Sec13 lochquifer alternatives
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Transcript of Sec13 lochquifer alternatives
Benefits: [E = Effectiveness, I = Environmental Impact, P = Practicability]
E Provides an extra 4700 AFY most years, over 3 times SqCWD’s 1500 AFY target E Recharges aquifers 2 to 3 times faster: Purisima in as little as 7 years,
Santa Margarita in as little as 4 years E Fills a vast water bank 5x bigger than the Loch and 30x bigger than SqCWD’s 1500 AF target. E Protects all of mid-County against long-term droughts. E Gives good yield even in most dry years, because winter storm water usually is still abundant. I Increases fish populations: cool water seeps from recharged aquifers into habitat base flows. I Increases dry-season flows at Tait Street Diversion, easier to meet bypass requirements. I Uses water which is not needed by fish habitat; reduces big turbid flows that may harm fish. IP Fisheries’ approvals may be quick as a result, speeding water rights approval. I Good carbon footprint: Energy use per gallon is only about the same as SCWD’s
is today. EIP Hydroelectricity can be generated in the gravity feed to customers. (see Section
15 for details) EP When river is turbid, allows GHWTP to draw water while Loch is being filled. P Operating cost per gallon is comparable to SCWD’s current operating cost per gallon. P Low capital cost per AF of capacity, potentially 6 times lower than that of desal plant. P High yield on capital cost, because of long project operating lifetime. Potential profit on pond.
Summary: Increase Felton diversions and pre-treat water to a standard suitable for storage in Loch Lomond. Increase Loch pipeline capacity to about 28 mgd by upgrading existing aging 14 mgd pipeline and adding a second one. Quarry storage of stormwater surges probably will be unnecessary. Transfer to Felton some of the County’s reserved 17,000 AFY Zayante Creek water right and/or obtain San Lorenzo River stormwater rights at Felton Diversion.
Build an 8 mgd conventional water treatment plant to treat Loch water all year for the benefit of SqCWD, SCWD, SVWD and other water districts--which would rest their wells substantially and thus let all of the region’s aquifers recharge at the highest possible rates. Locate the treatment plant at about the same elevation as the Loch so getting water from the Loch takes little energy, and so most customers can be fed via gravity only, without needing electric pumps. Such a good site for the plant might be in the Scotts Valley area, perhaps in a corner of one of the quarry properties.
For water diversions use Ranney collectors predominantly, as they filter out most turbidity before it even enters their system, and because they are very friendly to fish. (See Section 12 for details) To pre-treat conventional (non-Ranney) Felton diversions for turbidity, build a low-cost settling pond nearby using large drain pipes to define its periphery and provide floodwater bypass routes. (See Section 11 for details.) Years later when sediment has filled it up and aquifers are recharged, sell it as buildable land. (At that point, most of the Ranney collectors could be rested as well, except in drought-recovery years.) Background: Of the 190,000 AFY which flows through the streams of SCWD and SqCWD, only some 11,000 AFY (6%) is diverted (all by SCWD). The other 94% flows into the ocean unused.1 The Lochquifer Alternative simply would divert an extra 5400 AFY each winter and would save it in Loch Lomond. The Loch has a capacity of 8400 AF2, quite ample for the job. In the past the Loch has been drawn to as low as 28%, and has been at or below the 36% level five times in the last 41 years, as shown by the chart below.3 _______________________ 1 The amounts of water diverted by upstream communities are negligible here, because the amounts are small and because irrigation and septic systems return much of these amounts via underground pathways.
2 SCWD 2010 Urban Water Management Plan (UWMP) Sec. 3.1.3 3 Chart from the SCWD2 Seawater Desalination Draft Environmental Impact Report (dEIR):
Although SCWD can resort to its bountiful streams, SqCWD is entirely dependent on wells presently. Scotts Valley Water District (SVWD) is heavily dependent upon wells, which draw from the Santa Margarita Aquifer which extends into the San Lorenzo River valley. SCWD’s Loch Lomond reservoir currently is doing double-duty as mitigator of both the “long-term drought” problem (once in 6.5 years average) and the “short-term” a.k.a. “winter/summer” problem: it rains lots in the winter but almost not at all in the summer—and summer demand is twice that of winter. The Lochquifer Alternative would relieve the Loch of double-duty so as to recharge the Purisima, Santa Margarita and Lompico Aquifers at virtually the fastest possible rates. The long-term drought problem is caused by an extremely high variability in rainfall year-to-year, per SCWD’s Confluence computer model. A comparison of 71 years of data about San Lorenzo River flow reveals that flow in the wettest year exceeded flow in the driest year by 29 times. (See Section 5 for a graph and details regarding weather variability and stream flow magnitudes.)
