv
  • MobileSensorReadings.csv

Static Sensors

There are 9 static sensors in St. Himark based on the picture above, where one sensor (sensor-id 15) is placed at the entrance to the Always Safe nuclear power plant and eight dispersed around the city. These detectors provide near-real-time monitoring in the unlikely event of a radiological emergency.

Fresi DC 1.png

Looking on the static sensor location data, we notice a problem.

Issue: The StaticSensorReadings lacks of location-id and the neighbourhood attributes

Solution: Using the StaticSensorLocations and Figure 1, we update the record by adding additional 2 column which are (1) location-id and (2) neighbourhood.

Fresi DC 2.png

Mobile Sensors

There are 50 mobile sensors attached to the vehicles. The timestamps are reported in 5-second intervals. The locations travelled by the mobile sensors are based on the longitude and latitude values.

Fresi DC 3.png

Issue: Like StaticSensorLocations.csv’s problem, the MobileSensorReadings.csv only has Longitude and Latitude attributes to match the vehicle with its location.

Solution: Combine the MobileSensorReading.csv to St.Himark.sph by using inner join function in Tableau.

Fresi DC 4.png

We use inner join (Intersects) between Join calculation of MAKEPOINT([Lat], [Long]) on MobileSensorReadings.csv and Geometry on St.Himark.shp.

Fresi DC 5.png

Once done, Tableau will produce three additional attributes, which are (1) Id – neighbourhood id number, (2) Neighbourhood, and (3) Geometry.

Combining Static and Mobile Data

Next, we need to combine the static and the mobile sensor data. The structure of the captured data by both the static sensor and mobile sensor is similar. However, the static sensor doesn’t have a longitude and latitude attributes and therefore unable to identify the exact location of the sensor. Below image shows the main differences of attributes between static and mobile data captured:

Fresi DC 6.png

The following section illustrates the issues faced in the data analysis phase and the data transformation needed to create the desired data structure used for insight generation.

Issue: The details of Longitude and Latitude of the static sensor is presented in the StaticSensorLocation instead of StaticSensorReading. We need to combine the two data together to enable the visualization of static sensor location on the St. Himark’s map.

Fresi DC 7.png

Solution: Combine the StaticSensorLocation file with the StaticSensorReading file by using inner joint of sensor-id in Tableau Prep.

Fresi DC 8.png

Once the data is joined, there will be a duplicate of Sensor-id1 attributes which we removed afterwards through the cleaning process. At the end in the Output 2 (picture below), we have the StaticSensorReading with the Latitude and Longitude attributes.

Fresi DC 9.png

Before we combine Mobile and Static sensors data, we need to rename the id column and Nbrhood attribute in the mobile sensors file (name: Extract (Extract)). We rename id to Location-id and Nbrhood to Neighbourhood for easy understanding of the data.

Fresi DC 10.png

Issue: Once, the union between static and mobile sensor is formed, it will be hard to distinguish if a sensor is a static or a mobile sensor especially the number of static sensor-id is the same as mobile sensor-id.

Solution: Rename the Table Name attribute from the union table to “Sensor Type” while we change the 2 values from MobileSensorReading.csv and StaticSensorReading.csv to “Static” and “Mobile” respectively. Afterwards, we removed the Units attribute as both static and mobile has the same measurement of CPM. We also trim spaces in User-id attribute as some input has extra space.

Fresi DC 11.png

Lastly, we will extract the finalized data that contains both static and mobile sensor reading.

Fresi DC 12.png

Interactive Visualization

The visualization platform can be accessed here: https://public.tableau.com/profile/fresi3383#!/vizhome/Fresi_VASTChallenge_MiniProject2/HomeDashboard

Home Dashboard

The following shows the home dashboard:

Fresi Interactive 1.png

For easy navigation, the following interactions are implemented:

Interactive Technique Reason Brief Implementation Steps
Use button to navigate across 2 major categories of analysis with buttons
To provide flexibility of moving from one dashboard to another dashboard.
  1. Drag Button under Objects to the worksheet.
  2. Click the button and link it to the targeted dashboard.
  3. Choose Text Button and then give a name to it.
Use tooltip when the user hover over the button
To inform the user that there are 2 main sensors reading in this analysis. It also facilitate easy exploration of the data.
  1. Add the explanation on the tooltip under the button setting.

