Livestock in Riparian Zones - Reality vs Greenspin
The introductory text said;
“Inappropriate livestock grazing is one of the most significant causes of degradation to the land-water interface in Australia. Livestock have long been part of the Australian landscape. Cattle, sheep, horses, goats and pigs arrived with the first settlers in the 1780s and moved with them across NSW into the Central West. Settlements sprang up along river systems supported by clean water and fertile floodplain soils. Since that time, livestock have caused damage to the most sensitive part of the landscape – our riparian lands.”
This picture was captioned;
True, we see cattle by a creek and some exposed soil which would lead most urban punters to conclude that this picture is representative of the entire length of the creek on that farm and representative of all grazed creek banks on all farms.
But we can be quite certain, given the proven MO of CMA’s and their staff, that the picture shows worse than average impacts. A random inspection of the first, second and third order farm streams that account for most of the riparian interface in the landscape is unlikely to provide a single example of conditions like those shown. It is also highly improbable that anything like those conditions would be replicated over the entire length of that particular stream. Indeed, there may be only one or two such examples on the entire property.
Stock can produce physical modifications to a small portion of a riparian zone when they are first introduced to a landscape or when a major increase in animal traffic at a particular point takes place. If the stocking rate has essentially remained the same and the number of access points is not reduced in a way that increases traffic on the remaining access points then there is minimal on-going impact. But the CMA text merely indicates that this “significant” damage has taken place “since that time” (ie implying it is on a continuous basis, in the past and in future). It converts an historical event as evidence of a future threat.
And it begs the question, do we regard a road culvert as evidence of land degradation? Or do we regard it as a piece of infrastructure that is a normal and necessary part of the prevailing use of the land as a road? Clearly, we view it as the latter. So why do we regard customary tracks (roads) made by cattle for their own continuing use as anything different to our own road culverts?
Both involve an initial excavation that exposes soil and both then involve only minimal soil disturbance for many decades after. And just like our road system, the more traffic cattle tracks have, the greater the visual impact. Do we begrudge Elephants or Caribou their right to shape creek crossings? No, only domestic stock.
To its credit, the site does include some helpful tools for minimising on-going soil movement. And just as for our own road culverts, this involves paving the most prone parts of the road with rock and concrete. The irony is that this simple, logical solution can only be carried out with the approval of DPI and the additional cost and effort that involves. And it is also fairly obvious that any approval for such works would only come with very significant and expensive conditions like fencing off the entire riparian zone and installing unnecessary watering points and piping.
This photo was captioned;
"Sheep are said to have a greater impact than cattle in the riparian zone. (NSW DPI)"
It shows a fairly normal steep bank of a deep riverine cross section. Yes, there are sheep in the picture but one is left to wonder what, exactly, is the impact of those, or the past century of previous sheep, on the steepness of the river bank? Sure, they graze on the grass and may also graze on any tree seedlings that might germinate there. But the chances of such stems surviving the first flood event are quite low as they are more rigid than grass and much more likely to get tangled with passing debris.
Is there any evidence that the bank is not maintaining its form? No.
Would the bank structure be any different if there were trees atop the bank? No
In fact, if trees were present we would probably observe exposed roots as evidence that additional erosion had taken place. The area of exposed soil would be greater because the grasses would be competing for moisture with the trees and this would present a more erodible face to flood waters with greater potential for snags.
The third photo is just as misleading. We are told; “This creek was severely polluted with sediment and animal waste laden run-off. The rapid increase in nutrient levels caused a massive toxic blue-green algae bloom, rendering the creek water unusable for stock or domestic consumption.”
But what they do not tell us is that this is a temporary condition that starts at the beginning of a dry season and will only last until the pool dries up later in the season. More importantly, they do not mention that most high faecal E. coli counts and algal blooms are the result of self reproduction in the warm stagnant water. As was found to be the case with Canberra’s Lake Burley Griffin, most algae in a bloom is of a secondary or “regrowth” nature.
The severity of an algal bloom or the ultimate concentration of faecal E . coli, is not a function of the initial volume of coli being supplied to the pools in runoff. Rather, the longer the dry season, the warmer the temperature, the shallower the pools and the less frequent the intermittent runoff events take place, the greater the exponential rate of bacterial and algal growth becomes.
Algae reproduce faster and more often in favourable conditions, get used to it, folks.
The official CMA summary is in black type, below. It does not present a true and fair view so we have added a few comments in green to get closer to the truth about the impacts of grazing on riparian zones;
The real impacts of riparian grazing
• isolated, once-off loss of vegetation cover in the first few years exposure to grazing
• once-off soil compaction at a few specific points and initial erosion
• once-off bank instability followed by long term stability of the modified landforms
• isolated instances of reduced water quality
• no evidence of reduced property values from the presence of stock modifications
• enhanced germination of native tree species in hoof depressions etc
• localised instances of poor water quality (increased turbidity, nutrients and salinity)
• very localised loss of in-stream habitat
• isolated, once-off changes to river channel shape of minor consequence
• minor silting of rivers and creeks compared to that produced by unsealed roads
• enhanced natural regeneration of native trees along previously cleared creek banks
Clearly, a picture can, indeed, tell a thousand lies. And government and green pictures seem to tell the most lies of all.