APPENDICES
Appendix A. Particulate Matter Quality Assurance/Quality Control Discussion
General Notes on Quality Assurance/Quality Control Procedures
Quality assurance/quality control (QA/QC) procedures are used to ensure the precision, accuracy, completeness, representativeness, comparability, and method detection limit of the results. The co-located samples and blanks are a primary means of assessing each of the data quality indicators. Comparing the results of two co-located samples provides information on the precision of the results as a whole. Comparing sample results to their associated blanks can help identify some potential errors in accuracy. Comparing the results received to those expected and necessary to draw conclusions about the data can help in understanding the completeness and reliability of the results. Comparability can be assessed by looking at the results taken from different sampling locations of the same building—or from different buildings for the same type of location. The reviews are generally qualitative and provide a qualitative assessment of how well the data actually represents the sampled location.
The method detection limit is a more quantitative review. It is accomplished by calculating the lowest result the analytical method can accurately identify. It is based on an analysis of the blank samples and is specific for the sampling/analysis method. Reliable information can only be obtained from sample results with method detection limits significantly lower than the average value of the results and significantly lower than any comparison values to which the sample results will be compared.
The analytical results of the concentration of airborne particulate matter were provided by the laboratory as the initial weight of the filter prior to the sampling event and the final weight of the filter after the sampling event. The concentration of the particulate matter was calculated by dividing the weight of the material collected on the filter by the volume of air drawn through the filter by the pump using the following formulas.
Weight Gain of Filter = Final Weight – Initial Weight
Sample Volume = Average Pump Flow Rate × Sample Collection Time
Average Air Sampling Pump Flow Rate=(Presampling Flow Rate + Postsampling Flow Rate) ÷ 2
Concentration = Weight Change ÷ Sample Volume
Airborne Particulate Matter Sample ResultsEach area that was sampled for airborne asbestos was also sampled for airborne particulate matter (PM). The sample results from the PM measurements did not meet the data QA/QC objectives. A variety of statistical and graphical analyses were performed on, and with, the measured results in an attempt to identify the cause and extent of inconsistencies of the measured results. A subset of the measured results that are not potentially affected by these inconsistencies were not identified. Therefore, the entire data set describing airborne particulate matter concentrations was rejected. In addition, the specific cause of the inconsistencies was not identified. The following information explains why the airborne particulate matter results were rejected.
Ideally, the particulate matter data would have provided information about the airborne concentration with an aerodynamic diameter of 100 microns and less (PM100), of 10 microns and less (PM10), of 4 microns and less (PM4), and of 2.5 microns and less (PM2.5). These different size fractions (PM100, PM10, PM4, and PM2.5) are collected using slightly different equipment, but following the same basic procedures. A pump draws air into a sampling head, and size specific particulate matter is deposited onto a filter. The difference in filter weight, before and after the sampling, represents the mass of the particulate matter that was captured by the filter. Knowing the presampling and postsampling air flow rates of the pump and the time duration for sample collection allows us to calculate the average volume of air that was drawn through the filter. The concentration of the size fraction in the sampled air is then calculated by dividing the PM mass by the air volume sampled.
In addition to the filters that were used to measure the concentration of airborne particulate matter, the laboratory also sent filters to be used as field blanks. Two blanks were sent for each PM fraction for each of the two sampling teams for each building. The blanks traveled with the sample filters, went to the sampled building or area, and were treated just like the sample filters—except that they were not used. Ideally, there should be very little difference in the weight of the blanks before the sampling and after the sampling because they were not used. A weight gain in field blanks may indicate improper sample handling in the field or problems in filter weighing in the lab. For the latter a decrease in post field blank filter weight is also an indication of lab weighing error.
The graph shown with this discussion shows the frequency distribution of the air sample filter weight change in all but seven of the blanks used. Seven blanks were not included because their weight change (from a negative -90 milligrams (mg) to 5.99 mg) was greater than the limits shown in this graph (-0.2 mg to 0.5 mg). The vertical axis represents the number of blanks that had a weight change within 0.01 mg of the weight change shown on the horizontal axis.
The dashed vertical lines show the upper and lower limits of detection expected for this method (+/– 0.03 mg). The distance between limits of detection represents the maximum weight gain expected for the blanks if the entire sampling procedure was followed as required by standard sampling methodologies. All of the size fractions had at least two blanks outside the limit of detection boundaries. (The two out of range blanks for PM100 are not shown on the graph because they are also beyond the boundaries of the graph). Approximately 6% of the PM100, 70% of the PM10, 57% of the PM4, and 8% of the PM2.5 blanks had weight changes greater than the limit of detection.
In general, blanks are used (1) to assess the ability of the sampling and laboratory analysis methodology to accurately estimate the concentration of particulate matter in the air at the sampled location and (2) to validate that there is no filter contamination problem from the time the blanks are initially weighed in the laboratory until the time the blanks are weighed in the laboratory after sampling. Errors could occur at any step in the process.
The large weight change of the blanks indicates errors in either the laboratory weighing process or the air sampling process. The graph illustrates that the results of the airborne particulate matter sampling cannot be used to reliably estimate the actual concentration of any of the particulate matter size fractions; therefore, the entire data set was rejected from further consideration.
|
Summary of Residential Sampling Survey Form Results and Review of Photographs (Abbreviations and terms used in the table are defined on the last page in this table.) |
|||||||||
|
Event Number |
Location |
Number of Broken Windows |
Dust Visible Initially |
Dust Visible Currently |
Residence Occupied |
Cleaning Method |
Aggressive Sampling |
Level of Dust in Photo |
Photo Comments |
|
1 |
Outside |
28 |
None Visible |
||||||
|
1 |
Common |
0 |
SI |
N |
C |
None Visible |
Prepared for asbestos abatement |
||
|
1 |
Residence 1 |
2 |
LI |
Y |
U |
None |
N |
Large Amount |
Large amount of WTC dust; more than other locations sampled |
|
1 |
Residence 2 |
0 |
NI |
N |
U |
None |
Y |
None Visible |
|
|
2 |
Outside |
1 |
Y |
None Visible |
|||||
|
2 |
Common |
0 |
NI |
N |
C |
Slight Amount |
|||
|
2 |
Residence 1 |
0 |
SI |
N |
Y |
C |
N |
None Visible |
Residence window faces WTC site |
|
2 |
Residence 2 |
0 |
SI |
N |
U |
C |
Y |
None Visible |
|
|
3 |
Outside |
0 |
N |
None Visible |
Sampled from courtyard several floors up |
||||
|
3 |
Common |
0 |
LI |
N |
AA |
None Visible |
|||
|
3 |
Residence 1 |
0 |
LI |
N |
Y |
AA |
N |
None Visible |
|
|
3 |
Residence 2 |
0 |
MI |
N |
Y |
C |
N |
None Visible |
|
|
4 |
Outside |
0 |
N |
Slight Amount |
|||||
|
4 |
Common |
0 |
NI |
Y |
O |
None Visible |
|||
|
4 |
Residence 1 |
0 |
SI |
Y |
N |
None |
Y |
None Visible |
|
|
4 |
Residence 2 |
0 |
SI |
Y |
N |
None |
Y |
None Visible |
|
|
5 |
Outside |
50 |
Y |
Large Amount |
|||||
|
5 |
Common |
0 |
SI |
N |
AA |
None Visible |
|||
|
5 |
Residence 1 |
6 |
LI |
LI |
Y |
AA |
Y |
None Visible |
|
|
5 |
Residence 2 |
6 |
LI |
LI |
Y |
AA |
Y |
None Visible |
Room looks clean but lots of WTC dust outside one window sill |
