(→‎Mixed Bottles: Lost Coast Brewery in Eureka, California)
m (Replace references template for plain references tag per better compatibility with visual editor and other software)
 
(41 intermediate revisions by 7 users not shown)
Line 1: Line 1:
{{Tocright}}
[[File:CO2 Emissions of a Washed Bottle (1).png|thumb|]]
==Introduction==
 
During the fall of 2019, this research project was conducted with a partnership between [[Engr308 Technology and the Environment]] and Zero Waste Humboldt (ZWH). The client liaison on this project is  
{{Project data}}
 
The research project was a collaboration between [[Cal Poly Humboldt]]'s [[Engr308 Technology and the Environment]] and Zero Waste Humboldt (ZWH) during the Fall of 2019. The client liaison on this project is
 
* Maggie Gainer, Zero Waste Humboldt
* Maggie Gainer, Zero Waste Humboldt


The objective of this project is to analyze and compare the effects of the impacts of current glass bottles for beer compared to local beer bottle washing, based upon their embedded [[carbon dioxide]] emissions and [[embedded energy]]. Within research on a local and state level, we compared what goes into each option and gave options for bottle washing machines moving forward. The beer bottles observed were from Lost Coast Brewery.
The objective of this project is to analyze and compare the impacts of recycling beer bottles to local beer bottle washing in the terms of embedded [[carbon dioxide]] emissions and [[embedded energy]]. While researching, we were able to conduct a comparative examination between the life cycle analysis' for both recycled bottles and washed bottles. The glass beer bottles we used for observation were from Lost Coast Brewery in Humboldt County.
 
== Findings ==
 
[[File:Embedded Energy of Mixed Versus Washed Bottles.png|thumb|left|Embedded energy of the production of a single mixed bottle versus a single washed bottle. Source as produced by [[File:Bottle Washing Analysis.xlsx|Bottle Washing Analysis]].]]


==Findings==
[[File:Embedded CO2 of Mixed Versus Washed Bottles.png|thumb|left|Embedded CO2 of the production of a single mixed bottle versus a single washed bottle. Source as produced by [[File:Bottle Washing Analysis.xlsx|Bottle Washing Analysis]].]]
[[File:Embedded_Energy_of_Mixed_Versus_Washed_Bottles.png|thumb|left|Embedded energy of the production of a single mixed bottle versus a single washed bottle. Source as produced by [[Media:Mason Jar Analysis.xlsx|Mason Jar Analysis]].]]
[[File:Embedded_CO2_of_Mixed_Versus_Washed_Bottles.png|thumb|left|Embedded CO2 of the production of a single mixed bottle versus a single washed bottle. Source as produced by [[Media:Mason Jar Analysis.xlsx|Mason Jar Analysis]].]]
Many assumptions were made in the study; see [[#Caveats| Caveats]] below for more detailed information. This study of Virgin Bottles, Mixed Bottles, and Washed Bottles compared two metrics: carbon dioxide emissions and embedded energy. It was concluded that the materials used, the transport of, and packaging of a single beer bottle requires 0.72 kilowatt-hours of energy and is responsible for 0.323 pounds of carbon dioxide emissions. In comparison, a single mixed bottle is responsible for using 0.69 kilowatt-hours of energy, releasing 0.306 pounds of carbon dioxide. A single washed bottle is responsible for using 0.021 kilowatt-hours of energy, releasing 0.010 pounds of carbon dioxide emissions.


This study of Virgin Bottles, Mixed Bottles, and Washed Bottles compared two metrics: carbon dioxide emissions and embedded energy. It was concluded that the materials used, the transport of, and packaging of a single beer bottle requires 0.72 kilowatt-hours of energy and is responsible for 0.323 pounds of carbon dioxide emissions. In comparison, a single mixed bottle is responsible for using 0.69 kilowatt-hours of energy, releasing 0.306 pounds of carbon dioxide. A single washed bottle is responsible for using 0.021 kilowatt-hours of energy, releasing 0.010 pounds of carbon dioxide emissions.


The assumptions used to obtain these results can be seen below in further detail in the section titled [[#Caveats|Caveats]].


{| class="wikitable"
{| class="wikitable"
|-
!
!  
! Virgin Bottles
! Virgin Bottles
! Mixed Bottles
! Mixed Bottles
Line 29: Line 34:
| 0.306
| 0.306
| 0.010
| 0.010
|-
|}
|}


Based on the numbers shown above, we are able to conduct a comparative analysis showing the embedded energy and CO<sub>2</sub> between a single mixed bottle and a single washed bottle. The calculations and assumptions used to aquire these results can be seen in further detail in the following spreadsheet:


* [[File: Bottle Washing Analysis.xlsx|Bottle Washing Analysis]]


Based on the numbers shown above, we are able to conduct a comparative analysis showing the embedded energy and CO<sub>2</sub> between a single mixed bottle and a single washed bottle. The calculations and assumptions used to obtain these results can be seen in further detail in the following spreadsheet:
The spreadsheet allows for others interested in performing a similar analysis to easily input values pertaining to their particular study area. It is our hope that with this information and the pre-assembled spreadsheet, other institutions will be able to reach similar compelling conclusions that have the potential to influence future policies.
*[[File:Mason Jar Analysis.xlsx|Mason Jar Analysis.xlsx]]
The spreadsheet allows for others interested in performing a similar analysis to easily input values pertaining to their particular study area. It is our hope that with this information and the pre-assembled spreadsheet, other institutions will be able to reach similar compelling conclusions that have the potential to influence future policies.
 
 
 


=== Virgin Bottles ===


[[File:EE Energy Virgin Bottle.png|thumb|Embedded energy in the production of a virgin beer bottle by source as produced by [[File:Bottle Washing Analysis.xlsx|Bottle Washing Analysis]].]]


[[File:CO2 Emissions of a Virgin Bottle.png|thumb|Carbon Dioxide emissions from the production of a virgin beer bottle by source as produced by [[File:Bottle Washing Analysis.xlsx|Bottle Washing Analysis]].]]


