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Great Lakes Emissions Inventory Meeting Minutes: May 9-10, Madison Wisconsin



 

May 9-10 Meeting, Madison Wisconsin

 

Participants

Illinois: Buzz Asselmeier

Indiana:

Michigan: Dennis McGeen and Allan Ostrander (phone)

Minnesota: Chun Yi Wu

New York: Carlos Mancilla

Ohio: Tom Velalis

Ontario: Cong Doan

Pennsylvania: Karen Gee (phone)

Wisconsin: Orlando Cabrera-Rivera

GLC: Jon Dettling and Pete Giencke

EPA: Suzanne King (phone)

Other: Mark Young (phone)

 

Project Staffing Changes

 

Jon will be leaving the GLC this summer, likely around the end of June. There is a good chance he will remain with the project under some sort of arrangement for some period of time beyond June, but how long is uncertain and will depend both on the GLC's progress in replacing him and on his own job-hunting progress.

 

Orlando noted that he will likely be leaving the WDNR for a  2-year position with the Commission for Environmental Cooperation in Montreal. He will be the project manager for the CEC North American pollutant release inventory. 

 

WDNR Emissions Inventory System Demo

 

Orlando gave the group a demonstration of the AEMS system Wisconsin uses to compile the emissions inventory. The basic  structure is similar to RAPIDS, with a few exceptions.  Some of the screen navigation features in AEMS could be considered in the new RAPIDS re-design. There is an ability to change the  emissions  data year by selecting from a menu. There is a "select" feature allowing the user to select sources based on a wide variety of criteria. Orlando gave an example where all sources emitting arsenic were selected and this then becomes the working group of sources. A source can be selected from the list. >From that point, in addition to the usual RAPIDS functions, there is an ability to look at all emissions from that source. This can be done from the source level without needing to drill down to the stream.

 

Orlando showed that within the process screen, the SCC description is shown, including the 4 description levels. Cong asked whether changing the SCC will trigger the calculator to recalculate emissions with the new SCC. Orlando responded that this depends on whether the emissions are reported or calculated.

 

Orlando showed the emission factor table. This includes a column for the reporting threshold for each pollutant. This can be used to check the calculations that are done by WDNR to determine whether emissions were properly reported.  This screen also allows for the selection of the emission factor to be used in the calculations. Buzz recalled that previously there was an ability to see what emission factors are being used by other sources with the same SCC elsewhere in the state.

 

Orlando sent to the group previously a link to a video on the WDNR website that shows the web reporting feature. Chun Yi asked whether the web interface requires manually entering the numbers or if a data file can be uploaded. Orlando was unsure and will try to find someone during the break who can better answer questions regarding how the web tool works.

 

Within AEMS, the query screens have a "save file" button that allows a text file of the  list of selected sources to be exported.

 

Orlando also showed that within the source selector, there is a field for "region," which are groups of counties. You can therefore select sources a run queries by regions. WDNR used this to allow looking at sources based on the WDNR management regions (e.g., SE Wisconsin).

 

Orlando showed that he uses a set of queries in Access to produce RAPIDS import files from AEMS. He has done this also for the NIF format for mobile sources.

 

Orlando showed that there is a standard function in AEMS that shows two consecutive years of emissions reported for a given source. This is useful for quality assurance purposes.

 

Project Wiki Website

 

Jon demonstrated to project Wiki website (http://www.glos.us/wiki/display/RAPIDS/Home). This website allows users to make edits to the content through their web browser. Potentially, this can replace many of the other project file sharing and storage tools as a place to keep track of project documents. Because of the editing and change-tracking features, it will be an advantage to have many project documents moved to Wiki pages so that there is a single version and when edits are made, they are made to this common page. Jon has already begun moving various items to the website as a starting point. This includes the area source methodologies, project pollutant list, the project protocol and much of the content of the original project website. The Wiki allows a high level of access control, so that some items can be viewable by the public and others only by those within the group. Similar control settings are available for editing content.

 

The site allows for attachments to be posted to web-pages and links to documents or other webpages to be inserted. There is a search function that will search all the pages in the site as well as the text of all attachments (e.g., .xls, .doc, .pdf files). This is a powerful tool for locating documents within the site. Very large documents (100MB or bigger) can be attached, so the site has the potential to replace the FTP site as a means of exchanging and storing project documents.

 

Jon briefly demonstrated how to log into the site and view and edit pages. All group members are able to make edits to the web pages and it should be a group responsibility to keep things up to date. If there are any questions on how to access or edit the site, people should contact Jon.