|
6 |
Outside |
200 |
N |
None Visible |
|||||
|
6 |
Common |
0 |
SI |
N |
C |
Couldn't identify photos for common area |
|||
|
6 |
Residence 1 |
0 |
LI |
N |
U |
C |
Y |
None Visible |
|
|
6 |
Residence 2 |
0 |
SI |
N |
U |
C |
Y |
None Visible |
|
|
7 |
Outside |
2 |
N |
None Visible |
|||||
|
7 |
Common |
0 |
MI |
N |
C |
None Visible |
Many window sills (not sure where) have significant amount of WTC dust on outside ledge, not noticeable on inside of window. |
||
|
7 |
Residence 1 |
0 |
MI |
N |
Y |
C |
N |
None Visible |
|
|
7 |
Residence 2 |
0 |
MI |
N |
Y |
C |
N |
None Visible |
Resident has window view of WTC site |
|
8 |
Outside |
0 |
N |
None Visible |
|||||
|
8 |
Common |
0 |
MI |
N |
C |
None Visible |
|||
|
8 |
Residence 1 |
1 |
SI |
N |
Y |
O |
N |
None Visible |
|
|
8 |
Residence 2 |
1 |
MI |
N |
Y |
C |
N |
None Visible |
Resident has window view of WTC site |
|
9 |
Outside |
2 |
N |
None Visible in Picture |
Utility/road construction occurring near building and across the street from the front door. |
||||
|
9 |
Common |
0 |
LI |
N |
C |
None Visible |
|||
|
9 |
Residence 1 |
0 |
MI |
Y |
Y |
C |
Y |
None Visible |
|
|
9 |
Residence 2 |
0 |
MI |
Y |
Y |
C |
Y |
Slight Amount |
|
|
10 |
Outside |
0 |
Y |
Slight Amount |
|||||
|
10 |
Common |
0 |
SI |
N |
AA |
None Visible |
|||
|
10 |
Residence 1 |
0 |
NI |
N |
Y |
AA |
Y |
None Visible |
View of Statue of Liberty |
|
10 |
Residence 2 |
1 |
SI |
N |
Y |
AA |
Y |
None Visible |
|
|
11 |
Outside |
0 |
LI |
N |
None Visible |
Looks like many dried, fallen leaves on sidewalk |
|||
|
11 |
Common |
0 |
SI |
N |
MS |
None Visible |
|||
|
11 |
Residence 1 |
0 |
SI |
N |
V |
None |
Y |
None Visible |
|
|
11 |
Residence 2 |
0 |
UNK |
N |
V |
UNK |
Y |
None Visible |
Wall AC unit was removed, it was just a hole to the outside |
|
12 |
Outside |
0 |
N |
None Visible |
Looks like many dried, fallen leaves on sidewalk |
||||
|
12 |
Common |
0 |
SI |
N |
MS |
None Visible |
|||
|
12 |
Residence 1 |
0 |
MI |
Y |
V |
None |
N |
Large Amount |
Very messy, doesn't look like “WTC dust” (has “'post-move-out”' look) |
|
12 |
Residence 2 |
0 |
SI |
N |
V |
None |
Y |
None Visible |
|
|
13 |
Outside |
0 |
N |
Slight Amount |
A little messy, but does not look like WTC dust |
||||
|
13 |
Common |
0 |
MI |
N |
MS |
None Visible |
|||
|
13 |
Residence 1 |
0 |
MI |
N |
V |
C |
Y |
None Visible |
|
|
13 |
Residence 2 |
0 |
MI |
Y |
V |
C |
Y |
Large Amount |
Very messy, but not with WTC dust (post-move-out look) |
|
14 |
Outside |
0 |
N |
None Visible |
Air sample from garden area; no bulk sample taken; WTC dust visible on neighboring building. |
||||
|
14 |
Common |
0 |
SI |
N |
C |
None Visible |
|||
|
14 |
Residence 1 |
0 |
MI |
Y |
U |
None |
Y |
Large Amount |
Light dust on floors; one pile of “material,” could be from remodeling activity |
|
14 |
Residence 2 |
0 |
MI |
Y |
U |
None |
Y |
None Visible |
Pile of trash swept into center of room; no WTC dust |
|
15 |
Outside |
0 |
N |
None Visible |
Bulk sample from roof top courtyard, |
||||
|
15 |
Common |
0 |
SI |
Y |
MS |
None Visible |
Dust visible in (and sampled from) cracks between tiles. |
||
|
15 |
Residence 1 |
0 |
SI |
Y |
U |
O |
Y |
None Visible |
|
|
15 |
Residence 2 |
0 |
SI |
N |
U |
O |
Y |
None Visible |
|
|
16 |
Outside |
0 |
N |
None Visible |
|||||
|
16 |
Common |
0 |
MI |
N |
C |
None Visible |
|||
|
16 |
Residence 1 |
0 |
MS |
None Visible |
|||||
|
16 |
Residence 2 |
0 |
LI |
N |
Y |
O |
N |
No picture |
|
|
17 |
Outside |
0 |
N |
Slight Amount |
Dirty/messy, but doesn't look like WTC dust |
||||
|
17 |
Common |
0 |
SI |
Y |
C |
None Visible |
|||
|
17 |
Residence 1 |
0 |
SI |
N |
Y |
C |
N |
None Visible |
|
|
17 |
Residence 2 |
0 |
MI |
Y |
U |
C |
Y |
Slight Amount |
|
|
18 |
Outside |
0 |
N |
M |
Sample looks granular and sandy, not gray like WTC dust |
||||
|
18 |
Common |
0 |
LI |
N |
MS |
None Visible |
Leaf track-in visible |
||
|
18 |
Residence 1 |
0 |
MI |
N |
Y |
C |
N |
None Visible |
Window view of WTC site |
|
18 |
Residence 2 |
0 |
LI |
N |
Y |
C |
N |
None Visible |
|
|
19 |
Outside |
0 |
N |
Moderate |
Visible in, and sampled from, sidewalk joint with building; sidewalk looked cleaner. |
||||
|
19 |
Common |
0 |
SI |
N |
C |
None Visible |
|||
|
19 |
Residence 1 |
0 |
LI |
N |
Y |
O |
N |
None Visible |
|
|
19 |
Residence 2 |
0 |
NI |
N |
Y |
O |
N |
No picture |
|
|
20 |
Outside |
0 |
N |
Unk |
Too distant to see surface dust |
||||
|
20 |
Common |
0 |
SI |
N |
MS |
None Visible |
|||
|
20 |
Residence 1 |
0 |
NI |
N |
Y |
O |
N |
None Visible |
|
|
20 |
Residence 2 |
0 |
SI |
N |
Y |
O |
N |
No picture |
|
|
21 |
Outside |
0 |
N |
None Visible |
|||||
|
21 |
Common |
0 |
SI |
N |
C |
None Visible |
|||
|
21 |
Residence 1 |
0 |
SI |
N |
Y |
C |
N |
None Visible |
|
|
21 |
Residence 2 |
0 |
NI |
N |
Y |
C |
N |
None Visible |
|
|
22 |
Outside |
8 |
Y |
None Visible |
Sidewalk/entrance to building and roof courtyard look clean, but there is a pile of material to sample on roof; location is unknown. |
||||
|
22 |
Common |
1 |
LI |
N |
C |
None Visible |
|||
|
22 |
Residence 1 |
0 |
MI |
Y |
Y |
MS |
N |
None Visible |
|
|
22 |
Residence 2 |
0 |
LI |
N |
Y |
C |
N |
None Visible |
|
|
23 |
Outside |
0 |
N |
None Visible |
|||||
|
23 |
Common |
0 |
SI |
N |
C |
None Visible |
|||
|
23 |
Residence 1 |
0 |
MI |
Y |
Y |
O |
N |
None Visible |
|
|
23 |
Residence 2 |
0 |
MI |
N |
Y |
O |
N |
None Visible |
|
|
24 |
Outside |
0 |
N |
None Visible |
|||||
|
24 |
Common |
0 |
LI |
N |
MS |
None Visible |
|||
|
24 |
Residence 1 |
0 |
SI |
N |
Y |
O |
N |
None Visible |
|
|
24 |
Residence 2 |
0 |
SI |
N |
Y |
C |
N |
None Visible |
|
|
25 |
Outside |
0 |
N |
None Visible |
|||||
|
25 |
Common |
0 |
NI |
N |
MS |
None Visible |
|||
|
25 |
Residence 1 |
0 |
NI |
N |
Y |
O |
N |
None Visible |
|
|
25 |
Residence 2 |
0 |
SI |
N |
Y |
C |
N |
None Visible |
|
|
26 |
Outside |
0 |
N |
None Visible |
|||||
|
26 |
Common |
0 |
NI |
N |
MS |
None Visible |
Floor area sampled contained some broken tiles. |
||
|
26 |
Residence 1 |
0 |
NI |
N |
Y |
O |
N |
None Visible |
|
|
26 |
Residence 2 |
0 |
SI |
N |
Y |
O |
N |
None Visible |
|
|
27 |
Outside |
0 |
N |
None Visible |
|||||
|
27 |
Common |
0 |
MI |
N |
MS |
None Visible |
|||
|
27 |
Residence 1 |
0 |
LI |
N |
Y |
C |
N |
None Visible |
|
|
27 |
Residence 2 |
0 |
SI |
N |
Y |
C |
N |
None Visible |
|
|
28 |
Outside |
0 |
None Visible |
Bulk sample from 4-inch wide strip between two different tiled areas; thick with granular/dusty/other material, not sure if any is WTC. |
|||||
|
28 |
Common |
0 |
LI |
Y |
C |
None Visible |
|||
|
28 |
Residence 1 |
3 |
LI |
N |
U |
C |
N |
None Visible |
|
|
28 |
Residence 2 |
0 |
MI |
N |
U |
C |
N |
None Visible |
|
|
29 |
Outside |
0 |
N |
None Visible |
Bulk sample from small pile at an inside corner of the building wall |
||||
|
29 |
Common |
0 |
NI |
N |
C |
None Visible |
|||
|
29 |
Residence 1 |
0 |
SI |
N |
Y |
O |
N |
None Visible |
|
|
29 |
Residence 2 |
0 |
SI |
Y |
Y |
O |
N |
None Visible |
|
|
30 |
Outside |
0 |
No picture |
||||||
|
30 |
Common |
0 |
No picture |
||||||
|
30 |
Residence 1 |
0 |
SI |
N |
Y |
O |
N |
None Visible |
|
|
30 |
Residence 2 |
0 |
MI |
N |
Y |
C |
N |
None Visible |
|
|
31 |
Outside |
0 |
None Visible |
||||||
|
31 |
Common |
0 |
NI |
N |
MS |
None Visible |
|||
|
31 |
Residence 1 |
0 |
NI |
N |
N |
MS |
Y |
None Visible |
|
|
31 |
Residence 2 |
0 |
NI |
UNK |
Y |
O |
N |
None Visible |
|
|
32 |
Outside |
0 |
None Visible |
Trash visible on sidewalk |
|||||
|
32 |
Common |
0 |
NI |
N |
MS |
None Visible |
|||
|
32 |
Residence 1 |
0 |
NI |
N |
Y |
O |
N |
None Visible |
|
|
32 |
Residence 2 |
0 |
|||||||
|
33 |
Outside |
0 |
None Visible |
||||||
|
33 |
Common |
0 |
|||||||
|
33 |
Residence 1 |
0 |
|||||||
|
33 |
Residence 2 |
0 |
NI |
Y |
Y |
O |
N |
None Visible |
|
|
34 |
Outside |
0 |
N |
None Visible |
|||||
|
34 |
Common |
0 |
NI |
N |
MS |
None Visible |
|||
|
34 |
Residence 1 |
0 |
|||||||
|
34 |
Residence 2 |
0 |
UNK |
N |
Y |
O |
N |
None Visible |
|
|
AA = asbestos abatement professionals C = contractor LI = large increase M = moderate increase MS = building management staff N = no NI = no Increase O = owner/tenant SI = slight increase over normal UNK = unknown Y = yes |
|||||||||
Results of Fiber Analyses
Results of fiber analyses in air and dust samples from 30 residential buildings (1–30) in lower Manhattan and 4 comparison buildings (31–34) above 59th Street. The range of values measured in the comparison buildings is shown in the summary of comparison areas above 59th Street.
