Environmental Justice in the
ARSC 110 CAPSTONE SEMINAR PROPOSAL
Interdisciplinary Minor in Environmental Ethics
Table of Contents
1. Introduction,
by Emily Byrum
2. E coli and Milwaukee County Beaches: A Case Study in
Environmental Injustice by
Thomas Jensen
3. Brownfields,
Spills, and Environmental Justice in the Milwaukee Area, collaborative project
4. Disproportionate Risk of
Fish Dioxins among Minorities by Laura Farrell
5. Asbestos
Remediation by Mark D. Forstner
6. Lead Poisoning and
Abatement by Katherine Keefe
7. Abandoned Gas Stations
by Noelle Gilbreath
8. Noise Pollution in
Milwaukee County by Christine Scherman
9. Distribution of
Park Amenities and Recreational Opportunities in Milwaukee County by Drew
Albright
10. Statistical
Analysis of Park Distribution by Ernest Hanson
11. The Menomonee Valley
Redevelopment Plan by Louis Thorson
12. Conclusion by Emily
Byrum
13. Appendix: Environmental
Justice, Ethical Theory, and Political Philosophy by Matthew Manning
by Emily Byrum
The
history of
In the
year 1999, the average household size for an African-American family in
In his 1996 article The Heart of Racism, J.L.A. Garcia defines racism as “a vicious kind of racially based disregard for the welfare of certain people” (Garcia 6). He does not ask his readers to renounce the term “race,” as philosophers such as W.E.B. DuBois have done in the past. Instead, he asserts that even if race is not real, “what we call racism could still be real” (Garcia 7). Racism can affect both the individual and the institution. “Institutional racism begins when racism extends from the hearts of individual people to become institutionalized. What matters is that racist attitudes contaminate the operation of the institution; it is irrelevant what its original point may have been, what its designers meant it to do” (Garcia 10). Minorities nation-wide continue to feel the wrath of racism both by individuals and by institutions of all kinds.
john a.
powell of the Institute on Race and Poverty at the
Another
recent term, “environmental racism” is sometimes used in regard to spatial racism. It is called “environmental racism.” This term encompasses a number of instances
including, but not limited to, the unequal distribution of natural resources which
promote good health or the unequal distribution of environmental hazards. Although toxic waste and landfills have to be
placed somewhere, they are often placed in areas with the lowest
property value. This is so for a number
of reasons, including corporate costs.
It is problematic for minorities, as they make up a large percent of
low-income neighborhoods. It is
uncertain whether minorities were forced to live in areas with higher levels of
environmental and health risks or if the causes of these risks were located in
minority neighborhoods after the fact because it appeared to be the most cost
efficient at the time. Regardless, the
placement of new environmental hazards, such as landfills or incinerators, and
the removal of those ongoing, such as toxin exposures and abandoned gas
stations, cannot be unequally distributed through minority neighborhoods
without the question arising as to whether environmental racism is at work. Major metropolitan areas throughout the
In an attempt to end environmental
racism, in February of 1994, President
Clinton signed an Executive Order, stipulating the promotion of equal
distribution by federal agencies. “Each
Federal agency shall make achieving environmental justice part of its mission
by identifying and addressing, as appropriate, disproportionately high and
adverse human health or environmental effects of its programs, policies, and
activities on minority populations and low-income populations…” (
The
purpose of this contributive report is to examine symptoms and causes of
environmental injustice in the
E
coli and
A Case Study in Environmental Injustice
By Thomas Jensen
Background:
For
decades now,
In 2005, the DNR reported disturbing news about Milwaukee County Beach Health in its Annual Report Beach Season 2005.[3] A graph indicates Milwaukee County Beaches continue to lead the way in number of beach closures across the state:

Although down compared to 2004,

Hence, it is important for the County to assess likely sources of the E coli and ways to prevent its entry and contamination of County beaches. Recent studies have been done, which attempt to identify these sources.
E coli Sources:
It is thought that there were four potential sources for E coli contamination of local beaches: water fowl, algae, sewage overflow, and rain runoff directly into the lake. Each source will now be examined.
Water Fowl:
It is thought that water fowl such as sea gulls contribute to levels of beach water E coli through fecal matter. It is known that sea gull fecal matter alone contains 368,000,00 cfu/1 gram. It is possible that beaches that contain large numbers of zebra mussels attract large numbers of water fowl that feed upon them.
Yet in
a phone interview, Toni Glymph, Wisconsin Beach Program Manager, mentioned that
EPA studies have found that a relatively small amount of water fowl bird E coli
levels is pathologic to humans (few of 0 type 157 H type 7 strain). It only represents a low risk to beach goers. Also, water fowl are not as big an issue in
Algae:
The algae, Cladophora, has been indicated as a possible cause of high levels of E coli at beaches. A study done by Erika Jensen of the Great Lakes Water Institute and UW Milwaukee, found that E coli was found to be in high levels in Cladophora mats along Milwaukee County beaches.[5] This was only true though for decaying mats of the algae. Fresh algae contained little or no E coli when tested.
It was later determined that these decaying mats offered an ideal environment for E coli to grow and replicate while protecting E coli from harsh elements that would typically lead to death of the bacterium after a couple days. The algae essentially allows for E coli to survive and develop, but is not the source of E coli.
Cladophora is a naturally occurring in Lake Michigan and during the 60’s and 70’s saw large blooms due to high levels of phosphorous from fertilizers and other sources contaminating lake water. Restrictions had lead to decreases, but it has recently risen unexpectedly.
Sewage Overflow:
Sewage
overflow during intense storms has lead to a great fear among residents about
the relationship of sewage contamination and local beach E coli levels. Human pathogenic E coli is found in greater
abundance in human sewage. Overflow
occurs when the Milwaukee Metropolitan Sewer District releases sewage into
rivers and streams. According to Mike
Richie of MMSD this is due to the structure of the current sewer system, which
contains a common sewer/rain runoff system that is treated at Jones Island
Waste Water Treatment Plant. During
heavy storms, runoff from
Yet in an interview another member of MMSD, Chuck Bernie, stated that sewage overflow is not the predominant cause of high E coli levels at the beach. Essentially, sewage overflow goes out deep into the harbor, but is not found to wash up on shore. In fact, as one goes farther out, according to Mr. Bernie, ten meters from shore, all water samples will pass EPA standards.
Rain Runoff:
The
other source thought to be contaminating local beaches is rain runoff during
storms that directly flows into the
According
to Chuck Bernie, this is thought to be the major source of E coli at the
beaches according to research done by the Great Lakes WATER Institute at
Milwaukee County Beaches:

