Light v. State Water Resources Control Board

water, the Board can weigh the use of water for certain public purposes, notably the protection of wildlife habitat, against the commercial use of water by riparian users and early appropriators. Further, the Board may exercise its regulatory powers through the enactment of regulations, as well as through the pursuit of judicial and quasi-judicial proceedings. Because this is a facial challenge, our ruling is a narrow one, grounded in the general authority of the Board; we have no occasion to rule on the validity of any particular substantive regulation that might be approved by the Board in the process of implementation.

We also conclude the Board properly found the regulation to be necessary to enforce water use statutes and did not unlawfully delegate its authority by requiring local governing bodies to formulate the substantive regulations. Finally, we find no error in the Board’s certification of the environmental impact report.

The stream system of the Russian River is home to three species of salmon classified as either threatened or endangered under the federal Endangered Species Act of 1973 ( 16 U.S.C. § 1531 et seq.). The river and its tributaries, which flow to the sea through Mendocino and Sonoma Counties, contain over 1,700 miles of potential salmon habitat. In late fall and winter, adult salmon enter the river from the ocean, swim upstream, and lay eggs in gravel on the streambed. The eggs typically hatch in late winter, and the fry emerge from the gravel after four to eight weeks and move to shallow water, typically near the margins of the stream. Here the young salmon, known as salmonids, spend several months, moving into deeper water as they mature.^[1]

In April 2008, when unseasonably cold weather followed an exceptionally dry winter, the National Marine Fisheries Service (Fisheries Service) discovered two episodes of fatal strandings of salmonids in the mainstem Russian River and a tributary stream. “Strandings” occur when salmonids in shallow areas of the watercourse are left without water or are trapped in isolated pools. There is evidence suggesting the problem is not necessarily one of low water levels per se, but of sudden decreases in water level, which allow the salmonids insufficient time or opportunity to seek the protection of deeper water. Because the salmonids spend their time in shallower water near the stream banks, they may be particularly susceptible to such sudden decreases. Extrapolating from the available limited data, the Fisheries Service reached a “coarse but conservative” estimate that some 25,000 salmonids had been killed throughout the stream system in the April 2008 events.

The Fisheries Service blamed the strandings, in large part, on agriculturalists, especially grape growers, located along the system. The watershed of the Russian River is home to over 60,000 acres of vineyards, of which 70 percent are within 300 feet of salmonid habitat. Grape plants are particularly susceptible to frost damage when new growth appears in the spring. The newly emerged vegetation is delicate, and a tissue-killing freeze can result in substantial crop loss. A time-tested method of preventing frost damage is to spray the new growth with water, which by freezing on the plants insulates them against the colder air. If a number of growers anticipating a frost all draw their water directly from a stream at the same time, the net effect can be a sudden decrease in the volume of flowing water. The problem occurs both because the growers’ diversion of water is effectively synchronized—all growers in a threatened area must frost protect at the same time—and because the overhead sprayers necessary for frost protection consume relatively large quantities of water. Examining data for March through May 2008, the Fisheries Service found an association between near-freezing air temperatures and sudden and substantial drops in the flow of a stream in the system.^[2]

In a letter, the Fisheries Service urged the Board to undertake regulatory activity to reduce the risk of frost-protection-related salmonid deaths. Although the Fisheries Service pointed the finger at growers, other factors were potentially involved. Most obviously, the affected area of the stream system is downriver of two large reservoir lakes created by the Coyote and Warm Springs Dams. The pace of water release from these dams directly affects the level of water in the system. Following the discovery of the stranding deaths, the agency responsible for controlling the release of water from the dams, the Sonoma County Water Agency (SCWA), experimented with anticipatory releases of water to counteract the effects of frost protection diversion. The SCWA concluded such releases were impractical, given the long time, up to 14 hours, necessary for the released water to reach the more distant portions of the stream system and the difficulty in predicting frost events, which gave rise at times to wasteful “false alarm” releases. In addition, the coordinated nature of the frost protection diversions made it difficult to counteract their impact. The SCWA told the Board additional anticipatory releases would be ineffective in preventing the sudden drawdowns.

