
SCUBA DIVING & UNDERWATER CULTURAL RESOURCES: DIFFERENCES IN ENVIRONMENTAL BELIEFS,
ASCRIPTIONS OF RESPONSIBILITY, AND MANAGEMENT PREFERENCES BASED ON LEVEL OF
DEVELOPMENT[1]
Sharon
L. Todd
Assistant
Professor, Recreation & Leisure Studies, SUNY Cortland, P.O. Box 2000,
Cortland, NY 13045.
Tiffany
Cooper
Graduate
Student, Recreation & Leisure Studies, SUNY Cortland, P.O. Box 2000,
Cortland, NY 13045.
Alan
R. Graefe
Associate
Professor, Leisure Studies Program, School of Hotel, Restaurant &
Recreation Management, 201 Mateer Building, The Pennsylvania State University,
University Park, PA 16802.
Abstract: This study examined SCUBA divers’ level of
development in relationship to environmental beliefs, ascriptions of
responsibility, and management preferences concerning the use and management of
New York’s Great Lakes’ underwater cultural resources. More than 850 New York State divers were
surveyed during the fall of 1999, ranging from novices to experts and post-experts. Particular emphasis was placed on measuring
extent of agreement with statements that focused on the use and preservation of
underwater artifacts, which implicitly involved issues related to accessibility
of abandoned shipwrecks. Although
divers of all levels of development did tend to share certain beliefs,
ascriptions of responsibility, and management preferences, the strength of agreement with half of the
statements did differ by level of development.
The predicted pattern of increasing in strength from beginner to expert
and declining again for post-expert stages was supported in nine cases, while
post-experts continued a more direct linear relationship with three items. In these particular cases, a “history
effect” may have had an influence on post-expert divers. The results of this study documented the
need for continuing support to educate divers on safe and responsible use of
underwater resources.
Tourism
professionals, community developers, and SCUBA divers are concerned with the
protection and use of underwater cultural resources in New York’s Great Lakes,
an area encompassing the two lakes bordering the state (Ontario and Erie) as
well as the two rivers that feed into them (the Niagara and St. Lawrence). Increased interest in SCUBA diving in this
area has been attributed to two recent factors.
First,
water clarity has significantly increased within the last ten years, due not
only to pollution control programs, but also to zebra mussel infestations. This overpopulated exotic species is
predominantly known for its negative environmental impacts: disturbing the natural balance of the Great
Lakes’ ecosystem as well as clogging drainage pipes to and from water,
electrical, and industrial plants (Hogan, 1996). However, by filter feeding on phytoplankton and zooplankton, this
dominating pest has dramatically increased the water clarity of murky waters, a
positive effect appreciated by SCUBA divers (Hogan, 1996). Instead of seeing only a few feet under the
water’s surface (as was the case prior to 1988, the year the first zebra mussel
appeared in the Great Lakes), divers can now see 20 to 60 feet (Zeidner,
1996).
Second,
the passage of the 1987 Abandoned Shipwreck Act (ASA) has led to greater
interest in shipwreck diving and artifact finding. Due to its vast cultural resources, the Great Lakes region is
considered by many to be the best cold water diving location in the United
States; in fact, the region has a
reputation of offering the best shipwreck diving in the world, with vessels
dating back to the Revolutionary War (brochure, no author).
Importantly,
the ASA shifted ownership of underwater shipwrecks from the federal government
to each individual state in which they are found. New York allows and even encourages exploration, but divers are
prohibited from taking and even touching artifacts that are found under the
surface. When a diver removes an item
from its original setting the value, integrity, and significance are lost
because the whole picture and its surroundings are missing. According to researchers, historians, and
state agencies, however, removal of
items from under the surface is a noticeable problem because the act is so hard
to enforce (Zeidner, 1996).