 
The bottles analyzed in this study were 12oz glass bottles, produced by a company in Los Angeles, California and then transported to Lost Coast Brewery in Eureka, California. We measured embedded energy of a virgin bottle by accounting for materials, transportation, and packaging. A virgin bottle is defined as a bottle that has completely new materials. Therefore, the life cycle analysis was determined through the manufacturing processes necessary for the creation of a new glass bottle. The embedded carbon dioxide comes from the melting of materials, heating water, and other CO<sub>2</sub> emitted during transportation. The embedded energy for a virgin bottle is 0.72 kWh/bottle and releases 0.323 pounds of CO<sub>2</sub>
 
 
===Virgin Bottles===
[[File:EE_Energy_Virgin_Bottle.png|thumb|Embedded energy in the production of a single Mason jar by source as produced by [[Media:Mason Jar Analysis.xlsx|Mason Jar Analysis]].]]
[[File:CO2_Emissions_of_a_Virgin_Bottle.png|thumb|Carbon Dioxide emissions from the production of a single Mason jar by source as produced by [[Media:Mason Jar Analysis.xlsx|Mason Jar Analysis]].]]
The Bottles analyzed in this study were the 12 oz glass bottles. The bottles were produced by a company in Los Angeles, California and then transported Lost Coast Brewery in Eureka, California. We measured embedded energy through a virgin bottle accounting for materials, transportation, and packaging. A virgin bottle is defined as one that has completely new materials. Therefore, this was determined through the necessary manufacturing processes. '''The total embedded energy is''' '''1.33 kWh/bottle for a virgin bottle'''. The embedded carbon dioxide comes from the melting of materials, heating water, and other CO2 emitted during transportation. To calculate CO<sub>2</sub> emissions, we looked at embedded CO<sub>2</sub> emissions of those same processes. ''' The Carbon Dioxide Emissions released are''' '''0.578 lb CO<sub>2</sub> emissions for a virgin bottle''' .


{| class="wikitable"
{| class="wikitable"
|-
! Output
! '''Output'''
! Embedded Energy
! Embedded Energy
! Carbon Dioxide Emissions
! Carbon Dioxide Emissions
|-
|-
| Materials
| Materials
| 1.26 kWh/bottle
| 0.63 kWh/bottle
| 0.537 lb CO<sub>2</sub>/bottle
| 0.269 lb CO<sub>2</sub>/bottle
|-
|-
|Transportation
| Transportation
| 0.064 kWh/bottle
| 0.086 kWh/bottle
| 0.038 lb CO<sub>2</sub>/bottle
| 0.051 lb CO<sub>2</sub>/bottle
|-
|-
| Packing
| Packaging
| 0.007 kWh/bottle
| 0.007 kWh/bottle
| 0.003 lb CO<sub>2</sub>/bottle
| 0.003 lb CO<sub>2</sub>/bottle
|-
|-
|'''Total (1 bottle)'''
! Total (1 bottle)
|'''1.33 kWh/bottle'''
! 0.72 kWh/bottle
|'''0.578 lb CO<sub>2</sub>/bottle'''
! 0.323 lb CO<sub>2</sub>/bottle
|-
|-
|'''Total (all sold bottles)'''
! Total (100,000 bottles sold)
|'''133,389 kWh'''
! 72,487 kWh
|'''57,810 lb CO<sub>2</sub>'''
! 32,286 lb CO<sub>2</sub>
|}
|}


===Mixed Bottles===
=== Mixed Bottles ===
[[File:EE_of_Mixed_Bottle.png|thumb|Embedded energy in the production of a single disposable paper cup by source as produced by [[Media:Mason Jar Analysis.xlsx|Mason Jar Analysis]].]]
 
[[File:CO2_Emissions_of_a_Mixed_Bottles.png|thumb|Carbon Dioxide emissions from the production of a single disposable paper cup by source as produced by [[Media:Mason Jar Analysis.xlsx|Mason Jar Analysis]].]]
[[File:EE of Mixed Bottle.png|thumb|Embedded energy in the production of a mixed beer bottle by source as produced by [[File:Bottle Washing Analysis.xlsx|Bottle Washing Analysis]].]]
The recycled bottles analyzed in this study were the 12oz amber glass bottles from Lost Coast Brewery located in Humboldt County, California. These bottles were produced by the company Saxco based out of Sacramento, California, and were transported to Lost Coast Brewery in Eureka, California. It was estimated that 20% of all the bottles purchased were recycled. This is a user input that we assumed based on dialog with Lost Coast Brewery. As recycled bottles are made into bottles again, the melting process was found to be similar to creating a virgin bottle. It takes the same technology and emits a little under that of a virgin bottle. Further, the transportation was less in a recycled bottle for one reason being distance. The two go through similar processes we found.  
 
[[File:CO2 Emissions of a Mixed Bottles.png|thumb|Carbon Dioxide emissions from the production of a mixed beer bottle by source as produced by [[File:Bottle Washing Analysis.xlsx|Bottle Washing Analysis]].]]
 
The recycled bottles analyzed in this study were the 12oz glass bottles from Lost Coast Brewery in Eureka, California. These bottles were produced by the company Saxco based out of Sacramento, California and were transported to Lost Coast Brewery in Eureka, California. It was estimated that 20% of all the bottles purchased were recycled. This is a user input that we assumed based on dialog with Lost Coast Brewery and is changeable on the spreadsheet. As recycled materials are made into bottles again, the melting process was found to be similar to creating a virgin bottle. It takes a similar process and emits a little under that of a virgin bottle. Further, the transportation was less in a recycled bottle because of the difference in distance. The embedded energy a mixed bottle was 0.69 kWh/bottle and released 0.306 pounds of carbon dioxide emissions.


