In today's sustainability market where there are several tools to rate and grade the ‘green’ level of modern day infrastructure, the multi-tiered credit rating system called Envision provides an holistic approach to tackle the issue. Developed by the Institute for Sustainable Infrastructure (ISI), Envision has around 60 sustainability credits to score points in order to reach a recognized level of achievement. Life cycle assessment (LCA) is another tool that is gaining industry-wide acceptance for assessing potential environmental impacts. LCA is recognized by Envision as a good way to assess several of the available credits in their system. An LCA performed for Blue Plains Advanced Wastewater Treatment Facility (AWTF), Washington, D.C., USA was used as an example case study to show how credits could be calculated for a used water treatment facility.

A Life Cycle Assessment (LCA) is a ‘cradle to grave’ assessment of the environmental impact that a product, process or set of activities has during its whole life (Bauman & Tillman 2004 and ISO 2006). The assessment includes direct environmental impacts from the use of the process and also its indirect impacts due to the manufacture and transportation of the required raw materials, chemicals and equipment. The LCA attempts to build a comprehensive, life cycle accounting of the resource use and global environmental impacts accumulated by the abstraction of raw materials from the environment all the way to the final emissions and disposal of materials back to the environment. It is a truly ‘holistic’ method for assessing environmental impacts.

There are several programs that can be used to carry out an LCA for a product or process, which are listed in Table 1 below.

Table 1

List of LCA vendors

ToolsDeveloper/VendorLatest VersionWebsite
SimaPro PRe Consultant Version 8 http://www.pre-sustainability.com/simapro 
GaBi thinkstep Version 6 http://www.gabi-software.com/america/index/ 
OpenLCA GreenDelta TC Version 1.4 http://www.openlca.org/ 
Economic Input-Output LCA Green Design Institute
Carnegie Mellon University 
2002 http://www.eiolca.net/ 
ToolsDeveloper/VendorLatest VersionWebsite
SimaPro PRe Consultant Version 8 http://www.pre-sustainability.com/simapro 
GaBi thinkstep Version 6 http://www.gabi-software.com/america/index/ 
OpenLCA GreenDelta TC Version 1.4 http://www.openlca.org/ 
Economic Input-Output LCA Green Design Institute
Carnegie Mellon University 
2002 http://www.eiolca.net/ 

Envision is a tool that uses an objective framework of criteria for the sustainable planning, design, construction and operation of infrastructure projects (ISI 2012). It can be used for such things as bridges, dams, water and wastewater treatment plants, and other civil infrastructure. It is not intended to be used for buildings and facilities that are more commonly assessed using programs such as LEED (Leadership in Energy and Environmental Design). Envision is a system with a broad perspective that recognizes that the sustainability of a project must be considered from the planning stage through the lifecycle of the project.

Envision consists of up to 60 credits categorized into 5 categories: Quality of Life; Leadership; Resource Allocation; Natural World; and Climate and Risk. LCA could be used to assist in assessing impacts across all of these categories, but is particularly useful for quantifying credits in the 2 categories of Resource Allocation and Climate and Risk. Whilst not mandating its use, Envision recognizes LCA as a useful tool that can be used to estimate the impacts of a project on the environment in general and also identifies specific credits for which an LCA could be used.

Table 2 presents a list of Envision credits that explicitly mention the use of LCA to assess sustainability improvements or require mass flows to be quantified, which can be effectively done using LCA.

Table 2

List of LCA credit in Envision 2.0 (ISI 2012)

Credit NumberCredit descriptionHow to use LCA for credit
RA 1.1 Reduce net embodied energy 
  • Perform LCA for the material of construction to understand the net impacts

  • Identify the energy required for extraction, refinement and manufacturing of the raw material

  • Identify and select any raw materials that can be used to reduce net embodied energy

  • Document the net reduction in the embodied energy for the product

 
RA 1.5 Divert waste from landfills 
  • Perform LCA for the material of construction to understand the net impacts

  • Identify waste material mass flows going to landfills

  • Identify and select any waste materials that can be or recycled

  • Document the percentage of waste materials being recycled

 
RA 2.1 Reduce energy consumption 
  • Perform LCA to determine the energy consumption across the wastewater treatment plant

  • Identify the larger energy sinks across the facility

  • Identify any processes or technologies to reduce the energy consumption

  • Document net energy savings

 
RA 2.2 Use renewable energy 
  • Perform LCA for the existing energy mix used by the treatment facility

  • Identify other sources of renewable energy available around the facility. For example, biogas vs natural gas, solar, hydro, wind, etc.

