OPINION
DIETZEN, Justice.
The Minnesota Pollution Control Agency (MPCA or agency) reissued a National Pollutant Discharge Elimination System/State Disposal System (NPDES) permit to Alexandria Lake Area Sanitary District (ALASD) that allowed ALASD to operate and expand its wastewater treatment facility. By writ of certiorari, the Minnesota Center for Environmental Advocacy (MCEA) challenged the MPCA’s decision, arguing that the effluent discharge authorized by the permit would increase the concentration of phosphorus in a lake that has been identified as impaired under the Clean Water Act. The court of appeals reversed the MPCA’s decision to reissue the permit and remanded for further proceedings. In re Alexandria Lake Area Sanitary Disk NPDES/SDS Permit No. MN0040788 (ALASD), No. A06-1371, 2007 WL 2421527 (Minn. App. Aug.28, 2007). Both the MPCA and ALASD filed petitions for review, which we granted.
The issues in this appeal are whether: (1) the MPCA has flexibility under 40 [306]*306C.F.R. 122.44(d)(l)(vi)(A) (2008)1 to establish effluent limits for phosphorus that comply with state narrative water quality standards while a total-maximum-daily-load (TMDL) study is being completed; and (2) whether the permit condition that requires the facility to comply with the future TMDL implementation plan constitutes a “schedule of compliance” under the Clean Water Act and state law. We conclude that the regulation in question, 40 C.F.R. 122.44(d)(l)(vi)(A), is ambiguous when applied to an existing wastewater treatment facility that discharges phosphorus into an impaired waterbody, and that the agency’s interpretation of the regulation is reasonable. Specifically, we conclude that the agency had the authority under the federal regulation to reissue the permit, provided that the permit established effluent limits for phosphorus that comply with applicable state water quality standards and required compliance with the TMDL study and implementation plan. Further, the permit condition that required the facility to comply with the TMDL implementation plan is enforceable under the Clean Water Act and state law. Therefore, we reverse the decision of the court of appeals.
ALASD operates a wastewater treatment facility that discharges treated effluent containing phosphorus into Lake Winona, a shallow lake located at the Alexandria chain of lakes, which consists of Lakes Agnes, Henry, and Winona. The facility has served the City of Alexandria and surrounding townships since 1977.
In 2002, the MPCA classified Lake Wi-nona as impaired under the Clean Water Act (CWA) due to violation of the agency’s water quality standard for nutrients (excess algae), which is related to excess phosphorus levels. Excess phosphorus levels are associated with nuisance algae blooms, reduced transparency, and lower oxygen content in lakes. According to the MPCA, the ALASD facility contributes 70 to 80 percent of the phosphorus entering Lake Winona each year.
As a result of Lake Winona’s impaired status, the MPCA commenced a TMDL study in early 2006. A TMDL study is a scientific study that calculates the maximum amount of a pollutant that may be introduced into a surface water and still ensure that applicable water quality standards for that water are restored and maintained.2 Minn.Stat. § 114D.15, subd. 10 (2008). After completing a TMDL study, the agency prepares and adopts a TMDL implementation plan that details restoration activities needed to meet the approved TMDL’s pollutant load allocations identified by the TMDL study. Id., subd. 11 (2008). In short, the TMDL implementation plan for Lake Winona will quantify the reductions in phosphorus needed to restore the lake to its designated uses of recreation and preservation of aquatic life. See Minn. R. 7050.0222 (2007). The TMDL process typically requires three to four years to complete. Minnesota Pollution Control Agency, TMDLS Underway, http://www.pca.state. mn.us/water/tmdI/tmdl-development.html (last visited March 6, 2009). The TMDL study for Lake Winona should be completed in 2009.
ALASD applied to the MPCA in June 2005 to reissue its five-year NPDES permit and to expand the existing facility to [307]*307meet the needs of a growing population. ALASD proposed an expanded facility with a flow rate that increased from 3.75 to 4.7 million gallons per day (mgd) and capital improvements, including a new filtration system, which would limit the phosphorus concentration in the discharge to 0.30 milligrams per liter (mg/L). ALASD suggested that the new facility would consistently reduce the phosphorus discharge into the lake by using the best technology available for this type of wastewater treatment facility. The MPCA placed a draft permit on public notice in January 2006.