{| class="wikitable"
{| class="wikitable"
|-
! Output
! '''Output'''
! Embedded Energy
! Embedded Energy
! Carbon Dioxide Emissions
! Carbon Dioxide Emissions
|-
|-
| Materials
| Materials
| 0.91 kWh/bottle
| 0.60 kWh/bottle
| 0.368 lb CO<sub>2</sub>/bottle
| 0.252 lb CO<sub>2</sub>/bottle
|-
|-
|Transportation
| Transportation
| 0.064 kWh/bottle
| 0.086 kWh/bottle
| 0.038 lb CO<sub>2</sub>/bottle
| 0.051 lb CO<sub>2</sub>/bottle
|-
|-
| Packing
| Packaging
| 0.007 kWh/bottle
| 0.007 kWh/bottle
| 0.003 lb CO<sub>2</sub>/bottle
| 0.003 lb CO<sub>2</sub>/bottle
|-
|-
|'''Total (1 bottle)'''
! Total (1 bottle)
|'''0.98 kWh/bottle'''
! 0.69 kWh/bottle
|'''0.409 lb CO<sub>2</sub>/bottle'''
! 0.306 lb CO<sub>2</sub>/bottle
|-
|-
|'''Total (all sold bottles)'''
! Total (100,000 bottles sold)
|'''97,946 kWh'''
! 68,942 kWh
|'''40,864 lb CO<sub>2</sub>'''
! 30,592 lb CO<sub>2</sub>
|}
|}


===Washed Bottles===
=== Washed Bottles ===
[[File:Embedded_Energy_of_a_Washed_Bottle.png|thumb|Embedded energy in the production of a single disposable plastic cup by source as produced by [[Media:Mason Jar Analysis.xlsx|Mason Jar Analysis]].]]
 
[[File:CO2_Emissions_of_a_Washed_Bottle_(1).png|thumb|Carbon Dioxide emissions from the production of a single disposable plastic cup by source as produced by [[Media:Mason Jar Analysis.xlsx|Mason Jar Analysis]].]]
[[File:Embedded Energy of a Washed Bottle.png|thumb|Embedded energy in washed bottles (including making the bottle and washing it 35 times) by source (note that materials include the washing process) as produced by [[File:Bottle Washing Analysis.xlsx|Bottle Washing Analysis]].]]
The bottles that we foresee being washed, were virgin or recycled bottles to begin. Transportation was assumed to add no extra energy to washed bottles due to consumers traveling to drop off at the brewery being stacked with a trip happening regardless. Embedded energy and CO2 came from each time a new or recycled bottle was made, along with the process of running the bottle washing machine. The amount of times a bottle can be re-washed ranges from 25 to 50 times and is a number a user can input - we used 35 for the following findings.  
 
[[File:CO2 Emissions of a Washed Bottle (1).png|thumb|Carbon Dioxide emissions from washed bottles (including making the bottle and washing it 35 times) by source (note that materials include the washing process) as produced by [[File:Bottle Washing Analysis.xlsx|Bottle Washing Analysis]].]]
 
We predicted that the bottles being washed were 20% recycled bottles to begin with (although the bottle might need to be thicker for washing, which would raise the embedded energy and CO2 somewhat). It was assumed that transportation would not emit extra energy for a washed bottles because consumers could drop off their bottles during a regular shopping trip. Embedded energy and CO2 came from each time a new or recycled bottle was made, along with the process of running the bottle washing machine. The amount of times a bottle can be re-washed ranges from 25 to 50 times and is a number a user can input - we used 35 for the following findings. The embedded energy in a washed bottle is 0.021 kWh/bottle and releases 0.010 carbon dioxide emissions.


{| class="wikitable"
{| class="wikitable"
|-
! Output
! '''Output'''
! Embedded Energy
! Embedded Energy
! Carbon Dioxide Emissions
! Carbon Dioxide Emissions
|-
|-
| Materials
| Materials
| 0.036 kWh/bottle
| 0.019 kWh/bottle
| 0.015 lb CO<sub>2</sub>/bottle
| 0.008 lb CO<sub>2</sub>/bottle
|-
|-
|Transportation
| Transportation
| 0.002 kWh/bottle
| 0.002 kWh/bottle
| 0.001 lb CO<sub>2</sub>/bottle
| 0.002 lb CO<sub>2</sub>/bottle
|-
|-
| Packing
| Packaging
| n/a kWh/bottle
| 0.00 kWh/bottle
| n/a lb CO<sub>2</sub>/bottle
| 0.00 lb CO<sub>2</sub>/bottle
|-
|-
|'''Total (1 bottle)'''
! Total (1 bottle)
|'''0.038 kWh/bottle'''
! 0.021 kWh/bottle
|'''0.016 lb CO<sub>2</sub>/bottle'''
! 0.010 lb CO<sub>2</sub>/bottle
|-
|-
|'''Total (all sold bottles)'''
! Total (for 100,000 bottles sold)
|'''371 kWh'''
! 2,141 kWh
|'''165 lb CO<sub>2</sub>'''
! 1,039 lb CO<sub>2</sub>
|}
|}


==Impacts==
== Research Synthesis ==
*****environmental impacts


==Research Synthesis==
==== Embedded Energy, CO<sub>2</sub> Emissions in Materials ====
====Embedded Energy, CO<sub>2</sub> Emissions in Materials====


During the Fall of 2019, Humboldt State University chose to support the Zero Waste Humboldt, specializing in providing waste reduction solutions
During the Fall of 2019, Cal Poly Humboldt chose to support the Zero Waste Humboldt, specializing in providing waste reduction solutions
through public education, advocacy, and technical assistance and training <ref>https://zerowastehumboldt.org/</ref>, to end the use of transporting beer bottles to be recycled and to promote local bottle washing. This project hopes to influence Lost Coast Brewery’s possibility of investing in a bottle washing machine. Students in ENRG 308, kept in contact with Scot, the manager of Lost Coast brewery, to determine factors such as bottle sold, materials, and where shipments go etc. By analyzing the materials used, transportation, and the packaging, we were able to determine embedded energy and carbon dioxide emissions within a virgin, recycled, and washed beer bottle. This type of bottle washing is a common practice in many European countries and our findings show why. The energy used to wash a bottle is far less than a mixed bottle consisting of virgin and recycling materials. This literature review will go over the embedded energy and CO<sub>2</sub> emissions of the individual products, the energy, and carbon impact of transporting the products, as well as creating a total energy and carbon dioxide impact of the product once the virgin bottle is bought.  
through public education, advocacy, and technical assistance and training,<ref>http://web.archive.org/web/20210123144400/https://zerowastehumboldt.org/</ref> to end the use of transporting beer bottles to be recycled and to promote local bottle washing. This project hopes to influence Lost Coast Brewery's possibility of investing in a bottle washing machine. Students in ENRG 308, kept in contact with Scot, the manager of Lost Coast brewery, to determine factors such as bottle sold, materials, and where shipments go etc. By analyzing the materials used, transportation, and the packaging, we were able to determine embedded energy and carbon dioxide emissions within a virgin, recycled, and washed beer bottle. This type of bottle washing is a common practice in many European countries and our findings show why. The energy used to wash a bottle is far less than a mixed bottle consisting of virgin and recycling materials. This literature review will go over the embedded energy and CO<sub>2</sub> emissions of the individual products, the energy, and carbon impact of transporting the products, as well as creating a total energy and carbon dioxide impact of the product once the virgin bottle is bought.