  • Identify processes that replace existing energy sources with renewable energy. For example, digester heating, Combined Heat and Power, solar, hydro, wind, etc.

  • Document net reduction in environmental impacts

 
RA 3.1 Protect fresh water availability 
  • Perform LCA to determine the water footprint of the facility during construction and operation

  • Identify the processes that can use reuse/reclaimed water from the facility

  • Estimate the additional environmental impacts of producing reclaimed water, if the facility is not already designed for it

  • Document the positive impacts of using reuse/reclaimed water on fresh water availability in the area

 
RA 3.2 Reduce potable water consumption 
  • Perform LCA to determine the water footprint of the facility during construction and operation

  • Identify the processes that can use greywater, reuse/reclaimed water from the facility or stormwater

  • Document the percent reduction in potable water consumption by the facility

 
CR 1.1 Reduce greenhouse gas emissions 
  • Perform LCA to determine the net greenhouse gas emissions at the facility

  • Identify processes or technologies that can reduce the net carbon emissions. For example, land application of biosolids vs landfill

  • Document the net reduction in carbon emissions

 
CR 1.2 Reduce air pollutant emissions 
  • Perform LCA to determine the emissions from six criteria pollutants: particulate matter, ground level ozone, carbon monoxide, sulphur oxides, nitrogen oxides and noxious odors. Alternatively, use a summation of normalized air emission impact categories using a recognized LCA method

  • Identify processes or technologies that can reduce the criteria pollutants or end point impacts

  • Document the net reduction in pollutant load

 
Credit NumberCredit descriptionHow to use LCA for credit
RA 1.1 Reduce net embodied energy 
  • Perform LCA for the material of construction to understand the net impacts

  • Identify the energy required for extraction, refinement and manufacturing of the raw material

  • Identify and select any raw materials that can be used to reduce net embodied energy

  • Document the net reduction in the embodied energy for the product

 
RA 1.5 Divert waste from landfills 
  • Perform LCA for the material of construction to understand the net impacts

  • Identify waste material mass flows going to landfills

  • Identify and select any waste materials that can be or recycled

  • Document the percentage of waste materials being recycled

 
RA 2.1 Reduce energy consumption 
  • Perform LCA to determine the energy consumption across the wastewater treatment plant

  • Identify the larger energy sinks across the facility

  • Identify any processes or technologies to reduce the energy consumption

  • Document net energy savings

 
RA 2.2 Use renewable energy 
  • Perform LCA for the existing energy mix used by the treatment facility

  • Identify other sources of renewable energy available around the facility. For example, biogas vs natural gas, solar, hydro, wind, etc.

  • Identify processes that replace existing energy sources with renewable energy. For example, digester heating, Combined Heat and Power, solar, hydro, wind, etc.

  • Document net reduction in environmental impacts

 
RA 3.1 Protect fresh water availability 
  • Perform LCA to determine the water footprint of the facility during construction and operation

  • Identify the processes that can use reuse/reclaimed water from the facility

  • Estimate the additional environmental impacts of producing reclaimed water, if the facility is not already designed for it

  • Document the positive impacts of using reuse/reclaimed water on fresh water availability in the area

 
RA 3.2 Reduce potable water consumption 
  • Perform LCA to determine the water footprint of the facility during construction and operation

  • Identify the processes that can use greywater, reuse/reclaimed water from the facility or stormwater

  • Document the percent reduction in potable water consumption by the facility

 
CR 1.1 Reduce greenhouse gas emissions 
  • Perform LCA to determine the net greenhouse gas emissions at the facility

  • Identify processes or technologies that can reduce the net carbon emissions. For example, land application of biosolids vs landfill

  • Document the net reduction in carbon emissions

 
CR 1.2 Reduce air pollutant emissions 
  • Perform LCA to determine the emissions from six criteria pollutants: particulate matter, ground level ozone, carbon monoxide, sulphur oxides, nitrogen oxides and noxious odors. Alternatively, use a summation of normalized air emission impact categories using a recognized LCA method

  • Identify processes or technologies that can reduce the criteria pollutants or end point impacts

  • Document the net reduction in pollutant load

 

In previous work (Tarallo et al. 2011), LCA was used for the Blue Plains Advance Wastewater Treatment Facility (AWTF) in Washington, D.C., USA as a tool of process selection to achieve lower effluent total nitrogen values in their two stage activated sludge system. Figure 1 presents the block diagram for the system used for the analysis.

