the Creative Commons Attribution 4.0 License.
the Creative Commons Attribution 4.0 License.
Methodology and uncertainty estimation for measurements of methane leakage in a manufactured house
Abstract. Methane emissions from natural gas appliances and infrastructure within buildings have historically not been captured in greenhouse gas inventories, leading to under-estimates, especially in urban areas. Recent measurements of these post-meter emissions have indicated non-negligible emissions within residences, with impacts on both indoor air quality and climate. As a result, methane losses from residential buildings have recently been included in the latest U.S. national inventory, with emission factors determined from a single study of homes in California. To facilitate future additional studies investigating building methane emissions, we conducted a controlled experiment to document a methodology for such measurements and estimated associated uncertainties. We determined whole-house methane emission rates with a mass balance approach using near-simultaneous measurements of indoor and outdoor methane mole fractions at a manufactured house. We quantified the uncertainty in whole-house methane emission rates by varying the forced outdoor air ventilation rate of the manufactured house, measuring the outdoor air change rate using both sulfur hexafluoride and carbon dioxide tracers, and performing methane injections at prescribed rates. We found that the whole-house quiescent methane emission rate in the manufactured house averaged 0.34 g d-1 with methodological errors on the calculated emission rates to be approximately 20 % (root-mean-square-deviation). We also measured the quiescent leakage from the manufactured house over three months to find 24 % (1-sigma) variability in emissions over two seasons. Our findings can be used to inform plans for future studies quantifying indoor methane losses after residential meters using similar methods. Such quantification studies are sorely needed to better understand building methane emissions and their drivers to inform inventories and plan mitigation strategies.
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Notice on discussion status
The requested preprint has a corresponding peer-reviewed final revised paper. You are encouraged to refer to the final revised version.
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Preprint
(1450 KB)
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The requested preprint has a corresponding peer-reviewed final revised paper. You are encouraged to refer to the final revised version.
- Preprint
(1450 KB) - Metadata XML
- BibTeX
- EndNote
- Final revised paper
Journal article(s) based on this preprint
Interactive discussion
Status: closed
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RC1: 'Comment on egusphere-2024-2129', Hossein Maazallahi, 12 Aug 2024
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AC1: 'Reply on RC1', Anna Karion, 18 Oct 2024
The comment was uploaded in the form of a supplement: https://egusphere.copernicus.org/preprints/2024/egusphere-2024-2129/egusphere-2024-2129-AC1-supplement.pdf
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AC1: 'Reply on RC1', Anna Karion, 18 Oct 2024
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RC2: 'Comment on egusphere-2024-2129', Anonymous Referee #2, 10 Sep 2024
Methodology and uncertainty estimation for measurements of
methane leakage in a manufactured house
Anna Karion, Michael F. Link, Rileigh Robertson, Tyler Boyle, Dustin Poppendiec
Top-down (atmospheric) and bottom-up (inventory) methods of determining greenhouse gas emissions are complementary approaches, with the goal of providing feedback as to the most effective mitigation strategies. There is a significant discrepancy between these approaches for methane, and in-home emissions are probably a major contributor. The EPA methane inventory now includes an estimate of these emissions, but the emission factors are all based on one study. This manuscripts documents controlled release experiments to optimize the methods to determine these emission factors and to quantify the uncertainty using the mass balance method which quantifies whole-house emissions rates as a sum of all of the leaks in the house. This work is an important first step, laying the groundwork for future studies of different types of homes in different cities (with different types and ages of infrastructure) and in different climates. The manuscript is well-organized and well-written and I feel it should be published with very minor changes.
Abstract: Don’t need to specify “recently” AND “latest”.
Section 2: Confusing wording to discuss the overall 3-part plan in the previous paragraph and then specify measuring whole-house emissions rates of methane (part 2 of the plan) as the first sentence of the methods. Suggest changing ” We measured whole-house emission rates of methane in a manufactured …” to a more general statement along the lines of “We performed the controlled experiments described above in a manufactured house…”
Section 2.1: “A flush pump pulled air at 10 L min-1 through whichever inlet line the valve was set to.” Awkward wording. Maybe “through the appropriate inlet line”
I’m confused about the flowrates but I think it’s just that there are three total tubes: indoor for CO2/CH4, outdoor for CO2/CH4, and indoor for SF6. First two lines: 10 L/min flush, CRDS sipping. Third line: PTR-MS flowrate of 15 L/min with inlet flowrate of 120 mL/min. Should this be PTR-MS flush rate of 15 L/min with inlet flowrate of 120 mL/min?
The gas heating component of the furnace and the HVAC gas heating element are the same things, so the sentences in lines 113-115 in this section were confusing to me. I think the tracer experiments were in October(?) and then the heating element was turned on in December during quiescent emissions measurements.
How far away is the weather station in Arlington, VA?
It’s obvious, but consider specifying that the windows were closed.
Section 2.3: You used mean indoor, but median outdoor. I’m not sure which is correct here. The spikes are real, so isn’t the mean more appropriate since some of that air exchanges with the indoor air? During the afternoon, it’s hopefully a small difference. How different would the results be if you used mean for outdoor?
Section 2.6: For the first experiment, does the ERquiescent have to be taken into account? I see that you do mention that in Section 3.2 (This should be moved to the methods.)
Section 3.1 You didn’t find any correlation with wind speed like Nabinger et al did?