Embodied or embedded energy (EE) is defined as the energy used during the entire life cycle of a product. For example, the EE of a virgin bottle or mixed bottle could include extraction and processing of raw materials, manufacturing, transportation, distribution, use, reuse, recycling. Assuming that in all cased disposal is needed, this was kept out. The process of returning a used bottle to Lost Coast Brewery is assumed that it takes no extra transportation. This was a portion of EE calculations for the three bottle types. And if a bottle washing machine was purchased by Lost Coast Brewery, people who drop off bottles would be coming for more than just a drop-off. EE calculations are used to conduct [[life cycle assessment]]s (LCA). LCA is a well-explored concept and has been used as an environmental management tool since the late 1960’s.<ref>Menzies, Gillian F., Seyhan Turan, and Philip FG Banfill. "Life-cycle assessment and embodied energy: a review."Proceedings of the Institution of Civil Engineers-Construction Materials 160.4 (2007): 135-144</ref> LCA provides a tool for evaluating the relative environmental impact of various materials and calculates externalities otherwise excluded from pricing. Our LCA will include emissions and the EE of the materials and shipping.<ref>http://buildingsdatabook.eren.doe.gov/TableView.aspx?table=Notes/</ref>
Embodied or embedded energy (EE) is defined as the energy used during the entire life cycle of a product. For example, the EE of a virgin bottle or mixed bottle could include extraction and processing of raw materials, manufacturing, transportation, distribution, use, reuse, recycling. Assuming that in all cased disposal is needed, this was kept out. The process of returning a used bottle to Lost Coast Brewery is assumed that it takes no extra transportation. This was a portion of EE calculations for the three bottle types. And if a bottle washing machine was purchased by Lost Coast Brewery, people who drop off bottles would be coming for more than just a drop-off. EE calculations are used to conduct [[life cycle assessment]]s (LCA). LCA is a well-explored concept and has been used as an environmental management tool since the late 1960's.<ref>Menzies, Gillian F., Seyhan Turan, and Philip FG Banfill. "Life-cycle assessment and embodied energy: a review."Proceedings of the Institution of Civil Engineers-Construction Materials 160.4 (2007): 135-144</ref> LCA provides a tool for evaluating the relative environmental impact of various materials and calculates externalities otherwise excluded from pricing. Our LCA will include emissions and the EE of the materials and shipping.<ref>http://buildingsdatabook.eren.doe.gov/TableView.aspx?table=Notes/</ref>


Some background information:
Some background information:
* [https:///www.lostcoast.com/ Lost Coast Brewery]
* [https:///www.lostcoast.com/ Lost Coast Brewery]


====Embedded Energy and CO<sub>2</sub> Emissions in materials====
==== Embedded Energy and CO<sub>2</sub> Emissions in materials ====


Embedded Energy and CO<sub>2</sub> emissions of Virgin Bottle Material


Embedded Energy and CO<sub>2</sub> emissions of Virgin Bottle Material
{| class="wikitable"
! Material
! Embedded Energy (kWh/bottle)
! CO<sub>2</sub> Emissions (lb CO<sub>2</sub>/bottle)
|-
| Sand
| 0.057
| 0.026
|-
| Limestone
| 0.002
| 0.001
|-
| Feldspar
| 0.017
| 0.008
|-
| Soda Ash
| 0.130
| 0.060
|-
| Virgin Melting
| 0.644
| 0.295
|-
! Total
| 0.850
| 0.390
|}


{| class="wikitable sortable"
! Material !! Embedded Energy (kWh/bottle) !! CO<sub>2</sub> Emissions (lb CO<sub>2</sub>/bottle)
|-
| Sand || 0.057 || 0.026
|-
| Limestone || 0.002 || 0.001
|-
| Feldspar || 0.017 || 0.008
|-
| Soda Ash || 0.130 || 0.060
|-
| Virgin Melting || 0.644 || 0.295
|-
|'''Total''' || 0.850 || 0.390
|}


'''Mixed Bottles and Washed Bottles'''
'''Mixed Bottles and Washed Bottles'''


-The mixed bottles are made up the Virgin bottle material along with a mixed amount of recycled amber glass material. Here are the materials broken down:
* The mixed bottles are made up the Virgin bottle material along with a mixed amount of recycled amber glass material. Here are the materials broken down:
*Sand: 70% of a new bottle is made up of sand
* Sand: 70% of a new bottle is made up of sand
*Soda Ash: Around 2% of soda ash is used in creating a bottle. Soda ash plays a vital role to reduce the furnace temperature necessary to melt the silica used. This reduces the energy required to produce the glass.  
* Soda Ash: Around 2% of soda ash is used in creating a bottle. Soda ash plays a vital role to reduce the furnace temperature necessary to melt the silica used. This reduces the energy required to produce the glass.
*Feldspar: Each bottle is about 8% feldspar
* Feldspar: Each bottle is about 8% feldspar
*Limestone: Each bottle is about 15% Limestone
* Limestone: Each bottle is about 15% Limestone
*Recycled amber glass: The amount of glass that is recycled in a recycled bottle is normally around 80% of the bottle
* Recycled amber glass: The amount of glass that is recycled in a recycled bottle is normally around 80% of the bottle
 
====Embedded Energy and CO<sub>2</sub> Emissions in Transportation====


==== Embedded Energy and CO<sub>2</sub> Emissions in Transportation ====


'''Transport by Land'''
'''Transport by Land'''


For Trucks the Fuel efficiency of Class 8 Truck by Vehicle Weight Range on Flat Terrain at 65 mph 9.2 miles/gal <ref name="cta">http://cta.ornl.gov/vtmarketreport/pdf/chapter3_heavy_trucks.pdf</ref> which we then convert into km which is 14.8 km/gal.
For Trucks the Fuel efficiency of Class 8 Truck by Vehicle Weight Range on Flat Terrain at 65 mph 9.2 miles/gal<ref name="cta">http://cta.ornl.gov/vtmarketreport/pdf/chapter3_heavy_trucks.pdf</ref> which we then convert into km which is 14.8 km/gal.