On the other hand, while protecting sensitive crops from frost is of critical commercial importance, the practice can be managed to reduce the immediate demand on streamflows. Growers can minimize their use of sprayed water by

precisely targeting truly threatened acreage, and better frost forecasting and temperature monitoring can avoid unnecessary sprayings. Many growers have constructed basins to collect water at times of high streamflow. Drawing water from such basins or from wells, rather than directly from the stream system, serves the same frost protection purpose without an immediate impact on streamflow. In addition, there are alternative methods, such as wind machines, heaters, and cold air drains, that will work under certain circumstances to protect against frost damage.

Following the 2008 discovery of salmonid deaths, the Fisheries Service formed a task force and attempted to organize voluntary efforts to reduce the impact of frost protection on the stream system. While it praised the efforts of participating growers, the Fisheries Service eventually concluded the problem could not be managed through voluntary efforts. The submitted proposals for voluntary action generally did not address diversion in the tributary streams of the river, where the problem was most acute, and the inability to compel the compliance of all growers with a voluntary plan made success unlikely. Based on the Fisheries Service’s experience, the Board concluded voluntary efforts would not solve the problem.

Following a series of public hearings and the preparation of an environmental impact report, in September 2011 the Board adopted a regulation addressing diversion for frost protection, codified as California Code of Regulations, title 23, section 862 (hereafter Regulation 862). Regulation 862 applies to “any diversion of water from the Russian River stream system . . . for purposes of frost protection from March 15 through May 15.”^[3] (Reg. 862, subd. (a).) The section contains no substantive regulation of water diversion for the purpose of frost protection, instead delegating the development of such regulation to “water demand management program[s]” (WDMP’s). (Ibid.) Regulation 862 is silent as to how and by whom the WDMP’s are to be developed, but they must be administered by “an individual or governing body . . . capable of ensuring that the requirements of the program are met.” (Id., subd. (b).) The parties reasonably assume the WDMP’s will be created by self-organized groups of agricultural diverters, who will act as the “governing bodies.” Each WDMP must be submitted annually to the Board for approval. (Ibid.)

As described in Regulation 862, the fundamental functions of the WDMP’s are to develop and implement methods for monitoring the “stage,” or height,

of the affected watercourses, determining when that stage poses a threat to young salmon, and responding with “corrective actions” to reduce a threat once detected. (Id., subds. (b), (c)(2)-(4).) Among other requirements, the WDMP must contain an inventory of potential diverters “within the area subject to the WDMP,” including diverters who “declined to participate,” a stream stage monitoring program, and a plan for managing frost protection diversion to prevent strandings. (Id., subds. (c)(1)—(5).)

Regarding potential “corrective actions,” Regulation 862, subdivision (c)(4) states: “If the governing body determines that diversions for purposes of frost protection have the potential to cause stranding mortality, the governing body shall notify the diverter(s) of the potential risk. The governing body, in consultation with the diverters, shall develop a corrective action plan that will prevent stranding mortality. Corrective actions may include alternative methods for frost protection, best management practices, better coordination of diversions, construction of off stream storage facilities, real-time stream gage and diversion monitoring, or other alternative methods of diversion. ... In developing the corrective action plan the governing body shall consider the relative water right priorities of the diverters . . . .”

Once a program has been developed and approved, “[t]he diverters shall implement corrective actions in accordance with the corrective action plan, or cease diverting water for frost protection.” (Reg. 862, subd. (c)(4).) Reinforcing this ban, Regulation 862 declares, “The diversion of water in violation of this section, including the failure to implement the corrective actions included in any corrective action plan developed by the governing body, is an unreasonable method of diversion and use and a violation of Water Code section 100, and shall be subject to enforcement by the board.” (Id., subd. (e).)

In the resolution adopting Regulation 862, the Board stated the portion of the regulation requiring corrective actions would not be implemented immediately. Instead, the resolution established a schedule allowing for the collection and analysis of baseline data during the first two and a half years following adoption.^[4]

Regulation 862 was challenged in two petitions for writs of mandate filed in Mendocino and Sacramento Counties. The Mendocino County action was filed by Rudolph H. Light and Linda Light, owners of 23 acres of vineyard in the affected area that are crossed by a stream from which the Lights draw water for purposes of irrigation and frost protection. The Sacramento County action was filed by a grower association, three individuals, and a limited partnership (the Sacramento plaintiffs), all of whom either grow grapes in the affected area or have members who do so.^[5] Both petitions alleged, for a variety of reasons, that Regulation 862 would unlawfully interfere with plaintiffs’ use of water drawn from the Russian River stream system. The petitions were consolidated for decision in Mendocino County Superior Court. In February 2012, the trial court stayed enforcement of Regulation 862 pending resolution of the litigation.