|
Building Number |
Sample Location |
Results From Air Samples |
Results From Dust Samples |
||||
|
Fibers in Air PCM (f/cc) |
Asbestos in Air TEM (f/cc) |
SVF in Air SEM (f/cc) |
Asbestos in Dust PLM (%) |
Asbestos in Dust TEM (%) |
SVF in Dust PLM (%) |
||
|
Summary of Comparison Areas Above 59th Street |
|||||||
|
Outside |
<.001–0.001 |
NA |
ND–<.000043 |
Not Sampled |
Not Sampled |
Not Sampled |
|
|
Common |
<.001–0.002 |
NA |
ND–0.000043 |
ND |
ND |
ND |
|
|
Residences |
<.001–0.003 |
NA |
ND–0.000087 |
ND |
ND |
ND |
|
|
Results for Individual Buildings Sampled in Lower Manhattan (Buildings 1–30) |
|||||||
|
1 |
Outside |
0.001 |
ND |
<1 |
22 |
||
|
1 |
Common |
<.001 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
1 |
Residence 1 |
0.006 |
<.001 |
0.000162 |
ND |
NA |
20 |
|
1 |
Residence 2 |
<.001 |
ND |
NA |
20 |
||
|
2 |
Outside |
0.003 |
<1 |
1.2 |
28 |
||
|
2 |
Outside co-located |
Not Sampled |
Not Sampled |
Not Sampled |
1.3 |
NA |
25 |
|
2 |
Common |
0.005 |
<.001 |
0.000255 |
ND |
NA |
27 |
|
2 |
Residence 1 |
<.001 |
ND |
NA |
25 |
||
|
2 |
Residence 2 |
0.002 |
ND |
NA |
20 |
||
|
2 |
Window sill |
Not Sampled |
Not Sampled |
Not Sampled |
<1 |
<1 |
30 |
|
3 |
Outside |
<.001 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
3 |
Res 2 co-located |
<.001 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
3 |
Common |
<.001 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
3 |
Residence 1 |
<.001 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
3 |
Residence 2 |
<.001 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
4 |
Outside |
0.001 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
4 |
Outside co-located |
<.001 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
4 |
Common |
0.001 |
ND |
<1 |
15 |
||
|
4 |
Common co-located |
0.001 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
4 |
Residence 1 |
<.001 |
ND |
<1 |
2 |
||
|
4 |
Residence 2 |
0.001 |
ND |
<1 |
5 |
||
|
5 |
Outside |
0.002 |
3.4 |
NA |
25 |
||
|
5 |
Outside co-located |
0.003 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
5 |
Common |
0.002 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
5 |
Residence 1 |
0.002 |
<1 |
<1 |
10 |
||
|
5 |
Residence 2 |
<.001 |
ND |
<1 |
20 |
||
|
6 |
Outside |
<.001 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
6 |
Common |
<.001 |
ND |
<1 |
10 |
||
|
6 |
Res 2 co-located |
0.002 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
6 |
Residence 1 |
<.001 |
ND |
ND |
15 |
||
|
6 |
Residence 2 |
<.001 |
ND |
ND |
15 |
||
|
7 |
Outside |
<.001 |
ND |
1.7 |
35 |
||
|
7 |
Common |
0.001 |
ND |
ND |
5 |
||
|
7 |
Residence 1 |
0.001 |
ND |
ND |
ND |
||
|
7 |
Residence 2 |
<.001 |
ND |
ND |
5 |
||
|
7 |
Window sill (R2) |
Not Sampled |
Not Sampled |
Not Sampled |
ND |
ND |
40 |
|
8 |
Outside |
0.001 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
8 |
Common |
0.002 |
ND |
ND |
ND |
||
|
8 |
Residence 1 |
0.003 |
ND |
ND |
ND |
||
|
8 |
Residence 2 |
0.002 |
ND |
ND |
ND |
||
|
9 |
Outside |
<.001 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
9 |
Common |
0.001 |
ND |
ND |
7 |
||
|
9 |
Common co-located |
0.001 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
9 |
Residence 1 |
0.001 |
ND |
<1 |
2 |
||
|
9 |
Residence 2 |
0.003 |
ND |
<1 |
5 |
||
|
10 |
Outside |
0.001 |
ND |
ND |
ND |
||
|
10 |
Common |
0.002 |
ND |
1.5 |
20 |
||
|
10 |
Common, TEM re-analysis |
<1 |
|||||
|
10 |
Residence 1 |
0.001 |
ND |
ND |
15 |
||
|
10 |
Residence 2 |
0.001 |
ND |
ND |
10 |
||
|
11 |
Outside |
<.001 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
11 |
Common |
<.001 |
ND |
ND |
ND |
||
|
11 |
Common co-located |
<.001 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
11 |
Residence 1 |
<.001 |
ND |
<1 |
ND |
||
|
11 |
Residence 2 |
<.001 |
ND |
1.5 |
ND |
||
|
12 |
Outside |
<.001 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
12 |
Common |
<.001 |
ND |
ND |
ND |
||
|
12 |
Residence 1 |
0.001 |
ND |
ND |
5 |
||
|
12 |
Residence 2 |
<.001 |
ND |
ND |
5 |
||
|
13 |
Outside |
0.001 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
13 |
Common |
0.001 |
ND |
ND |
ND |
||
|
13 |
Residence 1 |
0.003 |
ND |
ND |
10 |
||
|
13 |
Residence 2 |
0.002 |
ND |
ND |
ND |
||
|
14 |
Outside |
<.001 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
14 |
Common |
0.0013 |
ND |
ND |
5 |
||
|
14 |
Residence 1 |
0.001 |
ND |
ND |
ND |
||
|
14 |
Res 1 co-located |
<.001 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
14 |
Residence 2 |
<.001 |
ND |
ND |
ND |
||
|
15 |
Outside |
<.001 |
ND |
1.9 |
72 |
||
|
15 |
Common |
0.001 |
ND |
ND |
ND |
||
|
15 |
Residence 1 |
<.001 |
ND |
<1 |
ND |
||
|
15 |
Residence 2 |
<.001 |
ND |
ND |
5 |
||
|
16 |
Outside |
<.001 |
ND |
ND |
1 |
||
|
16 |
Common |
<.001 |
ND |
ND |
ND |
||
|
16 |
Residence 1 |
Not Sampled |
Not Sampled |
Not Sampled |
Not Sampled |
Not Sampled |
Not Sampled |
|
16 |
Residence 2 |
<.001 |
ND |
ND |
ND |
||
|
16 |
Res 2 co-located |
Not Sampled |
Not Sampled |
Not Sampled |
ND |
NA |
ND |
|
16 |
Res 2 filter piece |
Not Sampled |
Not Sampled |
Not Sampled |
ND |
NA |
ND |
|
17 |
Outside |
<.001 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
17 |
Common |
<.001 |
ND |
ND |
2 |
||
|
17 |
Residence 1 |
<.001 |
ND |
ND |
ND |
||
|
17 |
Residence 2 |
<.001 |
ND |
ND |
ND |
||
|
18 |
Outside |
<.001 |
ND |
ND |
30 |
||
|
18 |
Common |
<.001 |
ND |
ND |
ND |
||
|
18 |
Residence 1 |
0.002 |
ND |
ND |
30 |
||
|
18 |
Residence 2 |
0.002 |
ND |
ND |
35 |
||
|
19 |
Outside |
<.001 |
ND |
NA |
ND |
||
|
19 |
Common |
overloaded |
<.006 |
ND |
ND |
ND |
|
|
19 |
Residence 1 |
<.001 |
ND |
ND |
ND |
||
|
19 |
Residence 2 |
<.001 |
ND |
ND |
ND |
||
|
20 |
Outside |
<.001 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
20 |
Outside co-located |
<.001 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
20 |
Common |
<.001 |
ND |
ND |
ND |
||
|
20 |
Residence 1 |
<.001 |
ND |
ND |
ND |
||
|
20 |
Residence 2 |
<.001 |
ND |
ND |
ND |
||
|
21 |
Outside |
<.001 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
21 |
Common |
<.001 |
ND |
ND |
ND |
||
|
21 |
Residence 1 |
<.001 |
ND |
ND |
ND |
||
|
21 |
Residence 2 |
<.001 |
ND |
ND |
ND |
||
|
22 |
Outside |
<.001 |
ND |
ND |
7 |
||
|
22 |
Common |
0.001 |
ND |
ND |
3 |
||
|
22 |
Residence 1 |
<.001 |
ND |
ND |
2 |
||
|
22 |
Residence 2 |
<.001 |
ND |
ND |
ND |
||
|
22 |
Res 2 co-located |
<.001 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
23 |
Outside |
<.001 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
23 |
Common |
<.001 |
ND |
ND |
ND |
||
|
23 |
Residence 1 |
<.001 |
ND |
ND |
ND |
||
|
23 |
Residence 2 |
<.001 |
ND |
ND |
ND |
||
|
24 |
Outside |
0.002 |
ND |
ND |
55 |
||
|
24 |
Common |
0.001 |
ND |
<1 |
5 |
||
|
24 |
Residence 1 |
0.001 |
ND |
ND |
ND |
||
|
24 |
Residence 2 |
0.005 |
<.001 |
0.000037 |
ND |
ND |
10 |
|
24 |
Res 2 co-located |
0.005 |
<.001 |
Not Sampled |
Not Sampled |
Not Sampled |
|
|
25 |
Outside |
<.001 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
25 |
Common |
<.001 |
ND |
ND |
5 |
||
|
25 |
Residence 1 |
<.001 |
ND |
ND |
5 |
||
|
25 |
Residence 2 |
0.001 |
ND |
ND |
ND |
||
|
26 |
Outside |
0.001 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
26 |
Common |
0.004 |
<.001 |
<0.00004 |
ND |
ND |
5 |
|
26 |
Residence 1 |
0.012 |
<.001 |
<0.00004 |
ND |
ND |
ND |
|
26 |
Residence 2 |
<.001 |
ND |
ND |
ND |
||
|
27 |
Outside |
<.001 |
ND |
<1 |
15 |
||
|
27 |
Common |
<.001 |
ND |
<1 |
10 |
||
|
27 |
Residence 1 |
<.001 |
ND |
<1 |
10 |
||
|
27 |
Residence 2 |
<.001 |
ND |
ND |
10 |
||
|
28 |
Outside |
<.001 |
ND |
ND |
15 |
||
|
28 |
Common |
0.001 |
ND |
ND |
10 |
||
|
28 |
Residence 1 |
<.001 |
ND |
Insufficient Material |
ND |
||
|
28 |
Residence 2 |
0.002 |
ND |
ND |
ND |
||
|
29 |
Outside |
<.001 |
ND |
ND |
ND |
||
|
29 |
Common |
<.001 |
ND |
ND |
ND |
||
|
29 |
Residence 1 |
<.001 |
ND |
ND |
ND |
||
|
29 |
Residence 2 |
<.001 |
ND |
ND |
ND |
||
|
30 |
Outside |
Not Sampled |
Not Sampled |
Not Sampled |
Not Sampled |
Not Sampled |
Not Sampled |
|
30 |
Common |
Not Sampled |
Not Sampled |
Not Sampled |
Not Sampled |
Not Sampled |
Not Sampled |
|
30 |
Residence 1 |
<.001 |
ND |
ND |
ND |
||
|
30 |
Residence 2 |
<.001 |
ND |
ND |
ND |
||
|
Results for Comparison Buildings Sampled Above 59th Street (Buildings 31–34) |
|||||||
|
31 |
Outside |
<.001 |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
31 |
Outside co-located |
0.001 |
0.000039 |
Not Sampled |
Not Sampled |
Not Sampled |
|
|
31 |
Common |
<.001 |
ND |
ND |
ND |
||
|
31 |
Residence 1 |
<.001 |
<0.000039 |
ND |
ND |
ND |
|
|
31 |
Residence 2 |
<.001 |
<0.000038 |
ND |
ND |
ND |
|
|
32 |
Outside |
<.001 |
<0.000039 |
Not Sampled |
Not Sampled |
Not Sampled |
|
|
32 |
Common |
0.002 |
<0.00004 |
ND |
ND |
ND |
|
|
32 |
Residence 1 |
<.001 |
ND |
ND |
ND |
||
|
32 |
Res 1 co-located |
0.001 |
0.000087 |
Not Sampled |
Not Sampled |
Not Sampled |
|
|
32 |
Residence 2 |
Not Sampled |
Not Sampled |
Not Sampled |
Not Sampled |
Not Sampled |
Not Sampled |
|
33 |
Outside |
Not Sampled |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
33 |
Common |
Not Sampled |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
33 |
Residence 1 |
Not Sampled |
Not Sampled |
Not Sampled |
Not Sampled |
||
|
33 |
Residence 2 |
<.001 |
<0.000041 |
ND |
ND |
ND |
|
|
34 |
Outside |
<.001 |
<0.000043 |
Not Sampled |
Not Sampled |
Not Sampled |
|
|
34 |
Common |
<.001 |
0.000043 |
ND |
ND |
ND |
|
|
34 |
Residence 1 |
Not Sampled |
Not Sampled |
Not Sampled |
Not Sampled |
Not Sampled |
Not Sampled |
|
34 |
Residence 2 |
0.002 |
ND |
Insuf. Material |
ND |
||
|
34 |
Res 2 co-located |
0.003 |
<0.000047 |
Not Sampled |
Not Sampled |
Not Sampled |
|
f/cc: fibers per cubic centimeter of air
NA: not analyzed
ND: not detected
PCM: phase contrast microscopy
PLM: polarized light microscopy
SEM: scanning electron microscopy
SVF: synthetic vitreous fibers
TEM: transmission electron microscopy
%: percent
Results of Mineral Analyses in Dust and Air
The following table shows the results of analyses of the minerals in settled dust and air samples for 30 residential buildings in lower Manhattan (1–30) and 4 comparison buildings (31-34) above 59th Street. For each building, the table shows the highest estimated air concentration of mineral for each size fraction. In addition, estimated levels of each mineral in the settled surface dust are shown for each sampled location within a building.