Static Sensors Reading Dashboard

The following shows the home dashboard:

Fresi Interactive 2.png

For easy navigation, the following interactions are implemented:

Interactive Technique Reason Brief Implementation Steps
Use of single value drop down to select All sensors or specific static sensor
To enable the user to gain insight on the static radiation measures over time and view the cumulative sum of radiation over time.
  1. Select sensor-id as the filter
  2. Click "Apply to worksheet" > Selected worksheet > Tick the desired graph/s in which we want to apply the filter to.

Static Sensors Distribution per Region Dashboard

The following shows the home dashboard:

Fresi Interactive 3.png

For easy navigation, the following interactions are implemented:

Interactive Technique Reason Brief Implementation Steps
Filter dates with the use of time range slider
To enable user to include or exclude the desired dates so as to faciliate their insight generation.
  1. Choose Timestamp as the filter under "Pages" pane
  2. Click the triangle on the Timestamp pill and choose "Minute"

Mobile Sensors Reading Dashboard

The following shows the home dashboard:

Fresi Interactive 4.png

For easy navigation, the following interactions are implemented:

Interactive Technique Reason Brief Implementation Steps
Use of single value drop down to select All sensors or specific static sensor
To enable the user to gain insight on the mobile radiation measures over time and view the cumulative sum of radiation over time.
  1. Select sensor-id as the filter
  2. Click "Apply to worksheet" > Selected worksheet > Tick the desired graph/s in which we want to apply the filter to.

Mobile Sensors Distribution per Region Dashboard

The following shows the home dashboard:

Fresi Interactive 5.png

For easy navigation, the following interactions are implemented:

Interactive Technique Reason Brief Implementation Steps
Filter dates with the use of time range slider
To enable the user to inlude or exclude the desired dates to gain insights on radiation measures per region and spot the highest possible contaminated mobile sensors
  1. Drag the Timestamp into the "Pages" panes.
  2. Click the triangle on the Timestamp pill and choose "Minute"
  3. Under the dashboard page, select the Timestamp filter > Apply to worksheet > Selected worksheet > Tick the desired graphs which we want to apply the filter to
Drop down of multi values neighbourhood
To allow the user to select the desired region that they want to focus on to gain insights
  1. Drag Neighbourhood to the filter pane

Mobile Sensors Trajectories Dashboard

The following shows the home dashboard:

Fresi Interactive 6.png

For easy navigation, the following interactions are implemented:

Interactive Technique Reason Brief Implementation Steps
Filter dates with the use of time range slider
To enable the user to inlude or exclude the desired dates to gain insights on the path travelled by the mobile sensors. It helps to spot possible region with highest radiation and contamination carried by the vehicles.
  1. Drag the Timestamp into the "Pages" panes.
  2. Click the triangle on the Timestamp pill and choose "Minute"
  3. Under the dashboard page, select the Timestamp filter > Apply to worksheet > Selected worksheet > Tick the desired graphs which we want to apply the filter to
Drop down of multi values of mobile sensor-id
To allow the user to select the desired sensor-id that they want to focus on to gain insights
  1. Drag the sensor-id to the filter pane

Interesting & Anomalies Observations

Using the graphs from the visualization platform to perform investigation and analysis, the following aims to provide the answer to the questions posed.

Q1: Visualize radiation measurements over time from both static and mobile sensors to identify areas where radiation over background is detected. Characterize changes over time. Limit your response to 6 images and 500 words. Provide your answer and corresponding images here.