The trial court later entered a 41-page decision finding the Board’s action unlawful on the following grounds: (1) the Board exceeded its authority in adopting a regulation that limited the use of water by riparian users; (2) the regulation violated the “rule of priority,” which governs the manner in which insufficient water is divided among users; (3) the regulation improperly delegated regulatory authority to the WDMP’s; and (4) the declaration of necessity for the regulation was not supported by substantial evidence. Given its ruling, the trial court initially declined to rule on plaintiffs’ claims under the California Environmental Quality Act (Pub. Resources Code, § 21000 et seq.; CEQA), but in a subsequent order the court found several flaws in the environmental impact report prepared in connection with Regulation 862. The court entered judgment directing issuance of a peremptory writ of mandate requiring the Board to set aside its certification of the environmental impact report and its adoption of Regulation 862.

The Board has appealed the trial court’s judgment.

A. Legal Background

We begin with a summary of four areas of law that converge in the resolution of plaintiffs’ claims.

1. California’s Dual System of Water Rights and the Rule of Priority

Ownership of California’s water is vested generally in the state’s residents, but individuals and entities can acquire “water rights,” the right to

divert water from its natural course for public or private use. (Wat. Code,^[6] § 102; see generally United States v. State Water Resources Control Bd. (1986) 182 Cal.App.3d 82 , 100 [ 227 Cal.Rptr. 161 ] (United States).) California maintains a “dual system” of water rights, which distinguishes between the rights of “riparian” users, those who possess water rights by virtue of owning the land by or through which flowing water passes, and “appropriators,” those who hold the right to divert such water for use on noncontiguous lands. (See El Dorado Irrigation Dist. v. State Water Resources Control Bd. (2006) 142 Cal.App.4th 937 , 961 [ 48 Cal.Rptr.3d 468 ] (El Dorado).) For historical reasons, California further subdivides appropriators into those whose water rights were established before and after 1914.^[7] Post-1914 appropriators may possess water rights only through a permit or license issued by the Board, and their rights are circumscribed by the terms of the permit or license. Riparian users and pre-1914 appropriators need neither a permit nor other governmental authorization to exercise their water rights. (California Farm Bureau Federation v. State Water Resources Control Bd. (2011) 51 Cal.4th 421 , 428-429 [ 121 Cal.Rptr.3d 37 , 247 P.3d 112 ] (Farm Bureau).) Inevitably, given the nature of the resource, “water rights are limited and uncertain. The available supply of water is largely determined by natural forces.” (United States, at p. 104; see Gray, The Uncertain Future of Water Rights in California: Reflections on the Governor’s Commission Report (2005) 36 McGeorge L.Rev. 43 , 49-51 [discussing factors creating uncertainty in the exercise and administration of water rights].)

The differences between and among riparian users and appropriators become most pronounced when the available supply of water is inadequate to satisfy the needs of all those holding water rights. Under the “rule of priority,” which governs diversion in such circumstances, the rights of riparian users are paramount. Although riparian users must curtail their use proportionately among themselves in times of shortage, they are entitled to satisfy their reasonable needs first, before appropriators can even begin to divert water. (United States, supra, 182 Cal.App.3d at p. 104.) As a result, appropriators may be deprived of all use of water when the supply is short. In turn, senior appropriators—those who acquired their rights first in time—are entitled to satisfy their reasonable needs, up to their full appropriation, before more-junior appropriators become entitled to any water. (Id. at pp. 104-105; North Kern Water Storage Dist. v. Kern Delta Water Dist. (2007) 147 Cal.App.4th 555 , 561 [ 54 Cal.Rptr.3d 578 ].)

