- Posted By: Jaime Adler
- Written by: Sheila Barry, UCCE Advisor Santa Clara County
Public land managers and livestock operators often question whether or not open space management objectives including public access for recreation are compatible with livestock grazing. Public concerns ranging from the potential environmental degradation to fear of conflict have led some public land managers to limit or curtail the use of grazing on open spaces public lands. For example in 2009, officials from the City of Walnut Creek decided to end grazing in two parks based on park users’ complaints of cattle trampling trails and “increases in attacks by cattle on dogs and people. Cattle had grazed these parks for decades for weed abatement and the decision came after years of public outcry (TriValley 2009).
Studies have shown that perceptions of livestock use of public lands are associated with type of recreational pursuit, land classification, environmental beliefs, and demographics. Sanderson et al. 1986 found that the more experience recreationalist had on grazed lands the less likely they had negative perceptions of grazing. Brunson and Gilbert 2003 documented that hikers were more likely to feel negatively toward livestock use in a Grand Staircase Escalante National Monument than hunters. Research has also shown rural and urban divide in attitudes and beliefs, especially when the rural economy depends on rangelands. Little is known about the attitudes of the urban public recreating on grazed park lands. In particular how widespread is fear, how is fear dealt with, and how do they feel about “natural landscapes” managed with grazing cattle.
Land managers increasingly recognize the value of grazing as a land management tool (Barry et al., 2007). But where public access is also a priority they must also be able to address public concerns. Land Managers need information about the perceptions that recreational visitors have regarding cattle. By understanding the concerns managers are better equipped to address recreation/grazing conflicts and educate the public.
With the exponential growth in social media and the willingness of people to share ideas with internet communities there is a growing interest in what we can gleem from a photo sharing website like Flickr.comTM. Past efforts to learn from Flickr data have focused largely on tagging and geospatial information (Kennedy et al. 2007). Recent efforts have followed earlier work on understanding the social use of personal photography (Harrison 2004, ) and now, image-sharing (Van House 2007). This project used this rich data set found on Flickr to understand perceptions of cattle grazing on park lands by addressing the following questions:
- When people visit public lands with grazing livestock present, what do they photogragh?
- How do park users respond when they encounter and choose to photograph something seemingly undesirable or potentially frightening i.e. cow pies, a rutted trail, cows on the trail?
Methods
A data set (Table 1) was developed from photos and associated comments posted on Flickr using location and subject as search terms.
Table 1. Data sets developed from Flickr
Data sets |
Search terms |
Number of photos |
Number of photographers |
|
Location |
Subject |
|||
Grazing in Parks |
33 parks in Alameda, Contra Costa, and Santa Clara counties |
cow, cows, grazing |
1087 |
328 |
Photo information in the date set included photo date, posting date, photographer’s name, photo name, photo comments by photographer, posted comments and commenter’s name. Photo titles and all comments were categorized for each data set in the following categories: descriptive, photo quality statement, positive cow, positive grazing, positive landscape, negative cowt, negative landscape, fear (perceived i.e. not based on an actual event), fear (actual i.e. included a description of an event).
Results
When people visit public lands with grazing livestock present, what do they photograph?
More specifically, what do people who post photos from parks with grazing include in photo comments or photograph title?
Photo Elements |
Number of photos |
% of photos (n=1087) with this element |
Cow(s) |
772 |
.71 |
Dogs |
177 |
.16 |
Dogs and cow(s) |
31 |
.03 |
People |
128 |
.12 |
People and cow(s) |
52 |
.05 |
Cow pies |
22 |
.02 |
Trail |
232 |
.21 |
Landscape photo |
728 |
.67 |
How do park users respond when they encounter and choose to photograph and post something seemingly undesirable i.e. cow pies, a rutted trail?
Although 2% of the photos included cows pies in the photos and one picture featured a rutted trail, few comments were made about either of these elements. Comments were matter-of-fact in nature including:
No doubt about it, the cows were here;
Lots of cow poop;
A bumpy path;
How do park users respond when they encounter and choose to photograph and/ or reflect on something potentially frightening (i.e. cows on trails)?
Approximately 5 % (n= 43) of the comments from photos in grazed parks expressed fear of the cattle including comments like these:
I try to conquer my fear of cows by photographing them;
Watch out for those cows;
Got it close to this cow for this shot. You can see she’s giving me the stink eye here so I put the camera away;
The cows scared us to death;
Beware! Mad cows!