Sensor Type Radiation Measures Proof
Static Sensor
There is an increase of radiation measures recorded from 8 April 2020 at approximately 1500. The radiation level is persisted until the end of the recording period.
Fresi Fig1.1.png

Figure 1.1

Static Sensor
Based on Figure 1.2, all the static sensors displayed constant radiation with minor random variation within the healthy range of 75 CpM and random but infrequent spikes from 6 April 2020 at 1200 to around 8 April 2020 at 1600. From 8 April 2020 at approximately 16:00, sensor-id 15 which is the nearest to the nuclear plant showed a significant increase in radiation level. It followed by the raised of radiation in sensor-id 12, 13, 14 (all 3 are located near to the power plant) and 15 for around 20 minutes. From 9 April 2020 at approximately 1430 to the end of the recording period, there were elevated background radiation from all sensor except for sensor-id 15.
Fresi Fig1.2.png

Figure 1.2

Static Sensor
Based on Figure 1.3, again, we spot the slight rise of radiation level in sensor-id 15 on 8 April 2020 at approximately 1600, followed by the rise of radiation level in sensor-id 12 (Jade Bridge) at approximately 1700 on the same day. Sensor-id 9 (Old Town) and 11 (Broadview) displayed an increase of radiation level on 8 April 2020 from 2200 to 9 April 2020 at 0600.
Fresi Fig1.3.png

Figure 1.3

Mobile Sensor
We spot obvious patterns in the mobile radiation reading as followed:
Sensor-id Area Pattern Timestamp
7, 8, 10, 11, 12, 46
Jade Bridge and Old Town
Increase in radiation level
9 April 2020 from approximately 0700 - 1930
7, 8, 10, 11, 12, 46
Jade Bridge and Old Town
Decrease in radiation level
10 April 2020 from 0700 - 2130
5, 9, 14
Jade Bridge
High and stable radiation level
9 April 2020 at 0800 to 10 April 2020 at 2030
21, 22, 24, 25, 27, 28, 29, 30, 45
Wilson Forest Highway
Increase in radiation level
9 April 2020 at 1930 to 10 April 2020 at 0830
Fresi Fig1.4.png

Figure 1.4

Mobile Sensor
Mobile sensor-id 10 (Jade Bridge) showed the highest amount of radiation level after the earthquake hit St. Himark. The rise of radiation began from 8 April 2020 at about 1700 to 2100. As the contamintation is spread, mobile sensor-ids (5, 7, 8, 9, 10, 11, 12, 14, and 46) recorded a high radiation when passing through the Jade Bridge area as what we could observed from Figure 1.3.

From 9 April 2020 at approximately 1900 to 10 April 2020 at 0600, mobile sensor-id 21, 22, 24, 25, 27, 28, 29, and 45 which pass through the Wilson Forest Highway recorded a substantial increase in radiation level. The increment in these sensors is aligned with the observation from Figure 1.3.
Fresi Fig1.5.png

Figure 1.5

Mobile Sensor
Sensor-id 9 showed an increase of radiation level for about 2 hours on 8 April 2020. It followed by the rise of radiation level on sensor-id 11 which lasted for 5 hours on the same day. On 9 April 2020 from 1800 onwards, sensor-id 29, 45, 21, 25, 27, 28, 22 and 24 recorded a huge increase of radiation level.
Fresi Fig1.6.png

Figure 1.6

Q2 – Use visual analytics to represent and analyse uncertainty in the measurement of radiation across the city.

a. Compare uncertainty of the static sensors to the mobile sensors. What anomalies can you see? Are there sensors that are too uncertain to trust?

Sensor Type Uncertainties and Anomalies Evidence
Static Sensor
Referring to Figure 1.3, sensors-id 15 and 12 recorded an increase in radiation starting from 8 April 2020 at around 1600. Subsequently, all static sensors displayed a surge of radiation except for sensor-id 15 which stopped recording from 8 April 2020 at 2200 to 10 April 2020 at 2000 (based on Figure 1.2).

Looking at the distribution of static sensors boxplot, we see static sensor-id 12 displayed an extreme radiation on 8 April 2020. By 10 April 2020, there are 2 categories of outlier, (1) sensors-id 9 and 12 showed highest value of radiation and (2) sensor-id 15 recorded an extreme low value given the proximity of the sensor to the nuclear power plant.