Because
SCUBA diving is gaining in popularity, the potential to affect not only underwater
cultural resources, but also marine resources and fragile ecosystems, is high
(Davis & Tisdell, 1996; Fabbri,
1990). The underwater environment is
delicate and can become unbalanced and threatened more easily than
realized. However, as most studies incorporating
Dunlap & Van Liere’s (1978) “New Environmental Paradigm” scale have shown,
those who participate in outdoor recreation and are members of environmental
organizations tend to have positive attitudes toward the environment. Possessing pro-environmental attitudes,
however, has not been shown to automatically lead to environmentally
responsible behaviors. Only recently
have several studies demonstrated fairly strong support for the relationship
between outdoor recreation participation and pro-environmental behaviors (Nord,
Luloff, & Bridger, 1998; Theodori,
Luloff, & Willits, 1998; Tarrant & Green, 1999; Theodori & Luloff, 1999).
Water
recreationists are generally less aware than land-based outdoor recreation
participants of the negative effects they may cause the marine environment,
because a change in water quality may happen over a period of time with less
indication of the direct cause (Wall & Wright, 1977). Of particular note, inexperienced divers
tend to contribute more to environmental damage than skilled divers because of
their inability to control buoyancy under the surface. A direct result of this lack of control is
stirring up silt clouds that suffocate and kill organisms, as well as touching,
bumping, and crashing into shipwrecks, reefs, and other ecologically and
culturally significant resources (Davis & Tisdell, 1995). In order to minimize effects on the
environment, Graver (1999) suggests diving should be a “no contact” activity. Although SCUBA diving is a self-regulated
industry, participation does require certification. Many certification agencies include environmental awareness in
their courses, but because certification does not expire, being kept informed
of how not to negatively affect the environment may not occur (Davis &
Tisdell, 1995).
As
the above discussion demonstrates, factors such as skill level, experience, and
knowledge seem to be directly related to divers’ level of development. In the literature two prominent leisure
theories, amateur/professionalism and specialization, form the basis for
studying the growth, progress, and development of participants in leisure
activities.
Perhaps
best known for proposing a progression of commitment, Stebbins (1979, 1992)
studied “serious leisure” and amateurism in art, entertainment, science, and
sport. According to his theory, as an
activity becomes more important to participants, they progress from dabblers to
novices, amateur participants, or amateur devotees, or may even become paid
professionals. In describing participants’
career histories, however, Stebbins also described a stage of decline or
post-professionalism. Scanlan, Ravizza
& Stein (1989) demonstrated many of Stebbins’ concepts in their study of
elite figure skaters by documenting five phases of development (with the final
two characterized as retirement from competitive skating, and staying involved
past retirement through coaching or show performing), based on skaters’
evolving commitment, achievement, and involvement. In her study of quiltmakers, Todd (1998) also documented a
progression and retrogression of development.
Data from 459 quiltmakers (including 24 inactive quiltmakers) showed
that level of quiltmaking development was related to measures of equipment,
knowledge, experience level, perceived skill, participation, and
commitment; mean scores for each of
these factors increased from beginners through experts and then declined for
post-experts.
On
the other hand, Bryan (1977) defined specialization as “a continuum of behavior
from the general to the particular, reflected by equipment and skills … and
activity preferences” (p. 175). Degree
of specialization was defined as a function of one’s time, money, equipment,
skill, and psychic commitment to an activity.
In his study of fly fishermen, as specialization increased, Bryan found
that attitudes and values about the activity changed, affected in part by the
prominence of a leisure social world.
Bryan suggested that the activity was linked to the properties of the
resource in which the sport was practiced, with the specialist wanting to be
able to control and manipulate the resource setting in such a way that skill
and luck could be differentiated.
In
addition, Bryan (1977, 1979) found that more experienced anglers developed a
preservationist focus where nature and the setting were more important than
actually catching fish, versus the consumptive point of view found in less
developed anglers. Similarly, when Katz
(1981) evaluated the relationship between environmental attitudes and
specialization of fly fishermen, he found that concern for the environment
increased as specialization increased.
Kauffman (1984) reinforced this notion in his study of canoeists; environmental attitudes toward the resource
base increased as level of specialization increased, and were strongest for
highly specialized canoeists. However,
it is important to note that none of these studies accounted for what
eventually happens to specialists once their levels of development begin to
decline, i.e., the existence of a post-professional or post-expert phase.