*For Diesel Fuel
* For Diesel Fuel
**Energy intensity: 135.8 MJ/gal<ref>https://www.extension.iastate.edu/agdm/wholefarm/pdf/c6-87.pdf</ref>
** Energy intensity: 135.8 MJ/gal<ref>https://www.extension.iastate.edu/agdm/wholefarm/pdf/c6-87.pdf</ref>
 
** Carbon Intensity 10.15 kg CO<sub>2</sub> /gal<ref name= "EIA">http://www.eia.gov/tools/faqs/faq.cfm?id=307&t=11</ref>
**Carbon Intensity 10.15 kg CO<sub>2</sub> /gal <ref name= “EIA”>http://www.eia.gov/tools/faqs/faq.cfm?id=307&t=11</ref>
* General embedded energy in shipping by land<ref>http://pubs.acs.org/doi/pdf/10.1021/es702969f</ref>
 
*General embedded energy in shipping by land <ref>http://pubs.acs.org/doi/pdf/10.1021/es702969f</ref>


traveled by truck: 2.7 MJ/ t-km
traveled by truck: 2.7 MJ/ t-km


Traveled by Truck: 180 (t CO<sub>2</sub>E / t-km x 10^6)  
Traveled by Truck: 180 (t CO<sub>2</sub>E / t-km x 10^6)


36.63 MJ/vehicle km<ref>http://cta.ornl.gov/data/chapter2.shtml </ref>
36.63 MJ/vehicle km<ref>http://cta.ornl.gov/data/chapter2.shtml</ref><ref>http://www.dot.ca.gov/trafficops/trucks/quickguide.html</ref>
<ref>http://www.dot.ca.gov/trafficops/trucks/quickguide.html</ref>


General embedded CO<sub>2</sub> in shipping by land
General embedded CO<sub>2</sub> in shipping by land
80 g/tonne/km<ref> http://www.ics-shipping.org/docs/co2,</ref>
80 g/tonne/km<ref>http://www.ics-shipping.org/docs/co2,</ref>


====Embedded Energy and CO<sub>2</sub> Emissions in Materials====
==== Embedded Energy and CO<sub>2</sub> Emissions in Materials ====


It was found that Humboldt County transfers their beer bottles to Sacramento California and/or Los Angeles, California. <ref>https://humboldtgov.org/DocumentCenter/View/4203</ref>
It was found that Humboldt County transfers their beer bottles to Sacramento California and/or Los Angeles, California.<ref>https://humboldtgov.org/DocumentCenter/View/4203</ref>


The efficiency for a variety of trash trucks was averaged at 3 miles per gallon which was then converted to km instead of miles<ref>http://www.cert.ucr.edu/events/pems2014/liveagenda/25sandhu.pdf</ref> which ended being 4.8 km/gal.
The efficiency for a variety of trash trucks was averaged at 3 miles per gallon which was then converted to km instead of miles<ref>http://www.cert.ucr.edu/events/pems2014/liveagenda/25sandhu.pdf</ref> which ended being 4.8 km/gal.
Line 221: Line 233:
Diesel Energy intensity: 135.8 MJ/gal<ref>https://www.extension.iastate.edu/agdm/wholefarm/pdf/c6-87.pdf</ref>
Diesel Energy intensity: 135.8 MJ/gal<ref>https://www.extension.iastate.edu/agdm/wholefarm/pdf/c6-87.pdf</ref>


Carbon Intensity 10.15 kg CO<sub>2</sub> /gal <ref>http://www.eia.gov/tools/faqs/faq.cfm?id=307&t=11</ref>
Carbon Intensity 10.15 kg CO<sub>2</sub> /gal<ref>http://www.eia.gov/tools/faqs/faq.cfm?id=307&t=11</ref>
 
== Caveats ==
 
* To obtain the numbers for the total embedded energy and total CO<sub>2</sub> for washed bottles, we assumed that 20% of the bottle was recycled material. This assumptions can be easily changed to any % recycled content in the spreadsheet.
* We did not include labels because the comparison would have been the same, as all bottles have labels.
* We assumed that the trucks were 100% full each time when transporting bottles to Lost Coast Brewery.
* For bottle washing we used the XP1 (with a 6000 bottles/hour capacity) machine and assumed a 12 hours per day workload and that the water will stay warm for that entire time. When selecting a bottle washing machine, these assumptions will need to be refined based upon that machine's specifications.
* We did not include the transportation of the raw and recycled materials.
* We did not include the slightly extra embedded energy needed to manufacture a thicker glass bottle for washing.
 
== Next Steps ==


==Caveats==
After completing the initial analysis, there are various alterations to the methods that could be made to create even more accurate results. These include:
*To obtain the numbers for the total embedded energy and total CO<sub>2</sub> for washed bottles, we assumed that 20% of the bottle was recycled material.
*In the spreadsheet, the percentage of the material recycled is interchangeable based on different finding and/or needs.
*In these calculations we did not include labels in our study because the comparison would have been the same, as all bottles have labels.
*In our calculations, we assumed that the trucks were 100% full each time when transporting virgin and/or recycled bottles to Lost Coast Brewery.
*In these calculations we assumed that the average bottle washing machine works 12 hours per day.
*In these calculations we did not include the transportation of the raw and recycled materials.