which, if applied to the full extent of their scope, would occupy the field of allocation of stream waters to the exclusion of any competing system of legal thought.” (Audubon Society, supra, 33 Cal.3d at p. 445.) In bringing the two together, the court held the doctrine (1) prevents any party from acquiring a vested right to appropriated water in a manner harmful to the interests protected by the public trust; (2) “the Legislature, acting directly or through an authorized agency such as the Water Board, has the power to grant usufructuary licenses that will permit an appropriator to take water . . . , even though this taking does not promote, and may unavoidably harm, the trust uses at the source stream”; and (3) “[t]he state has an affirmative duty to take the public trust into account in the planning and allocation of water resources, and to protect public trust uses whenever feasible.”^[8] (Audubon Society, at pp. 445-446, fn. omitted.)

4. The Board

The Board was created as the State Water Commission in 1913 to administer the appropriation of water for beneficial purposes. As originally created, the Board had the “limited role” of granting use rights to water that was not being applied to beneficial purposes and was not otherwise appropriated. (Audubon Society, supra, 33 Cal.3d at p. 442.) “[T]he function of the Water Board was restricted to determining if unappropriated water was available; if it was, and no competing appropriator submitted a claim, the grant of an appropriation was a ministerial act.” (Ibid.) The enactment of Article X, Section 2, however, “radically altered water law in California and led to an expansion of the powers of the board.” (Audubon Society, at p. 442.) Through subsequent legislation and judicial decisions, “the function of the Water Board has steadily evolved from the narrow role of deciding priorities between competing appropriates to the charge of comprehensive planning and allocation of waters.” (Id. at p. 444.)

As currently constituted, the Board “has been granted broad authority to control and condition water use, insuring utilization consistent with public interest.” (Environmental Defense Fund, Inc. v. East Bay Mun. Utility Dist. (1977) 20 Cal.3d 327 , 342 [ 142 Cal.Rptr. 904 , 572 P.2d 1128 ] (EBMUD).) Its enabling statute describes the Board’s function as “to provide for the orderly and efficient administration of the water resources of the state” and grants it

Farm Bureau, supra, 51 Cal.4th at p. 429.) The Board’s authority to enact regulations in furtherance of this purpose was addressed and upheld nearly 40 years ago in Forni. In that case, the Board had adopted a regulation, then codified as section 659 of title 23 of the former California Administrative Code, which held, “ ‘diversion of water from the Napa River after March 15 for frost protection except to replenish water stored in reservoirs prior to March 15 is an unreasonable method of diversion within the meaning of [Article X, Section 2] and Section 100 of the Water Code.’ ” (Forni, supra, 54 Cal.App.3d at p. 752, fn. 4.) The regulation was motivated by a lack of adequate water to satisfy the frost protection demands of all users.^[9] (Forni, at p. 748.) Based on that regulation, the Board brought an action to enjoin certain vineyard owners from drawing water from the river for purposes of frost protection. (Id. at p. 747.) The defendants were granted summary judgment on the ground the Board lacked the authority to prohibit or limit the use of water by riparian users. (Id. at p. 748.) In reversing the trial court’s judgment invalidating the regulation, the court rejected the argument, made on several grounds, that the Board lacked the authority to interfere with water use by riparian users. (Forni, at pp. 751-752.) The court then upheld the Board’s power to enact a regulation governing reasonable use. Without extensive discussion, the court concluded the Board had not exceeded its authority in enacting the regulation because, “[p]roperly construed, section 659 amounts to no more than a policy statement which leaves the ultimate adjudication of reasonableness to the judiciary.” (Id. at p. 752.)

Plaintiffs rightly point out that, despite Form’s refusal to invalidate the regulation, its resolution of the issue was not a ringing endorsement of the Board’s power to enact regulations governing the unreasonable use of water. In effect, Forni chose to treat the regulation as an advisory statement of policy that left to the courts the ultimate authority to determine whether a particular use of water was reasonable. (Forni, supra, 54 Cal.App.3d at p. 752.) Of course, to the extent the bald declaration of unreasonableness in former California Administrative Code, title 23, section 659 constituted a valid “policy statement” under Forni, Regulation 862 is similarly valid. At a minimum, Form’s holding would require a reversal of the trial court’s invalidation of the regulation on the issue of authority.