This study therefore examined SCUBA divers’ level of development in relationship to their environmental beliefs, ascriptions of responsibility, and management preferences concerning the use and management of New York’s Great Lakes underwater environment. It was hypothesized that divers with higher levels of development (i.e., beginners through experts) would have stronger beliefs about the use of underwater cultural resources. It was also expected that divers with higher levels of development would tend to take more responsibility for their actions and prefer management actions that place more responsibility on divers to police themselves rather than encourage the use of invasive, controlling management actions. In each case, it was further hypothesized that post-expert divers would decrease in the strength of their responses when compared to experts.
This study could establish the extent to which theories of specialization and amateur/professionalism may be applied to SCUBA divers. By documenting a progression of novice through post-expert divers, the applicability and generalizability of the models could be significantly expanded. As Somers (1988) writes,
SCUBA diving is often referred to as a “recreational sport.” However, the term “sport” sometimes implies erroneous connotations and limits understanding. SCUBA diving can be an avocation or a vocation. It is a pastime, a pursuit, or even a lifestyle, that can be as limited or extensive as one makes it. A person’s level of commitment, degree of skill, and types of equipment all depend on what he/she wants out of SCUBA diving. (On-line abstract)
This study could also document the need for continuing support to educate divers on safe and responsible use of underwater resources so that they learn to preserve as well as appreciate them. Without users’ environmental awareness and the implementation of environmentally responsible management practices to help sustain the underwater environment, the very resource that SCUBA diving depends on may disappear and become unavailable for future use.
Methods
Two methods of data collection were used: focus group interviews and a mail survey. First, during the month of June 1999, six focus group interviews were conducted in five key locations across the New York Great Lakes Region: Buffalo/Niagara Falls, Rochester, Syracuse, Oswego, and Clayton (2 groups). For each meeting, a key informant helped organize 4 to 12 divers representing a wide range of diving levels. Using an established protocol, the primary investigator asked a series of 6 questions; each tape-recorded meeting lasted approximately 90 minutes. Major themes of discussion were then gleaned from the focus group data to aid in the development of a 16-page written questionnaire.
The
second method of data collection involved mailing 2850 surveys to a sample of
active and inactive New York State divers.
A database of approximately 6700 individuals was complied from various
resources, including a national certifying agency, a statewide organization, a
dive symposium, a dive shop, a non-profit organization, and several dive clubs.[2] In order to select a sample of 2850 divers,
addresses were stratified by major regions across the state. Primary emphasis was placed on contacting
divers in the regions closest to the Great Lakes, with subsequently less
emphasis placed the farther away one resided.
Consequently, those selected to receive the survey included all
available names from some regions and a random selection from other
regions. A total of 2850 surveys were
then mailed during October 1999, followed by reminder postcards and a second
mailing of the survey to non-respondents.
For
purposes of this study, respondents were asked to rate a total of 18 statements
concerning the use and management of the underwater environment on a 5-point
scale ranging from 1 (strongly disagree) to 5 (strongly agree). Statements were worded to reflect beliefs (9
statements), ascriptions of responsibility (3), and management preferences
(6). Particular emphasis was placed on
measuring extent of agreement with statements that focused on the use and
preservation of underwater artifacts, as well as issues of accessibility to
abandoned shipwrecks. Respondents were
also asked to rate the extent to which 6 specific management actions would
affect their diving experiences if they were to encounter them while diving in
New York’s Great Lakes region. Choices
on a 7-point scale ranged from –3 (negatively) to +3 (positively) with 0
representing no effect.
Level of development was operationalized by a self-selected single measure, where respondents were asked to characterize their current stage of development as a diver by choosing one of the following five categories: beginner, intermediate, advanced, expert, or “post-expert – not the expert I once was.”
One-way
analysis of variance was used to determine if a difference existed among mean
scores for each statement (worded as a belief, ascription of responsibility, management
preference, or effect of management action) by level of development. To compare the differences between mean
scores for each pair of developmental levels, Scheffé’s was used as a post hoc
test if the F-value was significant (p < .05).
Results
Although 2850 surveys were originally mailed, 490 (17 percent) were returned either as undeliverable or noted as having been sent to non-divers. (While an unusable rate of 10 percent is common for studies of this nature, the higher undeliverable rate for the current study was not unexpected. One focus of the overall project was to uncover why divers cease participating; thus, some of the addresses used were up to 10 years old, increasing the chance of incorrect addresses.) Of the remaining 2360 potential respondents, 869 usable questionnaires were returned, yielding a 37 percent response rate.