Except for sensor-id 15 which implied low certainty due to the absent of radiation reading from 8 April 2020 at 2200 to 10 April 2020 at 2000, all static sensors-id offer a consistent and reliable radiation measures over time given the condition of the city.
Fresi Fig2.1.png

Figure 2.1
Mobile Sensor
Mobile sensors present a more uncertainty in the radiation measures over time.

The first anomaly is there are 10 mobile sensors-id (1, 6, 23, 26, 34, 35, 47, 48 and 49) which had stopped recording on 8 April 2020 at around 0719 onwards as what shown in Figure 2.2.

Fresi Fig2.2.png

Figure 2.2
Mobile Sensor
Third, mobile sensors 18, 20, 38, 39, 43, 44, 47 and 48 displayed random variation and spikes of varied radiation measures, which should be within the healthy radiation bound before the quake happened. Also, sensor-id 18 stopped recording from 8 April 2020, 1623 to 9 April 1243. Last, sensor-id 43 showed a discrete drop in radiation from 10 April 1320 to 1535. /center>
Fresi Fig2.3.png

Figure 2.3
Mobile Sensor
Sensors-id 12, 19, 20 and 21 displayed a substantial background noise (low persistent spike below 75CpM) of radiation measure.

In conclusion, mobile sensors-id provide a less consistent and therefore less reliable radiation measure. More considerations need to be taken to draw conclusion based on the mentioned mobile sensors-id mentioned above.

Fresi Fig2.4.png

Figure 2.4

b. Which regions of the city have greater uncertainty of radiation measurement? Use visual analytics to explain your rationale.

Sensor Type Regions with uncertainties Evidence
Static Sensor
For the static sensors, all the neighbourhood without static sensor are excluded. The first uncertainty region is Safe Town as sensor-id 15 had stopped measuring the radiation from 8 April 2020 at around 2300 to 10 April 2020 at around 2000. The radiation in Safe Town should be much higher due to its proximity to the nuclear power plant. Second, the location of sensor-id in some regions like Broadview, Cheddar-ford, and Southwest is not in the centre. Therefore, there is chance that the measurement may not be accurate representation of the radiation level.
Fresi Fig2.5.png

Figure 2.5
Mobile Sensor
Easton and East Parton possessed high uncertainty as they are located right beside the Safe Town. Also, being the centre position of St. Himark city, regions such as Weston, Easton, Southton, West Parton, and East Parton has higher uncertainty as the radiation in these regions seem lower as compared to how almost all vehicles pass through these areas.
Fresi Fig2.6.png

Figure 2.6
Mobile Sensor
Wilson Forest region should be one of the higher uncertainty areas as there are no radiation measures records in this region. Furthermore, it is located right beside the Wilson Forest Highway which displayed one of the highest radiation records based on Figure 2.7. Last uncertainty area is the Old Town, with the highest concentrated mobile sensors travelled in and out of the area especially it is located near to the Jade Bridge which recorded the highest radiation level on 8 April 2020 at around 2000. /center>
Fresi Fig2.7.png

Figure 2.7


c. What effects do you see in the sensor readings after the earthquake and other major events? What effect do these events have on uncertainty?

Sensor Type Effects after the earthquake or other major events Evidence
Static Sensor
Referring to Figure 1.3, after the earthquake on 8 April 2020 at around 1500, static sensors-id 12 – 15 logged a rise of radiation from 1600 onwards on the same day. All the static sensors-id continued to log a rise of radiation except for sensor-id 15. Hence, sensor-id 15 contributed to the uncertainty of radiation measurements.
-
Mobile Sensor
On 8 April 2020, mobile sensor-id 10 recorded highest value of radiation. Subsequently, on 9 and 10 April 2020, mobile sensors-id 29, 45, 21, 25, 27, 28, 22, and 24 logged an extreme radiation value and become the outlier of radiation measures. Also, based on the CuSum graph on Figure 1.6, we spot several mobile sensors (29, 45, 21, 25, 27, 28, 22, and 24) recorded extreme radiation level as compared to other mobile sensors.

Both figure 1.6 and 2.8 pointed out the same mobile sensors with high radiation measures and therefore the measures is highly certain.