During the public comment period, the MPCA received several comments expressing concern that the expanded facility would discharge additional phosphorus into Lake Winona and would further pollute an already nutrient-impaired lake. The MCEA commented that the draft permit did not comply with the MPCA’s “phosphorus rule,” Minn. R. 7050.0211, subp. la (2007), or with 40 C.F.R. § 122.44(d)(1) (2008), an EPA regulation that requires all NPDES permits to contain effluent limits that will achieve applicable water quality standards.
Based on these comments, MPCA staff proposed amending the draft permit to set more stringent phosphorus limits. Staff applied the agency’s “phosphorus rule,” which requires that nutrients detrimental to the designated use of a waterbody be removed to the “fullest practicable extent” and at least 1 mg/L. Minn. R. 7050.0211, subp. la. As a result, staff proposed that the permit be amended to reduce the permissible phosphorus discharge from 0.80 mg/L to 0.30 mg/L and the daily mass load limit for phosphorus be reduced from 11.3 kilograms per day (kg/d) to 5.4 kg/d. According to MPCA staff, the 0.30 mg/L limit would achieve phosphorus removal to the fullest practicable extent for the expanded facility, and constitutes the most stringent limit imposed in Minnesota.3 Because of uncertainties associated with construction of the expanded facility, the staff proposed interim phosphorus limits of 0.8 mg/L during construction. The facility would be subject to an intervention limit of 0.47 mg/L. The permit required that ALASD report any discharge exceedance over 0.47 mg/L, together with a description of corrective actions taken, and a plan to avoid the exceedance in the future.
MPCA staff conducted scientific modeling to measure the potential effects of the expanded ALASD facility on Lakes Winona and Agnes. Staff used the “BATHTUB” model to predict the highest possible change in levels of phosphorus, chlorophyll-a, and water clarity that might occur under a worst-case scenario.4 Assuming an effluent concentration of 0.3 mg/L,5 the modeling predicted a small increase in phosphorus discharged by the ALASD facility but no measurable change in nutrient conditions in Lake Wi-nona, even if the expanded facility operated up to its maximum proposed expanded effluent flow.
Additionally, the staffs proposed amendment required the facility to comply with the results of the TMDL study and implementation plan to be completed in [308]*3082009. The staffs amended permit would require:
Once the Lake Winona TMDL is approved, the Permittee shall comply with permit conditions which are determined by the MPCA to be consistent with the Permittee’s waste load allocation for phosphorus. In the event that these permit conditions are determined prior to expiration of this permit, these conditions shall be the subject of a major modification of this permit.
The MPCA notified the EPA of the proposed amendments to the draft permit. The EPA did not object to the proposed interim and final effluent limits for phosphorus at the ALASD facility.
On June 27, 2006, the MPCA board incorporated staff recommendations into its findings of fact, conclusions of law, and order granting the five-year NPDES permit. The MPCA found, among other things, that compliance with the permit would achieve phosphorus removal to the fullest practicable extent in compliance with its regulations, that MPCA modeling predicted that the increased discharge would have no effect on the nutrient conditions of the lake, and that the limits in the permit fully complied with applicable state and federal laws that protect the designated uses of the waters from the effects of excess algae and eutrophication. The final permit was amended to set forth a “schedule of compliance,” within the meaning of the CWA and Minn.Stat. § 115.01, subd. 16 (2008), and required the ALASD facility to meet the phosphorus discharge limits in the permit to the “fullest practicable extent” and “to comply with permit conditions which are determined by the MPCA to be consistent with the [facility’s] waste load allocation for phosphorus once the Lake Winona nutrient TMDL is approved by the EPA.”
By writ of certiorari, the MCEA challenged the MPCA’s decision to reissue the permit. The court of appeals reversed, concluding that the permit violated the applicable federal regulation, 40 C.F.R. § 122.44(d)(1). ALASD, 2007 WL 2421527, at *1. According to the court of appeals, the permit violates federal law by setting effluent limits for the facility that do not comply with and protect water quality standards and which delay development of more stringent effluent limitations until after the TMDL process is completed. Id. at ⅞6-7. We granted the MPCA’s and ALASD’s petitions for review.6
I.
The resolution of this case turns on the meaning of 40 C.F.R. § 122.44(d)(1), which provides that if a proposed discharge to a waterbody will cause or has the reasonable potential to cause or contribute to the violation of water quality standards, the agency must establish an effluent limit for the pollutant that “will attain and maintain applicable narrative water quality criteria.” The parties dispute whether the regulation is ambiguous when applied to an existing facility that discharges phosphorus into a lake that is already impaired, and for which a TMDL study is underway that will develop an overall strategy to restore the lake and comply with water quality standards.