Flows Into the Loch Source: Water Supply Alternatives Study Camp Dresser & McKee January 1994
1 mgy = 3.07 AFY. From the above graph:
(thousand mgy) from (thousand AFY) from
Year Newell Creek
Felton Diversion Total Year
Newell Creek
Felton Diversion Total
1970 2.7 0.7 3.4 1970 8.3 2.1 10.4 1971 0.5 1.0 1.5 1971 1.5 3.1 4.6 1972 0.4 0.8 1.2 1972 1.2 2.5 3.7 1973 3.2 0.6 3.8 1973 9.8 1.8 11.7 1974 2.1 0.9 3.0 1974 6.4 2.8 9.2 1975 1.4 0.8 2.2 1975 4.3 2.5 6.8 1976 0.2 0.1 0.3 1976 0.6 0.3 0.9 1977 0.2 0.1 0.3 1977 0.6 0.3 0.9 1978 3.5 0.7 4.2 1978 10.7 2.1 12.9 1979 1.2 0.7 1.9 1979 3.7 2.1 5.8 1980 2.4 0.8 3.2 1980 7.4 2.5 9.8 1981 0.8 0.8 1.6 1981 2.5 2.5 4.9 1982 4.2 0.5 4.7 1982 12.9 1.5 14.4 1983 7.1 0.5 7.6 1983 21.8 1.5 23.3 1984 0.7 1.0 1.7 1984 2.1 3.1 5.2 1985 0.4 1.0 1.4 1985 1.2 3.1 4.3 1986 4.5 0.6 5.1 1986 13.8 1.8 15.7 1987 0.4 0.5 0.9 1987 1.2 1.5 2.8 1988 0.3 0.2 0.5 1988 0.9 0.6 1.5 1989 0.4 0.5 0.9 1989 1.2 1.5 2.8 1990 0.2 0.2 0.4 1990 0.6 0.6 1.2 1991 0.8 0.4 1.2 1991 2.5 1.2 3.7 1992 1.8 0.8 2.6 1992 5.5 2.5 8.0
Total 39.4 14.2 53.6 Total 121.0 43.6 164.6 Average 1.713 0.617 2.330 Average 5.259 1.895 7.154 Median 2.25 0.75 3.00 Median 6.91 2.30 9.21 Note: numbers in yellow exceed the 8400 AF capacity of the Loch; nevertheless, water was added from Felton. Why are medians higher than means?
EP PROPOSED ANNUAL LOCHQUIFER WATER BALANCE SHEET
for the Lochquifer Alternative in an Average Year, stated in acre-‐feet per year (AFY)
INFLOWS
AFY Source Comments
1932 Rain from 9 sq. mi. watershed above Loch; previous chart (Camp) says this = 5259 avg.
6000
Diversions from San Lorenzo River at Felton and from Zayante Creek; this is the proposed
maximum rate of diversion, not the increase in the rate over the historical rate.
7932 TOTAL 5600 of this goes into Loch; the balance of 2332 of this goes to water districts when diverted in the wet third of the year
OUTFLOWS
AFY Destination Comments
2332 WDs; wet goes directly to water districts when diverted in the wet third of the year;
its purpose is to rest wells, to let aquifers recharge quickly.
3494 WDs; dry goes from Loch to water districts, mostly in the dry 2/3 of the year;
its purpose is also to rest wells, to let aquifers recharge quickly.
5826 AFY is the total amount provided to WDs for resting wells.*
675 Evap. The Loch typically loses some 675 AFY to evaporation.
0
SLVWD San Lorenzo Valley Water District has not been exercizing their 320 AFY right,but
may begin to do so as a matter of degree sometime in the future.
145
Newell Cr. Fisheries regulators rules require 0.2 CFS to be let out of the Loch at all times;this
may be increased to 1.0 CFS, where it has been historically. 1286 SCWD Santa Cruz Water Department's approximate annual average Loch water use
7932 TOTAL 5600 AFY is the total amount coming from the Loch; it is the sum of all
Outflows items with the exception of the first item. This number was chosen so that a full Loch would be drawn down to a level no lower than 1/3 of capacity.
* The approximate amounts of new water which would be required to rest wells completely:
4100 SqCWD 1400 SVWD 450 SCWD
5950 TOTAL
EP NOTE: Even in most dry years, WDs do NOT need to “repay” SCWD with their aquifer water:
• SCWD will merely use a larger share from the Loch via the new treatment plant, and
• the rested wells will resume pumping somewhat, but for their own respective WDs only.
In general, actually taking more water out of the aquifers than we do now is an occurrence which would happen rarely. Even in dry years, aquifers may show gains.