Yet to the extent Form’s ruling was based on the implicit rationale that only the judiciary has the power to declare a particular water use unreasonable, we conclude Forni construed the Board’s authority too narrowly. Subsequent judicial decisions have rejected the contention that the

judiciary is vested with sole authority over unreasonable use, most forcefully California Trout, Inc. v. State Water Resources Control Bd. (1989) 207 Cal.App.3d 585 [ 255 Cal.Rptr. 184 ] (California Trout). At issue in California Trout was the validity of a Board-issued use permit conditioned on compliance with a state statute requiring the owner of any dam to “allow sufficient water at all times to pass . . . around or through the dam, to keep in good condition any fish that may be planted or exist below the dam.” (Fish & G. Code, § 5937.) Among other arguments, a plaintiff contended, “the Legislature may not impose a categorical priority for one use of water because reasonableness of use requires comparison of contending alternative uses which is an adjudicative question that cannot be constrained by a statutory rule.” (California Trout, at p. 622.) The court rejected the contention the Legislature lacked the power to enact broad rules governing reasonableness, using an analogy to the doctrine of reasonable conduct in tort law. As the court explained, “it is often asserted that ‘[w]hat constitutes a reasonable use or method of diversion is ordinarily a question of fact.’ [Citation.] Actually, since what occurs is development of a standard of reasonableness on the facts of the case it should be described as a making of law for the particular case. [Citation.] The typical example of such a process is case-by-case determination of the standard of reasonable care in the law of tort. However, the fact that, ordinarily, the standard of reasonableness is fixed ad hoc does not impel the view that the Legislature has no power to fashion rules concerning reasonableness, e.g., by enacting statutory safety obligations which become the basis of negligence per se.” (Id. at p. 624.) After analyzing the text and judicial construction of Article X, Section 2, the court concluded, “there is ‘broad legislative authority for the conservation and regulation of scarce water resources . . . .’ [Citation.] That authority is sufficient to authorize the Legislature to enact statutes which determine the reasonable uses of water.” (California Trout, at p. 625.)^[10]

If, as California Trout holds, the Legislature has the power to enact general rules governing the reasonable use of water, the Board has a similar regulatory authority. The Water Code authorizes the Board, in carrying out its statutory duty to administer the state’s water resources, to “exercise the adjudicatory and regulatory functions of the state.” (§ 174.) In that role, the Board is granted “any powers . . . that may be necessary or convenient for the exercise of its duties authorized by law” (§ 186, subd. (a)), including the

growers nor the public. Efficient regulation of the state’s water resources in these circumstances demands that the Board have the authority to enact tailored regulations.^[11]

2. Regulation of Riparian Users and Pre-1914 Appropriators

In contending the Board exceeded its authority, plaintiffs also cite the time-honored exemption of riparian users and pre-1914 appropriators from the permitting authority of the Board. (E.g., Farm Bureau, supra, 51 Cal.4th at p. 429.) While such users cannot be required to obtain permits as a condition of exercising their right to divert, that does not mean their use of California’s waters is free from Board regulation. “[N]o water rights are inviolable; all water rights are subject to governmental regulation.” (United States, supra, 182 Cal.App.3d 82 , 106.) The Supreme Court recognized as much in Farm Bureau; immediately after noting the Board “has no permitting or licensing authority over riparian . . . rights, or over appropriative rights acquired before 1914,” the court observed the Board “does have authority to prevent illegal diversions and to prevent waste or unreasonable use of water, regardless of the basis under which the right is held.” (Farm Bureau, at p. 429, fn. omitted.) That the Board cannot require riparian users and pre-1914 appropriators to obtain permits before making reasonable beneficial use of water does not mean the Board cannot prevent them from making unreasonable use. Any other rule would effectively read Article X, Section 2 out of the Constitution.

Plaintiffs argue that Regulation 862 effectively imposes a permit requirement, since it conditions their use of water on compliance with standards developed by a WDMP. The argument proves too much, since its acceptance would preclude any regulation of water use by riparian users and pre-1914 appropriators. Preventing these users from the unreasonable use of water necessarily requires the imposition of limits on that use by the Board. Limited and particularized prohibitions designed to prevent unreasonable use are different from, and by no means legally equivalent to, the comprehensive regulation embodied in a water use permit, which, as an allocation of “excess water,” typically limits the user’s rights without regard to the reasonableness of use. (See City of Pasadena v. City of Alhambra (1949) 33 Cal.2d 908 , 925-926 [ 207 P.2d 17 ].)

