556 EL CAMINO REAL - burlingame.org El Camino Real.App B... · regulations include the solid waste collection vehicle (SWCV) rule, in-use public and utility fleets, and the heavy-duty

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556 EL CAMINO REAL

RESIDENTIAL DEVELOPMENT

DRAFT CONSTRUCTION RISK

ASSESSMENT

Burlingame, CA

November 11, 2016

Prepared for:

Will Burns

David J. Powers & Associates, Inc.

1111 Broadway, Suite 1510

Oakland, CA 94607

Prepared by:

Tanushree Ganguly and

Joshua Carman

1 Willowbrook Court, Suite 120

Petaluma, CA 94954

(707) 794-0400

I&R Project# 16-159

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Introduction

The purpose of this report is to address community risk impacts associated with the proposed

condominium project located at 556 El Camino Real in Burlingame, California. The project

proposes the development of a 21-unit, five story condominium building. The proposed building

would include a lobby and a below-grade parking garage. The building would consist of ten,

three-bedroom units, eight, two-bedroom units and three, one-bedroom units for a total of 21

dwelling units. Common open space shall be provided in the rear yard along the northeastern

side of the building.

Community risk air quality impacts could occur due to temporary emissions from the

construction site and exposure of residences in the vicinity to toxic air contaminants (TACs).

This analysis addresses these issues following guidance provided by the Bay Area Air Quality

Management District (BAAQMD).

Setting

The project is located in the San Mateo County, which is in the San Francisco Bay Area Air

Basin. Ambient air quality standards have been established at both the State and federal level.

The Bay Area meets all ambient air quality standards with the exception of ground-level ozone,

respirable particulate matter (PM10), and fine particulate matter (PM2.5).

Toxic Air Contaminants

Toxic air contaminants (TAC) are a broad class of compounds known to cause morbidity or

mortality (usually because they cause cancer) and include, but are not limited to, the criteria air

pollutants. TACs are found in ambient air, especially in urban areas, and are caused by industry,

agriculture, fuel combustion, and commercial operations (e.g., dry cleaners). TACs are typically

found in low concentrations, even near their source (e.g., diesel particulate matter [DPM] near a

freeway). Because chronic exposure can result in adverse health effects, TACs are regulated at

the regional, State, and federal level.

Diesel exhaust is the predominant TAC in urban air and is estimated to represent about three-

quarters of the cancer risk from TACs (based on the Bay Area average). According to the

California Air Resources Board (CARB), diesel exhaust is a complex mixture of gases, vapors,

and fine particles. This complexity makes the evaluation of health effects of diesel exhaust a

complex scientific issue. Some of the chemicals in diesel exhaust, such as benzene and

formaldehyde, have been previously identified as TACs by the CARB, and are listed as

carcinogens either under the State's Proposition 65 or under the Federal Hazardous Air Pollutants

programs.

CARB has adopted and implemented a number of regulations for stationary and mobile sources

to reduce emissions of DPM. Several of these regulatory programs affect medium and heavy

duty diesel trucks that represent the bulk of DPM emissions from California highways. These

regulations include the solid waste collection vehicle (SWCV) rule, in-use public and utility

fleets, and the heavy-duty diesel truck and bus regulations. In 2008, CARB approved a new

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regulation to reduce emissions of DPM and nitrogen oxides from existing on-road heavy-duty

diesel fueled vehicles.1 The regulation requires affected vehicles to meet specific performance

requirements between 2014 and 2023, with all affected diesel vehicles required to have 2010

model-year engines or equivalent by 2023. These requirements are phased in over the

compliance period and depend on the model year of the vehicle.

The BAAQMD is the regional agency tasked with managing air quality in the region. At the

State level, the CARB (a part of the California Environmental Protection Agency [EPA])

oversees regional air district activities and regulates air quality at the State level. The BAAQMD

has recently published California Environmental Quality Act (CEQA) Air Quality Guidelines

that are used in this assessment to evaluate air quality impacts of projects.2 Attachment 1

includes detailed community risk modeling methodology.

Sensitive Receptors

There are groups of people more affected by air pollution than others. CARB has identified the

following persons who are most likely to be affected by air pollution: children under 16, the

elderly over 65, athletes, and people with cardiovascular and chronic respiratory diseases. These

groups are classified as sensitive receptors. Locations that may contain a high concentration of

these sensitive population groups include residential areas, hospitals, daycare facilities, elder care

facilities, elementary schools, and parks. The closest sensitive receptors to the project site are

the multi-family residential apartments to the north, west and east of the project site. Additional

residences are located further south.

Significance Thresholds

In June 2010, BAAQMD adopted thresholds of significance to assist in the review of projects

under CEQA. These Thresholds were designed to establish the level at which BAAQMD

believed air pollution emissions would cause significant environmental impacts under CEQA

and were posted on BAAQMD’s website and included in the Air District's updated CEQA

Guidelines (updated May 2011). The significance thresholds identified by BAAQMD and used

in this analysis are summarized in Table 1.

BAAQMD’s adoption of significance thresholds contained in the 2011 CEQA Air Quality

Guidelines was called into question by an order issued March 5, 2012, in California Building

Industry Association (CBIA) v. BAAQMD (Alameda Superior Court Case No. RGI0548693).

The order requires the BAAQMD to set aside its approval of the thresholds until it has conducted

environmental review under CEQA. The ruling made in the case concerned the environmental

impacts of adopting the thresholds and how the thresholds would indirectly affect land use

development patterns. In August 2013, the Appellate Court struck down the lower court’s order

to set aside the thresholds (Cal. Court of Appeal, First Appellate District, Case Nos. A135335 &

A136212). CBIA sought review by the California Supreme Court on three issues, including the

appellate court’s decision to uphold the BAAQMD’s adoption of the thresholds, and the Court

granted review on just one: Under what circumstances, if any, does CEQA require an analysis of

1 Available online: http://www.arb.ca.gov/msprog/onrdiesel/onrdiesel.htm. Accessed: November 21, 2014. 2 Bay Area Air Quality Management District. 2011. BAAQMD CEQA Air Quality Guidelines. May.

http://www.arb.ca.gov/msprog/onrdiesel/onrdiesel.htm

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how existing environmental conditions will impact future residents or users of a proposed

project? In December 2015, the Supreme Court determined that an analysis of the impacts of the

environment on a project – known as “CEQA-in-reverse” – is only required under two limited

circumstances: (1) when a statute provides an express legislative directive to consider such

impacts; and (2) when a proposed project risks exacerbating environmental hazards or conditions

that already exist (Cal. Supreme Court Case No. S213478). The Supreme Court reversed the

Court of Appeal’s decision and remanded the matter back to the appellate court to reconsider the

case in light of the Supreme Court’s ruling. Accordingly, the case is currently pending back in

the Court of Appeal. Because the Supreme Court’s holding concerns the effects of the

environment on a project (as contrasted to the effects of a proposed project on the environment),

and not the science behind the thresholds, the significance thresholds contained in the 2011

CEQA Air Quality Guidelines are applied to this project.

Table 1. Community Risk Significance Thresholds

Health Risks and Hazards for Single Sources

Excess Cancer Risk >10 per one million

Hazard Index >1.0

Incremental annual PM2.5 >0.3 µg/m3

Health Risks and Hazards for Combined Sources (Cumulative from all sources within 1,000 foot

zone of influence)

Excess Cancer Risk >100 per one million

Hazard Index >10.0

Annual Average PM2.5 >0.8 µg/m3

Note: ROG = reactive organic gases, NOx = nitrogen oxides, PM10 = course particulate matter or particulates with

an aerodynamic diameter of 10 micrometers (µm) or less, PM2.5 = fine particulate matter or particulates with an

aerodynamic diameter of 2.5µm or less;

Project Construction Activity

Construction equipment and associated heavy-duty truck traffic generates diesel exhaust, which

is a known TAC. These exhaust air pollutant emissions would not be considered to contribute

substantially to existing or projected air quality violations. Construction exhaust emissions may

still pose health risks for sensitive receptors such as surrounding residents. The primary

community risk impact issues associated with construction emissions are cancer risk and

exposure to PM2.5. Diesel exhaust poses both a potential health and nuisance impact to nearby

receptors. A health risk assessment of the project construction activities was conducted that

evaluated potential health effects of sensitive receptors at these nearby residences from

construction emissions of DPM and PM2.5.3 The closest sensitive receptors to the project site

include the multi-family residential apartments to the north; northeast and south of the project

site (see Figure 1). Emissions and dispersion modeling was conducted to predict the off-site

concentrations resulting from project construction, so that lifetime cancer risks and non-cancer

health effects could be evaluated.

3

DPM is identified by California as a toxic air contaminant due to the potential to cause cancer.

