I second the glee at getting to play with big equipment - I enjoyed a full hour out of the eight we rented on an excavator recently, playing with making piles of very large rocks, and trying to move mountains of earth with a mountain of a machine. Then I let my more experienced operator clean up the mess afterwards.
Grumpy warning: I seem to be in a particularly critical mood.
I did like the advice about earth-moving, I'm just starting to wonder how reliable some of this advice is.
Of the things I already know, I'm seeing typos and misleading statements amounting to maybe 10% of the content. This makes me very wary of trusting any other part of the content that I don't already know, since I assume the accuracy is about the same overall (90%, but not edited to anything better). Does anyone have a more recent edition which has been edited better? Mine's 1988, 3rd print run, apparently.
One thing that concerns me about this chapter is that "tracking and signs" and other forms of observation are almost afterthoughts.
Yes, it can be delightful to discover things in the depths of the earth, or on the blank faces of disturbed earth piles.
But it can also be horrifying, if you know what you're looking at. For example, wondering if you've broken up a plough-related salt pan, or permanently damaged a fragile lake bed (in my garden near the
pond, digging down to do buried hugel-type
water retention beds). Other things don't come clear until the next rain: for example the damage that heavy equipment can do to the clay tiles or septic drainage systems, resulting in noxious basement flooding of existing houses in every rainy season following ill-planned excavation. Or buried electrical wires, and other utilities. Carelessly planned "improvement" projects will now require further hours and expense to fix the new problems you've created. These particular problems are less likely on virgin sites, which makes me think again that this book is written as a "kinder and gentler" pioneer manual for destroying further tracts of wilderness, instead of for the urban and suburban reclamation projects that Mollison claims to support.
The type of water-diverting earth movement described here would be illegal in most Western states without a permit, as it has large effects on neighbors' water rights, and potentially on groundwater levels.
(Why groundwater is regulated, while the water drawn from
wells, aquifers, or altered by deforestation, is not well considered. Legal remedy is also hard to obtain when a neighbor's past actions have resulted in permanent changes to water flow or availability, but even if the laws aren't enforced, the ethical issues remain serious.)
We are trying to remediate a damaged natural pond, which is probably leaking and has also had some of its inflow diverted, due to two neighboring property owners valuing "drainage" over water storage in our arid climate. This is an easy mistake to make as a transplant from a wetter climate; and most people who can afford to buy
land here make their fortunes on the coastal cities or industries before moving here for
retirement / homesteading / vacation. Both Australia and the United States have some of the poorest cultural awareness for considering how private choices affect public welfare. (Doesn't help that we think "welfare" is a dirty word for someone taxing us to help lazy people.)
By "welfare" here I mean well-being. Public welfare is the community's well-being. Managing projects with the public welfare in mind means ensuring that your 'improvements' not only increase general abundance, but also being aware of the community's shared goals, often reflected in laws and
local enforcement priorities. Managing projects for private gain, by contrast, might involve limiting resources to create artificial scarcity that will drive up prices. A company that harvests clean water for bottling, while polluting downstream water so others are forced to purchase bottled water, destroys the public welfare for private gain. A landowner who diverts a stream or water catchment to serve his flock's needs, without regard for downstream neighbors, can be accused of the exact same lack of ethics. (Unfortunately, we seem to be getting around this issue by ignoring region-scale groundwater management, and depleting aquifers and watering our stock from subsurface waters instead.)
Most states have "call before you dig" lines, to discover buried utilities before accidents happen. If you are contemplating illegal earth-moving, you had probably best call anyway, and make up an excuse that sounds legal. Digging up a buried utility sounds like a terrible way to meet your local authorities, while in the midst of an illegal
project.
There's also HUGE potential for doing damage, if you don't know your region well
enough to plan a thoroughly useful and harmless project. I don't know any "call before you dig" lines for checking the soil type, microclimate rainfall, soil salt levels, or groundwater management issues, but local agricultural extension services seem like a good place to start. Regional conditions are key; and while some general regional terms have already been defined, I'd love to see a lot more specific, well-documented training material on site assessment and recognition of critical variables. The indicator plants for minerals in the preceding chapters were useful, but we need more fine-tuned info for specific regions. Is there a data bank available?
Missing INFO:
Mollison did emphasize being ready to replant immediately. And he mentions tarps in the context of preserving useful clay deposits. But there is ZERO attention to the general, proper caretaking of piles of destabilized earth.