Four out of five respondents were male. While ages ranged from 12 to 80, the average age reported was 43. Half of the respondents had earned 2- or 4-year college degrees, while another quarter had received advanced degrees. Half reported earning more than $60,000 in household income per year.
Due to the relatively low response rate, a non-respondent bias check was conducted by phone. Non-respondents did not differ significantly from respondents when age, gender, education level, number of years spent diving, or stage of development were compared. However, significantly lower percentages of non-respondents were certified or active divers. Thus, when interpreting results, it is important to remember that diving was likely to have been more salient for respondents than non-respondents.
When
rating a total of 18 statements concerning environmental beliefs, ascriptions
of responsibility, and management preferences on a 5-point agreement
scale, a majority of respondents tended
to agree with the six statements shown in Table 1. These statements generally reflected a pro-environmental attitude
and awareness of the consequences of disturbing underwater artifacts. A majority of respondents tended to disagree
with only two statements: “Zebra mussels should be removed from the surfaces of
shipwrecks so I can see them better,” and “If I don’t take an artifact as a
souvenir, someone else will.” (See Table 2.)
Interestingly, a majority of respondents tended to be neutral towards
three items: “Canada does a better job
of protecting and regulating shipwreck diving than the U.S.,” “There is government support of the diving
industry in Canada,” and “There is government support of the diving industry in
NY’s Great Lakes.” (See Table 3.) Those who were not neutral, however, were
much more likely to feel that Canada does a better job than the U.S. of
supporting the dive industry and protecting underwater resources. Responses for the remaining seven statements
were more evenly distributed among respondents, with no clear majority
agreeing, disagreeing, or being neutral.
(See Table 4.)
Respondents
were also asked to rate the extent to which six specific management actions would
affect their diving experiences if they were to encounter them while diving in
New York’s Great Lakes region. Choices
on a 7-point scale ranged from –3 (negatively) to +3 (positively) with 0
representing no effect. Approximately
75 percent of all respondents answered that three items would positively affect
their experience, with means ranging from +1.4 to +1.5: additional artificial reefs, more
intentionally sunk ships, and underwater parks and trails. About half of all respondents felt that two
items (interpretive signs [e.g., on shipwrecks, etc.], and collection and
display of artifacts in an accessible underwater location for the general
public to view) would positively affect their experience, but mean scores were
just +0.7. Finally, respondents felt
negatively more often than positively (44 vs. 32 percent) about underwater
protection of artifacts (e.g., roping them off, chaining them down, putting
them under plastic domes).
Consequently, the mean score for that item was slightly negative (-.3).
Of the 847
respondents who selected a category to represent level of development, 198 (23
percent) marked “beginner,” 267 (32
percent) were “intermediate,” and 250 (30 percent) considered themselves to be
“advanced.” However, less than 10
percent (77 respondents) rated themselves as “expert,” and only 6 percent (55
respondents) called themselves “post-expert – not the expert I once was.” (See Figure 1.)
Figure 1. Level of Development

As
with quiltmakers (Todd, 1998), these categories were found to adequately
reflect dive-related factors of equipment owned, knowledge, experience,
perceived skill, participation, and commitment, plus an additional scale
measuring amateur/professional growth (Todd, 2000). For six of the scales, mean scores increased from beginner to
expert and then decreased for post-experts.
Experience was the only scale that displayed a different pattern: instead of declining at the post-expert
stage, experience level continued to increase, due to its cumulative
nature. Figure 2 highlights how
post-expert scores tended to return to a level equal to those of advanced
divers for six of the seven indices.
It was hypothesized that divers with higher levels of development (i.e., beginners through experts) would have stronger beliefs toward the use of underwater cultural resources, but the strength of these responses would decrease for post-expert divers. It was also expected that divers with higher levels of development would tend to take more responsibility for their actions and prefer management actions that place more responsibility on divers to police themselves rather than encourage the use of invasive, controlling management actions; a decrease was again expected for post-expert divers. As shown in Table 5, partial support was found for these relationships. One-way analysis of variance yielded significant differences among the mean scores of half of the 24 items based on level of development (p < .01): 10 of the 18 environmental statements and 2 of the 6 effects on experience quality statements.