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Construction activities, particularly during site preparation and grading would temporarily

generate fugitive dust in the form of PM10 and PM2.5. Sources of fugitive dust would include

disturbed soils at the construction site and trucks carrying uncovered loads of soils. Unless

properly controlled, vehicles leaving the site would deposit mud on local streets, which could be

an additional source of airborne dust after it dries. Fugitive dust emissions would vary from day

to day, depending on the nature and magnitude of construction activity and local weather

conditions. Fugitive dust emissions would also depend on soil moisture, silt content of soil, wind

speed, and the amount of equipment operating. Larger dust particles would settle near the

source, while fine particles would be dispersed over greater distances from the construction site.

The BAAQMD CEQA Air Quality Guidelines consider these impacts to be less than significant

if best management practices are employed to reduce these emissions. Mitigation Measure 1

would implement BAAQMD-required best management practices.

Construction Period Emissions

Construction activity is anticipated to include demolition, grading, site preparation, building

construction, paving, and architectural coating. Construction period emissions were modeled

using the California Emissions Estimator Model, Version 2016.3.1 (CalEEMod). A construction

buildout schedule, including proposed equipment list, was provided by the project applicant and

input to the model. The proposed project land use was entered into CalEEMod, which included

21 dwelling units entered as “Condo/Townhouse”, and 41 spaces as “Enclosed Parking with

Elevator” on a 0.35-acre site. Construction of the project is anticipated to take about 23 months.

The CalEEMod modeling included emissions from truck and worker travel on or near the site,

assumed to occur over a distance of 0.5 miles. Export of 7,721 cubic yard (cy) of soil is

expected for the garage and was entered into the model. Additionally, demolition of 10,750

square feet (sf) of buildings and 6,779 sf of pavement is anticipated and was entered into the

model.

PM10 exhaust emissions (assumed to be Diesel Particulate Matter) from the off-road construction

equipment and from on-road vehicles, with total emissions from all construction stages were

computed by CalEEMod as 0.1505 tons (301 pounds). The on-road emissions are a result of

haul truck travel during demolition and grading activities, worker travel, and vendor deliveries

during construction. These emissions from on-road vehicles traveling at or near the site were

modeled as occurring at the construction site. Fugitive PM2.5 dust emissions were calculated by

CalEEMod as 28.9 pounds for the overall construction period.

Dispersion Modeling

The U.S. EPA AERMOD dispersion model was used to predict concentrations of DPM and

PM2.5 concentrations at existing sensitive receptors (residences) in the vicinity of the project

construction area. The AERMOD dispersion model is a BAAQMD-recommended model for use

in modeling analysis of these types of emission activities for CEQA projects.4 The AERMOD

modeling utilized two area sources to represent the on-site construction emissions, one for

4 Bay Area Air Quality Management District (BAAQMD), 2012, Recommended Methods for Screening and

Modeling Local Risks and Hazards, Version 3.0. May 2011.

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exhaust emissions and one for fugitive dust emissions. To represent the construction equipment

exhaust emissions, an emission release height of 6 meters (19.7 feet) was used for the area

source. The elevated source height reflects the height of the equipment exhaust pipes plus an

additional distance for the height of the exhaust plume above the exhaust pipes to account for

plume rise of the exhaust gases. For modeling fugitive PM2.5 emissions, a near-ground level

release height of 2 meters (6.6 feet) was used for the area source. Emissions from the

construction equipment and on-road vehicle travel were distributed throughout the modeled area

sources. Construction emissions were modeled as occurring daily between 7 a.m. to 4 p.m.,

when the majority of construction activity would occur. Figure 1 shows the project site and

nearby sensitive receptor (residences) locations where health impacts were evaluated.

The modeling used a five-year data set (2009-2013) of hourly meteorological data from the San

Francisco International Airport that was prepared for use with the AERMOD model by

BAAQMD for use in health risk assessments. Annual DPM and PM2.5 concentrations from

construction activities during 2017 and 2018 were calculated using the model.

The maximum-modeled DPM concentration occurred just east of the construction site at the

second floor level of a mutli-family residential apartment. The maximum PM2.5 concentration

occurred at the same location as the cancer risk maximally exposed individual (MEI). The

location where the maximum PM2.5 and DPM concentrations occurred (and maximum cancer

risk) is identified on Figure 1.

The detailed emission modeling results and health risk calculations can be found in Attachment

2.

Cancer Risks

Results of this assessment indicate that the maximum excess residential cancer risks would be

222.3 in one million for an infant exposure and 3.8 in one million for an adult exposure. The

maximum residential excess cancer risk would be greater than the BAAQMD significance

threshold of 10 in one million. Implementation of Mitigation Measures 1 and 2 would reduce

this impact to a level of less than significant.

Predicted Annual PM2.5 Concentration

The maximum-modeled annual PM2.5 concentration, which is based on combined exhaust and

fugitive dust emissions, was 1.12 μg/m3, occurring at the residential MEI. The maximum annual

PM2.5 concentration at the MEI residential receptor location would exceed the BAAQMD

significance threshold of 0.3 μg/m3. Implementation of Mitigation Measures 1 and 2 would

reduce this impact to a level of less than significant.

Non-Cancer Hazards

The maximum modeled annual residential DPM concentration (i.e., from construction exhaust)

was 0.967 μg/m3. The maximum computed HI based on this DPM concentration is 0.19, which

is lower than the BAAQMD significance criterion of a HI greater than 1.0.

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Combined Construction Risk Assessment

Community health risk assessments typically look at all substantial sources of TACs that can

affect sensitive receptors that are located within 1,000 feet of a project site. These sources

include freeways or highways, busy surface streets and stationary sources identified by

BAAQMD. Traffic on high volume roadways is a source of TAC emissions that may adversely

affect sensitive receptors in close proximity to the roadway. For local roadways, BAAQMD

considers roadways with traffic volumes of over 10,000 vehicles per day to have a potentially

significant impact. A review of the project area indicates that traffic on El Camino Real (SR-82)

is the only substantial sources of mobile TAC emissions within 1,000 feet of the project site.

BAAQMD’s Stationary Source Screening Tool did not identify any stationary sources with the

potential to affect the project site receptors or the nearby sensitive receptors. The combined

impacts from project construction and traffic on El Camino real have been summarized in Table

2.

BAAQMD provides a Highway Screening Analysis Google Earth Map tool to identify estimated risk

and hazard impacts from highways throughout the Bay Area. Cancer risk, non-cancer hazard and

PM2.5 impacts at various distances from the highway are estimated for different segments of the

highways. The tool uses the average annual daily traffic (AADT) count, fleet mix and other

modeling parameters specific to that segment of the highway. Impacts from El Camino Real (SR-

82), Link 129 (6ft elevation) were identified at the construction MEI using this tool.

Table 2. Cumulative Construction Risk Assessment

Source

Maximum

Cancer Risk

(per million)

Maximum

Annual PM2.5

Concentration

(µg/m3)

Maximum

Hazard

Index

Unmitigated project construction 222.3 1.12 0.19

El Camino Real at 90 feet 5.1 0.07 <0.01

Cumulative Total 227.4 1.19 <0.20

BAAQMD Threshold – Cumulative Sources >100 >0.8 >10.0

Significant? Yes Yes No

Mitigated Construction

Mitigated project construction 5.6 0.05 <0.01

El Camino Real at 90 feet 5.1 0.07 <0.01

Cumulative Total 10.7 0.12 <0.02

BAAQMD Threshold – Cumulative Sources >100 >0.8 >10.0

Significant? No No No

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Mitigation Measure 1: Include basic measures to control dust and exhaust during

construction.

During any construction period ground disturbance, the applicant shall ensure that the

project contractor implement measures to control dust and exhaust. Implementation of the

measures recommended by BAAQMD and listed below would reduce the air quality

impacts associated with grading and new construction to a less than significant level.

The contractor shall implement the following best management practices that are required

of all projects:

1. All exposed surfaces (e.g., parking areas, staging areas, soil piles, graded areas,

and unpaved access roads) shall be watered two times per day.

2. All haul trucks transporting soil, sand, or other loose material off-site shall be

covered.

3. All visible mud or dirt track-out onto adjacent public roads shall be removed

using wet power vacuum street sweepers at least once per day. The use of dry

power sweeping is prohibited.

4. All vehicle speeds on unpaved roads shall be limited to 15 miles per hour (mph).

5. All roadways, driveways, and sidewalks to be paved shall be completed as soon

as possible. Building pads shall be laid as soon as possible after grading unless

seeding or soil binders are used.

6. Idling times shall be minimized either by shutting equipment off when not in use

or reducing the maximum idling time to 5 minutes (as required by the California

airborne toxics control measure Title 13, Section 2485 of California Code of

Regulations [CCR]). Clear signage shall be provided for construction workers at

all access points.