This is the cow that blocked our path! Would you want to cross him;
I told them I’m a vegetarian and they let me go;
He wasn’t too keen about being photographed. In addition to the unfriendly stare, he made menacing noises;
A cow that was not happy to see us and almost chased us;
We turned back here as the cow as on the trail path;
We turned around when we were faced with the option of having to walk right through a herd of cows;
Only seven comments ( <1%) included a description of an actual event with “aggressive” animal. These comments described being chased, for example:
Ahh,we were chased last weekend by a young male-err;
At least these cows didn’t chase us like last week’s did;
Happy cows may come from California, but bored cows come from Fremont. I actually tried to have a picnic-but then a bull comes charging us. We got up and ran for our lives. Our bread, cheese and blanket didn’t make it;
How do shared photos and comments from grazed public lands compare to photos and comments from nearby ungrazed public lands?
Overall, most comments could be categorized as descriptive (637 from 934 comments). Examples of descriptive comments include:
- Lots of wildflowers and cows. Hello tiny cows on the hillside.
- Taken at Lake Del Valle.
- Cow pool party.
- I don’t know why but I thought cows in CA where kept indoors. (Points to a need for education!)
- A cow grazing….
- They are pastured to keep the fire danger low
- Cow munchin on some grass near the lake
However there were far more positive cow and grazing comments than negative cow comments ( 126 versus 8).
Positive subject cow and grazing comments included:
- Wonderful to see cows being just cows and happy ones. Beautiful scene.;
- Superb…love the cow;
- Beautiful spring at Morgan Territory. Green grass, clouds and the cows.;
- As much as I struggled over the steep hills on this hike, all the grazing cattle and howling coyotes made it worth the sweat.
- Oh I just love fuzzy winter cows
- Happy cows eating grass not corn
- I went on a really long hike and saw some cool thing from meadows to steephills to trees, cows and interesting rock forms
- Cows happily range over the lands of Sunol Regional Wilderness, keeping down the fuel load
- The sign said that cows have been known to nudge hikers when startled. Its hard to picture a cow nudging a hiker. I doubt that would be the adjective I would use to describe it if I saw it happen. Generally they are scared of hikers and actually help to spread sees, control non-native plants and overall keep a healthy preserve. I kind of like sharing the green hills with them.
Examples of negativecow comments include: it’s a little anti-climatic when you hike uphill for 2 hours and see a herd of cows upon arrival.
- However this kind of landscape also attracts a lot of cows which seem to have more priviledges than me in roaming around
- The only downside was/is that there are cows grazing there a lot and hence: cow patties! Many of the dogs had a taste and all rolled in cow poop quite thoroughly.
Questions to be further analyzed include:
How do shared photos and comments from grazed public lands compare to photos and comments of other subjects that people may find environmentally negative or fearful such as smog or snakes?
How do the type of comments compare to shared photos and comments about other parks with and without grazing?
Discussion and Implications
Is there overwhelmingly negative public opinion towards grazing on public lands as suggested by the article in the TriValley newspaper (Walnut Creek, CA) in 2009? Park users visiting grazed park parks in the Bay Area and sharing their photos didn’t seem to express this opinion. They largely shared descriptions and positive comments about the cattle they saw and the grazed landscape. In addition recent events in Walnut Creek indicate that there is some strong public opinion in support of grazing.. The Contra Costa Times reported in June 2011 that 150 park neighbors in Walnut Creek Open Space park signed a petition that requesting that the cows return to graze the park lands. They neighbors fear potential wildfire from the resulting unmanaged growth of vegetation. The grazing supporters also spoke at a Park Commission meeting where they outnumbered those opposed to the cattle returning 23 to 6.
While park managers have implemented some strategies to reduce public/cattle conflict including signage and timing of grazing, there are undoubtedly opportunities for improved public outreach. Park visitors would benefit from not only understanding the biological value of managed grazing programs but also from better information on livestock behavior and how to interact with livestock they may encounter. Continued education of our urban audience will be essential if livestock grazing is going to continue to be a viable took for managing open space lands.
Literature Cited
Barry, S. T.Schohr, and K. Sweet. 2007. The California Rangeland Conservation Coalition. Rangelands. 29(3):31-34.
Brunson,M. W. and L. Gilbert. 2003. Recreationist responses to livestock grazing in a new national monument. J. Range Manage. 56 (6): 570-576.
Harrison, B. 2004. Snap Happy: Toward a Sociology of “Everyday” Photography. In: C. Pole (Eds), Seeing is Believing? Approaches to Visual Research. Studies of Qualitative Methodolgy, Volume 7: 23-39.
Kennedy, L., M. Naaman, S. Ahern, R.Nair, T. Rattenbury. 2007. How Flickr Helps us Make Sense of the World: Context and Content in Community-Contributed Media Collections. MM’07, September 23-28,2007, Augsburg, Bavaria, Germany.
Sanderson, R.H., R.A. Meganck, and K.C. Gibbs. 1986. Range management and scenic beauty as perceived by dispersed recreationist. J. Range Manage. 39:464-469.