==Next Steps==
* What are people's methods of washing the bottles? Is it significant enough to change the final outputs?
After completing the initial analysis, there are various alterations to the methods that could be made to create even more accurate results. These include:
* Determine the volume of waste avoided by the implementation of a policy such as this.
*What are people's methods of washing the bottles? Is it significant enough to change the final outputs?
* Calculate the embedded energy and carbon dioxide emissions in each unit produced by the manufacturing facilities, and the acquisition of the raw materials.
*How often are the mixed bottles actually reused compared to the number of virgin bottles?
* Explore alternate options as to whether or not other viable products have the potential to reduce the embedded energy or carbon dioxide emissions from the bottles.
*How many times does the bottle need to be washed to be equivalent to a virgin bottle? What about a mixed bottle?
* Determine outlets for promoting and distributing this research to make it widely accessible.
*Determine the volume of waste avoided by the implementation of a policy such as this.
* Partnership with other CSUs to strive towards waste, energy, and CO2 reduction initiatives.
*Calculate the embedded energy and carbon dioxide emissions in each unit produced by the manufacturing facilities, and the acquisition of the raw materials.
*Explore alternate options as to whether or not other viable products have the potential to reduce the embedded energy or carbon dioxide emissions from the bottles.
*Determine outlets for promoting and distributing this research to make it widely accessible.
*Partnership with other CSUs to strive towards waste, energy, and CO2 reduction initiatives.


== Team 1:Bottle Washing Bosses==
== Teams ==
* [[User:TEAMMEMBER|Andrew Braswell]]
* [[User:TEAMMEMBER|Ileana Spoelstra]]
* [[User:TEAMMEMBER|Kelly Randazzo]]
* [[User:TEAMMEMBER|Anthony Pigone]]


==Team 2 Bad News Beers==
* '''Bottle Washing Bosses:''' Andrew Braswell, Ileana Spoelstra, Kelly Randazzo, Anthony Pigone
* [[User:Emilyread|Emily Read]]
* '''Bad News Beers:''' [[User:Emilyread|Emily Read]], [[User:Inesm|Ines Morales]], [[User:Aws216|Austin Sani]], [[User:Cad748|Clarissa Duron]]
* [[User:Inesm|Ines Morales]]
* '''Team 3:''' Gabe Kim, Kaitlyn McGinnis,Cassidy Mullennix
* [[User:Aws216|Austin Sani]]
* '''Brainstorm Boys:''' Bret Buck, Ivan Ramirez, Dale Ebersole
* [[User:Cad748|Clarissa Duron]]
* '''Bottle Washing Beaches (Meta Team):''' [[User:Alexe31|Alexandria Eastburn]], [[User:Sarajune|Sara June]], [[User:HappinessOnEarth|Alyssa Della Ripa]]


==Team 3==
== References ==
* [[Kim, Gabe]]
* [[McGinnis, Kaitlyn]]
* [[Mullennix, Cassidy]]


==Brainstorm Boys==
<references />
* [[User:BretB|Bret Buck]]
* [[User:Dale|Dale Ebersole]]
* [[User:Ivan|Ivan Ramirez]]


==Bottle Washing Beaches==
{{Page data}}
* [[User:Alexe31|Alexandria Eastburn]]
* [[User:Sarajune|Sara June]]
* [[User:HappinessOnEarth|Alyssa Della Ripa]]
* [[Fen Harley]]


==References==
[[Category:Life cycle analysis]]
[[Category:Engr308 Technology and the Environment]]

Latest revision as of 19:21, 8 June 2023

CO2 Emissions of a Washed Bottle (1).png
FA info icon.svg Angle down icon.svg Project data
OKH Manifest Download

The research project was a collaboration between Cal Poly Humboldt's Engr308 Technology and the Environment and Zero Waste Humboldt (ZWH) during the Fall of 2019. The client liaison on this project is

  • Maggie Gainer, Zero Waste Humboldt

The objective of this project is to analyze and compare the impacts of recycling beer bottles to local beer bottle washing in the terms of embedded carbon dioxide emissions and embedded energy. While researching, we were able to conduct a comparative examination between the life cycle analysis' for both recycled bottles and washed bottles. The glass beer bottles we used for observation were from Lost Coast Brewery in Humboldt County.

Findings[edit | edit source]

Embedded energy of the production of a single mixed bottle versus a single washed bottle. Source as produced by File:Bottle Washing Analysis.xlsx.
Embedded CO2 of the production of a single mixed bottle versus a single washed bottle. Source as produced by File:Bottle Washing Analysis.xlsx.

This study of Virgin Bottles, Mixed Bottles, and Washed Bottles compared two metrics: carbon dioxide emissions and embedded energy. It was concluded that the materials used, the transport of, and packaging of a single beer bottle requires 0.72 kilowatt-hours of energy and is responsible for 0.323 pounds of carbon dioxide emissions. In comparison, a single mixed bottle is responsible for using 0.69 kilowatt-hours of energy, releasing 0.306 pounds of carbon dioxide. A single washed bottle is responsible for using 0.021 kilowatt-hours of energy, releasing 0.010 pounds of carbon dioxide emissions.

The assumptions used to obtain these results can be seen below in further detail in the section titled Caveats.

Virgin Bottles Mixed Bottles Washed Bottles
Embedded Energy (kWh/bottle) 0.72 0.69 0.021
Carbon Dioxide (lbs/bottle) 0.323 0.306 0.010

Based on the numbers shown above, we are able to conduct a comparative analysis showing the embedded energy and CO2 between a single mixed bottle and a single washed bottle. The calculations and assumptions used to aquire these results can be seen in further detail in the following spreadsheet:

The spreadsheet allows for others interested in performing a similar analysis to easily input values pertaining to their particular study area. It is our hope that with this information and the pre-assembled spreadsheet, other institutions will be able to reach similar compelling conclusions that have the potential to influence future policies.

Virgin Bottles[edit | edit source]

Embedded energy in the production of a virgin beer bottle by source as produced by File:Bottle Washing Analysis.xlsx.
Carbon Dioxide emissions from the production of a virgin beer bottle by source as produced by File:Bottle Washing Analysis.xlsx.