The Lights contend the “vested rights” doctrine prevents the Board from “redefining” an existing beneficial use as unreasonable. The position has been rejected repeatedly. It is now recognized that, since enactment of Article X, Section 2, “there can no longer be any property right in the unreasonable use of water.” (In re Waters of Long Valley Creek Stream System, supra, 25 Cal.3d at p. 354.) What constitutes an unreasonable use of water changes with circumstances, including the passage of time. (Joslin, supra, 67 Cal.2d at p. 140; Tulare Dist. v. Lindsay-Strathmore Dist., supra, 3 Cal.2d at p. 567 [“What is a beneficial use at one time may, because of changed conditions, become a waste of water at a later time.”].) Thus, the extent of a particular user’s vested right to use water similarly may change. Riparian users’ vested water rights extend only to reasonable beneficial water use, which is determined at the time of use.^[12]

3. Violation of the Rule of Priority

The Lights additionally argue that, whatever the scope of the Board’s regulatory authority, it does not have the power “to adopt a definition that prohibits a ‘beneficial use,’ even though the amount of water being used for that beneficial use is no more than minimally required, in order to protect another ‘beneficial use’ to which it ascribes higher priority.” Essentially on this basis, the parties characterize the Board’s regulation as a violation of the rule of priority.

In analyzing this contention, we start with the premise that the supply of water in California is variable and at times insufficient to supply all possible beneficial uses. As the circumstances of this appeal demonstrate, this may be true on a temporary and localized basis, as well as on a more global one. When the supply of water in a particular stream system is insufficient to satisfy all beneficial uses, water rights users must curtail their use. As discussed above, , the rule of priority dictates that riparian users are satisfied first, but when the supply runs sufficiently short, even riparian users must curtail their beneficial use proportionately. (United States, supra, 182 Cal.App.3d at p. 104.)

So long as the only water uses involved are those governed by common law and statutory water rights, the Lights’ contention might have force. When

While it is possible, as the Sacramento plaintiffs argue, that the decentralized system of WDMP’s creates a risk of priority rule violations, such concerns are premature until WDMP’s have been put into effect. This is a facial challenge to Regulation 862, and we hold only that there is no basis for finding Regulation 862, on its face, violates the rule of priority. A determination of whether specific regulatory measures adopted by the WDMP’s violate the rule of priority, and whether any such violation is justified by the Board’s responsibilities under Article X, Section 2, must await implementation of the regulation.^[13]

C. Delegation of Regulatory Authority to WDMP Governing Bodies

The trial court concluded Regulation 862 improperly delegated the regulatory authority of the Board to WDMP’s, reasoning the requirement of the section that the governing body be “capable of ensuring that the requirements of the program are met” (Reg. 862, subd. (b)) means enforcement of the WDMP’s has been delegated to the governing boards. The court also concluded the section constituted an improper delegation of legislative authority because “[declaring the use of water for frost protection an unreasonable use of water is a fundamental shift in water policy in this state.” We review the constitutional issue of unlawful delegation de novo. (People ex rel. Lockyer v. Sun Pacific Farming Co. (2000) 77 Cal.App.4th 619 , 632 [ 92 Cal.Rptr.2d 115 ] (Sun Pacific).)

There is a tension when private industry shares responsibility for the governmental regulation of its commercial activities. On the one hand, members of the industry are well positioned to understand the regulatory needs and the impact of regulation on their business activities. In this respect, they are ideal partners in the formulation of appropriate regulations. Perhaps for this reason, it has never been held that the mere involvement of regulated private parties in the making of administrative regulations constitutes an improper delegation of governmental authority. On the other hand, by involving members of the regulated industry the agency runs the risks associated with the fox guarding the'henhouse. As a result, there is “a tight line between lawful and unlawful delegation of regulatory authority.” (International Assn. of Plumbing etc. Officials v. California Building Stds. Com. (1997) 55 Cal.App.4th 245 , 253 [ 64 Cal.Rptr.2d 129 ] (Plumbing etc.