|
Building Number |
Sample Type |
Method or Location |
Quartz |
Cristobalite |
Tridymite |
Calcite |
Portlandite |
Gypsum |
Mica |
Halite |
|
Summary of Comparison Areas Above 59th Street |
||||||||||
|
Air (µg/m3) |
PM100 |
ND |
ND |
ASN |
ND |
ND |
ND–3 J |
ND |
ND |
|
|
Air (µg/m3) |
PM10 |
ND |
ND |
ASN |
ND |
ND |
ND–3 J |
ND |
ND |
|
|
Air (µg/m3) |
PM4 |
ND |
ND |
ASN |
ND |
ND |
ND–5 J |
ND |
ND |
|
|
Air (µg/m3) |
PM2.5 |
ND |
ND |
ASN |
ND |
ND |
ND–3 J |
ND |
ND |
|
|
Settled surface dust (%) |
Common Area |
ND–1 J |
ND |
ND |
ND–0.4 J |
ND–0.05 J |
ND–3 J |
ND |
ND |
|
|
Settled surface dust (%) |
Outdoor |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
|
Settled surface dust (%) |
Residence 1&2 |
ND–2 J |
ND |
ND |
ND–0.9 J |
ND–0.08 J |
2–4 J |
ND–0.08 J |
ND–0.4 J |
|
|
Results for Individual Buildings Sampled in Lower Manhattan (Buildings 1–30) |
||||||||||
|
1 |
Air (µg/m3) |
PM100 |
ND |
ND |
ASN |
ND |
ND |
6 J |
ND |
ND |
|
1 |
Air (µg/m3) |
PM10 |
ND |
ND |
ASN |
ND |
ND |
14 J |
ND |
ND |
|
1 |
Air (µg/m3) |
PM4 |
ND |
ND |
ASN |
6 J |
84 J |
12 J |
ND |
ND |
|
1 |
Air (µg/m3) |
PM2.5 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
1 |
Settled surface dust (%) |
Common area |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
1 |
Settled surface dust (%) |
Outdoor |
27 J |
ND |
ND |
15 J |
6 J |
14 J |
ND |
ND |
|
1 |
Settled surface dust (%) |
Residence 1 |
19 J |
ND |
ND |
18 J |
2 J |
30 J |
0.3 J |
ND |
|
1 |
Settled surface dust (%) |
Residence 2 |
31 J |
ND |
ND |
21 J |
6 J |
4 J |
0.05 J |
ND |
|
2 |
Air (µg/m3) |
PM100 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
2 |
Air (µg/m3) |
PM10 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
2 |
Air (µg/m3) |
PM4 |
ND |
ND |
ASN |
ND |
ND |
7J |
ND |
ND |
|
2 |
Air (µg/m3) |
PM2.5 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
2 |
Settled surface dust (%) |
Common area |
1 J |
ND |
ND |
ND |
2 J |
14 J |
ND |
ND |
|
2 |
Settled surface dust (%) |
Outdoor |
21 J |
ND |
ND |
19 J |
3 J |
27 J |
ND |
<0.03 J |
|
2 |
Settled surface dust (%) |
Residence 1 |
3 J |
ND |
ND |
2 J |
0.9 J |
6 J |
ND |
ND |
|
2 |
Settled surface dust (%) |
Residence 2 |
23 J |
ND |
ND |
15 J |
4 J |
9 J |
ND |
ND |
|
3 |
Air (µg/m3) |
PM100 |
6 J |
15 J |
ASN |
5 J |
24 J |
5 J |
13 J |
ND |
|
3 |
Air (µg/m3) |
PM10 |
5 J |
ND |
ASN |
5 J |
25 J |
6 J |
ND |
ND |
|
3 |
Air (µg/m3) |
PM4 |
6 J |
ND |
ASN |
6 J |
26 J |
7 J |
ND |
ND |
|
3 |
Air (µg/m3) |
PM2.5 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
3 |
Settled surface dust (%) |
Outdoor |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
3 |
Settled surface dust (%) |
Common |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
3 |
Settled surface dust (%) |
Residence 1 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
3 |
Settled surface dust (%) |
Residence 2 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
4 |
Air (µg/m3) |
PM100 |
4 J |
ND |
ASN |
4 J |
16 J |
3 J |
9 J |
5 J |
|
4 |
Air (µg/m3) |
PM10 |
4 J |
ND |
ASN |
3 J |
16 J |
3 J |
ND |
4 J |
|
4 |
Air (µg/m3) |
PM4 |
6 J |
ND |
ASN |
6 J |
28 J |
5 J |
14 J |
8 J |
|
4 |
Air (µg/m3) |
PM2.5 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
4 |
Settled surface dust (%) |
Common area |
ND |
ND |
ND |
1 J |
0.4 J |
8 J |
ND |
ND |
|
4 |
Settled surface dust (%) |
Outdoor |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
4 |
Settled surface dust (%) |
Residence 1 |
0.2 J |
ND |
ND |
0.06 J |
0.7 J |
1 J |
ND |
ND |
|
4 |
Settled surface dust (%) |
Residence 2 |
14 J |
ND |
ND |
5 J |
2 J |
9 J |
ND |
0.1 J |
|
5 |
Air (µg/m3) |
PM100 |
ND |
ND |
ASN |
14 J |
95 J |
14 J |
ND |
14 J |
|
5 |
Air (µg/m3) |
PM10 |
ND |
ND |
ASN |
ND |
ND |
14 J |
ND |
ND |
|
5 |
Air (µg/m3) |
PM4 |
ND |
ND |
ASN |
ND |
ND |
15 J |
ND |
ND |
|
5 |
Air (µg/m3) |
PM2.5 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
5 |
Settled surface dust (%) |
Common area |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
5 |
Settled surface dust (%) |
Outdoor |
23 J |
ND |
ND |
8 J |
ND |
ND |
ND |
ND |
|
5 |
Settled surface dust (%) |
Residence 1 |
2 J |
ND |
ND |
ND |
ND |
9 J |
ND |
ND |
|
5 |
Settled surface dust (%) |
Residence 2 |
11 J |
ND |
ND |
4 J |
0.5 J |
2 J |
ND |
ND |
|
6 |
Air (µg/m3) |
PM100 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
6 |
Air (µg/m3) |
PM10 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
6 |
Air (µg/m3) |
PM4 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
6 |
Air (µg/m3) |
PM2.5 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
6 |
Settled surface dust (%) |
Common area |
17 J |
ND |
ND |
10 J |
3 J |
20 J |
0.6 J |
ND |
|
6 |
Settled surface dust (%) |
Outdoor |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
6 |
Settled surface dust (%) |
Residence 1 |
27 J |
ND |
ND |
17 J |
8 J |
13 J |
ND |
ND |
|
6 |
Settled surface dust (%) |
Residence 2 |
24 J |
ND |
ND |
15 J |
4 J |
4 J |
0.03 J |
ND |
|
7 |
Air (µg/m3) |
PM100 |
ND |
ND |
ASN |
8 J |
54 J |
10 J |
ND |
ND |
|
7 |
Air (µg/m3) |
PM10 |
ND |
ND |
ASN |
ND |
ND |
11 J |
ND |
ND |
|
7 |
Air (µg/m3) |
PM4 |
ND |
ND |
ASN |
ND |
ND |
11 J |
ND |
ND |
|
7 |
Air (µg/m3) |
PM2.5 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
7 |
Settled surface dust (%) |
Common area |
11 J |
ND |
ND |
8 J |
3 J |
15 J |
0.09 J |
0.04 J |
|
7 |
Settled surface dust (%) |
Outdoor |
14 J |
ND |
ND |
7 J |
1 J |
12 J |
ND |
0.1 J |
|
7 |
Settled surface dust (%) |
Residence 1 |
14 J |
ND |
ND |
13 J |
2 J |
2 J |
ND |
ND |
|
7 |
Settled surface dust (%) |
Residence 2 |
21 J |
ND |
ND |
16 J |
3 J |
4 J |
ND |
0.09 J |
|
7 |
Settled surface dust (%) |
Residence 2-co |
18 J |
ND |
ND |
9 J |
1 J |
2 J |
ND |
ND |
|
8 |
Air (µg/m3) |
PM100 |
ND |
ND |
ASN |
7 J |
ND |
10 J |
ND |
ND |
|
8 |
Air (µg/m3) |
PM10 |
ND |
ND |
ASN |
ND |
ND |
9 J |
ND |
ND |
|
8 |
Air (µg/m3) |
PM4 |
ND |
ND |
ASN |
6 J |
ND |
12 J |
43 J |
19 J |
|
8 |
Air (µg/m3) |
PM2.5 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
8 |
Settled surface dust (%) |
Common area |
19 J |
ND |
ND |
9 J |
2 J |
15 J |
ND |
ND |
|
8 |
Settled surface dust (%) |
Outdoor |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
8 |
Settled surface dust (%) |
Residence 1 |
15 J |
ND |
ND |
10 J |
3 J |
17 J |
ND |
ND |
|
8 |
Settled surface dust (%) |
Residence 2 |
28 J |
ND |
ND |
21 J |
4 J |
6 J |
ND |
ND |
|
9 |
Air (µg/m3) |
PM100 |
ND |
ND |
ASN |
ND |
ND |
3 J |
ND |
ND |
|
9 |
Air (µg/m3) |
PM10 |
ND |
ND |
ASN |
4 J |
ND |
6 J |
ND |
ND |
|
9 |
Air (µg/m3) |
PM4 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
9 |
Air (µg/m3) |
PM2.5 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
9 |
Settled surface dust (%) |
Common area |
25 J |
ND |
ND |
9 J |
4 J |
16 J |
0.09 J |
0.06 J |
|
9 |
Settled surface dust (%) |
Outdoor |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
9 |
Settled surface dust (%) |
Residence 1 |
10 J |
ND |
ND |
2 J |
0.9 J |
5 J |
ND |
ND |
|
9 |
Settled surface dust (%) |
Residence 2 |
4 J |
ND |
ND |
ND |
ND |
2 J |
ND |
ND |
|
10 |
Air (µg/m3) |
PM100 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
10 |
Air (µg/m3) |
PM10 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
10 |
Air (µg/m3) |
PM4 |
ND |
ND |
ASN |
8 J |
ND |
ND |
ND |
ND |
|
10 |
Air (µg/m3) |
PM2.5 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
10 |
Settled surface dust (%) |
Common area |
2 J |
ND |
ND |
3 J |
ND |
1 J |
ND |
ND |
|
10 |
Settled surface dust (%) |
Common area-co |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
10 |
Settled surface dust (%) |
Outdoor |
21 J |
ND |
ND |
14 J |
3 J |
5 J |
0.09 J |
0.05 J |
|
10 |
Settled surface dust (%) |
Residence 1 |
3 J |
ND |
ND |
ND |
0.06 J |
ND |
ND |
ND |
|
10 |
Settled surface dust (%) |
Residence 2 |
2 J |
ND |
ND |
ND |
ND |
0.8 J |
ND |
0.04 J |
|
11 |
Air (µg/m3) |
PM100 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
11 |
Air (µg/m3) |
PM10 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
11 |
Air (µg/m3) |
PM4 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
11 |
Air (µg/m3) |
PM2.5 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
11 |
Settled surface dust (%) |
Common area |
2 J |
ND |
ND |
ND |
ND |
1 J |
ND |
ND |
|
11 |
Settled surface dust (%) |
Outdoor |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