In Oregon and Washington (and likely most of the USA), the law requires erosion protection (tarps, absorbent barriers) to prevent piles of disturbed earth from washing away in rains.
Private landowners who do not have the construction
experience to be aware of this law can lose piles of topsoil, contaminate groundwaters with their piled soils, and generally underestimate the necessary time and costs to do earth-moving properly. The fines for disregarding such laws can also be severe, as they are designed to penalize large construction companies and speculative property developers. It pays to research local laws about water, earth, and fire management; these are not private choices, as the results can affect the entire neighborhood.
When building a home, or any complex structure involving precise grading, drainage, pipes and culverts, etc., there will always be delays between initial earth-moving, and the replacement and planting of topsoil. You can cover-crop the topsoil pile, but most people would see the cover-cropping of mineral soils as a waste of time. Site managers need to plan on physical protection of exposed mineral earth piles, equipment paths, and so on.
I'm also having some problems with the basic level of information presentation.
Little things like describing slope as "a proportion of base to height" and then proceeding to elaborate the usual (inverse) proportion: slope is expressed as "rise over run," or height over base. (p. 230, 9.4 paragraph 4)
This kind of convention is crucial for communication: telling your chimney supplier you need a roof kit for a roof with a 3:4 slope (common), when it's really 4:3 (very steep), will get you the wrong kit.
In Figure 9.27, "tilt" is shown twice with two different meanings.
In Figure 9.22, it's never made clear which is a levee and which is a polder. Wikipedia gives a general definition (polder is a lower elevation landscape protected by dikes; a levee is an artificial embankment or dike, like a long dam). Later on, the need to scrape out polders is mentioned. Do we need more info about long-term maintenance of these systems in general?
Nearby on p. 241, section 9.8 paragraph 3, he states that "designers and architects have seldom been personally involved in earth moving." Too true.
This reflects my original mental problem with the "design" approach to land management, period.
Often the people designers accuse of "doing it wrong" have in fact more local knowledge and experience than the designers, and "designed" systems often fail to achieve the same basic level of function and maintainability as the vernacular solutions. Only where the "locals" are recent transplants from a different biome, does an experienced designer have an advantage in laying out a more functional, productive, and
sustainable system. Wherever locals are available (even remnants of local tribes, or second or third generation farmers even if they are "doing it wrong"), locals
should be consulted about proposed designs, and local landscapes consulted to see how the results of previous "design improvements" have proven out over time.
It is unethical to experiment with someone else's land and livelihood, or with intact natural systems, when proven local methods are available and existing disturbed sites can be improved.
Once or twice in this manual, lip service is given to observing local conditions. In the specific, technical sections, lots of big theoretical changes are proposed, and the point about ongoing observation is poorly reinforced. The possibility of SUBSTANTIAL HARM must be considered alongside any proposed improvement. Occasionally, wry anecdotes are offered about the white man's casual and catastrophic disregard for
native wisdom, but the lesson is not carried over to humility on the part of the author himself, or the methods he advocates based on ... what? One human's brief years of personal experiment and observation? I would love to see more examples of the author's catastrophic early mistakes alongside blithe predictions of improvement.
p.240 (9.7 section 6) acknowledges, again toward the end of a long section on how to dredge and
berm marshlands, that "natural marshes need protection for their unique values and for waterfowl." This should be at the BEGINNING of a section on sensitive, protected, and largely underappreciated environments. Hopefully we'll get more reinforcement of the value of natural marshes later. He did mention the unsustainability of burning peat.
p. 231 Figure 9.5 has two dotted (dashed) lines, used for nearly opposite purposes (one indicating a theoretical slope compared to a concave curvature, the other indicating a natural concave curvature compared to an artificially straight-angled slope). This makes the reference in the text below somewhat unclear (section 9.4 paragraph 9).
230 - figure 9.3 - "recommended proportions of slopes for stable rest angles" in various materials. They look steep to me: like maximum "angle of repose" slopes, not stable non-erosive slopes. Anyone else have soil-moving experience enough to give a range for each soil type described?
I had some similar problems with the chemistry discussion in the previous chapter, which I'll be retroactively adding to that discussion if anyone's interested.
I did appreciate the range of possibilities mentioned. Maybe I'm just grumpy that they're mostly not legal, or ethical, in our forested slopes and level meadows. This chapter didn't have a lot that seemed personally applicable for my present situation.
-Erica W