Figure 1

Proposed bioaugmentation and no-bioaugmentation processes for Blue Plains AWTF.

Figure 1

Proposed bioaugmentation and no-bioaugmentation processes for Blue Plains AWTF.

Close modal

In the original analysis two different scenarios were analysed for this 370 million gallons per day (MGD) nutrient removal facility. The baseline case (or the no-bioaugmentation alternative) sent the nitrified wasting activated sludge (NWAS) to the biosolids handling facilities for further treatment. Alternative 1 – the bioaugmentation alternative – recycled the NWAS from the second stage activated sludge tank back to the first stage for further nitrogen removal. The LCA boundary was set around the biological treatment processes.

Subsequent to the original study, a further, hypothetical, ‘Alternative 2’ was also analysed, wherein the AWTF was hypothesized to be energy neutral and the biogas produced at the plant is used for all the facility needs. In addition, the methanol added to the denitrification tank for the baseline case was also replaced by biogenic methanol produced from biofuel. This is an assumed scenario for this paper and was not considered during the original study phase for the facility.

SimaPro developed by PRé was used as the LCA tool while the sustainability guidelines developed by Institute for Sustainable Infrastructure (ISI) were used to develop the Envision points. The overall results from the LCA are presented in Figure 2, which shows the weighted impacts of using Alternative 1 over the baseline conditions within various categories.

Figure 2

Normalized and weighted impacts of various LCA categories.

Figure 2

Normalized and weighted impacts of various LCA categories.

Close modal

The LCA outputs and the corresponding Envision scores for Alternative 1 are presented in Table 3, along with the hypothetical results for Alternative 2 in parentheses. The levels of achievement for various categories were developed using the percent improvements, with both alternatives over the baseline condition. Since the LCA categories corresponding to the Climate & Risk category of Envision (CR 1.2) have minimum impact on the total LCA (Figure 2), it was considered that the alternatives will have negligible impacts on the air quality. Therefore, ‘Conserving’ and ‘Restorative’ levels were assigned to Alternatives 1 and 2 respectively. The percent improvements of both the alternatives were used to determine the levels of achievement and finally the Envision scores. The table indicates that Alternatives 1 and 2 have respectively achieved 27% and 56% improvement over the baseline for these categories. Based on Envision recognition levels, this corresponds to a significant contribution toward a Bronze and Platinum award for the two cases if extrapolated to the total score, though the actual award level would be based on the overall percentage of points achieved for all categories, including those not directly measured using the LCA.

Table 3

Envision score for bioaugmentation at the facility for Alternatives 1 and 2

 
 

LCA is an holistic method for assessing environmental impacts. Envision is a broad-ranging tool that can be used to assess the sustainability of infrastructure projects. Coupling the two together provides a robust method not only to assess sustainability, but to investigate methods for improving the sustainability of a project across multiple objectives. An example is presented to show how this was carried out to show the positive environmental impact of bioaugmentation at a used water resource recovery facility, and how incorporation of biogenic energy and material sourcing could further improve sustainability.

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Refinement of life cycle assessment methods for water and wastewater treatment plant design. In Proceedings of the Water Environment Federation, WEFTEC 2011, pp. 1152–1163(12)
FURTHER INFORMATION
Corominas
L.
,
Foley
J.
,
Guest
J. S.
,
Hospido
A.
,
Larsen
H. F.
,
Morera
S.
&
Shaw
A.
2013
Life cycle assessment applied to wastewater treatment: state of the art
.
Water Research
47
(
15
),
5480
5492
.
IWA Working Group on Life Cycle Assessment (LCA) of Water and Wastewater Treatment on @LinkedIn (moderated group): https://www.linkedin.com/groups/4921250
Wikipedia entry for LCA: https://en.wikipedia.org/wiki/Life-cycle_assessment