The bottles analyzed in this study were 12oz glass bottles, produced by a company in Los Angeles, California and then transported to Lost Coast Brewery in Eureka, California. We measured embedded energy of a virgin bottle by accounting for materials, transportation, and packaging. A virgin bottle is defined as a bottle that has completely new materials. Therefore, the life cycle analysis was determined through the manufacturing processes necessary for the creation of a new glass bottle. The embedded carbon dioxide comes from the melting of materials, heating water, and other CO2 emitted during transportation. The embedded energy for a virgin bottle is 0.72 kWh/bottle and releases 0.323 pounds of CO2

Output Embedded Energy Carbon Dioxide Emissions
Materials 0.63 kWh/bottle 0.269 lb CO2/bottle
Transportation 0.086 kWh/bottle 0.051 lb CO2/bottle
Packaging 0.007 kWh/bottle 0.003 lb CO2/bottle
Total (1 bottle) 0.72 kWh/bottle 0.323 lb CO2/bottle
Total (100,000 bottles sold) 72,487 kWh 32,286 lb CO2

Mixed Bottles[edit | edit source]

Embedded energy in the production of a mixed beer bottle by source as produced by File:Bottle Washing Analysis.xlsx.
Carbon Dioxide emissions from the production of a mixed beer bottle by source as produced by File:Bottle Washing Analysis.xlsx.

The recycled bottles analyzed in this study were the 12oz glass bottles from Lost Coast Brewery in Eureka, California. These bottles were produced by the company Saxco based out of Sacramento, California and were transported to Lost Coast Brewery in Eureka, California. It was estimated that 20% of all the bottles purchased were recycled. This is a user input that we assumed based on dialog with Lost Coast Brewery and is changeable on the spreadsheet. As recycled materials are made into bottles again, the melting process was found to be similar to creating a virgin bottle. It takes a similar process and emits a little under that of a virgin bottle. Further, the transportation was less in a recycled bottle because of the difference in distance. The embedded energy a mixed bottle was 0.69 kWh/bottle and released 0.306 pounds of carbon dioxide emissions.

Output Embedded Energy Carbon Dioxide Emissions
Materials 0.60 kWh/bottle 0.252 lb CO2/bottle
Transportation 0.086 kWh/bottle 0.051 lb CO2/bottle
Packaging 0.007 kWh/bottle 0.003 lb CO2/bottle
Total (1 bottle) 0.69 kWh/bottle 0.306 lb CO2/bottle
Total (100,000 bottles sold) 68,942 kWh 30,592 lb CO2

Washed Bottles[edit | edit source]

Embedded energy in washed bottles (including making the bottle and washing it 35 times) by source (note that materials include the washing process) as produced by File:Bottle Washing Analysis.xlsx.
Carbon Dioxide emissions from washed bottles (including making the bottle and washing it 35 times) by source (note that materials include the washing process) as produced by File:Bottle Washing Analysis.xlsx.


We predicted that the bottles being washed were 20% recycled bottles to begin with (although the bottle might need to be thicker for washing, which would raise the embedded energy and CO2 somewhat). It was assumed that transportation would not emit extra energy for a washed bottles because consumers could drop off their bottles during a regular shopping trip. Embedded energy and CO2 came from each time a new or recycled bottle was made, along with the process of running the bottle washing machine. The amount of times a bottle can be re-washed ranges from 25 to 50 times and is a number a user can input - we used 35 for the following findings. The embedded energy in a washed bottle is 0.021 kWh/bottle and releases 0.010 carbon dioxide emissions.

Output Embedded Energy Carbon Dioxide Emissions
Materials 0.019 kWh/bottle 0.008 lb CO2/bottle
Transportation 0.002 kWh/bottle 0.002 lb CO2/bottle
Packaging 0.00 kWh/bottle 0.00 lb CO2/bottle
Total (1 bottle) 0.021 kWh/bottle 0.010 lb CO2/bottle
Total (for 100,000 bottles sold) 2,141 kWh 1,039 lb CO2

Research Synthesis[edit | edit source]

Embedded Energy, CO2 Emissions in Materials[edit | edit source]

During the Fall of 2019, Cal Poly Humboldt chose to support the Zero Waste Humboldt, specializing in providing waste reduction solutions through public education, advocacy, and technical assistance and training,[1] to end the use of transporting beer bottles to be recycled and to promote local bottle washing. This project hopes to influence Lost Coast Brewery's possibility of investing in a bottle washing machine. Students in ENRG 308, kept in contact with Scot, the manager of Lost Coast brewery, to determine factors such as bottle sold, materials, and where shipments go etc. By analyzing the materials used, transportation, and the packaging, we were able to determine embedded energy and carbon dioxide emissions within a virgin, recycled, and washed beer bottle. This type of bottle washing is a common practice in many European countries and our findings show why. The energy used to wash a bottle is far less than a mixed bottle consisting of virgin and recycling materials. This literature review will go over the embedded energy and CO2 emissions of the individual products, the energy, and carbon impact of transporting the products, as well as creating a total energy and carbon dioxide impact of the product once the virgin bottle is bought.

Embodied or embedded energy (EE) is defined as the energy used during the entire life cycle of a product. For example, the EE of a virgin bottle or mixed bottle could include extraction and processing of raw materials, manufacturing, transportation, distribution, use, reuse, recycling. Assuming that in all cased disposal is needed, this was kept out. The process of returning a used bottle to Lost Coast Brewery is assumed that it takes no extra transportation. This was a portion of EE calculations for the three bottle types. And if a bottle washing machine was purchased by Lost Coast Brewery, people who drop off bottles would be coming for more than just a drop-off. EE calculations are used to conduct life cycle assessments (LCA). LCA is a well-explored concept and has been used as an environmental management tool since the late 1960's.[2] LCA provides a tool for evaluating the relative environmental impact of various materials and calculates externalities otherwise excluded from pricing. Our LCA will include emissions and the EE of the materials and shipping.[3]

Some background information:

Embedded Energy and CO2 Emissions in materials[edit | edit source]