11 |
Settled surface dust (%) |
Residence 1 |
0.2 J |
ND |
ND |
0.02 J |
ND |
2 J |
ND |
ND |
|
11 |
Settled surface dust (%) |
Residence 2 |
0.07 J |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
12 |
Air (µg/m3) |
PM100 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
12 |
Air (µg/m3) |
PM10 |
3 J |
ND |
ASN |
5 J |
18 J |
4 J |
8 J |
5 J |
|
12 |
Air (µg/m3) |
PM4 |
5 J |
ND |
ASN |
7 J |
28 J |
6 J |
15 J |
7 J |
|
12 |
Air (µg/m3) |
PM2.5 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
12 |
Settled surface dust (%) |
Common area |
4 J |
ND |
ND |
2 J |
3 J |
1 J |
ND |
ND |
|
12 |
Settled surface dust (%) |
Outdoor |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
12 |
Settled surface dust (%) |
Residence 1 |
ND |
ND |
ND |
ND |
ND |
0.3 J |
ND |
ND |
|
12 |
Settled surface dust (%) |
Residence 2 |
0.4 J |
ND |
ND |
0.09 J |
0.06 J |
0.8 J |
ND |
ND |
|
13 |
Air (µg/m3) |
PM100 |
5 J |
ND |
ASN |
5 J |
16 J |
3 J |
ND |
ND |
|
13 |
Air (µg/m3) |
PM10 |
4 J |
ND |
ASN |
5 J |
16 J |
3 J |
ND |
ND |
|
13 |
Air (µg/m3) |
PM4 |
7 J |
ND |
ASN |
10 J |
26 J |
5 J |
ND |
ND |
|
13 |
Air (µg/m3) |
PM2.5 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
13 |
Settled surface dust (%) |
Common area |
0.05 J |
ND |
ND |
0.3 J |
0.04 J |
1 J |
ND |
ND |
|
13 |
Settled surface dust (%) |
Outdoor |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
13 |
Settled surface dust (%) |
Residence 1 |
ND |
ND |
ND |
ND |
ND |
1 J |
ND |
ND |
|
13 |
Settled surface dust (%) |
Residence 2 |
ND |
ND |
ND |
ND |
ND |
0.8 J |
ND |
ND |
|
14 |
Air (µg/m3) |
PM100 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
14 |
Air (µg/m3) |
PM10 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
14 |
Air (µg/m3) |
PM4 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
14 |
Air (µg/m3) |
PM2.5 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
14 |
Settled surface dust (%) |
Common area |
0.03 J |
ND |
ND |
ND |
ND |
2 J |
ND |
0.04 J |
|
14 |
Settled surface dust (%) |
Outdoor |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
14 |
Settled surface dust (%) |
Residence 1 |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
14 |
Settled surface dust (%) |
Residence 2 |
ND |
ND |
ND |
ND |
ND |
0.08 J |
ND |
ND |
|
15 |
Air (µg/m3) |
PM100 |
8 J |
ND |
ASN |
3 J |
18 J |
ND |
ND |
ND |
|
15 |
Air (µg/m3) |
PM10 |
ND |
ND |
ASN |
ND |
ND |
3 J |
ND |
ND |
|
15 |
Air (µg/m3) |
PM4 |
ND |
ND |
ASN |
ND |
ND |
5 J |
ND |
ND |
|
15 |
Air (µg/m3) |
PM2.5 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
15 |
Settled surface dust (%) |
Common area |
0.4 J |
ND |
ND |
0.02 J |
ND |
1 J |
ND |
ND |
|
15 |
Settled surface dust (%) |
Outdoor |
1 J |
ND |
ND |
ND |
0.3 J |
2 J |
ND |
ND |
|
15 |
Settled surface dust (%) |
Residence 1 |
ND |
ND |
ND |
ND |
ND |
1 J |
ND |
ND |
|
15 |
Settled surface dust (%) |
Residence 2 |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
16 |
Air (µg/m3) |
PM100 |
4 J |
ND |
ASN |
3 J |
17 J |
3 J |
ND |
ND |
|
16 |
Air (µg/m3) |
PM10 |
ND |
ND |
ASN |
ND |
ND |
4 J |
ND |
ND |
|
16 |
Air (µg/m3) |
PM4 |
18 J |
ND |
ASN |
5 J |
27 J |
7 J |
ND |
ND |
|
16 |
Air (µg/m3) |
PM2.5 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
16 |
Settled surface dust (%) |
Common area |
ND |
ND |
ND |
ND |
ND |
0.09 J |
ND |
ND |
|
16 |
Settled surface dust (%) |
Outdoor |
3 J |
ND |
ND |
1 J |
0.6 J |
0.04 J |
0.06 J |
0.04 J |
|
16 |
Settled surface dust (%) |
Residence 1 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
16 |
Settled surface dust (%) |
Residence 2 |
ND |
ND |
ND |
ND |
ND |
0.9 J |
ND |
ND |
|
16 |
Settled surface dust (%) |
R2 filter piece |
2 J |
ND |
ND |
0.3 J |
0.4 J |
1 J |
ND |
ND |
|
17 |
Air (µg/m3) |
PM100 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
17 |
Air (µg/m3) |
PM10 |
12 J |
ND |
ASN |
4 J |
17 J |
6 J |
ND |
5 J |
|
17 |
Air (µg/m3) |
PM4 |
5 J |
ND |
ASN |
5 J |
27 J |
6 J |
15 J |
ND |
|
17 |
Air (µg/m3) |
PM2.5 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
17 |
Settled surface dust (%) |
Common area |
2 J |
ND |
ND |
ND |
ND |
1 J |
0.06 J |
ND |
|
17 |
Settled surface dust (%) |
Outdoor |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
17 |
Settled surface dust (%) |
Residence 1 |
0.9 J |
ND |
ND |
ND |
0.05 J |
2 J |
0.05 J |
0.03 J |
|
17 |
Settled surface dust (%) |
Residence 2 |
1 J |
ND |
ND |
0.8 J |
ND |
1 J |
ND |
ND |
|
18 |
Air (µg/m3) |
PM100 |
3 J |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
18 |
Air (µg/m3) |
PM10 |
ND |
ND |
ASN |
ND |
ND |
3 J |
ND |
ND |
|
18 |
Air (µg/m3) |
PM4 |
5 J |
ND |
ASN |
ND |
ND |
5 J |
ND |
ND |
|
18 |
Air (µg/m3) |
PM2.5 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
18 |
Settled surface dust (%) |
Common area |
0.9 J |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
18 |
Settled surface dust (%) |
Outdoor |
7 J |
ND |
ND |
1 J |
ND |
ND |
0.2 J |
ND |
|
18 |
Settled surface dust (%) |
Residence 1 |
ND |
ND |
ND |
ND |
ND |
0.3 J |
ND |
ND |
|
18 |
Settled surface dust (%) |
Residence 2 |
ND |
ND |
ND |
ND |
ND |
1 J |
ND |
ND |
|
19 |
Air (µg/m3) |
PM100 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
19 |
Air (µg/m3) |
PM10 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
19 |
Air (µg/m3) |
PM4 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
19 |
Air (µg/m3) |
PM2.5 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
19 |
Settled surface dust (%) |
Common area |
1 J |
ND |
ND |
0.08 J |
0.05 J |
1 J |
ND |
ND |
|
19 |
Settled surface dust (%) |
Outdoor |
5 J |
ND |
ND |
1 J |
0.6 J |
1 J |
0.09 J |
0.04 J |
|
19 |
Settled surface dust (%) |
Residence 1 |
ND |
ND |
ND |
ND |
ND |
1 J |
ND |
ND |
|
19 |
Settled surface dust (%) |
Residence 2 |
ND |
ND |
ND |
ND |
ND |
2 J |
ND |
ND |
|
20 |
Air (µg/m3) |
PM100 |
3 J |
ND |
ASN |
3 J |
16 J |
3 J |
ND |
ND |
|
20 |
Air (µg/m3) |
PM10 |
3 J |
ND |
ASN |
3 J |
16 J |
4 J |
ND |
ND |
|
20 |
Air (µg/m3) |
PM4 |
5 J |
ND |
ASN |
5 J |
29 J |
6 J |
ND |
ND |
|
20 |
Air (µg/m3) |
PM2.5 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
20 |
Settled surface dust (%) |
Common area |
ND |
ND |
ND |
ND |
ND |
0.07 J |
ND |
0.04 J |
|
20 |
Settled surface dust (%) |
Outdoor |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
20 |
Settled surface dust (%) |
Residence 1 |
0.05 J |
ND |
ND |
ND |
ND |
1 J |
ND |
ND |
|
20 |
Settled surface dust (%) |
Residence 2 |
0.9 J |
ND |
ND |
0.6 J |
0.09 J |
1 J |
ND |
0.05 J |
|
21 |
Air (µg/m3) |
PM100 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
21 |
Air (µg/m3) |
PM10 |
R |
R |
R |
R |
R |
R |
R |
R |
|
21 |
Air (µg/m3) |
PM4 |
ND |
ND |
ASN |
ND |
ND |
5 J |
ND |
ND |
|
21 |
Air (µg/m3) |
PM2.5 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
21 |
Settled surface dust (%) |
Common area |
0.9 J |
ND |
ND |
ND |
ND |
2 J |
ND |
ND |
|
21 |
Settled surface dust (%) |
Outdoor |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
21 |
Settled surface dust (%) |
Residence 1 |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
21 |
Settled surface dust (%) |
Residence 2 |
ND |
ND |
ND |
ND |
ND |
1 J |
ND |
ND |
|
22 |
Air (µg/m3) |
PM100 |
13 J |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
22 |
Air (µg/m3) |
PM10 |
3 J |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
22 |
Air (µg/m3) |
PM4 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
22 |
Air (µg/m3) |
PM2.5 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
22 |
Settled surface dust (%) |
Common area |
14 J |
ND |
ND |
1 J |
0.4 J |
ND |
ND |
ND |
|
22 |
Settled surface dust (%) |
Outdoor |
26 J |
ND |
ND |
2 J |
0.8 J |
0.03 J |
0.07 J |
ND |
|
22 |
Settled surface dust (%) |
Residence 1 |
2 J |
ND |
ND |
0.07 J |
0.08 J |
1 J |
ND |
ND |
|
22 |
Settled surface dust (%) |
Residence 2 |
0.6 J |
ND |
ND |
ND |
ND |
2 J |
ND |
ND |
|
23 |
Air (µg/m3) |
PM100 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
23 |
Air (µg/m3) |
PM10 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
23 |
Air (µg/m3) |
PM4 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
23 |
Air (µg/m3) |
PM2.5 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
23 |
Settled surface dust (%) |
Common area |
2 J |
ND |
ND |
0.04 J |
0.05 J |
0.9 J |
ND |
ND |
|
23 |
Settled surface dust (%) |