Fresi Fig2.8.png

Figure 2.8
Mobile Sensor
Mobile sensor-id 12 recorded the highest radiation measure as compared to other sensors on 9 April 2020 at around 0243 yet the subsequent measures showed a high density of very low radiation value within the healthy range. Hence, it increased the uncertainty of the radiation level.
Fresi Fig2.9.png

Figure 2.9

Q3 – Given the uncertainty, you observed in question 2, are the radiation measurements reliable enough to locate areas of concern?

a. Highlight potential locations of contamination, including the locations of contaminated cars. Should St. Himark officials be worried about contaminated cars moving around the city?

Sensor Type Potential Contaminated Locations and Cars Evidence
Static Sensor
For static sensors, the potential areas of contamination are (1) Broadview, (2) Cheddar-ford, (3) Downtown, (4) Palace Hills, and (5) Safe Town.
Fresi Fig3.1.png

Figure 3.1
Mobile Sensor
For mobile sensors, the possible areas of contamination are (1) Old Town, (2) Scenic Vista, and (3) Wilson Forest Highway.
Fresi Fig3.2.png

Figure 3.2
Mobile Sensor
For the potential locations of contaminated car, we refer to Figure 1.6 which highlighted the 7 highest radiation values of mobile sensors which are 29, 45, 21, 25, 27, 28, 22, and 24. To discover the path travelled by the mobile sensors mentioned above, we will use the trajectories graph.

As we can see from Figure 3.3, the locations of contaminated cars are (1) Scenic Vista, (2) Terrapin Springs, (3) Chapparal, (4) Cheddar-ford, (5) Broadview, (6) Oak Willow, (7) East Parton, (8) Safe Town, (9) West Parton, (10) Southwest, (11) South-ton, (12) Downtown, and (13) Easton. Last, special attention needs to be given to (1) Jade Bridge and (2) Wilson Forest Highway as both areas recorded the highest radiation values.

The official should be worried about the contamination of cars travelling within the city as it increases the chance of more contamination to other objects and citizens. There are also possibilities that contamination will be spread out of St. Himark city as these vehicles travelled in and out via Jade Bridge and Wilson Forest Highway.
Fresi Fig3.3.png

Figure 3.3

b. Estimate how many cars may have been contaminated when coolant leaked from the Always Safe plant. Use visual analysis of radiation measurements to determine if any have left the area.

Sensor Type Number of cars tht may have been contaminated Evidence
Mobile Sensor
Mobile sensors-id 9, 13, 14, 15, 32, 39, and 43 has the 7 highest radiation values in Safe Town region.
Fresi Fig3.4.png

Figure 3.4
Mobile Sensor
Mobile sensor-id 10 logged the highest radiation value in Jade Bridge.
Fresi Fig3.5.png

Figure 3.5
Mobile Sensor
There is a possibility of cross contamination between mobile sensor-id 10 and mobile sensor-id 12 as both shared a similar trail by the end of recording period. Also, both sensors pass through the same path from Jade Bridge (where it recorded one of the highest radiation measure) to Old Town area.
Fresi Fig3.6.png

Figure 3.6
Mobile Sensor
Mobile sensors-id 29, 45, 21, 25, 27, 28, 22 and 24 began to record an increasing value of contamination from 9 April 2020 around 1800 onwards. In total, there are possibly 17 cars contaminated when a coolant leak from the nuclear power plant.
Fresi Fig3.7.png

Figure 3.7
Mobile Sensor
Moving on to the sensors that might have left the areas, we see, there are 2 possibilities of events where vehicles have left the city. First, based on Figure 3.5, we see sensor-id 10 travelled out of the city via Jade Bridge. Second, based on Figure 3.8, all the mobile sensors mentioned in the picture enter and then leave the city via the Wilson Forest Highway.
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Figure 3.8

c. Indicated where you would deploy more sensors to improve radiation monitoring in the city. Would you recommend more static sensors or more mobile sensors or both? Use your visualization of radiation measurement uncertainty to justify your recommendation.