Similarly, in formulating Regulation 862, the Board clearly set out the fundamental purposes of the WDMP’s: to develop and implement methods for monitoring the level of the affected watercourses, determining when that level poses a threat to young salmon, and responding with “corrective actions” to reduce a threat once detected. (Reg. 862, subds. (b), (c)(2)-(4).) It then established detailed standards for the manner in which the WDMP governing bodies are to monitor stream levels and the type of corrective measures that can be instituted to prevent sudden decreases in water level. (Ibid.) Finally, the Board placed itself between the governing bodies and the regulated growers. No program developed by a governing body will become effective—will acquire the force of law—until it has been approved by the Board, and that approval must be sought’ annually. Nothing more was required to prevent an unlawful delegation of authority.^[14]

Unlike the trial court, we do not construe Regulation 862 as delegating enforcement authority to the governing bodies. Read in context, the requirement a governing body be “capable of ensuring that the requirements of the program are met” (Reg. 862, subd. (b)) means only that the governing body must have the organization and financial resources sufficient to develop a program, monitor its implementation, and comply with the reporting requirements—in other words, be capable of administering a WDMP. The statute is clear that the failure to comply with a WDMP, once it has been approved, “shall be subject to enforcement by the board,” not the WDMP. (Reg. 862, subd. (e).) The enforcement obligation of the WDMP’s governing body is limited to reporting an uncooperative diverter to the Board. (Reg. 862, subd. (c)(5)(E).) While it is true, as the Sacramento plaintiffs argue, that the governing bodies will decide which growers must take corrective actions at any given time, those decisions must be made in accordance with the WDMP, which in turn must be approved by the Board. The role of the governing body is therefore the administration of a Board-approved policy.^[15]

The trial court’s conclusion that the issue of balancing water use for frost protection against water needs for the protection of wildlife is novel and “fundamental” was erroneous, both conceptually and factually. The Board first declared the use of water for frost protection to be unreasonable at least as early as Forni, decided in 1976. Moreover, the truly fundamental issue was decided by the Legislature over a half-century ago when it enacted section 1243 and amended section 1257. The former declares, “[t]he use of water for recreation and preservation and enhancement of fish and wildlife resources is a beneficial use of water” (§ 1243; Stats. 1959, ch. 2048, § 1, p. 4742), while the latter similarly characterizes “preservation and enhancement of fish and wildlife” as a beneficial use (§ 1257; Stats. 1959, ch. 2048, § 2, p. 4742). These sections represent a legislative declaration that the welfare of wildlife is a beneficial use on a par with the type of commercial use that has traditionally been recognized as beneficial. Because, as discussed above, the responsibility of the Board is to regulate the use of water for beneficial purposes, balancing the use of water for frost protection against its use for salmon habitat is simply an application of this fundamental policy decision.^[16]

The Lights contend section 1243 actually expresses a legislative preference for “riparian rights over fish,” based on the concluding sentence of the statute. Although section 1243 instructs the Board to “take into account, whenever it is in the public interest, the amounts of water required for recreation and the preservation and enhancement of fish and wildlife resources” when “determining the amount of water available for appropriation for other beneficial uses,” it ends with the statement, “This section shall not be construed to affect riparian rights.”^[17] In understanding the Legislature’s intent, it is important to recognize the context of section 1243, which is codified in the part of the Water Code dealing with the Board’s authority to issue permits and in an article defining beneficial uses, which begins with the declaration that such uses are a prerequisite for the granting of such a permit. (§ 1240.) Given this context, we interpret the final sentence in section 1243 to

constitute a reaffirmation of the freedom of riparian users from the permitting authority of the Board, rather than a general declaration that the rights of riparian users are paramount to the preservation of water as wildlife habitat.^[18]