A. Regulatory Framework
The CWA was enacted “to restore and maintain the chemical, physical, and biological integrity of the Nation’s waters.” 33 U.S.C. § 1251 (2006). To effectuate this policy, the CWA authorizes states to implement the NPDES permit program [309]*309under 33 U.S.C § 1342(a)-(d) (2006). The MPCA implements the NPDES program in Minnesota by issuing permits that comply with or are more stringent than federal permit conditions. Minn.Stat. § 115.03 (2008); 40 C.F.R. § 123.25(a) (2008).
Section 301 of the CWA mandates that every permit contain: (1) “effluent limitations” that reflect the practicable pollution reduction a state can achieve; and (2) any more stringent limitations required for a body of water to meet “water quality standards.” Am. Paper Inst., Inc. v. U.S. EPA, 996 F.2d 346, 349 (D.C.Cir.1993). “Effluent limitations”7 are promulgated by the EPA and restrict the quantities, rates, and concentrations of specific substances discharged from point sources. See 33 U.S.C. §§ 1311, 1314 (2006). “Water quality standards” are promulgated by the states and generally establish the desired condition of a waterway. See 33 U.S.C. § 1313 (2006). Thus, the CWA requires that all NPDES permits for point sources incorporate limitations necessary to satisfy the state’s promulgated water quality standards.
There are two kinds of water quality standards — numeric and narrative. Am. Paper, 996 F.2d at 349; 40 C.F.R. § 122.44(d)(1). If a state’s water quality standard is numeric, the NPDES permit “merely adopts a limitation on a point source’s effluent discharge necessary to keep the concentration of a pollutant in a waterway at or below the numeric benchmark.” Am. Paper, 996 F.2d at 350. This case concerns a narrative standard. A narrative standard is a statement of unacceptable conditions in or upon the waters. See Minn. R. 7050.0150, subp. 1 (2005) (stating that narrative water quality standards “prescribe the qualities or properties of surface waters that are necessary for the protection of designated public uses and benefits”). The applicable narrative standard in this case specifies “no material increase in undesirable slime growths or aquatic plants, including algae.” Minn. R. 7050.0150, subp. 3 (2007).8 A narrative standard is more difficult to implement in a permit than a numeric standard. Am. Paper, 996 F.2d at 350.
To address the difficulties of implementing a narrative standard, the EPA promulgated 40 C.F.R. § 122.44(d)(l)(vi). See Am. Paper, 996 F.2d at 350. Permits for new wastewater treatment facilities are governed by 40 C.F.R. § 122.44© (2008), and permits for existing and expanding facilities are governed by 40 C.F.R. § 122.44(d) (2008). Both of the applicable federal regulations require the MPCA, as a threshold matter, to determine if a new [310]*310or expanding facility will cause or contribute to the impairment of a waterbody. If the MPCA answers this question in the affirmative, the regulations either ban permitting altogether until the TMDL process has been completed (for new facilities) or require more stringent effluent limits than would ordinarily be required under the CWA (for existing facilities).
B. The Dispute
Section 122.44 (2008) sets forth certain conditions that apply to every NPDES permit. When a discharge into a water-body will cause or contribute to a violation of state water quality standards, the agency must establish more stringent requirements than ordinarily required by the CWA. 40 C.F.R. § 122.44(d)(1). Because Lake Winona has been identified as impaired, as it violates the narrative standard for nutrients (excess algae), the MPCA does not dispute that the phosphorus discharge from the ALASD facility will cause or contribute to the violation of applicable water quality standards. As a result, the MPCA is required to establish more stringent effluent limits in the NPDES permit for the ALASD facility than would ordinarily be required under the CWA.9
Section 122.44(d)(l)(vi) provides three options for the agency to use in establishing effluent limits when a state “has not established a water quality criterion” for the pollutant. Of the three options, the MPCA selected Option A to establish its effluent limits for phosphorus. Option A requires the agency to establish effluent limits that “will attain and maintain applicable narrative water quality standards and fully protect the designated use” of the waterbody. See id. The regulation requires the permitting authority to:
Establish effluent limits using a calculated numeric water quality criterion for the pollutant which the permitting authority demonstrates will attain and maintain applicable narrative water quality criteria and will fully protect the designated use. Such a criterion may be derived using a proposed State criterion, or an explicit State policy or regulation interpreting its narrative water quality criterion, supplemented with other relevant information which may include: EPA’s Water Quality Standards Handbook, October 1983, risk assessment data, exposure data, information about the pollutant from the Food and Drug Administration, and current EPA criteria documents[.]