7. All construction equipment shall be maintained and properly tuned in accordance

with manufacturer’s specifications. All equipment shall be checked by a certified

mechanic and determined to be running in proper condition prior to operation.

8. Post a publicly visible sign with the telephone number and person to contact at the

Lead Agency regarding dust complaints. This person shall respond and take

corrective action within 48 hours. The Air District’s phone number shall also be

visible to ensure compliance with applicable regulations.

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Mitigation Measure 2: Selection of equipment during construction to minimize emissions.

Such equipment selection would include the following.

The project shall develop a plan demonstrating that the off-road equipment used on-site

to construct the project would achieve a fleet-wide average 96 percent reduction in DPM

exhaust emissions or more. One feasible plan to achieve this reduction would include the

following:

All diesel-powered off-road equipment above 25hp operating on the site for more

than two days continuously shall, at a minimum, meet U.S. EPA particulate matter

emissions standards for Tier 4 engines or equivalent. Note that the construction

contractor could use other measures to minimize construction period DPM emission

to reduce the predicted cancer risk below the thresholds. The use of equipment that

includes CARB-certified Level 3 Diesel Particulate Filters5 or alternatively-fueled

equipment (i.e., non-diesel) would meet this requirement. Other measures may be

the use of added exhaust devices, or a combination of measures, provided that these

measures are approved by the City and demonstrated to reduce community risk

impacts to less than significant.

Effectiveness of Mitigation Measures 1 and 2

Implementation of Mitigation Measure 1 is considered to reduce exhaust emissions by 5 percent.

Implementation of Mitigation Measures 2 would further reduce on-site diesel exhaust emissions.

This would reduce the cancer risk proportionally, such that the mitigated risk would be less than

5.6 in one million. The annual PM2.5 concentration would be reduced to 0.05 μg/m3. After

implementation of these mitigation measures, the project would have a less-than-significant

impact with rest to community risk caused by construction activities.

5 See http://www.arb.ca.gov/diesel/verdev/vt/cvt.htm

http://www.arb.ca.gov/diesel/verdev/vt/cvt.htm

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Figure 1. Project Construction Site and Locations of Off-Site Sensitive Receptors

and Maximum TAC and PM2.5 Impact

Attachment 1: Health Risk Assessment Methodology

A health risk assessment (HRA) for exposure to Toxic Air Contaminates (TACs) requires the

application of a risk characterization model to the results from the air dispersion model to

estimate potential health risk at each sensitive receptor location. The State of California Office

of Environmental Health Hazard Assessment (OEHHA) and California Air Resources Board

(CARB) develop recommended methods for conducting health risk assessments. The most

recent OEHHA risk assessment guidelines were published in February of 2015.6 These

guidelines incorporate substantial changes designed to provide for enhanced protection of

children, as required by State law, compared to previous published risk assessment guidelines.

CARB has provided additional guidance on implementing OEHHA’s recommended methods.7

BAAQMD has not formally adopted recommended procedures for applying the newest OEHHA

guidelines. However, BAAQMD is in the process of developing new guidance and has proposed

HRA Guidelines as part of the amendments to Regulation 2, Rule 5: New Source Review of

Toxic Air Contaminants.8 Exposure parameters from the 2015 OEHHA guidelines and newly

proposed BAAQMD HRA Guidelines were used in this evaluation.

Cancer Risk

Potential increased cancer risk from inhalation of TACs are calculated based on the TAC

concentration over the period of exposure, inhalation dose, the TAC cancer potency factor, and

an age sensitivity factor to reflect the greater sensitivity of infants and children to cancer causing

TACs. The inhalation dose depends on a person’s breathing rate, exposure time and frequency of

exposure, and the exposure duration. These parameters vary depending on the age, or age range,

of the persons being exposed and whether the exposure is considered to occur at a residential

location or other sensitive receptor location.

The current OEHHA guidance recommends that cancer risk be calculated by age groups to

account for different breathing rates and sensitivity to TACs. Specifically, they recommend

evaluating risks for the third trimester of pregnancy to age zero, ages zero to less than two (infant

exposure), ages two to less than 16 (child exposure), and ages 16 to 70 (adult exposure). Age

sensitivity factors (ASFs) associated with the different types of exposure are an ASF of 10 for

the third trimester and infant exposures, an ASF of 3 for a child exposure, and an ASF of 1 for an

adult exposure. Also associated with each exposure type are different breathing rates, expressed

as liters per kilogram of body weight per day (L/kg-day). As recommended by the BAAQMD,

95th

percentile breathing rates are used for the third trimester and infant exposures, and 80th

percentile breathing rates for child and adult exposures. Additionally, CARB and the BAAQMD

recommend the use of a residential exposure duration of 30 years for sources with long-term

emissions (e.g., roadways).

6 OEHHA, 2015. Air Toxics Hot Spots Program Risk Assessment Guidelines, The Air Toxics Hot Spots Program

Guidance Manual for Preparation of Health Risk Assessments. Office of Environmental Health Hazard Assessment.

February. 7 CARB, 2015. Risk Management Guidance for Stationary Sources of Air Toxics. July 23.

8 BAAQMD, 2016. Workshop Report. Proposed Amendments to Air District Regulation 2, Rule 5: New Source

Review of Toxic Air Contaminants. Appendix C. Proposed Air District HRA Guidelines. January 2016.

Under previous OEHHA and BAAQMD HRA guidance, residential receptors are assumed to be

at their home 24 hours a day, or 100 percent of the time. In the 2015 Risk Assessment Guidance,

OEHHA includes adjustments to exposure duration to account for the fraction of time at home

(FAH), which can be less than 100 percent of the time, based on updated population and activity

statistics. The FAH factors are age-specific and are: 0.85 for third trimester of pregnancy to less

than 2 years old, 0.72 for ages 2 to less than 16 years, and 0.73 for ages 16 to 70 years.

BAAQMD recommends using these FAH factors for residential exposures.

Functionally, cancer risk is calculated using the following parameters and formulas:

Cancer Risk (per million) = CPF x Inhalation Dose x ASF x ED/AT x FAH x 106

Where:

CPF = Cancer potency factor (mg/kg-day)-1

ASF = Age sensitivity factor for specified age group

ED = Exposure duration (years)

AT = Averaging time for lifetime cancer risk (years)

FAH = Fraction of time spent at home (unitless)

Inhalation Dose = Cair x DBR x A x (EF/365) x 10-6

Where:

Cair = concentration in air (μg/m3)

DBR = daily breathing rate (L/kg body weight-day)

A = Inhalation absorption factor

EF = Exposure frequency (days/year)

10-6

= Conversion factor

The health risk parameters used in this evaluation are summarized as follows:

Exposure Type

Infant Child Adult

Parameter Age Range 3rd

Trimester 0<2 2 < 16 16 - 30

DPM Cancer Potency Factor (mg/kg-day)-

1

1.10E+00 1.10E+00 1.10E+00 1.10E+00

Daily Breathing Rate (L/kg-day)* 361 1,090 572 261

Inhalation Absorption Factor 1 1 1 1

Averaging Time (years) 70 70 70 70

Exposure Duration (years) 0.25 2 14 14

Exposure Frequency (days/year) 350 350 350 350

Age Sensitivity Factor 10 10 3 1

Fraction of Time at Home 0.85 – 1.0 0.72 – 1.0 0.72 – 1.0 0.73

* 95th

percentile breathing rates for 3rd

trimester and infants and 80th

percentile for children and

adults

Non-Cancer Hazards

Potential non-cancer health hazards from TAC exposure are expressed in terms of a hazard index

(HI), which is the ratio of the TAC concentration to a reference exposure level (REL). OEHHA

has defined acceptable concentration levels for contaminants that pose non-cancer health

hazards. TAC concentrations below the REL are not expected to cause adverse health impacts,

even for sensitive individuals. The total HI is calculated as the sum of the HIs for each TAC

evaluated and the total HI is compared to the BAAQMD significance thresholds to determine

whether a significant non-cancer health impact from a project would occur.

Typically, for residential projects located near roadways with substantial TAC emissions, the

primary TAC of concern with non-cancer health effects is diesel particulate matter (DPM). For

DPM, the chronic inhalation REL is 5 micrograms per cubic meter (μg/m3).

Annual PM2.5 Concentrations

While not a TAC, fine particulate matter (PM2.5) has been identified by the BAAQMD as a

pollutant with potential non-cancer health effects that should be included when evaluating

potential community health impacts under the California Environmental Quality Act (CEQA).

The thresholds of significance for PM2.5 (project level and cumulative) are in terms of an

increase in the annual average concentration. When considering PM2.5 impacts, the contribution

from all sources of PM2.5 emissions should be included. For projects with potential impacts from

nearby local roadways, the PM2.5 impacts should include those from vehicle exhaust emissions,

PM2.5 generated from vehicle tire and brake wear, and fugitive emissions from re-suspended dust

on the roads.