Other Integral Parts of the Lochquifer Alternative: Please refer to the sections listed below, as they are integral parts of the Lochquifer Alternative. Generally, they are also related to other projects or ideas as well, which is why they are not simply inserted here. Sec. 4 Include the Neighbors Sec. 8e 4 Time-spans of Loch Use Sec. 8g Dealing With Turbidity Sec. 9a Tide-Over Projects Sec. 9c Diversion Systems Sec. 9d Pond Buy/Sell/Lease Sec. 10a to g Regulatory Buy-ins First
Sec. 11 Multipurpose Settling Pond Sec. 12 Diversion Alternatives Sec. 14 Upgrade Existing Intertie Sec. 15 Cross-County (Raw) Pipeline Sec. 23 Loch-Down Alternatives Sec. 24 Cowell RR Pipeline Sec. 25 Guidance Questions
Illustrative Art The image below was created in 2013 by professional illustrator Erika Aitken of Santa Cruz. It compares the Lochquifer plan with recent past practice. The volume of each water transfer is represented approximately by the width of each arrow. In essence, abundant winter water not needed by fish goes from the river via Loch Lomond to the users. Water treatment facilities and wells are omitted here for simplicity. In the Lochquifer plan the aquifers are shown as having been filled by annual rainfall, because wells generally are no longer used and so do not compete. An exception occurs in the driest years, when wells dispense water from the aquifers’ vast store.
Cost estimates: M$ Comment (Figures represent costs for minimum configuration plus
hydroelectric option) 35 Conventional 8 mgd water treatment plant, including land acquisition 10 De-turbidifying diversion devices, installed: 2 @ $5M each
3 Settling pond/infiltration gallery and other pre-treatment at Felton Diversion 14 Raw water pipeline, 5 miles @ $1.1M/mile, and pumpstations
5 Potable water pipeline, 4 miles @ $1.1M/mile (no pump necessary) 5 Hydroelectric facility (small pre-fab turbine/generator)
15 Design and permitting 87 TOTAL capital cost 26 Bond interest* (30-year fixed rate at 3.125% on all but the first $35M = $52M x
50%) 103 Sum of capital cost plus finance cost
1.29 Amortized over 80-year operating life: annualized capital+finance cost 1.00 Operation and maintenance, per annum (includes credit earned for
hydroelectricity) 2.29 Total per annum cost
$380 Cost per acre-foot in $, not M$, producing 6,000 AFY -includes bond interest*
$348 -not including bond interest*
*Note: competing projects may or may not include bond interest in their cost estimates. Further study: Which Lochquifer option is the best?
• Minimum Lochquifer alternative: put a Ranney collector or two at Felton to fix the current pipeline gridlock, de-turbidify, and boost the amount diverted (Terry McKinney proposal).
• Cowell Railroad Pipeline plus the above: boosts yield, saves energy, water-loops, repurpo-ses Graham Hill Rd pipeline section to be a potable intertie with Scotts Valley. (Section 24)
• Original Lochquifer proposal: put a Ranney collector(s) at Felton, add a booster pump near Ben Lomond to increase the capacity of the pipeline, and add a second pipeline to the Loch to divert enough water to rest all the wells of several water districts and recharge aquifers ASAP.
• Original Lochquifer with buffer storage, e.g. add a pond, quarry and/or infiltration gallery. Probably unnecessary if pipeline flow rates to Loch are high enough, and especially if no pre-treatment is needed for Ranney water to enter the Loch.
• Loch-Down, which diverts water at elevations above the Loch, where water quality is higher, and to save energy, operate during power outages, provide flood control, etc. (Section 23)
• Cross-County Pipeline (Raw water at 500-foot elevation) enables diversion into the Loch of clean water from high-elevation streams from Bear Creek to Soquel Creek, as well as augmenting any of those streams during dry times; may get enthusiastic backing from fisheries regulators regarding water rights acquisition. (Section 15)
• Hydroelectric option: just before treated water gets all the way down the mountain to users, insert a pre-fab hydroelectric generator in-line with the pipeline. (Section 23)
What does it take to use Ranney collectors in the site areas contemplated for new diversions? What are the details of the optimal pre-treatment to meet Loch standard? What are the most important details regarding the new treatment plant; will it require membranes? How much sludge will the existing Felton Diversion & its new settling pond remove? (nil for Ranneys) What does it take to get regulators’ early buy-in, so as to obtain water rights in 3 to 4 years? What tide-over projects would be best, while we wait for water rights? What does it take to make a profit from the Felton settling pond/infiltration gallery? Would it be worth it to put a Ranney collector in the Loch? Benefits:
• the new treatment plant might not have to remove particulates, • which means it would not have to dispose of much sludge, • all contributing to lower construction and operating costs.
if and when the Loch silts up, the Ranney collector might continue to make the Loch useful as a reservoir.