As displayed in Figures 3 and 4, several distinct patterns emerged. First, the predicted pattern of responses increasing in strength from beginner to expert and decreasing again for post-experts was demonstrated in two ways: a progression of agreeing more strongly, or a progression of disagreeing more strongly. However, although all mean post-expert scores tended to decrease in strength when compared to experts in each of these cases, it is important to note that the decline was statistically significant for only one item: the belief that there is government support of the diving industry in New York’s Great Lakes. Interestingly, experts significantly disagreed more strongly with this belief when compared with any other level of development. On the other hand, experts tended to agree most highly with a total of 8 items: the 4 beliefs that underwater visibility is better than 10 years ago, Canada protects and regulates shipwreck diving better than the U.S., the Canadian government supports the diving industry, and touching objects is okay unless they are significant or fragile; and 4 management-related variables: information on shipwreck locations should be accessible, access to abandoned shipwrecks should be unrestricted, plus additional artificial reefs and more intentionally sunk ships would enhance their diving experiences.
For the second set of patterns, instead of post-experts decreasing in the strength of their responses when compared to experts, they followed a more direct linear relationship with several items: the belief that it is acceptable to recover objects that have sunk to the bottom and will disappear anyway; and the management preference statements that there should be stiff fines for taking artifacts, and that diving on shipwrecks should be monitored by authorized diving guides. As hypothesized, divers in the beginning stages of development responded more heavy-handedly, indicating significantly more support for invasive management practices (such as fines for taking artifacts and authorized diving guides for shipwreck diving). Beginner divers were also the least likely to believe that it is acceptable to touch or recover objects.
On the other hand, there were no significant differences between diver development levels for the remaining 12 items, including all 3 ascriptions of responsibility. Specifically, all divers tended to agree with 3 statements: the beliefs that they were more environmentally conscious and sensitive than they had been 10 years ago, and that directly contacting objects on abandoned shipwrecks causes them to deteriorate; and the ascription of responsibility that taking artifacts will leave nothing for anyone else to see. Regardless of developmental level, all divers tended to disagree with the following 3 statements: the ascriptions of responsibility that their bubbles impact the underwater environment and that if they don’t take an artifact someone else will; and the management preference for removing zebra mussels from shipwreck surfaces. Finally, all divers tended to be more neutral towards 2 statements: the belief that 50 years is a reasonable time period for dating significant artifacts, and the management preference for collecting and displaying artifacts in museums. When rating effects on experience quality, all divers felt slightly positive about encountering underwater parks and trails, interpretive signs, and displaying collected artifacts in an accessible underwater location, but were slightly negative towards noticeably invasive underwater protection of artifacts.

Conclusions and Implications
Based
upon the findings, divers of all levels of development do tend to share certain
beliefs, ascriptions of responsibility, and management preferences. For instance, all divers tended to agree
that they are more environmentally conscious and sensitive than they were 10
years ago, they all tended to disagree that the bubbles they blow have an
impact on the underwater environment, and they all tended to be neutral on
whether artifacts should be put in museums.
However,
some beliefs about the use of underwater cultural resources are related to
level of diving development, with a tendency to increase in strength from
beginner to expert and decrease again in strength for post-experts. Of particular note, disillusion with and/or
distrust of the U.S. government (especially versus the Canadian government)
seems to be most evident for divers at the expert level.
In
addition, some ascriptions of responsibility and management preferences also
appear to be related to level of development.
Divers with higher levels of development tend to take progressively more
responsibility for their actions and prefer the least invasive management
actions. The pattern, however, tends to
vary for the post-expert phase.
As
previously mentioned, beginners displayed more “purist” attitudes, i.e., were
more “heavy-handed” by supporting invasive practices of fines and authorized
guides, and disagreeing that it is acceptable to recover or touch objects. Perhaps beginners’ lack of experience is
causing them to perceive these as hypothetical situations, whereas divers with
higher levels of development have actually encountered these circumstances,
and, having faced reality, subsequently relaxed their purist perceptions based
on true feelings.
Looking
at it from a different angle, divers in the later stages of development tended
to feel most strongly about being able to collect artifacts unimpaired. This seemingly “anti-environmental” response
may be due in part to a history effect.