Embedded Energy and CO2 emissions of Virgin Bottle Material

Material Embedded Energy (kWh/bottle) CO2 Emissions (lb CO2/bottle)
Sand 0.057 0.026
Limestone 0.002 0.001
Feldspar 0.017 0.008
Soda Ash 0.130 0.060
Virgin Melting 0.644 0.295
Total 0.850 0.390


Mixed Bottles and Washed Bottles

  • The mixed bottles are made up the Virgin bottle material along with a mixed amount of recycled amber glass material. Here are the materials broken down:
  • Sand: 70% of a new bottle is made up of sand
  • Soda Ash: Around 2% of soda ash is used in creating a bottle. Soda ash plays a vital role to reduce the furnace temperature necessary to melt the silica used. This reduces the energy required to produce the glass.
  • Feldspar: Each bottle is about 8% feldspar
  • Limestone: Each bottle is about 15% Limestone
  • Recycled amber glass: The amount of glass that is recycled in a recycled bottle is normally around 80% of the bottle

Embedded Energy and CO2 Emissions in Transportation[edit | edit source]

Transport by Land

For Trucks the Fuel efficiency of Class 8 Truck by Vehicle Weight Range on Flat Terrain at 65 mph 9.2 miles/gal[4] which we then convert into km which is 14.8 km/gal.

  • For Diesel Fuel
    • Energy intensity: 135.8 MJ/gal[5]
    • Carbon Intensity 10.15 kg CO2 /gal[6]
  • General embedded energy in shipping by land[7]

traveled by truck: 2.7 MJ/ t-km

Traveled by Truck: 180 (t CO2E / t-km x 10^6)

36.63 MJ/vehicle km[8][9]

General embedded CO2 in shipping by land 80 g/tonne/km[10]

Embedded Energy and CO2 Emissions in Materials[edit | edit source]

It was found that Humboldt County transfers their beer bottles to Sacramento California and/or Los Angeles, California.[11]

The efficiency for a variety of trash trucks was averaged at 3 miles per gallon which was then converted to km instead of miles[12] which ended being 4.8 km/gal.

On one truck they can transport up to 20 pallets with holding 4,290 bottles per pallet

Diesel Energy intensity: 135.8 MJ/gal[13]

Carbon Intensity 10.15 kg CO2 /gal[14]

Caveats[edit | edit source]

  • To obtain the numbers for the total embedded energy and total CO2 for washed bottles, we assumed that 20% of the bottle was recycled material. This assumptions can be easily changed to any % recycled content in the spreadsheet.
  • We did not include labels because the comparison would have been the same, as all bottles have labels.
  • We assumed that the trucks were 100% full each time when transporting bottles to Lost Coast Brewery.
  • For bottle washing we used the XP1 (with a 6000 bottles/hour capacity) machine and assumed a 12 hours per day workload and that the water will stay warm for that entire time. When selecting a bottle washing machine, these assumptions will need to be refined based upon that machine's specifications.
  • We did not include the transportation of the raw and recycled materials.
  • We did not include the slightly extra embedded energy needed to manufacture a thicker glass bottle for washing.

Next Steps[edit | edit source]

After completing the initial analysis, there are various alterations to the methods that could be made to create even more accurate results. These include:

  • What are people's methods of washing the bottles? Is it significant enough to change the final outputs?
  • Determine the volume of waste avoided by the implementation of a policy such as this.
  • Calculate the embedded energy and carbon dioxide emissions in each unit produced by the manufacturing facilities, and the acquisition of the raw materials.
  • Explore alternate options as to whether or not other viable products have the potential to reduce the embedded energy or carbon dioxide emissions from the bottles.
  • Determine outlets for promoting and distributing this research to make it widely accessible.
  • Partnership with other CSUs to strive towards waste, energy, and CO2 reduction initiatives.

Teams[edit | edit source]

References[edit | edit source]

  1. ↑ http://web.archive.org/web/20210123144400/https://zerowastehumboldt.org/
  2. ↑ Menzies, Gillian F., Seyhan Turan, and Philip FG Banfill. "Life-cycle assessment and embodied energy: a review."Proceedings of the Institution of Civil Engineers-Construction Materials 160.4 (2007): 135-144
  3. ↑ http://buildingsdatabook.eren.doe.gov/TableView.aspx?table=Notes/
  4. ↑ http://cta.ornl.gov/vtmarketreport/pdf/chapter3_heavy_trucks.pdf
  5. ↑ https://www.extension.iastate.edu/agdm/wholefarm/pdf/c6-87.pdf
  6. ↑ http://www.eia.gov/tools/faqs/faq.cfm?id=307&t=11
  7. ↑ http://pubs.acs.org/doi/pdf/10.1021/es702969f
  8. ↑ http://cta.ornl.gov/data/chapter2.shtml
  9. ↑ http://www.dot.ca.gov/trafficops/trucks/quickguide.html
  10. ↑ http://www.ics-shipping.org/docs/co2,
  11. ↑ https://humboldtgov.org/DocumentCenter/View/4203
  12. ↑ http://www.cert.ucr.edu/events/pems2014/liveagenda/25sandhu.pdf
  13. ↑ https://www.extension.iastate.edu/agdm/wholefarm/pdf/c6-87.pdf
  14. ↑ http://www.eia.gov/tools/faqs/faq.cfm?id=307&t=11
FA info icon.svg Angle down icon.svg Page data
Authors Alexandria Eastburn, Sara June, Lonny Grafman, Alyssa Della Ripa
License CC-BY-SA-3.0
Language English (en)
Related 0 subpages, 10 pages link here
Impact 1,053 page views
Created November 15, 2019 by Lonny Grafman
Modified June 8, 2023 by Felipe Schenone
Cite as Alexandria Eastburn, Sara June, Lonny Grafman, Alyssa Della Ripa (2019–2023). "Bottle washing analysis". Appropedia. Retrieved April 24, 2024.
API queries basic, semantic, html, files, more
Retrieved from "https://www.appropedia.org/w/index.php?title=Bottle_washing_analysis&oldid=739567"
Cookies help us deliver our services. By using our services, you agree to our use of cookies.