 

Emissions Factor Tables

 

Jon sent a file of emission factors for area sources prior to the meeting. This file is based on tables of emission factors that many of the states/province sent to Jon several weeks prior to the meeting. For each area source SCC, a table is given showing the emission factors contained in each state's system, including the pollutant, the numeric factor and the denominator unit.

 

There is also a table showing for which SCCs each state has emission factors in their system. This is one means of comparing the emission factors used by each state/province for each area source category. Jon made a recommendation that a mapping of SCCs for area sources (and maybe also mobile and nonroad sources) be made for reporting of data and storage in the regional repository. This should help solve inconsistencies among states/provinces regarding which SCCs are used and should eliminate some confusion that can arise when inexperienced people are viewing the data, such as assuming the lack of emissions for a state within a certain SCC means that that state didn't estimate that source category. For mobile sources, this might result in some significant reductions in the data file size, as it's usually the mobile sources data that dominates the data volume due to the many divisions of SCCs. Each state province could still estimate and report emissions how they chose. These changes would be imposed at the level of the regional repository. After some discussion, the group agreed to this scheme.

 

For the emission factor tables, Chun Yi noticed that many of her factors were missing. She will look into this and send Jon an update. It was also noted that it would be useful to have the NEI methodology emission factors included for comparison. In many cases, it will be likely that the factors used by most states are the NEI numbers. For others, there is a need to document the source of the factors. Including the NEI numbers will help pinpoint those factors where information on the source is needed.

 

Jon noted that he eliminated from the list those pollutants that are not on the group's master list of material codes for the project. This included omitting PM and VOC factors. In some cases, the "emission factors" included by some states appear to actually be speciation factors in that the denominator is in units of PM or VOC. If possible, it may be good to restore these PM or VOC factors, at least for SCCs where this is the case.

 

Jon will work on continuing to update these tables. In the meantime, they can serve as a reference to people as they compile their 2005 area source files. If there are emission factors being used by others that they are not including, they can check with that state to get more information about that factor. For 2005, an attempt will be made to run a QC check on combinations of pollutants and SCCs to ensure that if emission factors are available, people are using them.

 

2005 Inventory

 

Each state/province gave an update on its progress in preparing the 2005 inventory:

IL: The 2005 inventory is complete

MI: Point sources are done and QA/QC'ed. Area sources are about 2/3 done. Will be completed shortly.

MN: Point sources are in progress. A few area source categories have been completed. Chun Yi will be on vacation until June 19th. She should be able to complete the inventory by early September.

NY: Point sources are done and QA/QC'ed. There were some errors in attempting to run this data through the RAPIDS import. The area source calculations are in progress. Mobile sources have been done. Non-road has been delayed due to staff being devoted to working on GHG emissions

OH: Currently working on the CAP inventory. Toxics will be completed by September.

ON: Most area source sectors are done. Pesticides and autobody refinishing have been added. Point sources is still waiting on some additional changes. Mobile and Nonroad have not yet been done.

WI: Point sources are done. Area sources are waiting on the EF discussion from this meeting to reach some resolution. Grant will be doing the nonroad data for toxics. The mobile source inventory should be completed by the end of June.

 

The group agreed that all data compilation could be completed and submitted for QA/QC by September 15th. It is expected that the RAPIDS3 imports will be working by that time and that data can be submitted in either RAPIDS2 format or NIF3 for import into the new system.

 

RAPIDS Design

 

Mark Young distributed some documents for discussion prior to the meeting. Based on the notes from the prior discussion, Mark has changed some of the description field to have longer lengths. The geographic table is not shown, but has been drafted. This will include the PostGIS format for processing the geographic data. In many cases, the numeric fields have been changed to double-precision. In addition, many fields have also been given a companion unit field to allow for more flexibility in which units are used. In some cases, certain fields may also need a denominator units code. There was a question about the "maximum nameplate capacity" field. This appears to be only for EGUs and it isn't used at all in the typical RAPIDS estimations. It is a part of the NIF format.

 

Chun Yi asked about the possibility to include multiple years of data. Mark responded that this would be up to the user; the design can support it if the user would like to do so. Chun Yi mentioned that some emission units in her state change their emission unit during the course of the year. She's not sure how this would be handled with start dates and end dates. Mark noted that operation start and end dates could be added to the system if this is needed to represent certain situations.

 

The geographic coordinates can correspond to any level, including both release points and source-level.

 

In addition to the coordinates, the regions is a component that is not yet in the ERDs. Mark will be able to send this later in the day.