40 C.F.R. § 122.44(d)(l)(vi)(A).
The crux of the dispute is whether Option A, as applied to the ALASD application, is ambiguous. “The meaning of words in a regulation is a question of law we review de novo.” In re Rate Appeal of Benedictine Health Ctr., 728 N.W.2d 497, 503 (Minn.2007). If the language of the regulation is clear and free from ambiguity, we must give effect to the plain meaning and give no deference to the agency’s interpretation. Id. “[A] regulation is ambiguous if it is unclear or reasonably susceptible to more than one reasonable interpretation.” In re Cities of Annandale & Maple Lake NPDES/SDS Permit Issuance for the Discharge of Treated Wastewater (Annandale), 731 N.W.2d 502, 517 (Minn.2007). Further, “our determination of whether words or phrases are ambiguous does not depend on a reading of those words or phrases in isolation, but relies on the meaning assigned to the words or phrases in accordance with the apparent purpose of the [311]*311regulation as a whole.” Id. (for the proposition that statutory language should not be viewed in isolation from its context).
The MCEA asserts that Option A “is straightforward and clear in its meaning.” According to the MCEA, the regulation unambiguously requires the agency to establish an effluent limit using a “calculated numeric water quality criterion” that will restore the lake to applicable water quality standards and fully protect its designated uses of recreation and preservation of aquatic life. Essentially, the MCEA argues that an NPDES permit may not be issued unless it reduces the phosphorus concentration in the lake to a level that satisfies water quality standards, restores the lake to its designated uses, and removes the classification of the lake as impaired.
The MPCA argues that Option A is ambiguous in the regulatory context here— the reissuance of an NPDES permit for an existing facility that discharges phosphorus into an already impaired lake for which a TMDL study is underway but has not yet been completed. The agency argues that the operative language, “will attain and maintain” and “will fully protect,” is expressed in the future tense to describe a future event, but the regulation does not express how quickly phosphorus concentrations in the lake must be reduced to restore the waterbody to water quality standards and its designated uses. According to the MPCA, because the regulation’s requirements are triggered when the facility will cause or contribute to the violation of applicable water quality standards for the lake, it follows that the regulation does not categorically ban the issuance of a permit, but rather allows a permit to be issued so long as one of the three options is met. The MPCA contends that the regulation was intended to give the agency flexibility to develop not only a TMDL study and implementation plan for the watershed, which incorporates the results of the TMDL study, but also to develop interim limits in the ALASD permit that are consistent with the overall plan to restore the lake to water quality standards within a reasonable period of time.
Based on our reading of the regulation, we conclude that Option A unambiguously requires the agency to establish effluent limits for phosphorus that “will attain and maintain applicable narrative water quality criteria” and “will fully protect the designated use” of the waterbody. 40 C.F.R. § 122.44(d)(l)(vi)(A). But we also conclude that the regulation is ambiguous when applied to an existing facility that discharges phosphorus into a lake that is already impaired, and for which a TMDL study is underway that will develop an overall strategy to restore the lake and comply with water quality standards.
Significantly, the regulation does not address how quickly the phosphorus concentration must be reduced and the lake restored to satisfy the regulation’s requirements. When a statute or regulation is silent on a precise issue, that silence may be evidence of ambiguity. See Burkstrand v. Burkstrand, 632 N.W.2d 206, 210 (Minn.2001) (concluding that statute was ambiguous given its silence on the precise issue of whether a district court was divested of subject-matter jurisdiction for failure to hold a hearing within a prescribed timeframe and competing interpretations). Accord Chevron U.S.A., Inc. v. Natural Res. Def. Council, Inc., 467 U.S. 837, 842-43, 104 S.Ct. 2778, 81 L.Ed.2d 694 (1984) (noting that “if the statute is silent or ambiguous with respect to the specific issue, the question for the court is whether the agency’s answer is based on a permissible construction of the statute”).
In American Paper, the D.C. Circuit Court of Appeals analyzed section 122.44(d)(l)(vi) and determined that an agency has the flexibility to develop ef[312]*312fluent limits in a permit that will attain water quality standards. 996 F.2d at 351. The court stated:
[A] permit writer [or agency] will inevitably have some discretion in applying the [narrative] criteria to a particular case. The general language of narrative criteria can only take the permit writer so far in her task.... [This] is an acknowledgment that the writer will have to engage in some kind of interpretation to determine what chemical-specific numeric criteria — and thus what effluent limitations — are most consistent with the state’s intent as evinced in its generic standard.