Attachment 2: Construction Schedule, CalEEMod Output and Health Risk

Calculations

Construction Schedule

Project Name: 556 El Camino Real, Burlingame

See Equipment Type TAB for type, horsepower and load factor

Project Size 21 Dwelling Units total project acres disturbed

s.f. residential

s.f. retail

s.f. office/commercial

s.f. other, specify:

s.f. parking garage spaces

s.f. parking lot spaces

Construction Hours am to pm

Qty Description HP Load Factor Hours/day

Total Work Days

Avg. Hours per

dayAnnual Hours Comments

Demolition Start Date: e.g., 1/1/2017 Total phase: 20 Overall Import/Export VolumesEnd Date: 1/28/2017

1 Concrete/Industrial Saws 81 0.73 8 0 0 Demolition VolumeExcavators 162 0.38 0 0 Square footage of buildings to be demolished

1 Rubber-Tired Dozers 255 0.4 1 0 0 (or total tons to be hauled)2 Tractors/Loaders/Backhoes 97 0.37 6 0 0 _?_ square feet or

_?_ Hauling volume (tons)Site Preperation Start Date: 1/30/2017 Total phase: 5 Any pavement demolished and hauled? _?_ tons

End Date: 2/6/20171 Graders 174 0.41 8 0 0

Rubber Tired Dozers 255 0.4 0 01 Tractors/Loaders/Backhoes 97 0.37 8 0 0

Grading / Excavation Start Date: 2/6/2017 Total phase: 60End Date: 4/24/2017 Soil Hauling Volume

1 Concrete/Industrial Saws 81 0.73 8 0 0 Export volume = 7721.41 cubic yards?Graders 174 0.41 0 0 Import volume = 0.00 cubic yards?

1 Rubber Tired Dozers 255 0.4 1 0 02 Tractors/Loaders/Backhoes 97 0.37 6 0 0

Other Equipment?

Trenching Start Date: Total phase: 30End Date:

Tractor/Loader/Backhoe 97 0.37 0 0Excavators 162 0.38 0Other Equipment?

Building - Exterior Start Date: 4/25/2017 Total phase: 250 Cement Trucks? _?_ Total Round-TripsEnd Date: 4/21/2018

1 Cranes 226 0.29 4 0 0 Electric? (Y/N) ___ Otherwise assumed diesel2 Forklifts 89 0.2 6 0 0 Liquid Propane (LPG)? (Y/N) ___ Otherwise Assumed diesel

Generator Sets 84 0.74 0 0 Or temporary line power? (Y/N) __yes_2 Tractors/Loaders/Backhoes 97 0.37 8 0 0

Welders 46 0.45 0 0Other Equipment? 0

Building - Interior/Architectural Coating Start Date: 4/23/2018 Total phase: 150End Date: 10/19/2017

1 Air Compressors 78 0.48 6 0 0Aerial Lift 62 0.31 0 0Other Equipment?

Paving Start Date: 10/22/2018 Total phase: 25End Date: 10/23/2018

4 Cement and Mortar Mixers 9 0.56 6 0 01 Pavers 125 0.42 7 0 0

Paving Equipment 130 0.36 0 01 Rollers 80 0.38 7 0 01 Tractors/Loaders/Backhoes 97 0.37 7 0 0

Other Equipment?Equipment types listed in "Equipment Types" worksheet tab.Equipment listed in this sheet is to provide an example of inputsIt is assumed that water trucks would be used during gradingAdd or subtract phases and equipment, as appropriateModify horepower or load factor, as appropriate

Asphalt? ___ cubic yards or ____ round trips?

Complete ALL Portions in Yellow

CalEEMod Output

Off-road Equipment -



1.3 User Entered Comments & Non-Default Data

Project Characteristics - Revised CO2 Emission Intensity

Land Use - From the project description and the site plan

Construction Phase - Applicant provided construction schedule

Off-road Equipment - Applicant provided equipment information


CO2 Intensity

(lb/MWhr)

429.6 CH4 Intensity

(lb/MWhr)

0.029 N2O Intensity

(lb/MWhr)

0.006

70

Climate Zone 5 Operational Year 2019

Utility Company Pacific Gas & Electric Company

1.2 Other Project Characteristics

Urbanization Urban Wind Speed (m/s) 2.2 Precipitation Freq (Days)

Condo/Townhouse 21.00 Dwelling Unit 0.35 29,070.00 60

Floor Surface Area Population

Enclosed Parking with Elevator 41.00 Space 0.00 16,400.00 0

1.0 Project Characteristics

1.1 Land Usage

Land Uses Size Metric Lot Acreage

CalEEMod Version: CalEEMod.2016.3.1 Page 1 of 1 Date: 11/11/2016 3:54 PM

556 El Camino Real, TAC Emissions - San Mateo County, Annual

556 El Camino Real, TAC Emissions

San Mateo County, Annual

tblConstructionPhase NumDays 100.00 250.00

tblConstEquipMitigation Tier No Change Tier 4 Interim










tblConstEquipMitigation NumberOfEquipmentMitigated 0.00 8.00










tblConstDustMitigation WaterUnpavedRoadVehicleSpeed 40 15


Demolition - 10750+6779 sf of building demolished

Grading - 7721.41 cy of soil exported during the grading phase

Construction Off-road Equipment Mitigation - Best Management Practices and Tier 4 Interim Mitigation for all Equipment > 25 HP

Table Name Column Name Default Value New Value



Trips and VMT - Reduced trip length for health risk assessment

tblTripsAndVMT VendorTripLength 7.30 0.50





tblTripsAndVMT HaulingTripLength 20.00 0.50






tblProjectCharacteristics CO2IntensityFactor 641.35 429.6

tblProjectCharacteristics OperationalYear 2018 2019

tblLandUse LotAcreage 0.37 0.00

tblLandUse LotAcreage 1.31 0.35

tblLandUse BuildingSpaceSquareFeet 21,000.00 29,070.00

tblLandUse LandUseSquareFeet 21,000.00 29,070.00

tblConstructionPhase PhaseStartDate 1/28/2017 1/30/2017

tblGrading MaterialExported 0.00 7,721.41





tblConstructionPhase PhaseEndDate 4/13/2018 4/9/2018







0.0000 147.9273 147.9273 0.0393 0.0000 148.90950.0162 2.6200e-

003

0.0188 3.5000e-

003

2.6100e-

003

6.1100e-

003

2017 0.0365 0.6757 1.0908 1.6100e-

003

Total CO2 CH4 N2O CO2e

Year tons/yr MT/yr

PM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2 NBio- CO2

Mitigated Construction

ROG NOx CO SO2 Fugitive

PM10

Exhaust

PM10

0.0000 147.9275 147.9275 0.0393 0.0000 148.90970.0343 0.1076 0.1419 0.0143 0.0999 0.1142Maximum 0.2821 1.6734 1.0959 1.6100e-

003

0.0000 69.8337 69.8337 0.0169 0.0000 70.25635.7000e-

004

0.0429 0.0434 1.6000e-

004

0.0404 0.04062018 0.2821 0.6635 0.5170 7.8000e-

004

0.0000 147.9275 147.9275 0.0393 0.0000 148.90970.0343 0.1076 0.1419 0.0143 0.0999 0.11422017 0.1704 1.6734 1.0959 1.6100e-

003

NBio- CO2 Total CO2 CH4 N2O CO2e

Year tons/yr MT/yr

Exhaust

PM10

PM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2

2.0 Emissions Summary

2.1 Overall Construction

Unmitigated Construction


PM10

tblTripsAndVMT WorkerTripLength 10.80 0.50







Acres of Grading (Site Preparation Phase): 2.5

Acres of Grading (Grading Phase): 0

150

6 Paving Paving 10/22/2018 11/23/2018 5 25

5 Architectural Coating Architectural Coating 4/23/2018 11/16/2018 5

60

4 Building Construction Building Construction 4/25/2017 4/9/2018 5 250

3 Grading Grading 2/6/2017 4/28/2017 5

20

2 Site Preparation Site Preparation 1/30/2017 2/3/2017 5 5

End Date Num Days

Week

Num Days Phase Description

1 Demolition Demolition 1/1/2017 1/27/2017 5

3.0 Construction Detail

Construction Phase

Phase

Number

Phase Name Phase Type Start Date

Highest 0.4798 0.1874

6 4-1-2018 6-30-2018 0.1654 0.1123

7 7-1-2018 9-30-2018 0.1671 0.1280

4 10-1-2017 12-31-2017 0.4739 0.1675

5 1-1-2018 3-31-2018 0.4012 0.1633

2 4-1-2017 6-30-2017 0.4798 0.1874

3 7-1-2017 9-30-2017 0.4741 0.1678

Quarter Start Date End Date Maximum Unmitigated ROG + NOX (tons/quarter) Maximum Mitigated ROG + NOX (tons/quarter)