Van House, N. A. 2007. Flickr and Public Image-Sharing: Distant Closeness and Photo Exhibition. CHI 2007, April 28-May 3, 2007, San Jose, CA, USA.
- Posted By: Jaime Adler
- Written by: Douglas D. McCreary
As everyone who lives in California knows, this has been a fairly unusual year weather-wise. In the fall there was abundant rainfall, but this was followed by a January when the tap shut off almost completely. Then in March it started raining and snowing almost continuously and has only recently stopped. There was a week or two of warm weather, but now in mid-April, it has turned cold again. Here at UC’s Sierra Foothill Research and Extension Center in Yuba County, almost all of the oaks have now leafed out. The trees are especially beautiful at this time of year since it seems that each of the different oak species has a distinctive color of green. However this new foliage is quite tender and vulnerable to frost damage. Damage to new foliage occurred in Northern California three years ago when there was a late frost and many trees had their new foliage killed. Interestingly it seemed to only occur at mid elevations between 1000 and 2000 feet. At lower elevations, temperatures were not cold enough to affect the foliage and at higher elevations, the trees were phenologically further behind and hadn’t yet leafed out. Fortunately oaks have evolved under conditions where leaf damage regularly occurs (also as a result of low intensity fires or insect defoliation) and normally suffer little long-term damage from late freezes.
Another risk at this time of year is cattle poisoning. Oak trees contain toxic chemicals in newly emerging foliage, including tannins and phenols, that can be lethal to cows if the foliage is a very high percentage of their diet. A couple of decades ago there was a late spring snowstorm that happened after the oaks had leafed out. In addition to knocking many limbs and branches to the ground, the snow covered up available grass so there was little for livestock to eat besides the young buds and foliage. As a result, about 2,700 cattle died due to oak toxicity. In the unlikely event such conditions occur again, livestock operators can prevent lethal damage by feeding their animals hay or other supplemental feed when the natural grass is covered up. But it is important to start hay supplementation immediately and not to wait until cattle get sick or die. A delay of only a day or two can easily result in many more deaths and ill cattle. If cattle are in conditions where toxicity is a longer-term possibility, the use of calcium hydroxide in a supplement can prevent sickness. The addition of 10% calcium hydroxide (hydrated lime) to a supplement will still be palatable to cattle. Then if the cattle will consume about two (2) pounds of this supplement per day it will prevent many cases of oak toxicity. This supplemental calcium hydroxide has to be consumed before exposure to be effective.*
* Information about oak toxicity was gleaned from an article by UC Extension Veterinarian, John Maas in the January 2008 issue of California Cattlemen’s Magazine.
- Posted By: Jaime Adler
- Written by: Douglas D. McCreary
For almost a century there has been concern that blue oak (Quercus douglasii Hook. & Arn.), a California endemic, is not regenerating adequately in portions of its range. For the last 20 years, there have been concerted efforts to develop successful procedures for artificially regenerating this species so that it can be planted in areas where natural regeneration is unsuccessful, or in areas where it once grew but has been lost. These efforts have been successful in identifying procedures that will work, but unfortunately, such procedures often require intensive management and are costly. Since 80% of the oak woodlands in California are privately owned and the principal activity is livestock grazing, many large woodland owners and managers have marginal incomes and are reluctant to spend a great deal to regenerate oak trees.
An alternative, but untested, approach is to use naturally regenerating oak seedlings and take measures to promote their advancement to the sapling stage. This could be critical since research has demonstrated that the bottleneck for successful regeneration is often getting seedlings to grow into saplings. If successful, using natural seedlings could result in considerable savings because no effort or cost would be expended to collect acorns, or to grow and plant seedlings. An additional advantage would be that only genetically adapted plant material would be used, alleviating concerns about using “offsite” planting stock. Because of these economic, ecologic, and low input (i.e., less work) advantages, the development of techniques to advance natural regeneration holds great promise for being adopted and implemented by landowners.
To test this strategy, a study was initiated in 2007 at six field sites in the range of blue oak throughout the state. At each site, 144 naturally occurring blue oak seedlings were identified. Half of these were under the canopy of onsite trees and half were in the open. In addition, treatments included protecting seedlings with tree shelters and controlling weeds. When the plots were established, the height of each seedling was recorded. Yearly assessments of survival and height growth have been made every fall since establishment to evaluate the efficacy of the treatments.
After three years, seedlings in treeshelters have consistently grown taller than unprotected seedlings. In addition, the survival of those receiving an annual weed treatment has been significantly higher than those not receiving it. These results suggest that utilizing existing natural seedlings could contribute to increased blue oak regeneration at lower cost, thus improving the chances that this important species can be managed sustainably and conserved for future generations.