Outdoor |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
23 |
Settled surface dust (%) |
Residence 1 |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
23 |
Settled surface dust (%) |
Residence 2 |
ND |
ND |
ND |
ND |
ND |
1 J |
ND |
ND |
|
24 |
Air (µg/m3) |
PM100 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
24 |
Air (µg/m3) |
PM10 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
24 |
Air (µg/m3) |
PM4 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
24 |
Air (µg/m3) |
PM2.5 |
3 J |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
24 |
Settled surface dust (%) |
Common area |
0.03 J |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
24 |
Settled surface dust (%) |
Outdoor |
2 J |
ND |
ND |
0.8 J |
0.07 J |
ND |
0.05 J |
0.04 J |
|
24 |
Settled surface dust (%) |
Residence 1 |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
24 |
Settled surface dust (%) |
Residence 2 |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
25 |
Air (µg/m3) |
PM100 |
ND |
ND |
ASN |
ND |
ND |
3 J |
ND |
ND |
|
25 |
Air (µg/m3) |
PM10 |
R |
R |
R |
R |
R |
R |
R |
R |
|
25 |
Air (µg/m3) |
PM4 |
ND |
ND |
ASN |
ND |
ND |
4 J |
ND |
ND |
|
25 |
Air (µg/m3) |
PM2.5 |
ND |
ND |
ASN |
ND |
ND |
3 J |
ND |
ND |
|
25 |
Settled surface dust (%) |
Common area |
ND |
ND |
ND |
ND |
ND |
2 J |
ND |
ND |
|
25 |
Settled surface dust (%) |
Outdoor |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
25 |
Settled surface dust (%) |
Residence 1 |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
25 |
Settled surface dust (%) |
Residence 2 |
ND |
ND |
ND |
ND |
ND |
2 J |
ND |
ND |
|
26 |
Air (µg/m3) |
PM100 |
8 J |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
26 |
Air (µg/m3) |
PM10 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
26 |
Air (µg/m3) |
PM4 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
26 |
Air (µg/m3) |
PM2.5 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
26 |
Settled surface dust (%) |
Common area |
0.7 J |
ND |
ND |
2 J |
0.6 J |
2 J |
0.07 J |
ND |
|
26 |
Settled surface dust (%) |
Outdoor |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
26 |
Settled surface dust (%) |
Residence 1 |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
26 |
Settled surface dust (%) |
Residence 2 |
ND |
ND |
ND |
ND |
ND |
0.05 J |
ND |
ND |
|
27 |
Air (µg/m3) |
PM100 |
3 J |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
27 |
Air (µg/m3) |
PM10 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
27 |
Air (µg/m3) |
PM4 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
27 |
Air (µg/m3) |
PM2.5 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
27 |
Settled surface dust (%) |
Common area |
0.04 J |
ND |
ND |
0.02 J |
ND |
0.1 J |
ND |
ND |
|
27 |
Settled surface dust (%) |
Outdoor |
4 J |
ND |
ND |
1 J |
0.8 J |
0.04 J |
0.07 J |
ND |
|
27 |
Settled surface dust (%) |
Residence 1 |
ND |
ND |
ND |
ND |
ND |
0.6 J |
ND |
ND |
|
27 |
Settled surface dust (%) |
Residence 2 |
ND |
ND |
ND |
ND |
ND |
1 J |
ND |
ND |
|
28 |
Air (µg/m3) |
PM100 |
3 J |
ND |
ASN |
ND |
ND |
3 J |
ND |
4 J |
|
28 |
Air (µg/m3) |
PM10 |
ND |
ND |
ASN |
ND |
ND |
3 J |
ND |
ND |
|
28 |
Air (µg/m3) |
PM4 |
ND |
ND |
ASN |
ND |
ND |
5 J |
ND |
ND |
|
28 |
Air (µg/m3) |
PM2.5 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
28 |
Settled surface dust (%) |
Common area |
ND |
ND |
ND |
ND |
ND |
1 J |
ND |
ND |
|
28 |
Settled surface dust (%) |
Outdoor |
8 J |
ND |
ND |
3 J |
2 J |
0.3 J |
0.09 J |
ND |
|
28 |
Settled surface dust (%) |
Residence 1 |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
28 |
Settled surface dust (%) |
Residence 2 |
ND |
ND |
ND |
ND |
ND |
1 J |
ND |
ND |
|
29 |
Air (µg/m3) |
PM100 |
4 J |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
29 |
Air (µg/m3) |
PM10 |
ND |
ND |
ASN |
ND |
ND |
3 J |
ND |
ND |
|
29 |
Air (µg/m3) |
PM4 |
19 J |
ND |
ASN |
ND |
ND |
5 J |
ND |
ND |
|
29 |
Air (µg/m3) |
PM2.5 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
29 |
Settled surface dust (%) |
Common area |
1 J |
ND |
ND |
0.09 J |
0.06 J |
2 J |
ND |
ND |
|
29 |
Settled surface dust (%) |
Outdoor |
8 J |
ND |
ND |
3 J |
2 J |
2 J |
0.3 J |
0.07 J |
|
29 |
Settled surface dust (%) |
Residence 1 |
0.2 J |
ND |
ND |
ND |
ND |
1 J |
ND |
ND |
|
29 |
Settled surface dust (%) |
Residence 2 |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
30 |
Air (µg/m3) |
PM100 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
30 |
Air (µg/m3) |
PM10 |
3 J |
ND |
ASN |
ND |
ND |
3 J |
ND |
ND |
|
30 |
Air (µg/m3) |
PM4 |
ND |
ND |
ASN |
ND |
ND |
5 J |
ND |
ND |
|
30 |
Air (µg/m3) |
PM2.5 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
30 |
Settled surface dust (%) |
Common area |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
30 |
Settled surface dust (%) |
Outdoor |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
30 |
Settled surface dust (%) |
Residence 1 |
1 J |
ND |
ND |
ND |
0.9 J |
4 J |
0.06 J |
0.05 J |
|
30 |
Settled surface dust (%) |
Residence 2 |
0.6 J |
ND |
ND |
0.4 J |
0.4 J |
4 J |
ND |
ND |
|
Results for Individual Comparison Buildings Sampled Above 59th Street (Buildings 31–34) |
||||||||||
|
31 |
Air (µg/m3) |
PM100 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
31 |
Air (µg/m3) |
PM10 |
ND |
ND |
ASN |
ND |
ND |
3 J |
ND |
ND |
|
31 |
Air (µg/m3) |
PM4 |
ND |
ND |
ASN |
ND |
ND |
5 J |
ND |
ND |
|
31 |
Air (µg/m3) |
PM2.5 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
31 |
Settled surface dust (%) |
Common area |
1 J |
ND |
ND |
0.03 J |
0.05 J |
2 J |
ND |
0.04 J |
|
31 |
Settled surface dust (%) |
Outdoor |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
31 |
Settled surface dust (%) |
Residence 1 |
ND |
ND |
ND |
ND |
ND |
2 J |
ND |
ND |
|
31 |
Settled surface dust (%) |
Residence 2 |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
32 |
Air (µg/m3) |
PM100 |
ND |
ND |
ASN |
ND |
ND |
3 J |
ND |
ND |
|
32 |
Air (µg/m3) |
PM10 |
ND |
ND |
ASN |
ND |
ND |
3 J |
ND |
ND |
|
32 |
Air (µg/m3) |
PM4 |
ND |
ND |
ASN |
ND |
ND |
5 J |
ND |
ND |
|
32 |
Air (µg/m3) |
PM2.5 |
ND |
ND |
ASN |
ND |
ND |
3 J |
ND |
ND |
|
32 |
Settled surface dust (%) |
Common area |
1 J |
ND |
ND |
0.4 J |
ND |
3J |
ND |
ND |
|
32 |
Settled surface dust (%) |
Outdoor |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
32 |
Settled surface dust (%) |
Residence 1 |
2 J |
ND |
ND |
0.9 J |
0.08 J |
4 J |
0.08 J |
0.4 J |
|
32 |
Settled surface dust (%) |
Residence 2 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
33 |
Air (µg/m3) |
PM100 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
33 |
Air (µg/m3) |
PM10 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
33 |
Air (µg/m3) |
PM4 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
33 |
Air (µg/m3) |
PM2.5 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
33 |
Settled surface dust (%) |
Common area |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
33 |
Settled surface dust (%) |
Outdoor |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
33 |
Settled surface dust (%) |
Residence 1 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
33 |
Settled surface dust (%) |
Residence 2 |
1 J |
ND |
ND |
ND |
0.08 J |
2 J |
ND |
ND |
|
34 |
Air (µg/m3) |
PM100 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
34 |
Air (µg/m3) |
PM10 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
34 |
Air (µg/m3) |
PM4 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
34 |
Air (µg/m3) |
PM2.5 |
ND |
ND |
ASN |
ND |
ND |
ND |
ND |
ND |
|
34 |
Settled surface dust (%) |
Common area |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
ND |
|
34 |
Settled surface dust (%) |
Outdoor |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
34 |
Settled surface dust (%) |
Residence 1 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
34 |
Settled surface dust (%) |
Residence 2 |
ND |
ND |
ND |
ND |
ND |
3 J |
ND |
ND |
ASN: Analytical sensitivity not available. Mineral was not detected at any measured location using the associated method, analytical sensitivity is not known.
Detect: Mineral was detected above the analytical sensitivity in at least one of the measured locations of the building using the associated method.
J: Estimated value. Due to inconsistencies during sample collection/analysis, the result is only an estimate of the actual value. The actual value could be higher or lower than the value shown.