Significantly, 50 percent of all experts and post-experts (specifically,
more than one-third of all experts, and exactly two-thirds of all post-experts)
had been diving more than 20 years (compared to just 10 percent of all
beginner, intermediate and advanced divers combined.) When a large portion of these experts and post-experts started
diving, artifact collecting was a major focus that was deemed highly acceptable
by the dive community. Thus, their
resistance to embracing and adopting the change in diving ethics may be well
founded in the length of their diving histories.
Being
aware of the environment and abiding by established regulations are important
considerations in order for divers to help preserve the marine
environment. Divers should be role models
for preservation, and proactively educate others to preserve the marine
environment as well.
Not
only is it essential for recreational divers to think in this manner, but these
attitudes also play a key role for management agencies, instructors, clubs, and
retailers. Divers often rely on charter
boat operators, SCUBA diving clubs, and gear shops for current information and
are influenced by their attitudes and practices when it comes to environmental
issues. Divers who are involved in the
community and work with organizations that advocate for the preservation of the
environment benefit the dive industry the most. Management agencies need to implement management plans like
Marine Protected Areas (MPAs), which use interpretive tools to educate divers
and prevent the destruction of the underwater resource (Davis & Tisdell,
1995, 1996; Vereka & Ponneleit,
1981). Well designed interpretive
programs can benefit the dive community by recommending dive locations,
assisting with site selections, and creating an understanding of the marine and
cultural environment while helping to preserve the resource (Graver, 1999;
Vereka & Ponneleit, 1981).
Bryan,
H. (1977). Leisure value system and
recreational specialization: The case
of trout-fishermen. Journal of Leisure Research, 9(3),
174-187.
Bryan,
H. (1979). Conflict in the great
outdoors. Bureau of Public
Administration, University of Alabama.
Sociological Studies No. 4.
Davis,
D., & Tisdell, C. (1995). Recreational SCUBA diving and carrying
capacity in marine protected areas. Ocean & Coastal Management, 26(1),
19-40.
Davis,
D., & Tisdell, C. (1996). Economic management of recreational SCUBA
diving and the environment. Journal of Environmental Management, 48(3),
229-248.
Dunlap,
R. E., & Van Liere, K. D.
(1978). The “New Environmental
Paradigm.” Journal of Environmental Education, 9(4), 10-19.
Fabbri,
P. (1990). Recreational use of coastal
areas. Dordrecht, The
Netherlands: Kluwer.
Graver,
D. K. (1999). SCUBA Diving. Champaign, IL: Human Kinetics.
Hogan,
J. (1996, Spring). Tracking the zebra mussel invasion. Coastlines, 22-23.
Katz,
M. (1981). An assessment of
intra-group differences in conservation attitudes and environmentalism as a
function of activity involvement among fly fishermen. Unpublished doctoral dissertation, The
Pennsylvania State University, University Park.
Kauffman,
R. B. (1984). The relationship between
activity specialization and resource related attitudes and expected rewards for
canoeists. Unpublished doctoral
dissertation, University of Maryland, College Park.
Nord,
M. Luloff, A. E., & Bridger,
J. (1998). The association of forest recreation with environmentalism. Environment
and Behavior, 30(2), 235-246.
Scanlan,
T. K., Ravizza, K., & Stein, G. L.
(1989). An in-depth study of
former elite figure skaters: I. Introduction to the project. Journal
of Sport & Exercise Psychology, 11, 54-64.
Somers,
L. H. (1988). Introduction to SCUBA
diving. Diver education series. (Available from the Michigan Sea Grant
Publications, 2200 Bonisteel Blvd., Ann Arbor, MI 48109-2099). Abstract from: ERIC ED293721.
Stebbins,
R. A. (1979). Amateurs – On the margin
between work and leisure. Beverly
Hills: Sage Publications.
Stebbins,
R. A. (1992). Amateurs, professionals,
and serious leisure. Montreal: McGill-Queen’s University Press.
Tarrant,
M. A., & Green, G. T. (1999). Outdoor recreation and the predictive
validity of environmental attitudes. Leisure Sciences, 21(1), 17-30.