1 1-1-2017 3-31-2017 0.3958 0.1810

0.00 0.00 0.00 0.00 0.00 0.0051.99 97.47 88.92 74.67 97.30 95.19

NBio-CO2 Total CO2 CH4 N20 CO2e

Percent

Reduction

42.38 58.22 0.20 0.00

Exhaust

PM10

PM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2ROG NOx CO SO2 Fugitive

PM10

0.0000 147.9273 147.9273 0.0393 0.0000 148.90950.0162 2.6200e-

003

0.0188 3.5000e-

003

2.6100e-

003

6.1100e-

003

Maximum 0.2243 0.6757 1.0908 1.6100e-

003

0.0000 69.8336 69.8336 0.0169 0.0000 70.25635.7000e-

004

1.1800e-

003

1.7500e-

003

1.6000e-

004

1.1800e-

003

1.3400e-

003

2018 0.2243 0.3006 0.5189 7.8000e-

004

0.50 0.50 LD_Mix HDT_Mix HHDTArchitectural Coating 1 4.00 0.00 0.00 0.50

0.50 0.50 0.50 LD_Mix HDT_Mix HHDT

0.50 0.50 LD_Mix HDT_Mix HHDT

Building Construction 5 22.00 5.00 0.00

Grading 4 10.00 0.00 965.00 0.50

0.50 0.50 0.50 LD_Mix HDT_Mix HHDT

0.50 0.50 LD_Mix HDT_Mix HHDT

Site Preparation 2 5.00 0.00 0.00

Demolition 4 10.00 0.00 80.00 0.50

Worker Trip

Length

Vendor Trip

Length

Hauling Trip

Length

Worker Vehicle

Class

Vendor

Vehicle

Class

Hauling

Vehicle

Class

Trips and VMT

Phase Name Offroad Equipment

Count

Worker Trip

Number

Vendor Trip

Number

Hauling Trip

Number

Paving Tractors/Loaders/Backhoes 1 7.00 97 0.37

Paving Rollers 1 7.00 80 0.38

Paving Pavers 1 7.00 130 0.42

Paving Cement and Mortar Mixers 4 6.00 9 0.56

Architectural Coating Air Compressors 1 6.00 78 0.48

Building Construction Tractors/Loaders/Backhoes 2 8.00 97 0.37

Building Construction Forklifts 2 6.00 89 0.20

Building Construction Cranes 1 4.00 231 0.29

Grading Tractors/Loaders/Backhoes 2 6.00 97 0.37

Grading Rubber Tired Dozers 1 1.00 247 0.40

Grading Concrete/Industrial Saws 1 8.00 81 0.73

Site Preparation Tractors/Loaders/Backhoes 1 8.00 97 0.37

Site Preparation Graders 1 8.00 187 0.41

Demolition Tractors/Loaders/Backhoes 2 6.00 97 0.37

Demolition Rubber Tired Dozers 1 1.00 247 0.40

Load Factor

Demolition Concrete/Industrial Saws 1 8.00 81 0.73

Acres of Paving: 0

Residential Indoor: 58,867; Residential Outdoor: 19,622; Non-Residential Indoor: 0; Non-Residential Outdoor: 0; Striped Parking Area:

984 (Architectural Coating – sqft)OffRoad Equipment

Phase Name Offroad Equipment Type Amount Usage Hours Horse Power

0.0000 0.0000 0.0000 0.0000 0.0000 0.00000.0000 0.0000 0.0000 0.0000 0.0000 0.0000Vendor 0.0000 0.0000 0.0000 0.0000

0.0000 0.3486 0.3486 6.0000e-

005

0.0000 0.35002.0000e-

005

1.0000e-

005

3.0000e-

005

0.0000 1.0000e-

005

1.0000e-

005

Hauling 1.1000e-

004

4.1300e-

003

1.2900e-

003

0.0000


Category tons/yr MT/yr

PM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2 NBio- CO2

Unmitigated Construction Off-Site


PM10

Exhaust

PM10

0.0000 10.6985 10.6985 2.1000e-

003

0.0000 10.75118.6300e-

003

7.3200e-

003

0.0160 1.3100e-

003

6.9800e-

003

8.2900e-

003

Total 0.0121 0.1050 0.0792 1.2000e-

004

0.0000 10.6985 10.6985 2.1000e-

003

0.0000 10.75117.3200e-

003

7.3200e-

003

6.9800e-

003

6.9800e-

003

Off-Road 0.0121 0.1050 0.0792 1.2000e-

004

0.0000 0.0000 0.0000 0.0000 0.0000 0.00008.6300e-

003

0.0000 8.6300e-

003

1.3100e-

003

0.0000 1.3100e-

003

Fugitive Dust



PM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2 NBio- CO2

3.2 Demolition - 2017

Unmitigated Construction On-Site


PM10

Exhaust

PM10

3.1 Mitigation Measures Construction

Use Cleaner Engines for Construction Equipment

Replace Ground Cover

Water Exposed Area

Reduce Vehicle Speed on Unpaved Roads

Clean Paved Roads

0.50 0.50 0.50 LD_Mix HDT_Mix HHDTPaving 7 18.00 0.00 0.00

3.3 Site Preparation - 2017


0.0000 0.4023 0.4023 6.0000e-

005

0.0000 0.40386.0000e-

005

1.0000e-

005

7.0000e-

005

1.0000e-

005

1.0000e-

005

2.0000e-

005

Total 2.2000e-

004

4.1800e-

003

1.9700e-

003

0.0000

0.0000 0.0537 0.0537 0.0000 0.0000 0.05384.0000e-

005

0.0000 4.0000e-

005

1.0000e-

005

0.0000 1.0000e-

005

Worker 1.1000e-

004

5.0000e-

005

6.8000e-

004

0.0000

0.0000 0.0000 0.0000 0.0000 0.0000 0.00000.0000 0.0000 0.0000 0.0000 0.0000 0.0000Vendor 0.0000 0.0000 0.0000 0.0000

0.0000 0.3486 0.3486 6.0000e-

005

0.0000 0.35002.0000e-

005

1.0000e-

005

3.0000e-

005

0.0000 1.0000e-

005

1.0000e-

005

Hauling 1.1000e-

004

4.1300e-

003

1.2900e-

003

0.0000



PM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2 NBio- CO2

Mitigated Construction Off-Site


PM10

Exhaust

PM10

0.0000 10.6985 10.6985 2.1000e-

003

0.0000 10.75113.8800e-

003

1.8000e-

004

4.0600e-

003

2.9000e-

004

1.8000e-

004

4.7000e-

004

Total 2.3700e-

003

0.0455 0.0794 1.2000e-

004

0.0000 10.6985 10.6985 2.1000e-

003

0.0000 10.75111.8000e-

004

1.8000e-

004

1.8000e-

004

1.8000e-

004

Off-Road 2.3700e-

003

0.0455 0.0794 1.2000e-

004

0.0000 0.0000 0.0000 0.0000 0.0000 0.00003.8800e-

003

0.0000 3.8800e-

003

2.9000e-

004

0.0000 2.9000e-

004

Fugitive Dust



PM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2 NBio- CO2

Mitigated Construction On-Site


PM10

Exhaust

PM10

0.0000 0.4023 0.4023 6.0000e-

005

0.0000 0.40386.0000e-

005

1.0000e-

005

7.0000e-

005

1.0000e-

005

1.0000e-

005

2.0000e-

005

Total 2.2000e-

004

4.1800e-

003

1.9700e-

003

0.0000

0.0000 0.0537 0.0537 0.0000 0.0000 0.05384.0000e-

005

0.0000 4.0000e-

005

1.0000e-

005

0.0000 1.0000e-

005

Worker 1.1000e-

004

5.0000e-

005

6.8000e-

004

0.0000



PM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2 NBio- CO2



PM10

Exhaust

PM10

0.0000 6.7100e-

003

6.7100e-

003

0.0000 0.0000 6.7200e-

003

0.0000 0.0000 0.0000 0.0000 0.0000 0.0000Total 1.0000e-

005

1.0000e-

005

9.0000e-

005

0.0000

0.0000 6.7100e-

003

6.7100e-

003

0.0000 0.0000 6.7200e-

003

0.0000 0.0000 0.0000 0.0000 0.0000 0.0000Worker 1.0000e-

005

1.0000e-

005

9.0000e-

005

0.0000

0.0000 0.0000 0.0000 0.0000 0.0000 0.00000.0000 0.0000 0.0000 0.0000 0.0000 0.0000Vendor 0.0000 0.0000 0.0000 0.0000