In order to look at the possibility of environmental injustice in the case of E coli levels at local beaches, it is necessary to look at E coli readings for various beaches, the demographics of beach goers, and efforts being done to lower levels of E coli. First, we look at a thirty-day period during the beach season. The following data is for monitoring of local beaches during May 23rd to June 21st, 2005.
|
|
|
|
McKinley |
Watercraft |
|
|
||
|
Day |
E coli
(cfu's/100ml) |
|
|
|
|
|
|
|
|
1 |
20 |
|
54 |
|
29 |
12 |
11 |
12 |
|
2 |
10 |
|
46 |
|
387 |
23 |
11 |
15 |
|
3 |
2 |
|
21 |
|
16 |
5 |
4 |
2 |
|
4 |
6 |
|
30 |
|
3 |
10 |
61 |
73 |
|
5 (.13) |
15 |
|
21 |
|
9 |
50 |
19 |
60 |
|
6 |
120 |
|
68 |
|
119 |
15 |
29 |
39 |
|
7 |
127 |
|
117 |
|
82 |
291 |
40 |
29 |
|
8 |
186 |
|
79 |
|
54 |
517 |
410 |
517 |
|
9 |
14 |
|
86 |
|
30 |
461 |
64 |
157 |
|
10 |
12 |
|
110 |
|
27 |
120 |
40 |
365 |
|
11 |
71 |
|
67 |
|
1203 |
34 |
186 |
488 |
|
12 |
24 |
|
108 |
|
193 |
90 |
2419 |
980 |
|
13 |
27 |
|
1120 |
|
687 |
186 |
687 |
548 |
|
14 (.28) |
2420 |
|
727 |
|
416 |
1046 |
2419 |
1733 |
|
15 |
156 |
|
410 |
|
71 |
17 |
23 |
23 |
|
16 (.93) |
548 |
|
579 |
|
5 |
6 |
28 |
19 |
|
17 |
71 |
|
687 |
|
69 |
13 |
72 |
56 |
|
18 |
108 |
|
113 |
|
2 |
1 |
18 |
12 |
|
19 |
83 |
|
214 |
|
214 |
10 |
326 |
209 |
|
20 |
79 |
|
225 |
|
2420 |
23 |
88 |
77 |
|
21 |
388 |
|
1300 |
|
365 |
52 |
74 |
83 |
|
22 |
194 |
|
2420 |
|
81 |
5 |
74 |
30 |
|
23 |
140 |
|
140 |
|
201 |
816 |
39 |
73 |
|
24 |
64 |
|
93 |
|
147 |
7 |
12 |
26 |
|
25 |
190 |
|
727 |
|
36 |
119 |
39 |
10 |
|
26 |
69 |
|
488 |
|
17 |
7 |
66 |
48 |
|
27 |
123 |
|
89 |
|
411 |
17 |
158 |
178 |
|
28 |
49 |
|
55 |
|
39 |
7 |
156 |
291 |
|
29 |
248 |
|
187 |
|
179 |
7 |
|
2419 |
|
30 |
16 |
|
31 |
|
102 |
4 |
99 |
20 |
Other beaches such as Bay View and Grant were not included since data was taken infrequently and there were few beach closures due to levels of 235cfu/100ml or more. Bold numbers represent infractions and the red represent days in which there was more than .10 inch of rain (amount of rain in parenthesis). All six beaches had infractions on the day it rained .28 inches. This appears to support the claim that a major source of E coli, but that does not explain the reasons for other infractions nor the fact that there were only two infractions when it rained .93 inches. One issue also at work is the fact that, as Ms. Glymph stated, monitors can have faulty readings on warm days in stagnant water leading to high, but inaccurate readings. Days where multiple infractions might suggest more accurate readings, but again, the fac