Fig 6: maybe should expect error bars to be larger on the blue symbols (low ACR)
Fig 6: The average seems lower in October than the rest of the analysis period.
Line 302 in Section 3.3 Consider rewording “The electric house cooling system was in operation with the heating system disabled for most of the study, including for all the tracer injection experiments.”to “ The electric house HVAC system was in operation for all of the study, with the heating system disabled for most of the study, including for all the tracer injection experiments. “ or something along those lines.
Citation: https://doi.org/10.5194/egusphere-2024-2129-RC2 -
AC2: 'Reply on RC2', Anna Karion, 18 Oct 2024
The comment was uploaded in the form of a supplement: https://egusphere.copernicus.org/preprints/2024/egusphere-2024-2129/egusphere-2024-2129-AC2-supplement.pdf
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AC2: 'Reply on RC2', Anna Karion, 18 Oct 2024
Interactive discussion
Status: closed
-
RC1: 'Comment on egusphere-2024-2129', Hossein Maazallahi, 12 Aug 2024
-
AC1: 'Reply on RC1', Anna Karion, 18 Oct 2024
The comment was uploaded in the form of a supplement: https://egusphere.copernicus.org/preprints/2024/egusphere-2024-2129/egusphere-2024-2129-AC1-supplement.pdf
-
AC1: 'Reply on RC1', Anna Karion, 18 Oct 2024
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RC2: 'Comment on egusphere-2024-2129', Anonymous Referee #2, 10 Sep 2024
Methodology and uncertainty estimation for measurements of
methane leakage in a manufactured house
Anna Karion, Michael F. Link, Rileigh Robertson, Tyler Boyle, Dustin Poppendiec
Top-down (atmospheric) and bottom-up (inventory) methods of determining greenhouse gas emissions are complementary approaches, with the goal of providing feedback as to the most effective mitigation strategies. There is a significant discrepancy between these approaches for methane, and in-home emissions are probably a major contributor. The EPA methane inventory now includes an estimate of these emissions, but the emission factors are all based on one study. This manuscripts documents controlled release experiments to optimize the methods to determine these emission factors and to quantify the uncertainty using the mass balance method which quantifies whole-house emissions rates as a sum of all of the leaks in the house. This work is an important first step, laying the groundwork for future studies of different types of homes in different cities (with different types and ages of infrastructure) and in different climates. The manuscript is well-organized and well-written and I feel it should be published with very minor changes.
Abstract: Don’t need to specify “recently” AND “latest”.
Section 2: Confusing wording to discuss the overall 3-part plan in the previous paragraph and then specify measuring whole-house emissions rates of methane (part 2 of the plan) as the first sentence of the methods. Suggest changing ” We measured whole-house emission rates of methane in a manufactured …” to a more general statement along the lines of “We performed the controlled experiments described above in a manufactured house…”
Section 2.1: “A flush pump pulled air at 10 L min-1 through whichever inlet line the valve was set to.” Awkward wording. Maybe “through the appropriate inlet line”
I’m confused about the flowrates but I think it’s just that there are three total tubes: indoor for CO2/CH4, outdoor for CO2/CH4, and indoor for SF6. First two lines: 10 L/min flush, CRDS sipping. Third line: PTR-MS flowrate of 15 L/min with inlet flowrate of 120 mL/min. Should this be PTR-MS flush rate of 15 L/min with inlet flowrate of 120 mL/min?
The gas heating component of the furnace and the HVAC gas heating element are the same things, so the sentences in lines 113-115 in this section were confusing to me. I think the tracer experiments were in October(?) and then the heating element was turned on in December during quiescent emissions measurements.
How far away is the weather station in Arlington, VA?
It’s obvious, but consider specifying that the windows were closed.
Section 2.3: You used mean indoor, but median outdoor. I’m not sure which is correct here. The spikes are real, so isn’t the mean more appropriate since some of that air exchanges with the indoor air? During the afternoon, it’s hopefully a small difference. How different would the results be if you used mean for outdoor?
Section 2.6: For the first experiment, does the ERquiescent have to be taken into account? I see that you do mention that in Section 3.2 (This should be moved to the methods.)
Section 3.1 You didn’t find any correlation with wind speed like Nabinger et al did?
Fig 6: maybe should expect error bars to be larger on the blue symbols (low ACR)
Fig 6: The average seems lower in October than the rest of the analysis period.
Line 302 in Section 3.3 Consider rewording “The electric house cooling system was in operation with the heating system disabled for most of the study, including for all the tracer injection experiments.”to “ The electric house HVAC system was in operation for all of the study, with the heating system disabled for most of the study, including for all the tracer injection experiments. “ or something along those lines.
Citation: https://doi.org/10.5194/egusphere-2024-2129-RC2 -
AC2: 'Reply on RC2', Anna Karion, 18 Oct 2024
The comment was uploaded in the form of a supplement: https://egusphere.copernicus.org/preprints/2024/egusphere-2024-2129/egusphere-2024-2129-AC2-supplement.pdf
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AC2: 'Reply on RC2', Anna Karion, 18 Oct 2024
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Michael F. Link
Rileigh Robertson
Tyler Boyle
Dustin Poppendieck
The requested preprint has a corresponding peer-reviewed final revised paper. You are encouraged to refer to the final revised version.
- Preprint
(1450 KB) - Metadata XML