0.0000 0.0000 0.0000 0.0000 0.0000 0.00000.0000 0.0000 0.0000 0.0000 0.0000 0.0000Hauling 0.0000 0.0000 0.0000 0.0000



PM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2 NBio- CO2



PM10

Exhaust

PM10

0.0000 2.2669 2.2669 6.9000e-

004

0.0000 2.28421.3300e-

003

1.1800e-

003

2.5100e-

003

1.4000e-

004

1.0900e-

003

1.2300e-

003

Total 2.1300e-

003

0.0263 0.0109 2.0000e-

005

0.0000 2.2669 2.2669 6.9000e-

004

0.0000 2.28421.1800e-

003

1.1800e-

003

1.0900e-

003

1.0900e-

003

Off-Road 2.1300e-

003

0.0263 0.0109 2.0000e-

005

0.0000 0.0000 0.0000 0.0000 0.0000 0.00001.3300e-

003

0.0000 1.3300e-

003

1.4000e-

004

0.0000 1.4000e-

004

Fugitive Dust



PM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2 NBio- CO2ROG NOx CO SO2 Fugitive

PM10

Exhaust

PM10

0.0000 32.0955 32.0955 6.3100e-

003

0.0000 32.25330.0230 0.0220 0.0450 0.0125 0.0209 0.0334Total 0.0363 0.3149 0.2376 3.6000e-

004

0.0000 32.0955 32.0955 6.3100e-

003

0.0000 32.25330.0220 0.0220 0.0209 0.0209Off-Road 0.0363 0.3149 0.2376 3.6000e-

004

0.0000 0.0000 0.0000 0.0000 0.0000 0.00000.0230 0.0000 0.0230 0.0125 0.0000 0.0125Fugitive Dust



PM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2 NBio- CO2

3.4 Grading - 2017



PM10

Exhaust

PM10

0.0000 6.7100e-

003

6.7100e-

003

0.0000 0.0000 6.7200e-

003

0.0000 0.0000 0.0000 0.0000 0.0000 0.0000Total 1.0000e-

005

1.0000e-

005

9.0000e-

005

0.0000

0.0000 6.7100e-

003

6.7100e-

003

0.0000 0.0000 6.7200e-

003

0.0000 0.0000 0.0000 0.0000 0.0000 0.0000Worker 1.0000e-

005

1.0000e-

005

9.0000e-

005

0.0000

0.0000 0.0000 0.0000 0.0000 0.0000 0.00000.0000 0.0000 0.0000 0.0000 0.0000 0.0000Vendor 0.0000 0.0000 0.0000 0.0000

0.0000 0.0000 0.0000 0.0000 0.0000 0.00000.0000 0.0000 0.0000 0.0000 0.0000 0.0000Hauling 0.0000 0.0000 0.0000 0.0000



PM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2 NBio- CO2



PM10

Exhaust

PM10

0.0000 2.2669 2.2669 6.9000e-

004

0.0000 2.28426.0000e-

004

4.0000e-

005

6.4000e-

004

3.0000e-

005

4.0000e-

005

7.0000e-

005

Total 4.4000e-

004

7.7500e-

003

0.0146 2.0000e-

005

0.0000 2.2669 2.2669 6.9000e-

004

0.0000 2.28424.0000e-

005

4.0000e-

005

4.0000e-

005

4.0000e-

005

Off-Road 4.4000e-

004

7.7500e-

003

0.0146 2.0000e-

005

0.0000 0.0000 0.0000 0.0000 0.0000 0.00006.0000e-

004

0.0000 6.0000e-

004

3.0000e-

005

0.0000 3.0000e-

005

Fugitive Dust

Total CO2 CH4 N2O CO2ePM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2 NBio- CO2



PM10

Exhaust

PM10

0.0000 32.0955 32.0955 6.3100e-

003

0.0000 32.25320.0104 5.3000e-

004

0.0109 2.8100e-

003

5.3000e-

004

3.3400e-

003

Total 7.1000e-

003

0.1363 0.2381 3.6000e-

004

0.0000 32.0955 32.0955 6.3100e-

003

0.0000 32.25325.3000e-

004

5.3000e-

004

5.3000e-

004

5.3000e-

004

Off-Road 7.1000e-

003

0.1363 0.2381 3.6000e-

004

0.0000 0.0000 0.0000 0.0000 0.0000 0.00000.0104 0.0000 0.0104 2.8100e-

003

0.0000 2.8100e-

003

Fugitive Dust



PM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2 NBio- CO2



PM10

Exhaust

PM10

0.0000 4.3662 4.3662 6.8000e-

004

0.0000 4.38323.2000e-

004

1.0000e-

004

4.2000e-

004

9.0000e-

005

9.0000e-

005

1.8000e-

004

Total 1.7100e-

003

0.0500 0.0176 4.0000e-

005

0.0000 0.1610 0.1610 1.0000e-

005

0.0000 0.16131.1000e-

004

0.0000 1.1000e-

004

3.0000e-

005

0.0000 3.0000e-

005

Worker 3.3000e-

004

1.5000e-

004

2.0400e-

003

0.0000

0.0000 0.0000 0.0000 0.0000 0.0000 0.00000.0000 0.0000 0.0000 0.0000 0.0000 0.0000Vendor 0.0000 0.0000 0.0000 0.0000

0.0000 4.2052 4.2052 6.7000e-

004

0.0000 4.22202.1000e-

004

1.0000e-

004

3.1000e-

004

6.0000e-

005

9.0000e-

005

1.5000e-

004

Hauling 1.3800e-

003

0.0498 0.0156 4.0000e-

005



PM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2 NBio- CO2



PM10

Exhaust

PM10

0.0000 1.0567 1.0567 7.0000e-

005

0.0000 1.05857.4000e-

004

2.0000e-

005

7.5000e-

004

2.0000e-

004

2.0000e-

005

2.1000e-

004

Worker 2.1900e-

003

1.0100e-

003

0.0134 1.0000e-

005

0.0000 2.3704 2.3704 3.6000e-

004

0.0000 2.37952.1000e-

004

8.0000e-

005

2.9000e-

004

6.0000e-

005

8.0000e-

005

1.4000e-

004

Vendor 1.0800e-

003

0.0302 0.0129 2.0000e-

005

0.0000 0.0000 0.0000 0.0000 0.0000 0.00000.0000 0.0000 0.0000 0.0000 0.0000 0.0000Hauling 0.0000 0.0000 0.0000 0.0000



PM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2 NBio- CO2



PM10

Exhaust

PM10

0.0000 94.6643 94.6643 0.0290 0.0000 95.38940.0769 0.0769 0.0707 0.0707Total 0.1147 1.1419 0.7223 1.0200e-

003

0.0000 94.6643 94.6643 0.0290 0.0000 95.38940.0769 0.0769 0.0707 0.0707Off-Road 0.1147 1.1419 0.7223 1.0200e-

003



PM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2 NBio- CO2

3.5 Building Construction - 2017



PM10

Exhaust

PM10

0.0000 4.3662 4.3662 6.8000e-

004

0.0000 4.38323.2000e-

004

1.0000e-

004

4.2000e-

004

9.0000e-

005

9.0000e-

005

1.8000e-

004

Total 1.7100e-

003

0.0500 0.0176 4.0000e-

005

0.0000 0.1610 0.1610 1.0000e-

005

0.0000 0.16131.1000e-

004

0.0000 1.1000e-

004

3.0000e-

005

0.0000 3.0000e-

005

Worker 3.3000e-

004

1.5000e-

004

2.0400e-

003

0.0000

0.0000 0.0000 0.0000 0.0000 0.0000 0.00000.0000 0.0000 0.0000 0.0000 0.0000 0.0000Vendor 0.0000 0.0000 0.0000 0.0000

0.0000 4.2052 4.2052 6.7000e-

004

0.0000 4.22202.1000e-

004

1.0000e-

004

3.1000e-

004

6.0000e-

005

9.0000e-

005

1.5000e-

004

Hauling 1.3800e-

003

0.0498 0.0156 4.0000e-

005


3.5 Building Construction - 2018


0.0000 3.4271 3.4271 4.3000e-

004

0.0000 3.43809.5000e-

004

1.0000e-

004

1.0400e-

003

2.6000e-

004

1.0000e-

004

3.5000e-

004

Total 3.2700e-

003

0.0312 0.0263 3.0000e-

005

0.0000 1.0567 1.0567 7.0000e-

005

0.0000 1.05857.4000e-

004

2.0000e-

005

7.5000e-

004

2.0000e-

004

2.0000e-

005

2.1000e-

004

Worker 2.1900e-

003

1.0100e-

003

0.0134 1.0000e-

005

0.0000 2.3704 2.3704 3.6000e-

004

0.0000 2.37952.1000e-

004

8.0000e-

005

2.9000e-

004

6.0000e-

005

8.0000e-

005

1.4000e-

004

Vendor 1.0800e-

003

0.0302 0.0129 2.0000e-

005

0.0000 0.0000 0.0000 0.0000 0.0000 0.00000.0000 0.0000 0.0000 0.0000 0.0000 0.0000Hauling 0.0000 0.0000 0.0000 0.0000