Id. The D.C. Circuit concluded that “permits must incorporate limitations necessary to meet standards that rely on nárra-tive criteria to protect a designated use.” Id. at 350. But the regulation does not specifically address how the permitting agency is to accomplish this task when a point source discharges to an impaired lake for which no TMDL study has- been completed.10
Based on the foregoing reasons, we conclude that section 122.44(d)(l)(vi)(A) as applied to the ALASD application is susceptible to differing interpretations in its regulatory context and, therefore, is ambiguous. We turn next to the agency’s interpretation of the regulation.
C. MPCA’s Interpretation of the Regulation
When “the language of a regulation is unclear or susceptible to different [313]*313interpretations,” we consider several factors to determine the level of judicial deference afforded to the agency’s interpretation. Annandale, 731 N.W.2d at 513-16. First, we consider the nature of the regulation at issue. See id. at 513. Clearly, the MPCA is responsible for administering and enforcing the regulation and, therefore, it is the agency’s “own regulation.” See id. (concluding that a federal CWA regulation administered and enforced by the MPCA is the MPCA’s own regulation). Second, we consider the agency’s expertise and judgment; specifically, we examine whether the subject matter of the regulation is within the agency’s technical training, education, and experience. Id. at 514; see also Minn. Ctr. for Envtl. Advocacy v. Minn. Pollution Control Agency, 644 N.W.2d 457, 463 (Minn.2002). It is undisputed that establishing effluent limits under Option A to protect and restore the waters of this state involves a subject matter uniquely within the agency’s expertise and special knowledge. Third, we will defer to the agency’s expertise and special knowledge when the agency’s interpretation of an unclear regulation is reasonable. Annandale, 731 N.W.2d at 515. Thus, we consider whether the MPCA’s interpretation of the regulation is “reasonable under the circumstances of this case.” Id. at 522 (emphasis in original).
The MPCA argues that Option A does not categorically ban reissuing an NPDES permit until the lake is restored, but rather gives the agency flexibility to restore the lake to water quality standards and its designated uses within a reasonable period of time. Specifically, the agency argues that the regulation gives it flexibility to establish interim effluent limits that will apply until the TMDL process is completed. See National Pollutant Discharge Elimination System; Surface Water Toxics Control Program, 54 Fed.Reg. 23868, 23876 (June 2, 1989) (“[Ojption A gives the states maximum flexibility in developing water quality-based effluent limits for pollutants for which the state has not adopted a water quality criterion.”). We conclude that the agency properly applied its technical judgment and expertise in concluding that Option A does not categorically ban reissuing an NPDES permit under these circumstances.
In Arkansas v. Oklahoma, 503 U.S. 91, 112 S.Ct. 1046, 117 L.Ed.2d 239 (1992), the United States Supreme Court addressed an analogous situation involving a water-body that was already impaired. The Court held that the CWA authorized the EPA to issue an NPDES permit that allows a new Arkansas sewage treatment plant to discharge effluent into the Illinois River, even though the river was already in violation of existing water quality standards. Id. at 107-08, 112 S.Ct. 1046. In doing so, the Court concluded that the CWA vests the EPA and the States with “broad authority to develop long-range, area-wide programs to alleviate and eliminate existing pollution.”. Id. at 108, 112 S.Ct. 1046. The Court reasoned:
[I]t might be wise to prohibit any discharge into the Illinois River, even if that discharge would have no adverse impact on water quality. But it was surely not arbitrary for the EPA to conclude — given the benefits to the river from the increased flow of relatively clean water and the benefits achieved in Arkansas by allowing the new plant to operate as designed — that allowing the discharge would be even wiser. It is not our role, or that of the Court of Appeals, to decide which policy choice is the better one, for it is clear that Congress has entrusted such decisions to the Environmental Protection Agency.
Id. at 114,112 S.Ct. 1046.