Theodori,
G. L., Luloff, A. E., & Willits, F. K.
(1998). The association of
outdoor recreation and environmental concern:
Reexamining the Dunlap-Heffernan thesis. Rural Sociology, 63(1),
94-108.
Theodori,
G. L., & Luloff, A. E. (1999).
Attitudes of outdoor recreationists toward environmental issues. Proceedings
of the 1999 Northeastern Recreation Research Symposium: General Technical Report NE-269, 309-316.
Todd,
S. L. (1998). Recreation specialization, amateur/professional leisure, and
level of development: Applying outdoor
recreation and sport concepts to quiltmakers.
Proceedings of the 1998
Northeastern Recreation Research Symposium:
General Technical Report NE-255, 57-62.
Todd,
S. L. (2000). SCUBA diving in New York’s
Great Lakes: From novice to
professional. (New York Sea Grant
Institute
Completion
Report). Cortland, NY: SUNY Cortland, Department of Recreation
& Leisure Studies.
Vereka,
J. A., & Ponneleit, S. A.
(1981). Interpretation as a
management tool for underwater parks.
Reprinted from Association of Interpretive Naturalists, Journal of Interpretation, 6(2).
Wall,
G., & Wright, C. (1977). The
environmental impact of outdoor recreation. Unpublished doctoral dissertation, University of Waterloo.
Zeidner,
J. (1996, Spring/Summer). Shipwreck fascination fuels regional
interest. Nor’Easter, 28-31.
Table 1. Environmental Statements with a Majority of
Respondents Agreeing
|
Item |
Mean |
% who disagreed |
% who were neutral |
% who agreed |
n |
|
If I
take an artifact and so does every one else, nothing will be left for anyone
to see. |
4.2 |
8.1 |
9.1 |
82.8 |
804 |
|
Compared
to 10 years ago, the underwater visibility in NY’s Great lakes is better. |
4.1 |
2.9 |
32.0 |
65.1 |
771 |
|
There
should be stiff fines for divers who take valuable historical artifacts. |
4.0 |
11.3 |
14.1 |
74.6 |
799 |
|
Compared
to 10 years ago, I am more environmentally conscious and sensitive to
environmental issues than I used to be. |
3.9 |
10.2 |
20.7 |
69.1 |
797 |
|
Information
about shipwreck locations should be made easily accessible to the public. |
3.8 |
7.7 |
22.7 |
69.5 |
801 |
|
Directly
contacting objects on abandoned shipwrecks causes them to deteriorate. |
3.7 |
10.1 |
28.0 |
61.9 |
801 |
Table 2. Environmental Statements with a Majority of
Respondents Disagreeing
|
Item |
Mean |
% who disagreed |
% who were neutral |
% who agreed |
n |
|
Zebra
mussels should be removed from the surfaces of shipwrecks so I can see them
better. |
2.4 |
55.0 |
34.1 |
11.0 |
797 |
|
If I
don’t take an artifact as a souvenir, someone else will. |
2.3 |
61.9 |
21.8 |
16.2 |
801 |
Table 3. Environmental Statements with a Majority of
Respondents Remaining Neutral
|
Item |
Mean |
% who disagreed |
% who were neutral |
% who agreed |
n |
|
Canada
does a better job of protecting and regulating shipwreck diving than the U.S. |
3.5 |
3.3 |
59.6 |
37.1 |
767 |
|
There is
government support of the diving industry in Canada. |
3.4 |
2.4 |
65.8 |
31.8 |
757 |
|
There is
government support of the diving industry in NY’s Great Lakes. |
2.6 |
31.7 |
61.6 |
6.7 |
757 |
Table 4. Environmental Statements with No Majority
Captured by Any Response Category
|
Item |
Mean |
% who disagreed |
% who were neutral |
% who agreed |
n |
|
Access
to abandoned shipwrecks should be unrestricted. |
3.3 |
30.6 |
22.7 |
46.7 |
801 |
|
Artifacts
should be collected and displayed in museums for the general public to view. |
3.2 |
24.7 |
32.8 |
42.6 |
799 |
|
Fifty
years is a reasonable time period to use when dating whether objects are of
significant archaeological interest. |
3.1 |
22.2 |
47.4 |
30.3 |