PM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2 NBio- CO2



PM10

Exhaust

PM10

0.0000 94.6642 94.6642 0.0290 0.0000 95.38931.6700e-

003

1.6700e-

003

1.6700e-

003

1.6700e-

003

Total 0.0213 0.4009 0.7126 1.0200e-

003

0.0000 94.6642 94.6642 0.0290 0.0000 95.38931.6700e-

003

1.6700e-

003

1.6700e-

003

1.6700e-

003

Off-Road 0.0213 0.4009 0.7126 1.0200e-

003



PM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2 NBio- CO2



PM10

Exhaust

PM10

0.0000 3.4271 3.4271 4.3000e-

004

0.0000 3.43809.5000e-

004

1.0000e-

004

1.0400e-

003

2.6000e-

004

1.0000e-

004

3.5000e-

004

Total 3.2700e-

003

0.0312 0.0263 3.0000e-

005



PM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2 NBio- CO2



PM10

Exhaust

PM10

0.0000 1.3513 1.3513 1.5000e-

004

0.0000 1.35523.7000e-

004

4.0000e-

005

4.1000e-

004

1.0000e-

004

3.0000e-

005

1.3000e-

004

Total 1.1400e-

003

0.0119 9.3600e-

003

1.0000e-

005

0.0000 0.4071 0.4071 2.0000e-

005

0.0000 0.40772.9000e-

004

1.0000e-

005

3.0000e-

004

8.0000e-

005

1.0000e-

005

8.0000e-

005

Worker 7.6000e-

004

3.4000e-

004

4.6400e-

003

0.0000

0.0000 0.9442 0.9442 1.3000e-

004

0.0000 0.94758.0000e-

005

3.0000e-

005

1.1000e-

004

2.0000e-

005

2.0000e-

005

5.0000e-

005

Vendor 3.8000e-

004

0.0116 4.7200e-

003

1.0000e-

005

0.0000 0.0000 0.0000 0.0000 0.0000 0.00000.0000 0.0000 0.0000 0.0000 0.0000 0.0000Hauling 0.0000 0.0000 0.0000 0.0000



PM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2 NBio- CO2



PM10

Exhaust

PM10

0.0000 36.9241 36.9241 0.0115 0.0000 37.21150.0252 0.0252 0.0232 0.0232Total 0.0385 0.3916 0.2752 4.0000e-

004

0.0000 36.9241 36.9241 0.0115 0.0000 37.21150.0252 0.0252 0.0232 0.0232Off-Road 0.0385 0.3916 0.2752 4.0000e-

004



PM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2 NBio- CO2ROG NOx CO SO2 Fugitive

PM10

Exhaust

PM10

0.0000 19.1494 19.1494 1.8200e-

003

0.0000 19.19490.0113 0.0113 0.0113 0.0113Total 0.2305 0.1504 0.1391 2.2000e-

004

0.0000 19.1494 19.1494 1.8200e-

003

0.0000 19.19490.0113 0.0113 0.0113 0.0113Off-Road 0.0224 0.1504 0.1391 2.2000e-

004

0.0000 0.0000 0.0000 0.0000 0.0000 0.00000.0000 0.0000 0.0000 0.0000Archit. Coating 0.2081



PM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2 NBio- CO2

3.6 Architectural Coating - 2018



PM10

Exhaust

PM10

0.0000 1.3513 1.3513 1.5000e-

004

0.0000 1.35523.7000e-

004

4.0000e-

005

4.1000e-

004

1.0000e-

004

3.0000e-

005

1.3000e-

004

Total 1.1400e-

003

0.0119 9.3600e-

003

1.0000e-

005

0.0000 0.4071 0.4071 2.0000e-

005

0.0000 0.40772.9000e-

004

1.0000e-

005

3.0000e-

004

8.0000e-

005

1.0000e-

005

8.0000e-

005

Worker 7.6000e-

004

3.4000e-

004

4.6400e-

003

0.0000

0.0000 0.9442 0.9442 1.3000e-

004

0.0000 0.94758.0000e-

005

3.0000e-

005

1.1000e-

004

2.0000e-

005

2.0000e-

005

5.0000e-

005

Vendor 3.8000e-

004

0.0116 4.7200e-

003

1.0000e-

005

0.0000 0.0000 0.0000 0.0000 0.0000 0.00000.0000 0.0000 0.0000 0.0000 0.0000 0.0000Hauling 0.0000 0.0000 0.0000 0.0000



PM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2 NBio- CO2



PM10

Exhaust

PM10

0.0000 36.9241 36.9241 0.0115 0.0000 37.21156.6000e-

004

6.6000e-

004

6.6000e-

004

6.6000e-

004

Total 8.4600e-

003

0.1590 0.2827 4.0000e-

004

0.0000 36.9241 36.9241 0.0115 0.0000 37.21156.6000e-

004

6.6000e-

004

6.6000e-

004

6.6000e-

004

Off-Road 8.4600e-

003

0.1590 0.2827 4.0000e-

004

Total CO2 CH4 N2O CO2ePM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2 NBio- CO2



PM10

Exhaust

PM10

0.0000 19.1494 19.1494 1.8200e-

003

0.0000 19.19493.0000e-

004

3.0000e-

004

3.0000e-

004

3.0000e-

004

Total 0.2122 0.0795 0.1374 2.2000e-

004

0.0000 19.1494 19.1494 1.8200e-

003

0.0000 19.19493.0000e-

004

3.0000e-

004

3.0000e-

004

3.0000e-

004

Off-Road 4.0900e-

003

0.0795 0.1374 2.2000e-

004

0.0000 0.0000 0.0000 0.0000 0.0000 0.00000.0000 0.0000 0.0000 0.0000Archit. Coating 0.2081



PM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2 NBio- CO2



PM10

Exhaust

PM10

0.0000 0.1564 0.1564 1.0000e-

005

0.0000 0.15661.1000e-

004

0.0000 1.1000e-

004

3.0000e-

005

0.0000 3.0000e-

005

Total 2.9000e-

004

1.3000e-

004

1.7800e-

003

0.0000

0.0000 0.1564 0.1564 1.0000e-

005

0.0000 0.15661.1000e-

004

0.0000 1.1000e-

004

3.0000e-

005

0.0000 3.0000e-

005

Worker 2.9000e-

004

1.3000e-

004

1.7800e-

003

0.0000

0.0000 0.0000 0.0000 0.0000 0.0000 0.00000.0000 0.0000 0.0000 0.0000 0.0000 0.0000Vendor 0.0000 0.0000 0.0000 0.0000

0.0000 0.0000 0.0000 0.0000 0.0000 0.00000.0000 0.0000 0.0000 0.0000 0.0000 0.0000Hauling 0.0000 0.0000 0.0000 0.0000



PM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2 NBio- CO2



PM10

Exhaust

PM10

0.0000 0.1173 0.1173 1.0000e-

005

0.0000 0.11758.0000e-

005

0.0000 9.0000e-

005

2.0000e-

005

0.0000 2.0000e-

005

Worker 2.2000e-

004

1.0000e-

004

1.3400e-

003

0.0000

0.0000 0.0000 0.0000 0.0000 0.0000 0.00000.0000 0.0000 0.0000 0.0000 0.0000 0.0000Vendor 0.0000 0.0000 0.0000 0.0000

0.0000 0.0000 0.0000 0.0000 0.0000 0.00000.0000 0.0000 0.0000 0.0000 0.0000 0.0000Hauling 0.0000 0.0000 0.0000 0.0000



PM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2 NBio- CO2



PM10

Exhaust

PM10

0.0000 12.1352 12.1352 3.4200e-

003

0.0000 12.22076.3900e-

003

6.3900e-

003

5.9200e-

003

5.9200e-

003

Total 0.0115 0.1093 0.0903 1.4000e-

004

0.0000 0.0000 0.0000 0.0000 0.0000 0.00000.0000 0.0000 0.0000 0.0000Paving 0.0000

0.0000 12.1352 12.1352 3.4200e-

003

0.0000 12.22076.3900e-

003

6.3900e-

003

5.9200e-

003

5.9200e-

003

Off-Road 0.0115 0.1093 0.0903 1.4000e-

004



PM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2 NBio- CO2

3.7 Paving - 2018



PM10

Exhaust

PM10

0.0000 0.1564 0.1564 1.0000e-

005

0.0000 0.15661.1000e-

004

0.0000 1.1000e-

004

3.0000e-

005

0.0000 3.0000e-

005

Total 2.9000e-

004

1.3000e-

004

1.7800e-

003

0.0000

0.0000 0.1564 0.1564 1.0000e-

005

0.0000 0.15661.1000e-

004

0.0000 1.1000e-

004

3.0000e-

005

0.0000 3.0000e-

005

Worker 2.9000e-

004

1.3000e-

004

1.7800e-

003

0.0000

0.0000 0.0000 0.0000 0.0000 0.0000 0.00000.0000 0.0000 0.0000 0.0000 0.0000 0.0000Vendor 0.0000 0.0000 0.0000 0.0000