According to the MPCA, Option A gives the agency considerable discretion in de[314]*314riving numeric effluent limits that meet narrative standards, particularly when the federal regulation expressly allows the state agency to derive the effluent limits using state policies and regulations that interpret the narrative water quality standard. See 40 C.F.R. § 122.44(d)(l)(vi)(A). In this case, the applicable narrative water quality standard provides for “no material increase in undesirable slime growths or aquatic plants, including algae” in Lake Winona. Minn. R. 7050.0150, subp. 3. To derive the effluent limits in the permit, the agency applied an explicit state policy and regulation — the MPCA’s “phosphorus rule,” which requires that “[w]here the discharge of effluent is directly to or affects a lake or reservoir, phosphorus removal to one milligram per liter shall be required.” Minn. R. 7050.0211, subp. la. More important, the rule also requires that “removal of nutrients from all wastes shall be provided to the fullest practicable extent wherever sources of nutrients are considered to be actually or potentially detrimental to preservation or enhancement of the designated water uses.” Id.
In applying the “phosphorus rule,” the MPCA determined that phosphorus removal to the “fullest practicable extent” requires a permit limit of 0.30 mg/L after the facility is fully operational and before the TMDL study is completed. Once the TMDL study is completed in 2009, the agency will have the numeric limits necessary to develop a TMDL implementation plan that will restore the Lake Winona watershed. The MPCA points out that the permit limit of 0.30 mg/L maximum phosphorus concentration discharge is three times more stringent than the existing ALASD permit and is the most stringent limit the agency has ever imposed on a wastewater treatment facility. Further, the permit reduces the daily mass load limit for phosphorus from the 11.3 kilograms allowed in the previous permit to 5.4 kilograms. The modeling study confirms that the effluent limits comply with the applicable narrative water quality standard and protect the lake against any further degradation until the TMDL study is completed. Finally, the final permit requires the ALASD facility to comply with new phosphorus limits established in the TMDL study and implementation plan.
We conclude that the agency reasonably interpreted and applied Option A when it reissued the permit to the ALASD facility. The phosphorus limit in the permit was based on several scientific and policy judgments, including the MPCA’s determination of the “fullest practicable extent” of phosphorus removal for the ALASD facility under the “phosphorus rule” and whether the effluent limits will achieve water quality standards using scientific lake modeling. Given the central importance of TMDLs in restoring impaired waters under the CWA, the MPCA reasonably interpreted the regulation as giving the agency flexibility to establish more stringent phosphorus limits under the MPCA’s “phosphorus rule” during the interim period while the TMDL study is underway and then to establish new limits in the TMDL implementation plan. The interim phosphorus limits in the permit will adequately control phosphorus in the lake until the TMDL study and implementation plan is completed.
The MCEA’s suggestion that the effluent limits in the reissued permit must fully restore Lake Winona within the span of the five-year NPDES permit is neither realistic nor supported by the regulatory scheme.11 Although the MCEA contends [315]*315that the phosphorus limits in the permit are not stringent enough, we defer to the MPCA’s technical knowledge and expertise in calculating the specific numeric water quality criteria under 40 C.F.R. § 122.44(d)(l)(vi)(A). In accordance with this regulation, the effluent limits were derived from explicit state policies and regulations, and the MPCA’s modeling study confirms that the phosphorus entering Lake Winona will have no measurable impact on algal conditions.12 Therefore, we uphold the MPCA’s interpretation and application of the regulation.
We recognize that any additional phosphorus discharge by the ALASD facility into the lake will, ipso facto, delay restoring the lake to water quality standards. But the MPCA needs the results of the TMDL study to determine the proper long-term effluent limits for phosphorus that will ultimately restore the lake. Once the TMDL study is completed in 2009, the MPCA must develop a TMDL implementation plan that will potentially reduce the phosphorus limit in the permit as part of its overall strategy to restore the water-body. The results of the TMDL study and the reasonableness of the TMDL implementation plan are not the subject of this appeal and, therefore, we decline to address them.
Although the dissent concludes there is no ambiguity in the words “will attain and maintain applicable narrative water criteria” and “will fully protect the designated use” in the regulation, the dissent does not explain these words in context — specifically, it does not explain how quickly water quality standards for a severely impaired lake such as Lake Winona must be attained when the TMDL process is already underway. Notably, the dissent does not adopt the MCEA’s position that no permit can be issued unless the phosphorus concentration in the lake will be reduced to a level that will restore the lake to its designated uses. Instead, acknowledging that restoring Lake Winona will be “a long and difficult task,” the dissent simply concludes that the MPCA has “not done enough.”