ND: Not detected. Mineral was not detected at any measured location using the associated method.
NS: Not sampled. The associated method was not used at any of the measured locations in the building.
R: Result was rejected. Due to inconsistencies during sample collection/analysis, the result values for the sample were rejected.
mg/m3: microgram per cubic meter of air.
Mineral Analyses in Air
Estimated levels of minerals in air for samples from 30 residential buildings (1–30) in lower Manhattan and 4 comparison residential buildings (31–34) above 59th Street are shown in the following table. The estimated air concentration of each mineral by size fraction is shown for each area sampled. Typically, samples were obtained from an outdoor area, an indoor common area, and two residences. In addition, co-located samples were obtained from some locations. However, due to inconsistencies during sample collection or analysis, the specific sampling location within the building is not noted.
|
Building Number |
Particle Size Fraction |
Sample Volume (L) |
Quartz (μg/m3) |
Cristobalite (μg/m3) |
Tridymite (μg/m3) |
Calcite μg/m3) |
Portlandite (μg/m3) |
Gypsum (μg/m3) |
Mica μg/m3) |
Halite (μg/m3)) |
|
Summary of Comparison Areas Above 59th Street |
||||||||||
|
PM100 |
-- |
-- |
-- |
-- |
-- |
ND–3 J |
-- |
-- |
||
|
PM10 |
-- |
-- |
-- |
-- |
-- |
ND–3 J |
-- |
-- |
||
|
PM4 |
-- |
-- |
-- |
-- |
-- |
ND–5 J |
-- |
-- |
||
|
PM2.5 |
-- |
-- |
-- |
-- |
-- |
ND–3 J |
-- |
-- |
||
|
Results for Individual Buildings Sampled in Lower Manhattan (Buildings 1–30) |
||||||||||
|
1 |
PM100 |
882 |
-- |
-- |
-- |
-- |
-- |
6 J |
-- |
-- |
|
1 |
PM100 |
830 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
1 |
PM100 |
818 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
1 |
PM100 |
892 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
1 |
PM10 |
861 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
1 |
PM10 |
835 |
-- |
-- |
-- |
-- |
-- |
7 J |
-- |
-- |
|
1 |
PM10 |
838 |
-- |
-- |
-- |
-- |
-- |
14 J |
-- |
-- |
|
1 |
PM10 |
899 |
-- |
-- |
-- |
-- |
-- |
8 J |
-- |
-- |
|
1 |
PM4 |
809 |
-- |
-- |
-- |
-- |
84 J |
10 J |
-- |
-- |
|
1 |
PM4 |
813 |
-- |
-- |
-- |
-- |
-- |
12 J |
-- |
-- |
|
1 |
PM4 |
820 |
-- |
-- |
-- |
6 J |
68 J |
10 J |
-- |
-- |
|
1 |
PM4 |
837 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
2 |
PM100 |
1229 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
2 |
PM100 |
1162 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
2 |
PM100 |
766 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
2 |
PM100 |
1240 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
|
2 |
PM10 |
1194 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
2 |
PM10 |
1168 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
2 |
PM10 |
1390 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
2 |
PM10 |
1216 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
2 |
PM4 |
757 |
-- |
-- |
-- |
-- |
-- |
7J |
-- |
-- |
|
2 |
PM4 |
717 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
2 |
PM4 |
849 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
2 |
PM4 |
762 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
3 |
PM100 |
868 |
-- |
-- |
-- |
-- |
-- |
5 J |
-- |
-- |
|
3 |
PM100 |
821 |
6 J |
15 J |
-- |
5 J |
24 J |
5 J |
13 J |
-- |
|
3 |
PM100 |
756 |
-- |
-- |
-- |
-- |
-- |
5 J |
-- |
-- |
|
3 |
PM100 |
761 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
3 |
PM10 |
858 |
-- |
-- |
-- |
-- |
-- |
6 J |
-- |
-- |
|
3 |
PM10 |
815 |
5 J |
-- |
-- |
5J |
25 J |
5 J |
-- |
-- |
|
3 |
PM10 |
765 |
-- |
-- |
-- |
-- |
-- |
5 J |
-- |
-- |
|
3 |
PM10 |
783 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
3 |
PM4 |
814 |
5 J |
-- |
-- |
-- |
-- |
6 J |
-- |
-- |
|
3 |
PM4 |
824 |
6 J |
-- |
-- |
6 J |
26 J |
7 J |
-- |
-- |
|
3 |
PM4 |
841 |
-- |
-- |
-- |
-- |
-- |
5 J |
-- |
-- |
|
3 |
PM4 |
823 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
4 |
PM100 |
1230 |
-- |
-- |
-- |
-- |
-- |
3 J |
-- |
-- |
|
4 |
PM100 |
1289 |
4 J |
-- |
-- |
4 J |
16 J |
3 J |
9 J |
5J |
|
4 |
PM100 |
1278 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
4 |
PM100 |
1221 |
-- |
-- |
-- |
-- |
-- |
3 J |
-- |
5J |
|
4 |
PM10 |
1218 |
-- |
-- |
-- |
-- |
16 J |
3 J |
-- |
-- |
|
4 |
PM10 |
1415 |
4 J |
-- |
-- |
3 J |
16 J |
3 J |
-- |
4J |
|
4 |
PM10 |
1294 |
-- |
-- |
-- |
-- |
-- |
3 J |
-- |
-- |
|
4 |
PM10 |
1201 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
4 |
PM4 |
751 |
-- |
-- |
-- |
-- |
27J |
5J |
-- |
-- |
|
4 |
PM4 |
793 |
6 J |
-- |
-- |
6J |
28J |
5J |
14 J |
8 J |
|
4 |
PM4 |
804 |
-- |
-- |
-- |
-- |
-- |
5 J |
-- |
-- |
|
4 |
PM4 |
757 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
5 |
PM100 |
783 |
-- |
-- |
-- |
14 J |
95 J |
14 J |
-- |
14 J |
|
5 |
PM100 |
786 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
5 |
PM100 |
804 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
5 |
PM100 |
800 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
5 |
PM10 |
780 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
5 |
PM10 |
797 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
5 |
PM10 |
846 |
-- |
-- |
-- |
-- |
-- |
14 J |
-- |
-- |
|
5 |
PM10 |
789 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
5 |
PM4 |
817 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
5 |
PM4 |
664 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
5 |
PM4 |
813 |
-- |
-- |
-- |
-- |
-- |
9 J |
-- |
-- |
|
5 |
PM4 |
813 |
-- |
-- |
-- |
-- |
-- |
15 J |
-- |
-- |
|
6 |
PM100 |
1241 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
6 |
PM100 |
1212 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
6 |
PM100 |
1238 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
6 |
PM100 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
6 |
PM10 |
1226 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
6 |
PM10 |
1197 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
6 |
PM10 |
1252 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
6 |
PM10 |
1254 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
6 |
PM4 |
775 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
6 |
PM4 |
762 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
6 |
PM4 |
775 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
6 |
PM4 |
772 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
7 |
PM100 |
1277 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
7 |
PM100 |
1260 |
-- |
-- |
-- |
8 J |
54 J |
10 J |
-- |
-- |
|
7 |
PM100 |
1243 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
7 |
PM100 |
1213 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
7 |
PM10 |
1227 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
7 |
PM10 |
1225 |
-- |
-- |
-- |
-- |
-- |
11 J |
-- |
-- |
|
7 |
PM10 |
1240 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
7 |
PM10 |
1231 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
7 |
PM4 |
787 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
7 |
PM4 |
784 |
-- |
-- |
-- |
-- |
-- |
10 J |
-- |
-- |
|
7 |
PM4 |
765 |
-- |
-- |
-- |
-- |
-- |
11 J |
-- |
-- |
|
7 |
PM4 |
748 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
8 |
PM100 |
1213 |
-- |
-- |
-- |
7 J |
-- |
10 J |
-- |
-- |
|
8 |
PM100 |
1254 |
-- |
-- |
-- |
-- |
-- |
6 J |
-- |
-- |
|
8 |
PM100 |
1223 |
-- |
-- |
-- |
-- |
-- |
7 J |
-- |
-- |
|
8 |
PM100 |
1206 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
8 |
PM100 |
1175 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
8 |
PM100 |
1259 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
8 |
PM10 |
1188 |
-- |
-- |
-- |
-- |
-- |
9 J |
-- |
-- |
|
8 |
PM10 |
1223 |
-- |
-- |
-- |
-- |
-- |
6 J |
-- |
-- |
|
8 |
PM10 |
1172 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
8 |
PM10 |
1256 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
8 |
PM4 |
757 |
-- |
-- |
-- |
-- |
-- |
12 J |
-- |
-- |
|
8 |
PM4 |
784 |
-- |
-- |
-- |
6 J |
-- |
10 J |
-- |
-- |
|
8 |
PM4 |
738 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
8 |
PM4 |
777 |
-- |
-- |
-- |
-- |
-- |
10J |
43J |
19 J |
|
9 |
PM100 |
1210 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
9 |
PM100 |
1218 |
-- |
-- |
-- |
-- |
-- |
3 J |
-- |
-- |
|
9 |