Fresi Fig3.9.png

Based on our analysis, we conclude that static sensors-id provides a more accurate and reliable radiation measure as compared to the mobile sensors-id. Therefore, it would be more useful for St. Himark to install more static sensors. For the new locations, a priority should be given to Safe Town and the proximity regions such as Pepper Mill, East Parton, and Easton which currently has no static sensor. The next locations are the entrance and exit routes of the city such as Friday Bridge, Magritte Bridge, Wilson Forest Highway, Himark Bridge, 12th of July Bridge.

Even though static sensors are more accurate, mobile sensors are important to monitor dynamic changes of radiation when a vehicle travels from one region to another. Therefore, the official should find a way to improve the mobile sensor reading as a mobile sensor enables the gathering of radiation measures far away from the static sensors.

Q4 – Summarize the state of radiation measurements at the end of the available period. Use your novel visualizations and analysis approaches to suggest a course of action for the city. Use visual analytics to compare the static sensor network to the mobile sensor network. What are the strengths and weaknesses of each approach? How do they support each other? Limit your response to 6 images and 800 words.

Fresi Fig4.1.png

Figure 4.1
Fresi Fig4.2.png

Figure 4.2

The summary status of the two types of sensors are:

  • Overall, by the end of the recording period, we can see an increase of values demonstrated by the static and mobile sensors.
  • Referring to Figure 4.1, all the static sensors recorded a rise in the radiation background except for sensor-id 15 which stopped recording on 8 April 2020 at around 1600. Sensor-id 12 located in Jade Bridge logged the highest accumulated radiation by the end of the recording followed by sensor-id 9 located in Old Town due to its proximity to the nuclear power plant and Jade Bridge. The city mayor should focus on decontaminating these two locations, e.g. barricade the areas to prevent people from entering until the decontamination processes are done.
  • For the mobile sensors, vehicles with sensor-id 21, 22, 24, 25, 27, 28, 30, and 45 recorded high level of radiation and possible cross-contamination in the Wilson Forest Highway. The government should search for these vehicles and decontaminated them as soon as possible.
  • Last, the government should invest more on sensors and placed at least one static sensor in each region, bridges, and highways.


Looking back at our discussion over the past 3 questions, we could safely claim that static sensors provide more accuracy and reliability in measuring the radiation measures. Based on the static readings, St.Himark’s officials and citizens can rely on these sensors to inform them about real-time and accurate measures. However, the static sensor is not mobile, and the coverage may be limited. For instance, static sensor-id 9 in Old Town will not represent all areas in that region due to the area size.

On the other hand, mobile sensors had been proven to be less accurate and bring about uncertainty to the radiation measures. However, mobile sensors are versatile and flexible as it can cover the specific areas that can’t be covered by static sensors. Also, as the mobile sensor is attached to a vehicle, it helps to (1) detect if the vehicle is exposed to the radiation, (2) possible cross-contamination between vehicles and (3) locate the vehicles in or out of the city.

Overall, both static and mobile sensors complement each other in measuring background radiation and detect any possible radiation leakage from the nuclear power plant. Many of St. Himark’s citizen will find the improvement in term of accuracy for mobile sensor measure to be necessary. By doing so, the government can gain more confidence from the people in the city.

Q5 - The data for this challenge can be analysed either as a static collection or as a dynamic stream of data, as it would occur in a real emergency. Describe how you analysed the data - as a static collection or a stream. How do you think this choice affected your analysis? Limit your response to 200 words and 3 images.

For this analysis, the data will be treated as dynamic steam as we wish to get insights on the real-time condition on the ground.

For example, the use of cumulative sum graph of static and mobile sensors enabled us to spot the most affected sensors and any other possible measures.

By analysing the data as a stream, we will monitor the change in radiation reading over time to (1) identify the sensors with highest radiation measure, (2) identify the areas with high radiation, and (3) identify vehicles with high contamination. The dynamic nature of radiation contamination required continuous monitoring in real-time to determine the next solution. Therefore, treating the data as the stream will be more suitable as compared to analyse the data as a static collection.

References

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