In doing so, the dissent implicitly substitutes its judgment for that of the MPCA in terms of what is “enough” and how quickly the lake must be restored to satisfy the regulation. The dissent asserts that the MPCA is delaying setting stringent effluent limits until after the TMDL process is completed, but the 0.30 mg/L phosphorus concentration limit in the reissued permit is three times more stringent than the 1.0 mg/L limit in the previous permit, and the reissued permit limits the mass load of [316]*316total phosphorus to 5.4 kg/d, which is half the 11.3 kg/d allowed under the previous permit. The dissent does not specify what further reductions in phosphorus concentration limits or mass load would have been “enough.” The .30 mg/L concentration limit is the most restrictive limit ever imposed by the MPCA and represents the “fullest practicable extent” of phosphorus removal the facility is capable of achieving.
Further, the dissent’s water quality analysis focuses exclusively on a potential increase in phosphorus levels in Lake Wi-nona. The dissent assumes that there will be an increase in phosphorus levels; however, this assumption is based on “the worst-case scenario” projected by the MPCA — the ALASD facility operating at full wet weather flow all year long and always at the maximum concentration limit of .30 mg/L — a situation that an MPCA technical analyst described as not likely. Under more realistic operating conditions, the MPCA asserts that there likely will be a net reduction of phosphorus in Lake Winona. Although the dissent takes “little solace” in the MPCA’s determination that there will not be any dramatic increase in algal levels or decrease in secchi depth, the narrative water quality standard at issue requires that the MPCA consider not only changes in phosphorus levels, but also changes in chlorophyll-a levels and light transparency. See Minn. R. 7050.0150, subp. 3 (specifying “no material increase” in algae). The MPCA found that even with the expanded facility operating at the maximum proposed expanded effluent flow, there will be no change in chlorophyll-a levels or water clarity. Thus, in concluding that the MPCA has not complied with the narrative standard, the dissent essentially has rewritten the narrative standard to consider only phosphorus levels, disregarding the scientific and technical judgment of the agency.
We do share the dissent’s concerns about the consequences of delaying the restoration of impaired waters in Minnesota. Nonetheless, after careful consideration of the multiple factors relevant to our deference analysis, see Amándole, 731 N.W.2d at 516, 525, we conclude that deference to the expertise of the MPCA is warranted under these circumstances.
D. Compliance with ⅛0 C.F.R. § 122.U(d)(l)(vii)
The MCEA also argues, and the court of appeals agreed, that the final permit fails to comply with 40 C.F.R. § 122.44(d)(l)(vii). See ALASD, 2007 WL 2421527, at *7-8. This regulation provides:
When developing water quality-based effluent limits under this paragraph the permitting authority shall ensure that:
(A) The level of water quality to be achieved by limits on point sources established under this paragraph is derived from, and complies with all applicable water quality standards; and
(B) Effluent limits developed to protect a narrative water quality criterion, a numeric water quality criterion, or both, are consistent with the assumptions and requirements of any available wasteload allocation for the discharge prepared by the State and approved by EPA pursuant to 40 CFR 130.7.
40 C.F.R. § 122.44(d)(l)(vii).
The MCEA concedes that a waste load allocation requires completion of a TMDL study for Lake Winona, which has not yet occurred and, therefore, is not “available” under the regulation. But the MCEA argues that absent a TMDL study the agency must adopt water quality-based effluent limits under section 122.44(d)(l)(vii)(B) and not (d)(1)(vi)(A). The MCEA’s argument is premised on its position that subpara-graph (d)(l)(vii) is more specific than sub-[317]*317paragraph (d)(l)(vi) and, therefore, applies. We disagree.
When there is no numeric criterion for the pollutant at issue, paragraph (d)(1) contemplates that the agency will develop effluent limits for the discharge as set forth in subparagraph (vi), not (vii). Therefore, we conclude that subparagraph (vi) is more specific and governs. See National Pollutant Discharge Elimination System; Surface Water Toxics Control Program, 54 Fed.Reg. at 23878 (“[F]or the purposes of complying with paragraph (vii), where a wasteload allocation is unavailable, effluent limits derived under paragraph (vi) must comply with narrative water quality criteria and other applicable water quality standards.”).