PM100 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
9 |
PM100 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
9 |
PM10 |
1203 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
9 |
PM10 |
1217 |
-- |
-- |
-- |
4 J |
-- |
6 J |
-- |
-- |
|
9 |
PM10 |
1231 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
9 |
PM10 |
1131 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
9 |
PM4 |
776 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
9 |
PM4 |
782 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
9 |
PM4 |
763 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
9 |
PM4 |
781 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
10 |
PM100 |
1201 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
10 |
PM100 |
1225 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
10 |
PM100 |
1220 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
10 |
PM100 |
1226 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
10 |
PM10 |
1181 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
10 |
PM10 |
1202 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
10 |
PM10 |
1227 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
10 |
PM10 |
1224 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
10 |
PM4 |
757 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
10 |
PM4 |
766 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
10 |
PM4 |
762 |
-- |
-- |
-- |
8 J |
-- |
-- |
-- |
-- |
|
10 |
PM4 |
767 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
11 |
PM100 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
11 |
PM100 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
11 |
PM100 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
11 |
PM100 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
11 |
PM10 |
1305 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
11 |
PM10 |
1301 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
11 |
PM10 |
1337 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
11 |
PM10 |
1237 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
11 |
PM4 |
832 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
11 |
PM4 |
806 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
11 |
PM4 |
834 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
11 |
PM4 |
779 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
12 |
PM100 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
12 |
PM100 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
12 |
PM100 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
12 |
PM100 |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
NS |
|
12 |
PM10 |
1412 |
3 J |
-- |
-- |
3 J |
14 J |
3 J |
-- |
-- |
|
12 |
PM10 |
1315 |
3 J |
-- |
-- |
5 J |
18 J |
4 J |
8 J |
5 J |
|
12 |
PM10 |
1337 |
3 J |
-- |
-- |
3 J |
17 J |
3 J |
-- |
5 J |
|
12 |
PM10 |
1553 |
R |
R |
R |
R |
R |
R |
R |
R |
|
12 |
PM10 |
1479 |
R |
R |
R |
R |
R |
R |
R |
R |
|
12 |
PM4 |
925 |
4 J |
-- |
-- |
4 J |
22 J |
4 J |
-- |
-- |
|
12 |
PM4 |
828 |
5 J |
-- |
-- |
7 J |
28 J |
6 J |
15 J |
7 J |
|
12 |
PM4 |
948 |
R |
R |
R |
R |
R |
R |
R |
R |
|
12 |
PM4 |
932 |
R |
R |
R |
R |
R |
R |
R |
R |
|
13 |
PM100 |
1281 |
-- |
-- |
-- |
-- |
-- |
3 J |
-- |
-- |
|
13 |
PM100 |
1300 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
13 |
PM100 |
1298 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
13 |
PM100 |
1284 |
5 J |
-- |
-- |
5 J |
16 J |
3 J |
-- |
-- |
|
13 |
PM100 |
1211 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
13 |
PM100 |
1203 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
13 |
PM100 |
1184 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
13 |
PM10 |
1263 |
-- |
-- |
-- |
-- |
-- |
3 J |
-- |
-- |
|
13 |
PM10 |
1325 |
4 J |
-- |
-- |
5 J |
16 J |
3 J |
-- |
-- |
|
13 |
PM10 |
1223 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
13 |
PM10 |
1205 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
13 |
PM4 |
802 |
-- |
-- |
-- |
5 J |
-- |
5 J |
-- |
-- |
|
13 |
PM4 |
818 |
7 J |
-- |
-- |
10 J |
26 J |
5 J |
-- |
-- |
|
13 |
PM4 |
762 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
13 |
PM4 |
761 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
14 |
PM100 |
1151 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
14 |
PM100 |
1169 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
14 |
PM100 |
1166 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
14 |
PM100 |
1142 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
14 |
PM100 |
1171 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
14 |
PM100 |
1149 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
14 |
PM10 |
1134 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
14 |
PM10 |
1138 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
14 |
PM10 |
1155 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
14 |
PM10 |
1179 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
14 |
PM10 |
1161 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
14 |
PM4 |
719 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
14 |
PM4 |
731 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
14 |
PM4 |
732 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
14 |
PM4 |
730 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
15 |
PM100 |
1219 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
15 |
PM100 |
1199 |
8 J |
-- |
-- |
3 J |
18 J |
-- |
-- |
-- |
|
15 |
PM100 |
1211 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
15 |
PM100 |
1156 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
15 |
PM10 |
1218 |
-- |
-- |
-- |
-- |
-- |
3 J |
-- |
-- |
|
15 |
PM10 |
1115 |
R |
R |
R |
R |
R |
R |
R |
R |
|
15 |
PM10 |
1212 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
15 |
PM10 |
1225 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
15 |
PM10 |
1171 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
15 |
PM4 |
783 |
-- |
-- |
-- |
-- |
-- |
5 J |
-- |
-- |
|
15 |
PM4 |
778 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
15 |
PM4 |
766 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
15 |
PM4 |
751 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
16 |
PM100 |
1254 |
-- |
-- |
-- |
-- |
-- |
3 J |
-- |
-- |
|
16 |
PM100 |
1225 |
4 J |
-- |
-- |
3 J |
17 J |
3 J |
-- |
-- |
|
16 |
PM100 |
1217 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
16 |
PM10 |
1269 |
-- |
-- |
-- |
-- |
-- |
4 J |
-- |
-- |
|
16 |
PM10 |
1228 |
-- |
-- |
-- |
-- |
-- |
4 J |
-- |
-- |
|
16 |
PM10 |
1210 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
16 |
PM4 |
808 |
-- |
-- |
-- |
-- |
-- |
7 J |
-- |
-- |
|
16 |
PM4 |
774 |
-- |
-- |
-- |
-- |
-- |
5 J |
-- |
-- |
|
16 |
PM4 |
769 |
18 J |
-- |
-- |
5 J |
27 J |
7 J |
-- |
-- |
|
16 |
PM4 |
769 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
17 |
PM10 |
1306 |
-- |
-- |
-- |
-- |
-- |
4 J |
-- |
-- |
|
17 |
PM10 |
1469 |
3 J |
-- |
-- |
3 J |
16 J |
3 J |
-- |
4 J |
|
17 |
PM10 |
1250 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
17 |
PM10 |
1259 |
-- |
-- |
-- |
-- |
-- |
3 J |
-- |
-- |
|
17 |
PM10 |
1293 |
12 J |
-- |
-- |
4 J |
17 J |
6 J |
-- |
5 J |
|
17 |
PM4 |
844 |
-- |
-- |
-- |
-- |
-- |
5 J |
-- |
-- |
|
17 |
PM4 |
816 |
5 J |
-- |
-- |
5 J |
27 J |
6 J |
15 J |
-- |
|
17 |
PM4 |
786 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
17 |
PM4 |
786 |
-- |
-- |
-- |
-- |
-- |
5 J |
-- |
-- |
|
17 |
PM4 |
803 |
-- |
-- |
-- |
-- |
26 J |
6 J |
-- |
-- |
|
18 |
PM100 |
1277 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
18 |
PM100 |
1247 |
3 J |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
18 |
PM100 |
1241 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
18 |
PM100 |
1265 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
18 |
PM100 |
1177 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
18 |
PM10 |
1234 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
18 |
PM10 |
1269 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
18 |
PM10 |
1258 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
18 |
PM10 |
1268 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
18 |
PM10 |
1196 |
-- |
-- |
-- |
-- |
-- |
3 J |
-- |
-- |
|
18 |
PM4 |
791 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
18 |
PM4 |
780 |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
-- |
|
18 |
PM4 |
785 |
5 J |
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