0.0000 0.0000 0.0000 0.0000 0.0000 0.00000.0000 0.0000 0.0000 0.0000 0.0000 0.0000Hauling 0.0000 0.0000 0.0000 0.0000


0.0000 0.1173 0.1173 1.0000e-

005

0.0000 0.11758.0000e-

005

0.0000 9.0000e-

005

2.0000e-

005

0.0000 2.0000e-

005

Total 2.2000e-

004

1.0000e-

004

1.3400e-

003

0.0000

0.0000 0.1173 0.1173 1.0000e-

005

0.0000 0.11758.0000e-

005

0.0000 9.0000e-

005

2.0000e-

005

0.0000 2.0000e-

005

Worker 2.2000e-

004

1.0000e-

004

1.3400e-

003

0.0000

0.0000 0.0000 0.0000 0.0000 0.0000 0.00000.0000 0.0000 0.0000 0.0000 0.0000 0.0000Vendor 0.0000 0.0000 0.0000 0.0000

0.0000 0.0000 0.0000 0.0000 0.0000 0.00000.0000 0.0000 0.0000 0.0000 0.0000 0.0000Hauling 0.0000 0.0000 0.0000 0.0000



PM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2 NBio- CO2



PM10

Exhaust

PM10

0.0000 12.1351 12.1351 3.4200e-

003

0.0000 12.22071.9000e-

004

1.9000e-

004

1.9000e-

004

1.9000e-

004

Total 2.0400e-

003

0.0500 0.0863 1.4000e-

004

0.0000 0.0000 0.0000 0.0000 0.0000 0.00000.0000 0.0000 0.0000 0.0000Paving 0.0000

0.0000 12.1351 12.1351 3.4200e-

003

0.0000 12.22071.9000e-

004

1.9000e-

004

1.9000e-

004

1.9000e-

004

Off-Road 2.0400e-

003

0.0500 0.0863 1.4000e-

004



PM10

Total

Fugitive

PM2.5

Exhaust

PM2.5

PM2.5

Total

Bio- CO2 NBio- CO2



PM10

Exhaust

PM10

0.0000 0.1173 0.1173 1.0000e-

005

0.0000 0.11758.0000e-

005

0.0000 9.0000e-

005

2.0000e-

005

0.0000 2.0000e-

005

Total 2.2000e-

004

1.0000e-

004

1.3400e-

003

0.0000

556 El Camino Real, Burlingame, CA 556 El Camino Real, Burlingame, CA

DPM Construction Emissions and Modeling Emission Rates - Unmitigated PM2.5 Fugitive Dust Construction Emissions for Modeling - UnmitigatedDPM PM2.5

Modeled Emission Modeled EmissionConstruction DPM Area DPM Emissions Area Rate Construction Area PM2.5 Emissions Area Rate

Year Activity (ton/year) Source (lb/yr) (lb/hr) (g/s) (m2) (g/s/m2) Year Activity Source (ton/year) (lb/yr) (lb/hr) (g/s) (m2) g/s/m2

2017 Construction 0.1076 1_DPM 215.2 0.06551 8.25E-03 1,446 5.71E-06 2017 Construction 1_FUG 0.0143 28.6 0.00871 1.10E-03 1,446 7.59E-072018 Construction 0.0429 1_DPM 85.8 0.02612 3.29E-03 1,446 2.28E-06 2018 Construction 1_FUG 0.0002 0.3 0.00010 1.23E-05 1,446 8.49E-09Total 0.1505 301 0.0916 0.0115 Total 0.0145 28.9 0.0088 0.0011

Construction Hours Construction Hourshr/day = 9 (7am - 4pm) hr/day = 9 (7am - 4pm)

days/yr = 365 days/yr = 365hours/year = 3285 hours/year = 3285

Emission Summary

Health Risk Calculations

556 ECR, Burlingame, CA - Construction Impacts - Unmitigated EmissionsMaximum DPM Cancer Risk Calculations From ConstructionOff-Site Residential Receptor Locations - 4.5 meters

Cancer Risk (per million) = CPF x Inhalation Dose x ASF x ED/AT x FAH x 1.0E6Where: CPF = Cancer potency factor (mg/kg-day)-1

ASF = Age sensitivity factor for specified age groupED = Exposure duration (years)AT = Averaging time for lifetime cancer risk (years)FAH = Fraction of time spent at home (unitless)

Inhalation Dose = Cair x DBR x A x (EF/365) x 10-6

Where: Cair = concentration in air (μg/m3)DBR = daily breathing rate (L/kg body weight-day)A = Inhalation absorption factorEF = Exposure frequency (days/year)10-6 = Conversion factor

ValuesInfant/Child Adult

Age --> 3rd Trimester 0 - 2 2 - 16 16 - 30Parameter

ASF = 10 10 3 1CPF = 1.10E+00 1.10E+00 1.10E+00 1.10E+00

DBR* = 361 1090 572 261A = 1 1 1 1

EF = 350 350 350 350AT = 70 70 70 70

FAH = 1.00 1.00 1.00 0.73* 95th percentile breathing rates for infants and 80th percentile for children and adults

Construction Cancer Risk by Year - Maximum Impact Receptor LocationInfant/Child - Exposure Information Infant/Child Adult - Exposure Information Adult

Exposure Age Cancer Modeled Age CancerExposure Duration DPM Conc (ug/m3) Sensitivity Risk DPM Conc (ug/m3) Sensitivity Risk Fugitive Total

Year (years) Age Year Annual Factor (per million) Year Annual Factor (per million) PM2.5 PM2.50 0.25 -0.25 - 0* - - 10 - - - - -1 1 0 - 1 2017 0.9670 10 158.83 2017 0.9501 1 2.73 0.1695 1.1202 1 1 - 2 2018 0.3861 10 63.42 2018 0.3861 1 1.11 0.0019 0.3883 1 2 - 3 0.0000 3 0.00 0.0000 1 0.00 4 1 3 - 4 0.0000 3 0.00 0.0000 1 0.005 1 4 - 5 0.0000 3 0.00 0.0000 1 0.006 1 5 - 6 0.0000 3 0.00 0.0000 1 0.007 1 6 - 7 0.0000 3 0.00 0.0000 1 0.008 1 7 - 8 0.0000 3 0.00 0.0000 1 0.009 1 8 - 9 0.0000 3 0.00 0.0000 1 0.0052 1 0.0000 1 0.00 0.0000 1 0.0053 1 0.0000 1 0.00 0.0000 1 0.0054 1 0.0000 1 0.00 0.0000 1 0.00.• .• .• .• .• .• .• .• .• .•.• .• .• .• .• .• .• .• .• .•.• .• .• .• .• .• .• .• .• .•60 1 0.0000 1 0.00 0.0000 1 0.0061 1 0.0000 1 0.00 0.0000 1 0.0062 1 0.0000 1 0.00 0.0000 1 0.0063 1 0.0000 1 0.00 0.0000 1 0.0064 1 0.0000 1 0.00 0.0000 1 0.0065 1 0.0000 - - 0.0000 1 0.0066 1 0.0000 - - 0.0000 1 0.0067 1 0.0000 - - 0.0000 1 0.0068 1 0.0000 - - 0.0000 1 0.0069 1 0.0000 - - 0.0000 1 0.0070 1 0.0000 - - 0.0000 1 0.00

Total Increased Cancer Risk 222.3 3.8* Third trimester of pregnancy

Results Summary

556 El Camino real, Burlingame, CA- Project Construction Health Impact Summary

Maximum Impacts at Off- Site ResidencesUnmitigated

Maximum Concentrations MaximumExhaust Fugitive Cancer Risk Hazard Annual PM2.5

Construction PM2.5/DPM PM2.5 (per million) Index ConcentrationYear (μg/m3) (μg/m3) Child Adult (-) (μg/m3)

2017 0.9670 0.2466 158.83 2.73 0.193 1.1202018 0.3861 0.0028 63.42 1.11 0.077 0.388Total - - 222.3 3.8 - -

Maximum Annual 0.9670 0.2466 - - 0.193 1.120

Documents

556 EL CAMINO REAL - burlingame.org El Camino Real.App B... · regulations include the solid waste collection vehicle (SWCV) rule, in-use public and utility fleets, and the heavy-duty