The Lights also argue that allowing the WDMP’s to develop their own regulations constitutes an unlawful delegation of the Board’s responsibilities under Schecter v. County of Los Angeles (1968) 258 Cal.App.2d 391 [ 65 Cal.Rptr. 739 ] (Schecter). Schecter involved a dispute between the county’s civil service commission and its board of supervisors over job classifications in the sheriff’s department. Pursuant to a commission mle requiring its chief staff member to develop job classifications, subject to the approval of the commission, the chief recommended to the commission the consolidation of certain sheriff’s department job classifications. The commission rejected the chief’s recommendation, instead adopting its own, different classifications. When the commission’s order was sent to the board of supervisors for adoption, the board refused, in effect arguing the commission’s rule permitted it only to accept or reject the chief’s recommendation, rather than to develop classifications on its own initiative. (Id. at pp. 393-396.) The court rejected the board’s position, finding the board’s interpretation of the regulation to constitute an improper delegation of the commission’s authority to its staff member. While the commission could rely on employees to “ ‘investigate and report the facts and their recommendation’ ” and to draft orders in the first instance, the court held, the members of the commission were required to exercise their own discretion in approving a final order. (Id. at pp. 396-397.) Accordingly, the court affirmed the trial court’s order requiring the board to adopt the commission’s classifications.

As is evident from this description, Schecter does not suggest that an unlawful delegation occurred here. In the same way that the civil service commission could use its employees to investigate and draft a proposed classification order, the Board can rely on WDMP’s to organize and draft programs. So long as the Board exercises its independent discretion in evaluating those programs, no unlawful delegation has occurred. The requirement of Regulation 862 that the Board approve any program implicitly requires just such an exercise of independent discretion.^[19]

to the impact of frost protection diversion. The Lights’ observations about the precise mechanism of stranding highlight the uncertainty about the type of corrective actions necessary and when they should be employed, but they do not suggest the Board’s conclusions about the need for some type of regulation are unsupported. Given the evidence discussed above, the Board’s inference associating salmonid mortality with the dramatic arid sudden declines observed during periods of low temperature is a reasonable one, as is the inference connecting those declines with diversion for the purpose of frost protection. Our standard of review requires us to draw all reasonable inferences in the Board’s favor. (Associated Builders & Contractors, Inc. v. San Francisco Airports Com., supra, 21 Cal.4th at p. 374.) While it may be uncertain from the record precisely what type of regulation of frost protection diversion is necessary to protect salmonids, the need for some type of regulation is supported by substantial evidence.^[20]

The Lights contend the Board’s evidence was “concocted,” citing an attorney letter submitted to the Board on behalf of a winery. The letter provides no evidence, or even argument, to refute the genuine nature of the strandings found by the Fisheries Service. Instead, it argues (1) voluntary efforts by growers combined with better coordination of water releases by the SCWA make future similar strandings less likely; (2) the combination of low flow and frost threat that led to the 2008 incident was relatively rare, having occurred in only five of the last 19 years; (3) and the actual cause of the strandings was the failure of the SCWA in April 2008 to meet its “instream flow requirements.”

None of these arguments demonstrate the finding of necessity for the Board’s regulation was not supported by substantial evidence. As the trial court recognized, it was within the Board’s discretion to disregard the effects of voluntary efforts to mitigate the problem, since these efforts could be reversed or abandoned in the absence of compulsory regulation.^[21] In any event, the evidence that voluntary efforts had mitigated the problem in the

areas immediately surrounding the documented strandings, cited in the letter, did not support a finding of successful mitigation elsewhere in the stream system. As to the release of more water by the SCWA, the Board was entitled to rely on the SCWA’s own conclusion that additional releases of water alone could not cure the problem, both because of the difficulty of accurately predicting the need for such releases and because the problem is one of sudden drops caused by uncoordinated diversion, rather than a more general lack of sufficient water in the system. Finally, as to the rarity of the causative conditions, this will presumably be taken into account in the WDMP’s. Given the potential impact on endangered and threatened salmon populations by these incidents, their rarity would be an argument for regulation responsive to environmental conditions, as Regulation 862 requires, not for an absence of regulation altogether.

E. CEQA^[22]

T

he order granting a preliminary .injunction and the judgment granting a writ of mandate are reversed, and the preliminary injunction is dissolved.

Dondero, J., and Banke, J., concurred.

Petitions for a rehearing were denied July 11, 2014, and the opinion was modified to read as printed above. The petitions of all respondents for review by the Supreme Court were denied October 1, 2014, S220256. Baxter, J., was of the opinion that the petition should be granted.