We conclude that the meaning of 40 C.F.R. § 122.44(d)(l)(vi)(A) is ambiguous when applied to an existing facility that discharges phosphorus into a lake that is already impaired, and for which a TMDL study is underway that will develop an overall strategy to restore the lake and comply with water quality standards. The MPCA’s interpretation of 40 C.F.R. § 122.44(d)(l)(vi)(A) (2008) that it had the authority to reissue an NPDES permit to ALASD was reasonable. Specifically, the agency had the authority under the federal regulation to reissue an NPDES permit to an existing wastewater treatment facility that discharged phosphorus into a water-body that was already impaired, provided that the reissued permit established effluent limits for phosphorus that comply with applicable state water quality standards and required compliance with the results of a TMDL study and implementation plan currently being conducted and developed by the agency.
II.
We next consider whether the reissued permit’s requirement that ALASD comply with the TMDL implementation plan constitutes a “schedule of compliance” under the NPDES program.
An NPDES “permit may, when appropriate, specify a schedule of compliance leading to compliance with CWA and regulations.” 40 C.F.R. § 122.47(a) (2008). A “schedule of compliance” means “a schedule of remedial measures including an enforceable sequence of actions or operations leading to compliance with an effluent limitation, other limitation, prohibition, or standard.”13 33 U.S.C. § 1362(17) (2006); see also Minn.Stat. § 115.01, subd. 16; Minn. R. 7000.0100, subp. 11 (2005). Minnesota Statutes § 115.03, subd. 1(e), authorizes the MPCA to implement a “schedule of compliance” “under such conditions as it may prescribe, in order to prevent, control, or abate water pollution.” Under Minn. R. 7001.0150, subps. 2 & 2A (2007), if the MPCA determines that the schedule of compliance is applicable to the circumstances “[e]ach draft and final permit must contain conditions necessary for the permittee to achieve compliance with applicable Minnesota or federal statutes or rules, including ... [a] schedule of compliance that leads to compliance with the appropriate Minnesota or federal statute or rule.”
The MPCA argues that the interim and final period limits in the permit, and the requirement that the facility comply with waste load allocations for phosphorus upon completion of the Lake Winona TMDL study and implementation plan, constitute a “schedule of compliance.” The MPCA [318]*318contends that the effluent limit needed to meet a waste load allocation established by a TMDL study and implementation plan is an enforceable “effluent limitation, other limitation, prohibition, or standard” within the meaning of “schedule of compliance.” The MPCA also argues that a TMDL-based effluent limit is enforceable by the MPCA because it is the final limit within the permit with which the facility must comply.
The MCEA concedes that the interim and final period limits represent a valid schedule of compliance. The MCEA argues that the lack of a date in the permit by which the facility will comply with an undetermined effluent limit calculated based on the TMDL study and implementation plan to achieve water quality standards means there is no enforceable effluent limitation in the permit. Essentially, the MCEA argues that without a date for completion of the TMDL process, the MPCA cannot issue a permit with a “schedule of compliance” that references TMDL-based phosphorus limits yet to be established.
The court of appeals concluded that the MPCA “misconstrue[d] the meaning of a ‘schedule of compliance’ ” because “[tjhere is no enforceable sequence of actions in the reissued permit leading to compliance with water quality-based effluent limits.” ALASD, 2007 WL 2421527, at *7. It appears that the court based this determination on its understanding that the MPCA had not appropriately established “water quality-based effluent limits” under its plain-language reading of 40 C.F.R. § 122.44(d)(l)(vi)(A) and (vii). Id. at *8 (reasoning that a schedule of compliance would have been an appropriate application of the regulation if the MPCA had developed effluent limits that comply with the narrative water quality standard and fully protect the designated use of the lake). Because we do not agree that the effluent limits in the permit are not water-quality based, we disagree with the court of appeals’ rationale.
We see no reason why the progressively more stringent effluent limits in the reissued permit do not constitute an “enforceable sequence of actions or operations leading to compliance with an effluent limitation.” 33 U.S.C. § 1362(17). There is nothing unenforceable about requiring the facility to meet an effluent limit set upon completion of the TMDL process. Nothing in the CWA’s definition of “schedule of compliance” requires that the sequence of events be tied to specific dates. Moreover, Minn. R. 7001.0150, subp. 2A, indicates that a “schedule of compliance” need only require compliance within “the shortest reasonable period of time.”
Therefore we hold that an NPDES permit condition that required a wastewater treatment facility to comply with effluent limits set by a TMDL study and implementation plan upon their future completion was enforceable within the meaning of “schedule of compliance” under 33 U.S.C. § 1362(17) and Minn.Stat. § 115.01, subd. 16.
Reversed.
MAGNUSON, C.J., not having been a member of this court at the time of the argument and submission, took no part in the consideration or decision of this case.