 

Tom raised the issue of "volume sources," which are fugitive emissions exiting a building from an opening at a given height. There may be some additional fields needed to represent this.  However, Tom said that after looking at the release points table further, he thinks the volume sources in his inventory can be represented adequately.

 

Chun Yi also mentioned that for geographic representation, EPA is planning to accept shapefiles in the future. Some additional information may be needed to generate these. For example, the location of tribal emissions could be a concern.

 

Cong asked whether it is necessary to have both numerator and denominator for flow rate and velocity units. The group agreed that it would be sufficient to have just a single unit field for these items, for example 'cubic feet per minute' all in one field. Generally, when the denominator is always of the same type (e.g., time or length), then it is easiest to just have one unit field. Mark noted that a new unit can always be defined. Mark advised that it will be important to have a standard conversion unit for each field and then any new unit can be defined as long as a conversion to that standard is also defined.

 

On the processes table, Mark asked whether the heat content, sulfur content and ash content fields are essentially activity-type data and whether they belong in the processes table. Are these always associated with processes? Tom suggested that these could perhaps be placed in the emissions table. These are items that are used in cases where emissions are based on a calculation rather than just an emission factor. Buzz asked whether anyone ever has multiple values for these fields for   the same process. If not, then the process table is the most logical place for this. Cong stated that these are characteristics of the fuel and not of the throughput. The group agreed to leave these items in the process table. This will influence how the calculation is set up, but it should be able to be done either way. Mark agreed that the calculation can go find the data wherever it is at. The issue to decide is where it makes the most sense to store the data. The heat content will need a units field (a single field).

 

It was agreed that for the sulfur and ash content can be changed to two decimal places for precision. For control efficiencies, it may be best to leave these as double-precision. 

 

Cong asked whether it makes sense for dioxins to include TEQ as a unit rather than as part of the material code. Chun Yi is not sure this will work because some emission factors do not specify the material, other than that it is a mixture of PCDDs. This will take some research to determine what is the best way to represent these.

 

Regarding control devices, Mark asked whether a sequence number is required to describe the order of the controls. If the controls are represented in separate records, the sequence might be needed. Buzz suggested that having data in the primary, secondary or tertiary control fields could indicate the order. Mark noted that there is a potential pitfall in the NEI export for doing that because primary control is required. However, the export may be able to work around this. The NEI only has the primary control efficiency and total control efficiency. It may come down to determining whether anyone is tracking their control devices individually. If so, it would be desirable to have multiple records, perhaps with a sequence indicator. However, if only total control efficiencies are being used, this may not be an issue. Tom suggested that in addition to the control efficiencies, the capture efficiencies would be important for determining the fugitives. Tom likes the table as it is currently shown. Mark reiterated that if there is any desire to represent multiple devices with their own control and capture efficiencies, a sequence field would be needed. There was some discussion on how to calculate capture and control efficiency and how this would be represented in the system. In the NEI there is only a single combined total of capture and control efficiency. This requires the user to do the calculations on the set-up in question outside of the system and then include the result.

 

In the activity data table, Mark asked whether there should be separate fields for maximum, minimum, potential, etc. These have been carried over into the emissions table. They may not be needed in other activities. For operating mode, nobody uses multiple values for these. Chun Yi asked what the value_calc field is relative to the other value fields. This is used by the calculator to hold the result of the value field and the exponent field. Several people expressed a preference not to have a separate exponent field, but to have the main value field have the exponent with it. The value fields can therefore be changed to include just a single field.

 

Chun Yi asked what the data_source_code is. This is the same as the data_code field in the old system, which indicates where the values came from (calculated, facility-supplied, etc.). Chun Yi also asked about the reference codes in the old system. This is now replaced by the combination of the scenario code and the inventory code.

 

Mark also noted that the emission_data_level field used to be a key field in RAPIDS. It's not required in NEI, but it might be useful to have this required still in RAPIDS. Having differing codes here, such as site, unit, release point and process, would allow data to be rolled-up or represented at various levels. Another approach may be to have a separate table that has roll-up (e.g. source-level) emissions.

 

Chun Yi asked about the emission_type field. This is used to specify a typical temporal category, such as annual or weekday.

 

Mark discussed a table he included showing how various data elements are defined, such as generic and state specific emission factors and rule effectiveness. Each of these may have a partition of the inventory, and entity level and other characteristics. Mark will be working on developing this table further. Orlando commented that this will be a little difficult to grasp. Once this is complete, there may be some additional changes to the data model.

 

Next call will be May 23 at 1:30 EST.

 

The next meeting will be late august / early September